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Greenville Utilities Commission,
Town of Farmville, Town of Winterville,
and Greene County
Proposed Interbasin Transfer
HEARING OFFICERS’ REPORT
Environmental Management Commission
North Carolina
Department of Environment and Natural Resources
Division of Water Resources
November 2010
A1
Environmental Management Commission
North Carolina Division of Water
Resources
‐ i ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville,
and Greene County
Proposed Interbasin Transfer
Hearing Officers’ Report‐ November 2010
HEARING OFFICERS’ RECOMMENDATIONS
The Environmental Management Commission held a Public Hearing on Greenville Utilities Commission’s
(GUC) Petition for an Interbasin Transfer Certificate (IBT) on November 5, 2009 at Pitt Community College
in Winterville, North Carolina. The public record for that hearing was scheduled to close on December 4,
2009, however the Hearing Officers agreed to grant a one‐time extension ending January 19, 2010. 37
people were in attendance for the Public Hearing on the IBT Petition. In total, 21 provided comments,
either at the hearing (10 speakers) or during the public comment period.
Having reviewed and considered the comments received during the public review process and the
requirements set forth in the North Carolina General Statutes, the Hearing Officers and the Division of
Water Resources Director recommend that the Environmental Management Commission grant the
Petitioners a 8.3 million gallon per day transfer from the Tar River Basin to the Contentnea Creek Basin
and a 4.0 million gallon per day maximum transfer from the Tar River Basin to the Neuse River Basin with
the following conditions:
1. If the Certificate Holders discontinue their cooperative service agreements with each other, the
Division of Water Resources (“Division”) shall specify the maximum amount of water each of the
joint Certificate Holders may transfer individually. The total of these amounts shall not exceed a
maximum of 8.3 million gallons on any calendar day from the Tar River Basin to the Contentnea
Creek Basin and shall not exceed a maximum of 4.0 million gallons on any calendar day from the
Tar River Basin to the Neuse River Basin. The allocations shall be based on projections of water
use for 2030 compiled by the Division at the time it is notified of the discontinuance of the
cooperative service agreement. The allocations shall take effect within 90 days of the Division
issuing the allocations, or at such other reasonable time as the Division specifies. At that time,
each condition of this Certificate shall apply to each Certificate Holder individually and the
Division may require the Certificate Holders to make individual submissions of plans, reports, etc.
as necessary.
2. This Certificate does not exempt the Certificate Holders or any other entity from compliance with
any other requirements of law, including the Central Coastal Plain Capacity Use Area (“CCPCUA”)
Rules (15A NCAC 02E .0500).
3. If the Commission determines that the record on which this Certificate is based is substantially in
error or if new information becomes available that clearly demonstrates that any Finding of Fact
(including those regarding environmental, hydrologic, or water use impacts) pursuant to G.S. §
143‐215.22I(f) was not or is no longer supported or is materially incomplete, the Commission
may reopen and modify this Certificate to ensure continued compliance with G.S. ch. 143, art. 21,
part 2A.
4. No individual unit of local government may receive surface water regulated under this Certificate
unless the local government maintains, throughout its jurisdiction, requirements that are at least
as stringent as the Division of Water Quality’s Phase 2 post‐construction stormwater controls or
the post‐construction stormwater controls of the Universal Stormwater Management Program
(“USMP”), for all new development that disturbs more than one acre of land, including those
projects that disturb less than one acre of land but are part of a common plan of development or
sale that disturbs more than one acre of land.
5. Persons (including a unit of local government) subject to the CCPCUA Rules (15A NCAC 2E .0500)
are required to reduce the volume and effects of withdrawals from ground waters through the
A2
Environmental Management Commission
North Carolina Division of Water
Resources
‐ ii ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville,
and Greene County
Proposed Interbasin Transfer
Hearing Officers’ Report‐ November 2010
minimum conservation program requirements identified in 15A NCAC 2E .0502(d)(5)(A)‐(C). In
order to assure that conservation measures are used by the applicant to assure efficient use of
water and avoid waste (in accordance with §143‐215.22I(c)(3), no individual unit of local
government or persons subject to the CCPCUA Rules (15A NCAC 2E .0500) may transfer water
under this Certificate without first meeting the minimum conservation program requirements
identified in 15A NCAC 2E .0502(d)(5)(A)‐(C).
6. The Certificate Holders shall implement drought management measures that become more
stringent as drought conditions increase in severity. These measures shall correspond to the
most severe level of drought existing in the Tar River Basin. Prior to each Certificate Holder
receiving any water under this Certificate, the Certificate Holder shall submit a Water Shortage
Response Plan (“Plan”) to the Division, for the Division’s approval. Each Certificate Holder shall
receive approval of the Plan from the Division, and shall have and maintain adequate authority
and resources to implement and enforce the Plan. In order to be approved, the Plan must meet
or exceed the requirements set forth in 15A NCAC 2E .0607 and be no less stringent than the
Plan in Attachment A, which is incorporated herein. Any subsequent modifications to the Plan
will be reviewed and approved by the Division. Adoption of the measures in Attachment A does
not imply compliance with G.S. 143‐355(l) or 15A NCAC 2E .0607.
The Certificate Holders shall not transfer any water to any other unit of local government unless
that unit of local government agrees to be bound by this condition in full.
7. The Certificate Holders shall report annually to the Division. The report shall detail water use
over the calendar year by providing the following information:
Interbasin Transfer Calculation
GUC shall calculate daily and maximum‐day interbasin transfers taking into account GUC’s own
metered water use for each billing cycle, with separate data provided for customers in the Tar
River and Neuse River Basins. The calculation shall also take into account GUC’s monthly average
wastewater treatment plant discharge, and the daily bulk purchases from the Towns of Farmville,
Winterville, and Greene County. GUC shall geocode (via the GUC GIS database) those water
customers located in the Neuse River Basin so that the consumptive use for the GUC customers
can be calculated. The consumptive use for Winterville, Farmville, and Greene County does not
need to be calculated so long as the entire metered water use to these communities is the
transfer to each of the respective Basins.
Ground Water Use
Farmville, Winterville, and Greene County shall submit their daily metered ground water use as
reported to DWR’s Ground Water Section for compliance with any CCPCUA permits. The
documentation shall note the maximum‐day water use by each system.
Banked Water Summary
Farmville, Winterville, and Greene County shall also provide a banked water summary. Each
summary shall include the total volume of banked water available at the beginning and end of
the calendar year, an accounting of any day during the year that banked water was used, and the
total volume of banked water that was used during that day.
A3
Environmental Management Commission
North Carolina Division of Water
Resources
‐ iii ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville,
and Greene County
Proposed Interbasin Transfer
Hearing Officers’ Report‐ November 2010
Compliance With Other Certificate Conditions
The Certificate Holders shall also provide a status report of compliance efforts for any other
conditions required by this Certificate.
All annual reports shall be submitted by March 31st of the following calendar year. Following the
submission of any reports under this Certificate, the Certificate Holders shall promptly provide to
the Division any information requested by the Division that the Division concludes is needed to
complete, correct or clarify the report. If the Certificate Holders believe that the Division’s
request does not conform to the reporting requirements, the parties shall confer promptly to
resolve any differences.
When an annual report indicates that a daily transfer equaled or exceeded eighty (80%) percent
of any transfer amount authorized by this Certificate, the Certificate Holders shall submit to the
Division, by June 1 of the year in which such annual report was required, a detailed plan that
specifies how the Certificate Holders intend to address future foreseeable water needs. So long
as the Certificate Holders are required to have a local water supply plan, then the plan to address
future foreseeable water needs shall be an amendment to the local water supply plan required
by G.S. 143‐355(l).
When an annual report indicates that a daily transfer equaled or exceeded ninety percent (90%)
of any transfer amount authorized by this Certificate, then:
1. The Certificate Holders shall begin implementation of the plan submitted to the Division.
2. GUC shall immediately begin monthly reporting to the Division. Monthly reports shall be
submitted within 45 days of the end of the month.
All reports submitted pursuant to this condition shall be signed by the Director of Public Utilities
or person of similar position who shall affirm that, based on information collected during and
belief formed after reasonable inquiry, the report is true, accurate and complete and that the
Certificate Holder complied with the Certificate continuously throughout the year, except as
specifically indicated in the report.
____________________________________
Stan L. Crowe, Hearing Officer
Environmental Management Commission
____________________________________
Kevin C. Martin, Hearing Officer
Environmental Management Commission
___________________________________
Stephen T. Smith, Chairman
Environmental Management Commission
A4
Environmental Management Commission
North Carolina Division of Water
Resources
‐ iv ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville,
and Greene County
Proposed Interbasin Transfer
Hearing Officers’ Report‐ November 2010
TABLE OF CONTENTS
Hearing Officer’s Recommendations........................................................................................................i
Table of Contents................................................................................................................................... iv
Interbasin Transfer Certificate................................................................................................................ 1
Findings of Fact....................................................................................................................................... 2
(1) The necessity, reasonableness, and beneficial effects of the transfer..................................... 2
(2) Detrimental effects on the source river basin .......................................................................... 4
(2a) The cumulative effect on the source major river basin of any water transfer or
consumptive water use ............................................................................................................ 6
(3) Detrimental effects on the receiving basin............................................................................... 6
(4) Reasonable alternatives to the proposed transfer .................................................................. 8
(5) Use of impounded storage ....................................................................................................... 9
(6) Purposes and water storage allocations in a US Army Corps of Engineers
multipurpose reservoir ............................................................................................................. 9
(7) Any other facts or circumstances necessary to carry out the law ........................................... 9
Decision................................................................................................................................................. 11
Attachment A – Minimum Criteria for Drought Management Plan .................................................... 15
Attachment B ‐ Staff Response to Comments...................................................................................... 19
Appendix 1: Explanation of IBT Management Strategy, ARCADIS
Appendix 2: Memo from DWR Concerning Compliance with CCPCUA program Requirements
Appendix 3: Summary of Water Conservation Requirements per CCPCUA Rules, ARCADIS
Appendix 4: Environmental and Economic Impacts of Water Supply Alternatives, ARCADIS
Appendix 5: Summary of Mitigation for Secondary and Cumulative Impacts
Appendix 6: Explanation of Hydrologic Analysis and Results Interpretation, ARCADIS
Appendix 7: Record of Public Comments received on IBT Petition
Attachment C‐ Notice of public hearings.........................................................................Attachment C 1
i. Appointment of hearing officers
ii. Copy of NC Register publication
iii. Letter to persons identified in G.S. 143‐215.22(i)
iv. Affidavit of Publication for The Standard Laconic
v. Affidavit of Publication for Washington Daily News
vi. Affidavit of Publications for The Daily Reflector
vii. Affidavit of Publication for the News Observer
Attachment D – Regulations.............................................................................................Attachment D1
1. Central Coastal Plain Capacity Use Area Rules 15A NCAC 2E .0500
2. Session Law 2006‐246 Section 9(c) Post‐Construction Practices
3. Regulation of Surface Water Transfers NCGS §143‐215.22I
4. North Carolina Administrative Code NCAC 15A NCAC 02E .0401
INTERBASIN TRANSFER CERTIFICATE
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Environmental Management Commission
North Carolina Division of Water Resources
‐ 1 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
ENVIRONMENTAL MANAGEMENT COMMISSION
Certificate Authorizing the Greenville Utilities Commission, the Towns of Farmville and
Winterville, and Greene County
To Transfer Surface Water
From the Tar River Basin to the Neuse River and Contentnea Creek Basins
Under the Provisions of G.S. 143‐215.22I
In April, 2009 the Greenville Utilities Commission (GUC), along with the Towns of Farmville, Winterville, and
Greene County petitioned the Environmental Management Commission (EMC) for a Certificate to transfer 8.3
million gallons per day (MGD) from the Tar River Basin to the Contentnea Creek Basin and 4.0 MGD from the
Tar River Basin to the Neuse River Basin. As part of the same Petition, they requested an emergency transfer
provision that would allow the transfer of up to a total of 9.3 MGD from the Tar River Basin to the
Contentnea Creek Basin and up to 4.2 MGD from the Tar River Basin to the Neuse River Basin.
A Public Hearing on the proposed transfer was held at Pitt Community College in Winterville, NC on
November 5, 2009 pursuant to G.S. 143‐215.22I. A Hearing Officer’s report was prepared in October of 2010
and mailed to members of the EMC. The EMC considered the Petitioners’ request at its regular meeting on
November 18, 2010.
According to G.S. 143‐215.22I(g), the EMC shall issue a transfer Certificate only if the benefits of the
proposed transfer outweigh the detriments of the proposed transfer, and the detriments have been or will
be mitigated to a reasonable degree. The EMC may grant the Petition in whole or in part, or deny it, and may
require mitigation measures to minimize detrimental effects. In making this determination, the EMC is
required to specifically consider:
1. The necessity, reasonableness, and beneficial effects of the transfer
2. Detrimental effects on the source river basin
2a. The cumulative effect on the source major river basin of any water transfer or consumptive water
use
3. Detrimental effects on the receiving basin
4. Reasonable alternatives to the proposed transfer
5. Use of impounded storage
6. Purposes and water storage allocations in a US Army Corps of Engineers multipurpose reservoir
7. Any other facts or circumstances necessary to carry out the law.
In addition, the Certificate must require a drought management plan describing the actions a Certificate
Holder will take to protect the source Basin during drought conditions.
The Commission Finds:
The members of the EMC reviewed and considered the complete record, which included the Hearing Officers’
report, staff recommendations, the applicants’ Petition, the Final Environmental Assessment (EA), the public
comments relating to the proposed interbasin transfer, and all of the criteria specified above. Based on that
record, the Commission makes the following findings of fact.
A7
Environmental Management Commission
North Carolina Division of Water Resources
‐ 2 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
FINDING OF FACT
Greenville Utilities Commission, Farmville, Winterville, and Greene County
Petition for an Interbasin Transfer Certificate
(1) Necessity, Reasonableness, and Benefits of the Requested Transfer Amount
In 2001, the North Carolina Environmental Management Commission (EMC) enacted the Central Coastal Plain
Capacity Use Area (CCPCUA) rules. These regulations were developed to control ground water withdrawals in
the Cretaceous Aquifers in response to decreasing ground water levels and saltwater intrusion. The CCPCUA
rules require that ground water users in 15 counties reduce their consumption in three phases between 2008
and 2018. Phase 1 requires a 25% reduction from an approved base rate by 2008, Phase II requires a 50%
reduction by 2013, and Phase III requires a 75% reduction by 2018. The Town of Farmville, Town of
Winterville, and Greene County currently rely on the Cretaceous Aquifers for water supply and are affected
by the CCPCUA rules. In order to comply with the required reductions, these communities plan to purchase
potable water from the Greenville Utilities Commission.
The Greenville Utilities Commission (GUC) operates an existing surface water treatment plant (WTP) on the
Tar River. This plant is capable of producing a maximum of 22.5 million gallons per day (MGD) of potable
water. In 2009, Greenville’s average daily water use was approximately 13 MGD. GUC’s excess plant capacity
is sufficient to provide the Towns of Farmville, Winterville, and Greene County with a replacement water
supply through 2030. Therefore, these three communities have signed purchase agreements with GUC.
The Town of Farmville and the majority of Greene County are located in the Contentnea Creek Basin‐ a sub‐
basin to the Neuse Major River Basin. The Town of Winterville and the southwestern portion of Greene
County are located in the Neuse River Basin. Since Greenville’s WTP is in the Tar River Basin, GUC’s sales to
these communities constitute an interbasin transfer from the Tar River Basin to the Neuse River Basin and
Contentnea Creek Basin.
To support the sale of water to these communities, GUC has requested an interbasin transfer certificate for
the transfer of up to 8.3 MGD to the Contentnea Creek Basin and 4 MGD to the Neuse River Basin. This
transfer request represents an estimated maximum‐day transfer capacity to each basin through 2030. GUC
does not have the ability to meet simultaneous, system‐wide peak demands; therefore the purchasing
systems will use banked ground water as an alternate source during times that peak demands exceed GUC’s
available capacity.
DWR supports this water banking concept where it is consistent with good management of the region’s
water resources and subject to prior review and approval of specific banking proposals. Many water systems
throughout the Central Coastal Plain Capacity Use Area (CCPCUA) utilize water banking as a means of
meeting their required reductions. Although all of the Petitioners are planning to bank ground water by
reducing pump rates as much as possible during the early CCPCUA phases (banking will likely not be possible
after 2015), there is no direct correlation between the amount of water that might be banked and the
amount of the IBT request. The amount of water that might be banked by 2018 is an unforeseeable quantity.
Similarly, it would be difficult to predict exactly when and how much banked water will be used. As a result,
it is essential that the banked water remain as a “savings account” used by each community if and when
supplemental water is required to meet peak demands. Therefore, the total volume of the anticipated water
bank was not subtracted from the applicant’s total IBT request.
A8
Environmental Management Commission
North Carolina Division of Water Resources
‐ 3 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
A supplemental analysis of the amount of the request, an evaluation of the peaking factors used by the
Petitioners in support of their request, and a discussion of the Petitioners’ IBT management strategy is
presented in the Staff Response to Comments, included as Attachment B to these findings. Based on these
analyses, the Petitioners’ IBT request for an 8.3 MGD maximum day transfer from the Tar River Basin to the
Contentnea Creek Basin and 4.0 MGD from the Tar River Basin to the Neuse River Basin is consistent with the
shortfall caused by the CCPCUA reductions.
GUC is also requesting an emergency transfer provision that would allow an additional 1 MGD transfer to the
Contentnea Basin (up to 9.3 MGD total) and an additional 0.2 MGD to the Neuse Basin (up to 4.2 total). This
provision would only apply during emergency events where ground water is not available to the purchasing
communities (such as major mechanical/electrical failure). GUC requests that DWR notification be required
to trigger the emergency transfer provision.
The Hearing Officers have chosen not to grant an emergency condition. G.S. §143‐215.22L(q) specifically
outlines the procedure by which water systems may request an emergency water transfer. Should the
Petitioners need such a transfer, that request should be submitted to the Department in accordance with the
applicable statutes.
§143‐215.22L(q) Emergency Transfers. – In the case of water supply problems caused by
drought, a pollution incident, temporary failure of a water plant, or any other temporary
condition in which the public health, safety, or welfare requires a transfer of water, the
Secretary of Environment and Natural Resources may grant approval for a temporary
transfer. Prior to approving a temporary transfer, the Secretary shall consult with those
parties listed in subdivision (3) of subsection (c) of this section that are likely to be affected by
the proposed transfer. However, the Secretary shall not be required to satisfy the public
notice requirements of this section or make written findings of fact and conclusions of law in
approving a temporary transfer under this subsection. If the Secretary approves a temporary
transfer under this subsection, the Secretary shall specify conditions to protect other water
users. A temporary transfer shall not exceed six months in duration, but the approval may be
renewed for a period of six months by the Secretary based on demonstrated need as set forth
in this subsection.
Based on the record the Commission finds the transfer of a maximum daily amount of 8.3 MGD from the Tar
River Basin to the Contentnea Creek Basin and a maximum daily amount of 4.0 MGD from the Tar River Basin
to the Neuse River Basin is necessary to provide a replacement water supply to Petitioners in the Central
Coastal Plain Capacity Use Area. Surface water from the source basin is readily available in that the
Greenville Utilities Commission has sufficient existing water treatment plant capacity to meet these systems’
needs through 2030.
Based on the record, the Commission finds that the IBT Management Strategy will be an important factor in
the ability of the Petitioners to meet demands while maintaining compliance with the Central Coastal Plain
Capacity Use Area Rules (15A NCAC 2E .0500) and the conditions of this Certificate. Therefore this Certificate
will include a Compliance and Monitoring Plan to ensure that the maximum daily transfer amounts are not
exceeded and the Petitioners’ IBT Management Strategy is followed in the manner set forth in the Petition.
The Commission also finds that G.S. §143‐215.22L(q) specifically outlines the procedure by which water
systems may request an emergency water transfer. Should GUC need such a transfer, that request should be
A9
Environmental Management Commission
North Carolina Division of Water Resources
‐ 4 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
submitted to the Department in accordance with the applicable statutes. Therefore an emergency transfer
provision will not be granted as a condition of this Certificate.
(2) Detrimental Effects on the Source Basin
The Greenville Utilities Commission performed a hydrologic analysis to evaluate the impact of the interbasin
transfer on the Tar River Basin. This analysis included the development of a long‐term flow record at
Greenville, the generation of flow statistics to characterize the Tar River under both existing and future water
use scenarios, and a spreadsheet‐based hydrologic accounting model.
The hydrologic accounting model simulates water withdrawals and wastewater discharges to predict their
effect on stream flow in the Tar River. The model accounts for all existing and projected withdrawals and
discharges on the Tar River, in excess of 100,000 gallons per day, from the Rocky Mount Dam to the GUC
WWTP discharge. The USGS flow record developed for the Greenville gage was used as the base flow record.
Model simulations included the following scenarios:
1. Current flows with no IBT
2. Current flows with 2030 average day IBT
3. Current flows with 2030 maximum IBT withdrawal
4. Predicted 2030 flows with no IBT
5. Predicted 2030 flows with 2030 average day IBT
6. Predicted 2030 flows with 2030 maximum IBT withdrawal
The hydrologic analysis performed by GUC was evaluated by the Hearing Officers and DWR staff during the
comment period for the Petition. A discussion of this analysis and its conclusions are included in the Staff
Reponses to Comments, presented in Attachment B to these Findings. In summary, the model shows that
the effects of the interbasin transfer are negligible at average stream flows and higher, with a slightly larger
impact during low flows. Tidal influences were not simulated in the model.
Although each of the modeling analyses performed in support of the Petition indicate a difference between
the IBT and non‐IBT scenarios, it is reasonable to categorize these differences as insignificant for the
following reasons:
1. The modeling analysis is conservative. DWR asked the applicant to include a number of very
conservative assumptions so that a “worst case impact” could be identified. These assumptions
include reducing GUC’s wastewater discharges on the Tar River by the amount of the IBT. For many
of the modeling scenarios, this change removed the entire volume of GUC’s existing and projected
wastewater discharge from the Tar River. The model also assumes a sustained maximum day
transfer (as opposed to a predicted average day transfer with peaks approaching the max‐day).
2. IBT and State Regulations require a drought management plan. GUC is required to have a Water
Shortage Response Plan (WSRP) containing specific, identifiable triggers that would be put into effect
in the event of drought. This plan is also required to be included in the Certificate. Therefore GUC
(and the other Petitioners) would likely be under water restrictions during low flow events. GUC’s
WSRP triggers are tied to the stage of water at the intake location and the location of the salt water
wedge.
A10
Environmental Management Commission
North Carolina Division of Water Resources
‐ 5 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
3. The model did not take into account tidal effects. An important feature of the lower Tar River is that
it is tidally influenced. Since salt water is heavier than freshwater, the salt water wedge creates a
dam‐like effect that pushes freshwater upstream during low flow periods. GUC closely monitors the
salt water wedge since their WTP is not designed to treat saline water. GUC has also noted instances
where net negative downstream flow has been recorded; however, there has been adequate water
over the raw water intake. Due to the tidal influence, the Tar River channel is never depleted. This
tidal buffering effect would also reduce the impact on aquatic life during critical periods.
4. The IBT request will be met with existing infrastructure. GUC has not requested an expansion of
their WTP due to this request. They have sufficient capacity in their existing WTP to meet Farmville,
Greene County, and Winterville’s projected demands. The direct impact of their withdrawal was
evaluated in the environmental documents developed (and approved) for the construction of the
water treatment plant.
Due to the above‐mentioned factors, and the fact that modeling results indicate that the IBT will have
minimal impact on the existing stream flow; there are no expected impacts to the wastewater assimilation
capacity of the Tar River Basin. Correspondingly, there are no anticipated impacts to water quality within the
source basin.
The City of Rocky Mount provided detailed comments concerning the possibility that future studies,
particularly DWR’s Tar River Basin Model or the Tar River Basin Plan, might reveal additional impacts to the
Tar River. In response, the Hearing Officers requested that Rocky Mount and GUC jointly recommend
language for the special condition. While the parties were not able to come to a mutual conclusion, each
entity individually recommended verbiage that was similar to reopeners previously used by the EMC in other
IBT Certificates. The most significant difference is that Rocky Mount proposed that any decision by the
Commission to grant or deny a request to reopen the certificate should be subject to administrative and
judicial review according to Chapter 150B of the General Statutes. However, the Hearing Officers have
determined that it would not appropriate for a condition of the Certificate to attempt to define any right a
party may or may not have in challenging the EMC’s decision. Therefore the Hearing Officers do not
recommend that Rocky Mount’s proposed language be used in the Certificate. Instead, the reopener
language will be consistent with language used in other IBT Certificates.
This interbasin transfer will not spur significant growth in the source basin. Farmville, Winterville, and Greene
County are not located in the Tar River Basin. Greenville is the only city in the Tar River Basin that receives
water from GUC’s WTP. This plant has sufficient capacity in its existing water and wastewater treatment
plants to continue providing water to the City of Greenville, and doing so would not require an IBT Certificate.
GUC’s wastewater treatment plant will not be modified as a result of this IBT.
There are no construction activities proposed in association with this project. Therefore, no direct or indirect
impacts to aquatic or terrestrial habitats are expected to occur from the proposed interbasin transfer.
Similarly, indirect impacts to state and federally protected species are expected to be insignificant.
No direct or indirect impacts to hydroelectric power generation, navigation, or recreation are expected to
occur within the Tar River Basin will occur as a result of the proposed transfer.
Based on the record and the results of the hydrologic evaluations that were performed, the Commission finds
that the interbasin transfer is not likely to have a significant impact on the source basin. However, due to the
A11
Environmental Management Commission
North Carolina Division of Water Resources
‐ 6 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Commission’s concerns that future studies may reveal additional impacts to the Tar River Basin, the Hearing
Officers have recommended that the following reopener be added to the Certificate:
“If the Commission determines that the record on which this Certificate is based is substantially in error or if
new information becomes available that clearly demonstrates that any Finding of Fact (including those
regarding environmental, hydrologic, or water use impacts) pursuant to G.S. § 143‐215.22I(f) was not or is no
longer supported or is materially incomplete, the Commission may reopen and modify this Certificate to
ensure continued compliance with G.S. ch. 143, art. 21, part 2A. “
The Commission finds that to protect the source basin during drought conditions and as authorized by G.S. §
143‐215.22I(h), a drought management plan is required. The drought management plan will describe the
actions that the Petitioners will take to protect the Tar River Basin during drought conditions.
2(a) Cumulative Effect on Source Basin of any Transfers or Consumptive Water Use Projected in Local
Water Supply Plans
Data from local water supply plans, including current and projected water use, was used to develop input
data sets for the hydrologic accounting model. The model accounted for all existing and proposed water
withdrawals and discharges to the Tar River over 100,000 gallons per day. Based on the results of that
model, there was no significant impact to the Tar River under the modeled scenarios.
Based on the record and as stated in (2) the Commission finds that the interbasin transfer is not likely to have
a significant impact to the source basin. However, due to the Commission’s concerns that future studies may
reveal additional impacts to the Tar River Basin, the Hearing Officers have recommended that the following
reopener be added to the Certificate:
“If the Commission determines that the record on which this Certificate is based is substantially in error or if
new information becomes available that clearly demonstrates that any Finding of Fact (including those
regarding environmental, hydrologic, or water use impacts) pursuant to G.S. § 143‐215.22I(f) was not or is no
longer supported or is materially incomplete, the Commission may reopen and modify this Certificate to
ensure continued compliance with G.S. ch. 143, art. 21, part 2A. “
(3) Detrimental Effects on the Receiving Basins
Direct Impacts
Winterville’s wastewater is treated by the Contentnea Metropolitan Sewerage District via the Contentnea
Creek Wastewater Treatment Plant (WWTP). This plant is permitted to discharge 2.58 MGD of wastewater to
an unnamed tributary to Contentnea Creek in the Neuse River Basin.
Farmville and the majority of Greene County are located in the Contentnea Creek Basin. Farmville operates a
3.5 MGD WWTP which discharges to this Basin. The majority of the wastewater treatment in Greene County
is handled by on‐site septic systems; however, there are three small centralized treatment systems: the Snow
Hill WWTP permitted for 0.5 MGD, the Hookerton WWTP permitted for 0.06 MGD, and the Maury Sanitary
Land District WWTP permitted for 0.225 MGD. All of these facilities discharge to the Contentnea Creek Basin.
A12
Environmental Management Commission
North Carolina Division of Water Resources
‐ 7 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Since none of these facilities will be requesting an expansion (or changes to existing permit limits) to
accommodate additional flows generated by the IBT, the IBT is not predicted to cause direct impacts to the
receiving basins.
There are no construction activities proposed in association with this project. Therefore, no significant direct
impacts to aquatic or terrestrial habitats within the receiving basin are expected to occur as a result of the
proposed transfer. No direct or indirect impacts to navigation, recreation, or flooding are predicted to occur
as a result of this proposed project based on the minimal effect on stream flows.
Indirect Impacts
Indirect impacts are expected to be insignificant and would occur with any replacement water source.
However, the following information is provided as a demonstration that any indirect impacts that might
occur will be mitigated. Included in the Staff Reponses to Comment (Attachment B) is a detailed summary of
all zoning ordinances, land use plans, and other mitigative measures that have been put in place or are under
development by the Petitioners.
Green County is rural and largely agricultural. According to the NC State Demographics Unit, the County is
expected to grow at a modest rate of approximately 1% per year between 2010 and 2030. The rural and
agricultural nature of the County is not predicted to change once the IBT replaces ground water as a water
supply; therefore indirect impacts to the receiving basin due to growth are expected to be insignificant.
The Town of Farmville has experienced limited growth in the last 15 years, adding 180 residents between
1990 and 2004. The Town does not consistently record yearly census data, nor have they conducted
population projections for the near future. It is reasonable to assume that the Town will continue to grow at
the historical growth rate of approximately 0.25% per year. Based on these projections, indirect impacts to
the receiving basin due to growth are expected to be insignificant.
Winterville has experienced increased growth and development within the past 15 years. The Town’s
population more than doubled between 1990 and 2006 when the population increased at an average rate of
11% per year. Based on its close proximity to Greenville, growth in Winterville is expected to remain strong
in the near future. Future projections estimate the Town’s growth at 4.5‐5.8% per year.
All communities in the Tar Pamlico and Neuse River Major Basins are subject to nutrient management
strategies. Both the Tar Pamlico and Neuse Nutrient Strategies have requirements for wastewater
discharges, agriculture, buffers, and stormwater. All of the requirements, except those involving the
development of a stormwater program, are applicable on a basin‐wide basis. However the stormwater
program requirements only apply to those local governments of a certain size, density, or estimated impact.
Pitt County (including Winterville) and Greenville are required to develop stormwater programs under the
Tar Pamlico Nutrient Strategy. However Farmville and Greene County fall below the thresholds for
development of a stormwater program under the Neuse Nutrient Strategy. Similarly, these governments do
not fall under the stormwater Phase II program due to their population and rural nature.
Therefore, the Hearing Officers have determined that an appropriate mitigative measure, above what these
communities are already required to do under the Tar Pamlico and Neuse Nutrient Management Strategies,
is the implementation of Phase II post‐construction stormwater controls. The intent of this measure is to
control any unforeseeable impacts due to growth that may occur as a result of the transfer. As previously
A13
Environmental Management Commission
North Carolina Division of Water Resources
‐ 8 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
stated, Pitt County (including Winterville) and Greenville are already required to develop stormwater
programs consistent with the Tar Pamlico Nutrient Strategy. Therefore this Certificate requirement would
primarily impact Greene County and Farmville. The Hearing Officers have determined that implementing
post‐construction stormwater controls in these systems would serve to put in effect the most impactful
control measures while not being overly burdensome to a small, rural water system.
Based on the record, the evaluation of impacts discussed in the Staff Response to Comments (included in
Attachment B), the existing Nutrient Management Strategies in effect in the Tar River and Neuse River Basins,
and the overall modest level of growth expected in Pitt and Greene Counties, the Commission finds that the
IBT will not cause significant detrimental effects to the Contentnea or Neuse River Basins. However the EMC
has determined that it is reasonable to require the Petitioner to mitigate any minor impacts due to growth
that might be expected.
The Certificate condition will read as follows:
“No unit of local government may receive surface water regulated under this Certificate unless the local
government maintains, for all areas that may receive surface water regulated under this Certificate,
requirements that are at least as stringent as the Division of Water Quality’s Phase 2 post‐construction
stormwater controls or the post‐construction stormwater controls of the Universal Stormwater Management
Program (USMP), for all new development that disturbs more than one acre of land, including those projects
that disturb less than one acre of land but are part of a common plan of development or sale that disturbs
more than one acre of land.”
(4) Alternatives to the Proposed Transfer
The Petitioner evaluated the following alternatives to the interbasin transfer:
1. Development of an independent surface water source on Contentnea Creek
2. Development of an independent ground water source
3. Purchase of finished water from the Neuse Regional Water and Sewer Authority (NRWASA)
4. Purchase of finished water from the City of Wilson
5. Purchase of finished water from the Greenville Utilities Commission
The analysis shows that all of the alternatives, with the exception of those requiring the development of
additional ground water wells, would require an interbasin transfer certificate for at least one of the
Petitioners (either Farmville, Winterville, or Greene County). However the ground water alternatives were
not identified as a sustainable due to the potential for the EMC to designate additional Capacity Use Areas in
the future.
The reservoir alternative has the greatest environmental and economic impact. It is also likely that the
construction of a reservoir in Greene County would be infeasible due to technical, environmental, and
permitting complications.
The option of returning water to the source basin was evaluated in the EA. This option was excluded as being
technically infeasible. Wastewater service in the area is not as widespread as water service. There is no
countywide, centralized wastewater treatment plant (WWTP) in Greene County. While there are three small
WWTPs (Snow Hill WWTP, the Hookerton WWTP, and the Maury Sanitary Land District WWTP), residents in
A14
Environmental Management Commission
North Carolina Division of Water Resources
‐ 9 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
unincorporated areas rely primarily on septic systems. Costs for the construction of a countywide collection
and treatment system were estimated at over $150 million. In Pitt County, wastewater is treated at the
Farmville WWTP, the Contentnea Creek WWTP, and the GUC WWTP. Wastewater from the Town of
Winterville is currently treated at the Contentnea Creek WWTP. According to the 2008 EA, Winterville has
had discussions with GUC concerning future wastewater service, but there are no immediate plans to
proceed with this option. If this option were pursued in the future, it would return a portion of the
transferred water to the Tar River Basin.
Of all the identified alternatives, the only viable options were identified as the purchase of finished water
from NRWASA, Wilson, or GUC. All of these options would utilize existing water treatment plant capacity and
have comparable environmental impacts. Also, as previously stated, all of the purchase alternatives would
require that at least one Petitioner receive an interbasin transfer Certificate. Of these options, the purchase
from GUC was identified as being the most economically practicable. A detailed summary of the alternatives,
including economic and environmental impacts is included in the Staff Response to Comments.
Based on the record, the Commission finds that the selected alternative of purchasing water from Greenville
Utilities Commission is the least environmentally damaging, the most cost effective, and the most technically
feasible alternative for Farmville, Winterville, and Greene County.
(5) Impoundment Storage
This criteria is not applicable, as the Petitioners do not have an impoundment.
(6) Multipurpose Reservoir constructed by the United States Army Corps of Engineers
This criteria is not applicable, as the Petitioners do not use a reservoir.
(7) Other Considerations
Conservation is identified in the IBT statutes and the CCPCUA rules as an important component of both
programs. NCGS §143‐215.22I(c)(3) states that any Petition for an IBT must include a description of the
conservation measures to be used by the applicant to assure efficient use of the water and avoidance of
waste.
The CCPCUA rules, 15A NCAC 2E .0504, are more specific in that they require water systems in the capacity
use area to develop a water conservation plan that includes the following elements. The rules require that
each community develop a schedule of implementation for any requirement that has not yet been met:
1. Adoption of a water conservation‐based rate structure, such as: flat rates, increasing block rates,
seasonal rates, or quantity‐based surcharges.
2. Implementation of a water loss reduction program if unaccounted for water is greater than 15%.
3. Adoption of a water conservation ordinance for irrigation, including such measures as: time‐of day
and day‐of‐week restrictions on lawn and ornamental irrigation, automatic irrigation system shut‐off
devices or other appropriate measures.
4. Implementation of a retrofit program that makes available indoor water conservation devices to
customers (such as showerheads, toilet flappers, and faucet aerators).
A15
Environmental Management Commission
North Carolina Division of Water Resources
‐ 10 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
5. Implementation of a public education program (such as water bill inserts, school and civic
presentations, water treatment plant tours, public services announcements, or other appropriate
measures).
6. Evaluation of the feasibility of water reuse as a means of conservation, where applicable.
The Hearing Officers concur with the public comments that the importance of conservation is critical and a
requisite of a community requesting IBT water. The Staff Response to Comments includes a summary of the
CCPCUA requirements and how those requirements have been met by each Petitioner. The Division of Water
Resources has also agreed to begin requesting this information from all CCPCUA Permit holders beginning
January 2011. Any permit holder whose conservation measures fail to meet the minimum program as
described in 15A NCAC 2E .0502(d)(5)(A‐C) will be required to adopt measures meeting these requirements
or they will be issued an NOV. All water use conservation measures described in the CCPCUA rules will have
to be adopted by the permit holder before their next permit renewal. Consequently, the minimum water
conservation efforts recognized in the CCPCUA rules will be met as a condition of the permit.
The Hearing Officers have also recommended the addition of a special condition to the IBT Certificate that
will not allow the Petitioners to transfer water until the minimum program requirements described in NCAC
2E .0502(d)(5)(A‐C) has been met. The condition reads: “No person subject to the Central Coastal Plain
Capacity Use Area Rules 15A NCAC 2E .0500 may transfer water under this Certificate without first meeting
the minimum conservation program requirements identified in 15A NCAC 2E .0502(d)(5)(A‐C) .“
Based on the record, the requirement outlined in NCGS §143‐215.22I(c)(3), and the requirements of 15A NCAC
2E .0500, the Commission finds that it is reasonable to require each Petitioner subject to the Capacity Use
Area Rules to meet the minimum conservation program requirements identified in 15A NCAC 2E
.0502(d)(5)(A‐C) before transferring water. The purpose of this requirement is to assure the efficient use of
water and avoid waste.
A16
Environmental Management Commission
North Carolina Division of Water Resources
‐ 11 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
DECISION
The Commission, on November 18, 2010, by duly made motions concludes that by a preponderance of the
evidence based upon the Findings of Fact stated above that, with the limitations and conditions described
herein, (1) the benefits of the proposed transfer outweigh the detriments of the proposed transfer, and (2)
the detriments of the proposed transfer will be mitigated to a reasonable degree. Therefore, and by duly
made motions, the Commission grants in part and denies in part the Petition of the Greenville Utilities
Commission, the Town of Farmville, the Town of Winterville, and Greene County (collectively, “Certificate
Holders”) to transfer surface water from the Tar River Basin to the Neuse River Basin and Contentnea Creek
Basin. The permitted transfer amount shall not exceed a maximum of 8.3 million gallons on any calendar day
from the Tar River Basin to the Contentnea Creek Basin and shall not exceed a maximum of 4.0 million
gallons on any calendar day from the Tar River Basin to the Neuse River Basin. These transfer amounts are
independent of each other. This Certificate is effective immediately.
The Certificate is subject to the following conditions, imposed under the authority of G.S. § 143‐215.22I:
I. COOPERATION OF CO‐CERTIFICATE HOLDERS
If the Certificate Holders discontinue their cooperative service agreements with each other, the Division of
Water Resources (“Division”) shall specify the maximum amount of water each of the joint Certificate Holders
may transfer individually. The total of these amounts shall not exceed a maximum of 8.3 million gallons on
any calendar day from the Tar River Basin to the Contentnea Creek Basin and shall not exceed a maximum of
4.0 million gallons on any calendar day from the Tar River Basin to the Neuse River Basin. The allocations
shall be based on projections of water use for 2030 compiled by the Division at the time it is notified of the
discontinuance of the cooperative service agreement. The allocations shall take effect within 90 days of the
Division issuing the allocations, or at such other reasonable time as the Division specifies. At that time, each
condition of this Certificate shall apply to each Certificate Holder individually and the Division may require
the Certificate Holders to make individual submissions of plans, reports, etc. as necessary.
II. COMPLIANCE WITH OTHER REGULATIONS
This Certificate does not exempt the Certificate Holders or any other entity from compliance with any other
requirements of law, including the Central Coastal Plain Capacity Use Area (“CCPCUA”) Rules (15A NCAC 02E
.0500).
III. REOPENER
If the Commission determines that the record on which this Certificate is based is substantially in error or if
new information becomes available that clearly demonstrates that any Finding of Fact (including those
regarding environmental, hydrologic, or water use impacts) pursuant to G.S. § 143‐215.22I(f) was not or is no
longer supported or is materially incomplete, the Commission may reopen and modify this Certificate to
ensure continued compliance with G.S. ch. 143, art. 21, part 2A.
IV. MITIGATION
No individual unit of local government may receive surface water regulated under this Certificate unless the
local government maintains, throughout its jurisdiction, requirements that are at least as stringent as the
A17
Environmental Management Commission
North Carolina Division of Water Resources
‐ 12 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Division of Water Quality’s Phase 2 post‐construction stormwater controls or the post‐construction
stormwater controls of the Universal Stormwater Management Program (“USMP”), for all new development
that disturbs more than one acre of land, including those projects that disturb less than one acre of land but
are part of a common plan of development or sale that disturbs more than one acre of land.
V. CONSERVATION
Persons (including a unit of local government) subject to the CCPCUA Rules (15A NCAC 2E .0500) are required
to reduce the volume and effects of withdrawals from ground waters through the minimum conservation
program requirements identified in 15A NCAC 2E .0502(d)(5)(A)‐(C). In order to assure that conservation
measures are used by the applicant to assure efficient use of water and avoid waste (in accordance with
§143‐215.22I(c)(3), no individual unit of local government or persons subject to the CCPCUA Rules (15A NCAC
2E .0500) may transfer water under this Certificate without first meeting the minimum conservation program
requirements identified in 15A NCAC 2E .0502(d)(5)(A)‐(C).
VI. DROUGHT MANAGEMENT
The Certificate Holders shall implement drought management measures that become more stringent as
drought conditions increase in severity. These measures shall correspond to the most severe level of drought
existing in the Tar River Basin. Prior to each Certificate Holder receiving any water under this Certificate, the
Certificate Holder shall submit a Water Shortage Response Plan (“Plan”) to the Division, for the Division’s
approval. Each Certificate Holder shall receive approval of the Plan from the Division, and shall have and
maintain adequate authority and resources to implement and enforce the Plan. In order to be approved, the
Plan must meet or exceed the requirements set forth in 15A NCAC 2E .0607 and be no less stringent than the
Plan in Attachment A, which is incorporated herein. Any subsequent modifications to the Plan will be
reviewed and approved by the Division. Adoption of the measures in Attachment A does not imply
compliance with G.S. 143‐355(l) or 15A NCAC 2E .0607.
The Certificate Holders shall not transfer any water to any other unit of local government unless that unit of
local government agrees to be bound by this condition in full.
VII. COMPLIANCE AND MONITORING PLAN
The Certificate Holders shall report annually to the Division. The report shall detail water use over the
calendar year by providing the following information:
1. Interbasin Transfer Calculation
GUC shall calculate daily and maximum‐day interbasin transfers taking into account GUC’s own
metered water use for each billing cycle, with separate data provided for customers in the Tar River
and Neuse River Basins. The calculation shall also take into account GUC’s monthly average
wastewater treatment plant discharge, and the daily bulk purchases from the Towns of Farmville,
Winterville, and Greene County. GUC shall geocode (via the GUC GIS database) those water customers
located in the Neuse River Basin so that the consumptive use for the GUC customers can be calculated.
The consumptive use for Winterville, Farmville, and Greene County does not need to be calculated so
long as the entire metered water use to these communities is the transfer to each of the respective
Basins.
A18
Environmental Management Commission
North Carolina Division of Water Resources
‐ 13 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
2. Ground Water Use
Farmville, Winterville, and Greene County shall submit their daily metered ground water use as
reported to DWR’s Ground Water Section for compliance with any CCPCUA permits. The
documentation shall note the maximum‐day water use by each system.
3. Banked Water Summary
Farmville, Winterville, and Greene County shall also provide a banked water summary. Each summary
shall include the total volume of banked water available at the beginning and end of the calendar year,
an accounting of any day during the year that banked water was used, and the total volume of banked
water that was used during that day.
4. Compliance With Other Certificate Conditions
The Certificate Holders shall also provide a status report of compliance efforts for any other conditions
required by this Certificate.
All annual reports shall be submitted by March 31st of the following calendar year. Following the submission
of any reports under this Certificate, the Certificate Holders shall promptly provide to the Division any
information requested by the Division that the Division concludes is needed to complete, correct or clarify
the report. If the Certificate Holders believe that the Division’s request does not conform to the reporting
requirements, the parties shall confer promptly to resolve any differences.
When an annual report indicates that a daily transfer equaled or exceeded eighty (80%) percent of any
transfer amount authorized by this Certificate, the Certificate Holders shall submit to the Division, by June 1
of the year in which such annual report was required, a detailed plan that specifies how the Certificate
Holders intend to address future foreseeable water needs. So long as the Certificate Holders are required to
have a local water supply plan, then the plan to address future foreseeable water needs shall be an
amendment to the local water supply plan required by G.S. 143‐355(l).
When an annual report indicates that a daily transfer equaled or exceeded ninety percent (90%) of any
transfer amount authorized by this Certificate, then:
1. The Certificate Holders shall begin implementation of the plan submitted to the Division.
2. GUC shall immediately begin monthly reporting to the Division. Monthly reports shall be submitted
within 45 days of the end of the month.
All reports submitted pursuant to this condition shall be signed by the Director of Public Utilities or person of
similar position who shall affirm that, based on information collected during and belief formed after
reasonable inquiry, the report is true, accurate and complete and that the Certificate Holder complied with
the Certificate continuously throughout the year, except as specifically indicated in the report.
A19
Environmental Management Commission
North Carolina Division of Water Resources
‐ 14 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
NOTICE: The Certificate Holders may be jointly and severally responsible for compliance with certain terms,
conditions and requirements stated herein, and therefore may be jointly and severally liable for penalties
assessed to enforce such terms, conditions and requirements as provided in G.S. §143‐215.6A.
This is the _________ day of ______________________, 2010.
______________________________________________
Stephen T. Smith, Chairman
A20
Environmental Management Commission
North Carolina Division of Water Resources
‐ 15 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
‐ Attachment A ‐
MINIMUM CRITERIA FOR DROUGHT MANAGEMENT PLAN
Section A. The Water Shortage Response Plan (“Plan”) shall include provisions that are at least as stringent as
the following specific procedural and substantive provisions:
Stage 1 ‐ Water Conservation Alert
A Stage 1 water emergency shall be declared in the event of an immediate water shortage or when
any of the following conditions exist:
There are three consecutive days when water demand exceeds 80% of the water production
capacity.
The average of the daily Tar River level measurements taken at the Water Treatment Plant
Raw Water Pump Station is ‐1.0 feet Mean Sea Level or less.
The location of the salt water interface in the Tar River is determined to be 10 miles or less
from the Water Treatment Plant Raw Water Pump Station.
Water production capacity shall be defined as the maximum volume of water that meets state and
federal standards that the water treatment process can produce during a twenty‐four hour period.
Water production capacity can vary depending on system component reliability and raw water
conditions. The salt water interface shall be defined as the point where chloride levels in the Tar
River are measured at 250 milligrams per liter just below the surface. During a declared Stage 1
water emergency the following voluntary water conservation practices shall be encouraged:
a) Inspect and repair all faulty and defective parts of faucets and toilets.
b) Use shower for bathing rather than bathtub and limit shower to no more than 5 minutes.
c) Do not leave faucets running while shaving, brushing teeth, rinsing or preparing food.
d) Limit the use of clothes washers and dishwashers and when used, operate fully loaded.
Operate dishwashers after the peak demand hours of 6 to 10 p.m.
e) Limit lawn watering to that necessary for plant survival. Water lawns before the peak
demand hours of 6 to 10 a.m.
f) Water shrubbery the minimum required. Water shrubbery before the peak demand hours of
6 to 10 a.m.
g) Limit vehicle washing.
h) Do not wash down outside areas such as sidewalks, driveways, patios, etc.
i) Install water saving showerheads and other devices.
j) Use disposable and biodegradable dishes where possible.
k) Install water saving devices in toilets such as early closing flappers.
l) Limit hours of water‐cooled air conditioners.
m) Do not fill swimming or wading pools.
A21
Environmental Management Commission
North Carolina Division of Water Resources
‐ 16 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Stage 2 ‐ Water Shortage Warning
A Stage 2 water emergency shall be declared in the event of an immediate water shortage or when
any of the following conditions exist:
There are two consecutive days when water demand exceeds 90% of the water production
capacity.
The average of the daily Tar River level measurements taken at the Water Treatment Plant
Raw Water Pump Station is ‐1.5 feet Mean Sea Level or less.
The location of the salt water interface in the Tar River is determined to be 7 miles or less
from the Water Treatment Plant Raw Water Pump Station.
Water production capacity shall be defined as the maximum volume of water that meets state and
federal standards that the water treatment process can produce during a twenty‐four hour period.
Water production capacity can vary depending on system component reliability and raw water
conditions. The salt water interface shall be defined as the point where chloride levels in the Tar
River are measured at 250 milligrams per liter just below the surface. During a declared Stage 2
water emergency the following activities shall be prohibited:
a) Watering lawns, grass, shrubbery, trees, flower and vegetable gardens except by hand held
hose, container, or drip irrigation system. A person who regularly sells plants will be
permitted to use water on their commercial stock. A golf course may water their greens.
State, County and City licensed landscape contractors may water by hand held hose or drip
irrigation any plants under a written warranty.
b) Filling swimming or wading pools, either newly constructed or previously drained. Make up
water for pools in operation will be allowed.
c) Using water‐cooled air conditioners or other equipment, in which cooling water is not
recycled, unless there are health or safety concerns.
d) Washing any type of mobile equipment including cars, trucks, trailers, boats, or airplanes.
Any persons involved in a business of washing motor vehicles may continue to operate.
e) Washing outside surfaces such as streets, driveways, service station aprons, parking lots, or
patios.
f) Washing the exterior of office buildings, homes, or apartments.
g) Using water for any ornamental fountain, pool, pond, etc.
h) Serving drinking water in food establishments such as restaurants or cafeterias, unless
requested to do so by a customer.
i) Using water from a public or private fire hydrant for any reason other than to suppress a fire
or other public emergency or as authorized by the General Manager or his authorized
representative.
j) Using water to control or compact dust.
k) Intentionally wasting water.
l) Commercial and industrial water customers shall achieve mandatory reductions in water
usage through whatever means are available. A minimum reduction of 20% shall be the
target, however a greater target reduction percentage may be required depending on the
severity of the water emergency. Compliance with the reduction target shall be determined
by the General Manager or his authorized representative. Variances to the target reduction
A22
Environmental Management Commission
North Carolina Division of Water Resources
‐ 17 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
may be granted by the General Manager or his authorized representative to designated
public health facilities.
Stage 3 – Water Shortage Danger
A Stage 3 water emergency shall be declared in the event of an immediate water shortage or when
any of the following conditions exist:
There is one day when water demand exceeds 100% of the water production capacity.
The average of the daily Tar River level measurements taken at the Water Treatment Plant
Raw Water Pump Station is ‐2.0 feet Mean Sea Level or less.
The location of the salt water interface in the Tar River is determined to be 4 miles or less
from the Water Treatment Plant Raw Water Pump Station.
Water production capacity shall be defined as the maximum volume of water that meets state and
federal standards that the water treatment process can produce during a twenty‐four hour period.
Water production capacity can vary depending on system component reliability and raw water
conditions. The salt water interface shall be defined as the point where chloride levels in the Tar
River are measured at 250 milligrams per liter just below the surface. During a declared Stage 3
water emergency the following activities shall be prohibited, in addition to activities prohibited
under Stage 2:
a) Watering lawns, grass, shrubbery, trees, and flowers.
b) Washing motor vehicles at commercial car wash establishments.
c) Watering any vegetable garden except by hand held hose, container, or drip irrigation.
d) Commercial and industrial water customers shall achieve mandatory reductions in water
usage through whatever means are available. A minimum reduction of 50% shall be the
target, however a greater target reduction percentage may be required depending on the
severity of the water emergency. Compliance with the reduction target shall be determined
by the General Manager or his authorized representative. Variances to the target reduction
may be granted by the General Manager or his authorized representative to designated
public health facilities.
e) In the event that the prohibition of the activities listed above is not sufficient to maintain an
adequate supply of water for fire protection, all use of water for purposes other than
maintenance of public health and safety shall be prohibited. Residential water use shall be
limited to the amount necessary to sustain life through drinking, food preparation and
personal hygiene.
The Certificate Holders may require that commercial and industrial water customers prepare plans
detailing measures to be taken by them to achieve mandatory reductions in daily water usage during
Stage 2 and Stage 3 emergencies. Such plans shall be completed within sixty (60) calendar days after
receipt of notice to prepare them.
Any User who is found to have failed to comply with any of the mandatory restrictions may be fined
up to five hundred dollars ($500) per day per violation. Enforcement of the mandatory restrictions
and imposition of fines will be implemented according to the following schedule except in cases of
gross noncompliance:
A23
Environmental Management Commission
North Carolina Division of Water Resources
‐ 18 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
First offense – Written warning
Second offense – Fine up to two hundred dollars ($200)
Third offense and further offenses – Fine up to five hundred dollars ($500)
Water service may be temporarily discontinued for failure to comply with the mandatory
restrictions. All applicable penalty fees may be applied in the event of such service suspensions. In
the event of continued noncompliance, removal of meter and service will be deemed proper and
service will be discontinued and tap fees and deposits will be forfeited.
Section B. The Plan shall also include the following:
The designation of a staff position or organizational unit responsible for the implementation of their
Plan;
Notification procedures that will be used to inform employees and water users about the
implementation of the plan and required water conservation response measures;
Specific measurements of available water supply, water demand and system conditions that will be used
to determine the severity of water shortage conditions and to initiate water use reduction measures and
the movement between various levels;
Procedures that will be used to regulate compliance with the provisions of the plan;
Procedures for affected parties to review and comment on the plan prior to final adoption;
Procedures to receive and review applications for variances from specific requirements of the plan and
the criteria that will be considered in the determination to issue a variance;
An evaluation method to determine the actual water savings and the effectiveness of the Plan in meeting
its stated objectives and reduction goals;
Procedures for revising and updating the Plan to improve effectiveness based on the results of the
evaluation method, and to adapt to new circumstances such as changes in the number or types of water
sources.
A24
Environmental Management Commission
North Carolina Division of Water Resources
‐ 19 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
‐Attachment B‐
STAFF RESPONSE TO COMMENTS
The Environmental Management Commission held a Public Hearing on Greenville Utilities Commission’s (GUC)
Petition for an Interbasin Transfer Certificate (IBT) on November 5, 2009. The public record for that hearing was
scheduled to close on December 4, 2009, however the Hearing Officers agreed to grant a one‐time extension
ending January 19, 2010. This document includes a record of the comments that were submitted during that time,
as well as responses from Division of Water Resources (DWR) staff. The Hearing Officers utilized the comments
and staff response to make the recommended changes that are addressed in this document.
37 people were in attendance for the Public Hearing on the IBT Petition. In total, 21 provided comments, either at
the hearing (10 speakers) or during the public comment period. The following individuals submitted comments.
Each commenter was given a distinct ID number.
Table 1: Record of Public Comments Received on the IBT Petition
Commenter ID Name Affiliation Method Date
Barney Kane Self Email 12/4/2009 1 Barney Kane Self Email 1/19/2010
2 Anne Bunnell Self Email 1/14/2010
3 John and Kathy Schermerhorn Self Email 10/27/2009
Heather Jacobs Deck Pamlico‐Tar Riverkeeper / SELC Email 12/2/2009
Heather Jacobs Deck Pamlico‐Tar Riverkeeper / SELC Email 12/4/2009
Heather Jacobs Deck Pamlico‐Tar Riverkeeper / SELC Mail 12/4/2009
Heather Jacobs Deck Pamlico‐Tar Riverkeeper / SELC Email 1/19/2010
4
Heather Jacobs Deck Pamlico‐Tar Riverkeeper / SELC Verbal 11/5/2009
Douglas Jackson Winterville Mail 12/3/2009 5 Terri Parker‐Eakes Winterville Email 12/4/2009
Peter F. Varney Rocky Mount Mail 12/1/2009
Glenn Dunn Rocky Mount Email 12/2/2009
Kalika Guthrie Rocky Mount Email 1/19/2010 6
Wayne Hollowell Rocky Mount Verbal 11/5/2009
7 Laura E. Williamson Self Email 1/13/2010
8 Wayne Caldwell Self Email 1/4/2010
9 Charles Schwartz Self Email 12/14/2009
10 Carolyn Reed Self Verbal/Written 11/5/2009
11 James Cooke, Jr. Self Mail 12/20/2009
12 Dave Schwartz Self Verbal/Written 11/5/2009
13 Alvin Woodlief, Jr. Oxford Mail 10/30/2009
Barry G. Parks Wilson Mail 12/8/2009 14 Barry Parks Wilson Email 12/4/2009
15 Don Davenport Greene County Mail 11/18/2009
Bennie Heath Greene County Mail 12/3/2009
Bennie Heath Greene County Verbal 11/5/2009 16
Lisa Johnson Greene County Email 12/3/2009
17 Albert V. Lewis Farmville/ Greene County Mail 12/3/2009
A25
Environmental Management Commission
North Carolina Division of Water Resources
‐ 20 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Robert Evans Farmville Verbal 11/5/2009
Randy Emory/ Ronald Elks GUC Email 1/15/2010 18 David Briley GUC Verbal 11/5/2009
19 Byron Bateman Self Verbal 11/5/2009
20 Art Langrish Sierra Club Verbal 11/5/2009
21 John Craft Town of La Grange Verbal 11/5/2009
DWR staff reviewed the submissions and separated each comment into distinct sub‐comments. Those sub‐
comments were then numbered. Those two ID numbers (the Commenter ID and the Sub‐Comment ID) were then
combined to yield a composite Comment ID #. The following figure provides an example of how public comments
were captured.
Figure 1: Determination of Sub‐Comments
Throughout this staff response document, individual sub‐comments are referenced by their assigned Comment ID
#. The full text of all the comments received during the comment period, including a record of how those
comments were characterized, is included for reference in Appendix 7.
The individual who submitted the following comment was assigned Commenter ID number 9. Within that
submission, DWR staff was able to identify three distinct sub-comments. Those sub-comments were
assigned Comment ID # 9.1, 9.2, and 9.3
A26
Environmental Management Commission
North Carolina Division of Water Resources
‐ 21 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TABLE OF CONTENTS
The staff response to comments has been organized into the following major topics. Within each topic
is a list of the pertinent comments and a staff response.
I. Amount of Transfer
II. Conservation
III. Analysis of Alternatives
IV. Mitigation of Secondary and Cumulative Impacts
V. Impacts to the Tar River
VI. Direct Impacts to the Receiving Basin
VII. Construction of Temporary Dam Structure
VIII. Existing Financial Investment
IX. Impacts to Air Quality
X. Aquifer Storage and Recovery System
XI. Other Comments
XII. Recommendations to the Environmental Management Commission (EMC)
Appendix 1: Explanation of IBT Management Strategy, ARCADIS
Appendix 2: Memo from DWR Concerning Compliance with CCPCUA Program Requirements
Appendix 3: Summary of Water Conservation Requirements per CCPCUA Rules, ARCADIS
Appendix 4: Environmental and Economic Impacts of Water Supply Alternatives, ARCADIS
Appendix 5: Summary of Mitigation for Secondary and Cumulative Impacts
Appendix 6: Explanation of Hydrologic Analysis and Results Interpretation, ARCADIS
Appendix 7: Record of Public Comments received on IBT Petition
A27
Environmental Management Commission
North Carolina Division of Water Resources
‐ 22 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC I: AMOUNT OF TRANSFER
Several comments expressed concern that the amount of the requested transfer is higher than should be
necessary to meet the needs of these communities. Comments point to such factors as the amount of the transfer
request, the peaking factors used in the analysis, and the inclusion of an emergency transfer condition as being
excessive.
Subtopic A: Necessity of Transfer Request
Comment ID # Comment Text
14.2 In our opinion, Greenville is asking for a larger IBT than the minimum required. In fact they are
requesting an amount large enough to supply as much as 93% of the maximum daily projected
demand for a short term and 151% continuously of the average daily demand. CCPCUA rules
only require up to a 75% reduction in the average daily demand of their permitted amount.
Subtracting 75% from the Approved Base rate for Greene County, Farmville, and Snow Hill
would only require 4.45 MGD from GUC to meet the demand for an average annual day and
only 8.5 MGD for a maximum demand day, which is the day that GUC will only be transferring a
minimal amount according to Table 2‐3. We do not see the necessity for a request of 8.3 and
9.2 MGD respectively, and a total of as much as 13.4 MGD since GUC is also requesting to send
111% of the maximum daily demand to Winterville and 117% of the maximum daily demand
for an emergency thru the year 2030. Even if you assume the unprecedented growth rates for
Greene County, Farmville and Winterville are correct, this volume of transfer is unnecessary.
4.14 Along with our concerns regarding the inadequacies of the EA, we are especially concerned
about the transfer amount requested by the applicant. The stated purpose of the IBT request in
GUC's Petition is to aid the receiving communities' compliance with CCPCUA regulations, which
require a 75% reduction in water withdrawals from the cretaceous aquifers phased over a 10‐
year period. The amount of ground water water withdrawal reductions that are required by the
receiving communities are outline in Table 1. The total amount the communities need to
replace this loss of ground water supply due to CCPCUA rules is 3.771 mgd. Therefore, the
proposed IBT allows for significant growth over the time period evaluated and is incongruent
with the project’s stated objective of compliance with CCPCUA rules. The IBT certificate
proposes an interbasin transfer of 8.3 mgd for the Towns of Farmville and Greene County
Regional Water authority, as well as an additional 1.0 mgd for emergency conditions. The
second certificate request proposes 4.0 mgd to the Town of Winterville with an additional 0.2
mgd for emergency conditions. The total transfer requested from the Tar River Basin to the
Neuse River Basin is 12.3 with emergency conditions allowing up to 13.5 mgd. This amount is
well in excess of the stated purpose of the IBT to aid the communities in compliance with the
CCPCUA rules. The IBT does allow for significant growth; growth that would not be viable
without the transfer of water via this IBT.
Staff Response
An important exercise in evaluating the amount of the transfer request is to examine the amount of water lost by
the required Central Coastal Plain Capacity Use Area (CCPCUA) rule reductions. This is a complicated task for a
number of reasons. First is that the allowable CCPCUA pump rate is a static volume that will not change as a
community continues to experience established growth trends. The allowable ground water withdrawal in 2018
will be the same as the allowable withdrawal in 2050. Therefore, in determining how much water is “lost” due to
the CCPCUA rules, a reference year must be chosen (i.e., X amount of water will be lost by Y date). However it is
important to keep in mind that the reduction in available ground water will continue to restrict a community
beyond any chosen date. A second complicating factor is that even during a year with a below average water use,
a water system could reasonably experience (and must meet) a maximum day demand with a high peaking factor.
So in answering the question of how much water is lost by the CCPCUA rules, it is important to consider that water
systems must maintain the ability to meet a peak demand for short periods of time throughout a year. This is a
critical issue to consider due to the fact that interbasin transfers are regulated based on a maximum day flow.
A28
Environmental Management Commission
North Carolina Division of Water Resources
‐ 23 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
One way estimate the amount of water “lost” to the CCPCUA rules is to examine the amount of ground water that
will no longer be available to meet average daily system demands by the time the necessary reductions have been
made. The following table shows the Approved Base Rate (ABR) for each system, the allowable ground water
withdrawal rate after each reduction, and the projected average daily shortfall for each community. All of the
values are expressed in millions of gallons per day.
Table 2: Projected Average Daily Shortfall
Farmville Greene County Winterville
Approved Base Rate* 1.572 2.96 0.496
Projected Average Daily Demand (ADD) 1.87 2.31 0.85
Allowable Ground Water Withdrawal
(after 25% CCPCUA Reduction) 1.179 2.22 0.372 2008
Projected Average Daily Shortfall 0.69 0.09 0.48
Projected Average Daily Demand (ADD) 1.97 2.51 1.1
Allowable Ground Water Withdrawal
(after 50% CCPCUA Reduction) 0.786 1.48 0.248 2013
Projected Average Daily Shortfall 1.18 1.03 0.85
Projected Average Daily Demand (ADD) 2.07 2.72 1.4
Allowable Ground Water Withdrawal
(after 75% CCPCUA Reduction) 0.393 0.74 0.124 2018
Projected Average Daily Shortfall 1.68 1.98 1.28
* 15A NCAC 2E .0504(1) defines the approved base rate as “the larger of a person’s January 1, 1997 through December 31,
1997 or August 1, 1999 through July 31, 2000 annual water use rate from the Cretaceous aquifer system, or an adjusted
water use rate determined through negotiation with the Division using documentation provided by the applicant.”
As shown in Table 2, by the time the CCPCUA reductions are complete in 2018, the communities will be
experiencing a combined average daily shortfall of 4.93 MGD (80% of 2030 average day demand). However,
interbasin transfers are regulated as a maximum day flow. These average day demand shortfalls can be translated
to a system wide maximum day demand shortfall by multiplying each system’s ADD by its selected peaking factor
and then subtracting the available ground water. This estimation provides a 2018 max‐day shortfall of 9.5 MGD,
which is 77% of the 2030 max‐day IBT request.
Similarly, we can calculate the average and max‐day shortfalls through 2030. Using the above methodology, we
find that the projected average daily shortfall in 2030 is expected to be 6.3 MGD. On a max‐day, this can be
translated to 11.9 MGD. This is consistent with GUC’s IBT request for 11.9 MGD to meet Farmville, Winterville and
Greene County’s demands through 2030, plus a small amount for GUC’s own service area in the Neuse River Basin.
As an aside, had GUC used historical maximum peaking factors to develop the IBT management strategy, the
communities would have needed to request a transfer in excess of 17 MGD.
Based on this methodology, 77% of GUC’s IBT request could be considered a total replacement of ground water
through 2018. The remaining 23% could be considered for growth and peak management during the remaining 12
years of the project horizon.
The Hearing Officers recommend that no changes be made to the Petitioner’s maximum day IBT request.
A29
Environmental Management Commission
North Carolina Division of Water Resources
‐ 24 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic B: Approved Base Rate (ABR)
Comment ID # Comment Text
1.1 The Approved Base Rate (ABR) used by the NCDWR to determine historical use from the
Cretaceous aquifer in the capacity use area is flawed. The ABR applied was determined based
on historical use at a time when there were no conservation rates in place, pumping and
treatment costs were low, and energy costs for water production were also low. Thus, these
ABR’s may be presumed to be based upon water use patterns that were excessive. There was
little reason to limit use or apply conservation practices. A more realistic (much lower) ABR
should have been used. It is therefore also true that the reductions proposed from the
artificially high ABR do not reflect any serious conservation effort. Neither is there serious
hardship caused in these capacity use areas by meeting the percent reductions required in the
early years of the limitations. Reductions of twenty‐five percent could be achieved quite simply.
Reductions of fifty percent represent only a small challenge in conservation and in planned
growth. The seventy‐five percent reduction would likely require access to surface water from
the Neuse if growth is to be facilitated. Similarly if these high ABRs are used the projections of
future needs are dramatically higher than needed. Offsetting these projected "needs" with the
proposed interbasin transfer would effectively support these former wasteful, luxury, water‐
use practices. My point is that these ABRs do not reflect the true base need. Rather they reflect
luxury use patterns that do not warrant the support of the interbasin transfers proposed. To
use these erroneous ABRs as the basis for projected future water "needs" only results in
support of continued wasteful consumption. A more critical, conservation‐motivated analysis is
needed in which limits are properly considered and conservation is practiced. If such analysis
were done there would be no basis for the proposed IBT.
1.12 ... Apply conservation based water supply base requirements needs to the proposed areas.
These should be much lower than the ABRs used in this proposal.
Staff Response
While it is correct that the ABR is based on historical data and certain reductions are achievable without undue
hardship on the communities, it is important to keep in mind that the annual ground water withdrawal volume will
have to decrease while the populations of the affected communities will continue to grow. Many of the measures
being put in place (including the IBT) are not to supplement supplies during the first few phases of the reduction,
but to ensure water supply during the later phases of the CCPCUA reductions. The following graphic illustrates the
required CCPCUA reductions for a general water system.
A30
Environmental Management Commission
North Carolina Division of Water Resources
‐ 25 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Figure 2
As illustrated Figure 2, water systems that are subject to the CCPCUA rules are expected to rely upon alternate
water sources to meet historical levels of water use. The above public comment states that “The seventy‐five
percent reduction would likely require access to surface water… if growth is to be facilitated”, however that is not
the case. CCPCUA communities would require alternate water sources even if there were no growth. The
reduction in ground water is not expected to be made up through conservation alone.
As described in the previous section and in Table 1, the combined average daily shortfall for Farmville, Winterville,
and Greene County is expected to be 4.93 MGD or 80% of 2018 average demand. Regardless of whether or not
the initial ABR could have been adjusted to reflect more of a conservation‐based rate, the final result is still a
significant reduction. The majority of this reduction must be met with alternative water sources.
The Hearing Officers recommended no changes be made based on these comments.
A31
Environmental Management Commission
North Carolina Division of Water Resources
‐ 26 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic C: Selection of Peaking Factors
Comment ID # Comment Text
1.3 The data used and the peaking factors applied in the Arcadis GUC Interbasin Management Strategy
are probably flawed. For one thing there is no way that the Maximum Daily Demand for 1990 and
1995 for GUC could be "Not Available." The record keeping at GUC during those years was carefully
documented and recorded. It is hard to imagine why the data are not presented here. I have too
much faith in GUC to believe there was a selective motive for listing them as "NA" and yet these data
are too important for Arcadis to overlook these values. This is puzzlement. NCDWR should ask for
these values and consider them in the determining the proper peaking factors.
1.4 The peaking factors of 1.7 and 1.8 used for communities in the Capacity Use Areas (CCAs) contrast
dramatically with the 1.5 factor found valid for GUC. Common sense would support the assumption
that the peaking factor applied to Greenville should be used for the CCA communities as well. The
GUC peaking factor is based upon a larger, more valid, data base and one that likely reflects the
management of water resources that will be needed in the future. The more rural communities tend
to have larger lots and less steady industrial water consumption. Thus these high peaking factors
may be now be supported by the current use patterns. In the future use will require more
conservation and less irrigation. MDDs will need to more closely approach ADDS as these
communities grow and as water resources become more restricted. Use of these high values of 1.7
and 1.8 for peaking factors is not reasonable and endorses wasteful use.
Staff Response
As described in the Petition and Environmental Assessment (EA), ARCADIS examined a range of historical peaking
factors for each community. Representative peaking factors were selected that are below the historic maximum
for each community, while still being representative of the system characteristics. For Winterville, in particular,
which experiences slightly higher peaking factors than the other water systems, ARCADIS selected a factor much
lower than the historical maximum of 2.75. For this community, in particular, the peaking factor was selected
based on the understanding that conservation (and a rigorous IBT Management Strategy) will be required to
ensure that Winterville does not exceed its maximum daily transfer.
In Appendix 1, Explanation of IBT Management Strategy (ARCADIS) it is also pointed out that it is not atypical for
smaller water systems such as Winterville, Farmville, and Greene County, to experience higher peaking factors
than larger communities, such as Greenville. This is generally understood to be due to the fact that smaller
communities have less buffering capacity in their distribution system (i.e. larger distribution main, elevated
storage, etc.). Therefore the higher peaking factors should not be necessarily be attributed to wasteful use or
extravagant irrigation.
The Hearing Officers recommended no changes be made based on these comments.
A32
Environmental Management Commission
North Carolina Division of Water Resources
‐ 27 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic D: IBT Management Strategy
Comment ID # Comment Text
1.7 Greenville has had a remarkably flat water consumption pattern over the past 15 years. This
may seem puzzling considering the growth in Greenville. It is likely attributed in part to several
factors, including good management at the utility, changes in water use practices at local
industries and other more minor practices. But there are limits to these benefits. It is probable,
perhaps even certain, that Greenville's demand for water will return to the steep growth curves
that were predicted by the consulting engineers in the mid 90's. If this is true Greenville will be
using its current plant capacity in the very near future. If that is the case, there will be very little
excess to commit to other basins.
4.15 All of the receiving communities have the option, and appear to be planning, to bank ground
water by reducing their required 75% reduction prior to the 201 8 deadline. Using the figures in
the EA, we have calculated that with maximum day demands minus the use of allocated ground
water withdrawal and banked water (assuming equal distribution for 20 year starting in 201 8),
the maximum transfer needs (to meet maximum day demands) is 11.3 mgd. This also assumes
that per capita demand will not change over the time period. Aggressive water conservation
activities that must accompany a transfer awarded could reduce demand upwards of 10% or
more, thereby reducing the maximum day water demands of the receiving communities. At the
moment, the Town of Winterville's per capita water use is the lowest of all the communities at
90 gpcd. Greenville's per capita use is currently at 120 gpcd.
18.1 The IBT Management Strategy was developed in 2007 as a significant component of the
Environmental Assessment (EA). The IBT Management Strategy is a balanced, managed
approach to the transfer of finished water to our neighboring communities. The Management
Strategy takes into account the use of banked water, the sale of finished water during off‐peak
periods, and the reduction of ground water supply due to the CCPCUA Rule. The IBT
Management Strategy was constructed to allow GUC and neighboring communities the
greatest flexibility in the purchase of water as well as the curtailment of service during peak
water demand or low flow in the Tar River.
14.3 At the same time GUC in Table 2‐3 stated that they have enough water plant capacity, but only
reflect a minimum withdrawal for the IBT transfer on these same days. Are we to assume that
Greenville can run easily at 100% of the plant rated capacity without any issues and that the
communities can reliably count on this minimum amount on the same day when their wells
cannot produce this increased demand?
16.4 The purchase of water from GUC, is for water currently permitted for withdrawal from the Tar
River. No additional Tar River withdrawal permits by GUC are to be requested or needed to
meet the obligations of GUC to supply water to Greene County. The contractual agreement
between GUC and Greene County is based upon a ninety percent availability factor. The
contract gives GUC the right to interrupt or curtail the supply of water to Greene County up to
ten percent of the time, or up to thirty‐six (36) days per year. This arrangement allows GUC to
curtail water to Greene County on days of peak demand during which time Greene County will
utilize their remaining 25% well capacity to meet their demand. Under this agreement GUC will
not need to increase its withdrawal permitting capacity from the Tar River not or in the future
as related to selling water to Greene county
Staff Response
Concerns about the available quantity of water that will be available for sale to these communities, as well as
concerns about how banked water will be managed, are addressed by GUC’s IBT Management Strategy. This
strategy was included in both the EA and the Petition; however, ARCADIS has developed a supplemental technical
memorandum to further illustrate the main components. This memorandum is included in Appendix 1, titled
“Explanation of IBT Management Strategy”. In this analysis, ARCADIS states the following:
A33
Environmental Management Commission
North Carolina Division of Water Resources
‐ 28 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Every community experiences minimum, average, and maximum day water demands throughout
the year. From year to year, the highs and lows in water demand will usually vary with season.
The perception is the maximum day demand occurs only in the hottest months of the year. This
perception is not valid every year. Water systems will experience maximum day demands at any
time during the year, including the coldest months.
To illustrate this concept, ARCADIS developed a diurnal curve based on 5 to 10 years of historical water use trends,
and projected this curve onto the average expected annual water demand for each community. The result is a
projected 2009 to 2030 water use trend for each water system. The purpose of these graphs is to illustrate the
typical high, average, and low daily water demands that could typically be expected by each water system. At no
time during the historic record do maximum day demands coincide for Greenville, Farmville, Winterville, or Greene
County.
Figure 1 in Appendix 1 illustrates what happens when the projected bulk purchase curves for each community are
“stacked” (e.g. added cumulatively) to show the total water treatment plant (WTP) demand though 2030. During
times when the demand exceeds 22.5 MGD (the capacity of the WTP) GUC will curtail water sales and the
communities will rely upon banked water to meet peak demands. The Purchase Agreement limits water
curtailment to a maximum of 10% of the year. According to GUC’s analysis, curtailment is not expected to occur
before 2018.
The analysis also states:
On an average day basis, Greenville Utilities will be able to sell water to each community entirely.
Greenville Utilities will also be able to sell water to a community if that community is experiencing a
maximum day. The maximum day for each community is not expected to occur on the same day (per the
aforementioned explanation).
However, if Greenville Utilities approaches a maximum day, the Water Purchase Agreements stipulate
that Greenville Utilities reserves the right to curtail water, if it is anticipated that WTP capacity may be
exceeded.
An important component of the IBT strategy is the management of banked water. DWR supports this water
banking concept where it is consistent with good management of the region’s water resources and subject to prior
review and approval of specific banking proposals. Many water systems throughout the Central Coastal Plain
Capacity Use Area (CCPCUA) utilize water banking as a means of meeting their required reductions. Although it is
correct that all of the Petitioners are planning to bank ground water by reducing pump rates as much as possible
during the early CCPCUA phases (banking will likely not be possible after 2015), there is no direct correlation
between the amount of water that might be banked and the amount of the IBT request. The amount of water that
might be banked by 2018 is an unforeseeable quantity. Similarly, it would be difficult to predict exactly when and
how much banked water will be used. As a result, it is essential that the banked water remain as a “savings
account” used by each community if and when supplemental water is required to meet peak demands. Therefore,
the total volume of the anticipated water bank was not subtracted from the applicant’s total IBT request.
The Hearing Officers recommended no changes be made based on these comments.
A34
Environmental Management Commission
North Carolina Division of Water Resources
‐ 29 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic E: Emergency Condition
Comment ID # Comment Text
19.2 GUC is asking for an emergency condition, but during an emergency (drought) would be the
time the River could least afford to lose the water
The Hearing Officers have chosen not to grant an emergency condition. G.S. §143‐215.22L(q) specifically outlines
the procedure by which water systems may request an emergency water transfer. Should GUC need such a
transfer, that request should be submitted to the Department in accordance with the applicable statutes.
§143‐215.22L(q) Emergency Transfers. – In the case of water supply problems caused by drought,
a pollution incident, temporary failure of a water plant, or any other temporary condition in
which the public health, safety, or welfare requires a transfer of water, the Secretary of
Environment and Natural Resources may grant approval for a temporary transfer. Prior to
approving a temporary transfer, the Secretary shall consult with those parties listed in subdivision
(3) of subsection (c) of this section that are likely to be affected by the proposed transfer.
However, the Secretary shall not be required to satisfy the public notice requirements of this
section or make written findings of fact and conclusions of law in approving a temporary transfer
under this subsection. If the Secretary approves a temporary transfer under this subsection, the
Secretary shall specify conditions to protect other water users. A temporary transfer shall not
exceed six months in duration, but the approval may be renewed for a period of six months by the
Secretary based on demonstrated need as set forth in this subsection.
A35
Environmental Management Commission
North Carolina Division of Water Resources
‐ 30 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC II: CONSERVATION
Many of the following comments express concern that conservation, explicitly stated as an important factor in
both the IBT statutes and the Central Coastal Plain Capacity Use Area (CCPCUA) rules, was not properly addressed
by the applicant in the EA or Petition. Some comments also state that specific conservation measures required by
the CCPCUA rules have not been implemented by the Petitioners.
Comment ID # Comment Text
4.12 Furthermore, all communities are required by the CCPCUA rules to adopt water conservation‐
based rate structures, implement conservation ordinances for irrigation, provide a retrofit
program for homeowners as well as an educational program and provide information to the
state regarding existing conservation measures and those to be implemented (NCAC 15A 2E
0.0502(d)(5)). Phone conversations with DWR staff reveal that such information has not been
supplied by these communities. Such information is crucial for the EMC to be able to make a
decision on the reasonableness of the IBT and whether or not conditions should be placed on
the certificate if the Petition is granted. The changes in 2007 to the Regulation of Surface Water
Transfers Act clearly reveal that the State is emphasizing the efficient use of water resources.
The Petition and EA submitted by GUC provides none of this critical information.
1.13 … as a matter of principle NCDWR should require vigorous conservation rate structures and
peak demand management in any area receiving an IBT. And the sword should cut both ways.
The area supplying the water should be required to adopt the same vigorous conservation rates
and peak demand management. The reason? Both would now be sharing the same water
resources. It is thus absurd for a utility to supply water from a common resource and have
disparate standard for allocation and use of that common resource. All users should abide by
the same rules.
2.2 As the population of eastern North Carolina continues to grow a strain will be placed on all
water resources. It seems logical to promote water conservation practices now. The reductions
in the withdrawal from underground sources should first be attained by reducing water usage
rather than by transferring water across miles.
3.3 Now is the time to address water waste as a condition of water transfer. There need to be
enforceable building/plumbing permit requirements (as well as environmental considerations)
that aggressively address the use and potential waste of our water resources for new homes,
businesses, industries and their eventual upgrade improvements. These requirements should
(must) be adopted and enforced by the local and county municipalities paid for by permit fees.
Incorporating an ongoing and far reaching educational process on the importance of this
resource and ways it must be protected and conserved must also be a part of this transfer
agreement.
3.4 Additionally, a stepped fee schedule for all water users in GUC's region must be implemented to
aid in the education and reduction of wasted water resources. A five level fee structure based
on amount of water used starting with a reasonable baseline use and climbing through
excessive use needs to be implemented. The monies generated by the excessive use fees will be
accounted for and expended in areas of education, retrofitting of household and business
fixtures with water conservation fixtures. This can be done through discount programs or out‐
right give‐a‐ways. This program in turn will reduce water waste and subsequently reduce water
bills, putting at least a temporary smile on the end‐users face.
4.11 Under the old rules, an applicant must provide information regarding the facilities to be used
for the water transfer, the proposed uses of the water to be transferred, the water
conservation measures to be used by the applicant and any other information deemed
necessary by the Commission. The EA failed to provide any information (except the short
paragraph below from GUC) regarding the source or receiving communities current and
planned water conservation measures. The only information provided was related to drought
management protocols. Useful data should include information on water rate structures,
presence or plans for retrofit programs, feasibility of reclamation projects, ordinances or
incentives for use of cisterns or other rain water harvesting practices, etc. 'Additionally, GUC
A36
Environmental Management Commission
North Carolina Division of Water Resources
‐ 31 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
and its wholesale customers strongly encourage the use of water saving devices. GUC is a
licensed member of the national "Water Use it Wisely" campaign. The Energy Services and
Public Information Offices incorporate water conservation messages into all communications.
This includes preparation of fact sheets, television and radio advertisements, print ads, and
billboards to provide local citizens with water conservation tips."
4.25 We also urge the EMC to consider conditions that seek to increase the long‐term water use
efficiency by both the receiving and source river basin communities. The IBT Petition includes
information on drought management response measures, but fails to include information on
long‐term efficiency measures. Conditions to address efficiency could include:‐ Implementation
of regional planning to ensure the most efficient management of the shared water resources in
both the source and receiving communities. ‐ Requirements that GUC and other wastewater
facilities in the receiving basins conduct a feasibility study and action plan for water
reclamation/reuse projects.‐ Plan for and implement strong water conservation programs and
activities with the goal of reducing customer water demand, including but not limited to:o
Home fixture retrofit programs o Requiring or incentivizing water harvesting practices (i.e.
cisterns) o Separate irrigation meters and pricing of irrigation water o Aggressive public
educational campaigns
7.1 Withdrawals from underground sources should first be addressed by reducing local water usage
rather than simply meeting demand by transporting water over long distances.
9.3 Should scarce water be diverted from the Tar River so that new sub‐divisions can create
expansive lawns? At a minimum, those communities requesting water should require their
residents to use landscaping alternatives as a part of a larger conservation program. There are
lawn substitutes for grass that tolerate light foot traffic and even moderate mowing.
20.5 Need for conservation
9.2 The folks in our region want to be good neighbors. In the event that an existing neighboring
community was experiencing a lack of suitable drinking water, one would expect assistance to
be forthcoming. However, if that neighboring community was expanding and using water in a
manner not consistent with good conservation practices, then one would expect questions to
be raised.
Staff Response
As previously stated, conservation is identified in both the IBT statutes and the CCPCUA rules as an important
component of both programs. NCGS §143‐215.22I(c)(3) states that any Petition for an IBT must include a
description of the conservation measures to be used by the applicant to assure efficient use of the water and
avoidance of waste.
The CCPCUA rules, 15A NCAC 2E .0504, are more specific in that they require water systems in the capacity use
area to develop a water conservation plan that includes the following elements. The rules require that each
community develop a schedule of implementation for any requirement that has not yet been met:
1. Adoption of a water conservation‐based rate structure, such as: flat rates, increasing block rates, seasonal
rates, or quantity‐based surcharges.
2. Implementation of a water loss reduction program if unaccounted for water is greater than 15%.
3. Adoption of a water conservation ordinance for irrigation, including such measures as: time‐of day and
day‐of‐week restrictions on lawn and ornamental irrigation, automatic irrigation system shut‐off devices
or other appropriate measures.
4. Implementation of a retrofit program that makes available indoor water conservation devices to
customers (such as showerheads, toilet flappers, and faucet aerators).
5. Implementation of a public education program (such as water bill inserts, school and civic presentations,
water treatment plant tours, public services announcements, or other appropriate measures).
6. Evaluation of the feasibility of water reuse as a means of conservation, where applicable.
A37
Environmental Management Commission
North Carolina Division of Water Resources
‐ 32 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
The Hearing Officers concur with the public comments that the importance of conservation is critical and a
requisite of a community requesting IBT water. Therefore they requested the Petitioners to develop, Table 1,
included in Appendix 3, which includes a summary of the CCPCUA requirements and how those requirements have
been met by each Petitioner.
Moreover, the Division of Water Resources has also agreed to begin requesting this information from all CCPCUA
Permit holders in January 2011. Any permit holder whose conservation measures fail to meet the minimum
program as described in 15A NCAC 2E .0502(d)(5)(A‐C) will be required to adopt measures meeting these
requirements or they will be issued an NOV. All water use conservation measures described in the CCPCUA rules
will have to be adopted by the permit holder before their next permit renewal. This means that the minimum
water conservation efforts recognized in the CCPCUA rules will be met as a condition of the permit. A memo from
the Division to the Hearing Officers detailing the above described efforts is included in Appendix 2.
Finally, the Hearing Officers have included the addition of a special condition to the IBT certificate that will not
allow the Petitioners to transfer water until the minimum program requirements described in NCAC 2E
.0502(d)(5)(A‐C) has been met.
A38
Environmental Management Commission
North Carolina Division of Water Resources
‐ 33 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC III‐ ANALYSIS OF ALTERNATIVES
The hearing officers received a number of comments on alternatives to the proposed transfer. Comments ranged
from general remarks on the sufficiency of the EA analysis, to specific opinions about the relative availability of
other water purchase options.
Subtopic A: Economic and Environmental Impact of Alternatives
Comment ID # Comment Text
4.3 While the EA does identify several alternatives to the proposed IBT, the discussion is woefully
inadequate to the task set forth in the applicable statutes and regulations. The overview
assigns a dollar amount to the financial cost associated with the construction of each
alternative. However, there is no discussion, evaluation, or modeling of environmental impacts,
the source basin.
16.5 Other alternative water supplies for Greene County are significantly more expensive. Failure of
GUC to obtain an IBT certificate will result in extreme hardship for the residents of Greene
County.
17.1 After many years of investigation and negotiation for an alternative water supply, Greenville
Utilities Commission, Greene County and the Town of Farmville contracted for the transfer of
water from Greenville Utilities Commission. The most economically, technically feasible
alternative with the least impact on the citizens of Farmville and Greene County was to obtain
their water supply from Greenville utilities Commission.
12.2 Because they will make money from selling Greenville's water to the communities of
Winterville, Farmville, and Greene County, I do not find it unreasonable that they could use
part of this money to build another pipeline. This parallel pipeline to the one drawing from our
river would return the treated wastewater from these communities back to our river and to us,
so our businesses, families, ECU, and visitors can continue prospering in Greenville
9.1 One of the major concerns that a number of individuals identified was that the proposed
transfer appears to be a one‐way flow of water from our area. In follow up comments, it was
said that if the water must be given, then a return of the waste water should be made
mandatory as a part of the agreement.
5.2 The Town of Winterville has explored several options as it prepares to meet the reductions
imposed by the capacity use area rules. Winterville has no local source of surface water
available to the Town and has therefore determined that the purchase of water from GUC is
the most economical and technically feasible engineering alternative.
Staff Response
Although the Petitioner’s Environmental Assessment (EA) did include an analysis for several water supply options,
ARCADIS developed a supplemental evaluation to answer questions raised during the comment period. This
analysis is included in Appendix 4. The alternatives include:
1. Development of an independent surface water source on Contentnea Creek
2. Development of an independent ground water source
3. Purchase of finished water from the Neuse Regional Water and Sewer Authority (NRWASA)
4. Purchase of finished water from the City of Wilson
5. Purchase of finished water from the Greenville Utilities Commission
A39
Environmental Management Commission
North Carolina Division of Water Resources
‐ 34 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
All of the above alternatives had been previously identified in either the Environmental Assessment (ARCADIS,
2008), or the Preliminary Engineering Report – Alternative Water Supply Evaluation for Greene County and
Farmville (McDavid and Associates, 2004). Appendix 4 provides estimated capital costs and expected usage rates
for all alternatives, as well as a matrix of environmental impacts. The metrics evaluated for the environmental
analysis include the following:
Interbasin Transfer
100‐Yr Floodplain
Wetlands
Stream Crossings
303(D) Listed Waters
Forestland
Anadromous Fish Spawning Areas
Federal Or State Owned Lands
State Or Municipal Parks
High Quality/ Outstanding Resource Waters
Hazardous Waste Facilities
Historic National Register Districts/
Structures
NPDES Sites
Non‐discharge systems
Landfills
Permitted Animal Operations
Natural Heritage Occurrence Sites
Significant Natural Heritage Areas
Schools, Libraries, or Churches
Land Managed for Conservation, Open
Space, and Recreational Lands
The analysis shows that all of the alternatives, with the exception of those requiring the development of additional
ground water wells, would require an interbasin transfer certificate for at least one of the Petitioners (either
Farmville, Winterville, or Greene County). However the ground water alternatives were not identified as a
sustainable due to the potential for the EMC to designate additional Capacity Use Areas in the future.
The reservoir alternative has the greatest environmental and economic impact. It is also likely that the
construction of a reservoir in Greene County would not be feasible due to technical, environmental, and permitting
complications.
The option of returning water to the source basin was evaluated in the EA. This option was excluded as being
technically infeasible. Wastewater service in the area is not as widespread as water service. There is no
countywide, centralized wastewater treatment plant (WWTP) in Greene County. While there are three small
WWTPs (Snow Hill WWTP, the Hookerton WWTP, and the Maury Sanitary Land District WWTP), residents in
unincorporated areas rely primarily on septic systems. Costs for the construction of a countywide collection and
treatment system were estimated at over $150 million. In Pitt County, wastewater is treated at the Farmville
WWTP, the Contentnea Creek WWTP, and the GUC WWTP. Wastewater from the Town of Winterville is currently
treated at the Contentnea Creek WWTP. According to the 2008 EA, Winterville has had discussions with GUC
concerning future wastewater service, but there are no immediate plans to proceed with this option. If this option
were pursued in the future, it would return a portion of the transferred water to the Tar River Basin.
Of all the identified alternatives, the only viable options were identified as the purchase of finished water from
either NRWASA, Wilson, or GUC. All of these options would utilize existing water treatment plant capacity and
have comparable environmental impacts. Also, as previously stated, all of the purchase alternatives would require
that at least one Petitioner receive an interbasin transfer certificate. Of these options, the purchase from GUC was
identified as being the most economically practicable.
The Hearing Officers recommended no changes be made based on these comments.
A40
Environmental Management Commission
North Carolina Division of Water Resources
‐ 35 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic B: Feasibility of Water Purchase from Neuse Regional Water And Sewer Authority (NRWASA)
Comment ID # Comment Text
1.2 Water is available from the Neuse for the communities in that basin. In fact if the proposed IBT
were approved water lines from the Tar would pass by lines from the Neuse providing water to
communities in what is partially a turf war for utility growth. Feigned statements of
cooperation and redundancy mask these turf wars including lawsuits over the right to serve
select communities (Bell Arthur Rural Water District vs. GUC, as an example). NC Water Supply
Branch should not facilitate these battles. Let GUC stay within its own basin and mandated
mission to provide for the needs of Greenville.
2.1 According to the map water from GUC and the Tar River is being piped to Snow Hill and water
from Kinston and the Neuse River Basin is being piped to Eastern Pines. The map itself revealed
the flaws in this plan. It doesn't take much to realize that it is inefficient to pipe water over long
distances rather than shorter ones. There is an increased chance of loss by leakage and an
increased need of additional purification for safety. This also makes economical sense.
4.5 For example, the alternative briefly mentioned in the EA for the receiving basins to purchase
water from the Neuse Regional Water and Sewer Authority does not provide an analysis of
cost, only that the costs would be "prohibitive."
7.2 Additionally it would appear that Greenville Utilities is willing to sell surface water cheaper than
Neuse Regional WASA. This, if nothing else, is not a satisfactory reason for approving IBT.
8.1 The transfer of GUC water to Greene County does not make sense since the Neuse Regional
WASA is in the best position to supply those needs and then there is no IBT.
8.2 Farmville should likewise get it's water from NR WASA.
8.3 NR WASA was created to supply these needs but apparently politics is playing out with the
requesters familiarity with GUC and probably lower cost water.
The Neuse Regional Water and Sewer Authority is a cooperative partnership of water and sewer service providers
that was formed in 2000. Current members are the Town of Ayden, the Bell Arthur Water Corporation, the Deep
Run Water Corporation, the Eastern Pines Water Corporation, the Town of Grifton, the City of Kinston, the North
Lenoir Water Corporation, and the Town of Pink Hill. These systems have collectively constructed a water
treatment plant and large distribution mains at the cost of $144 million dollars. The Authority’s water source is
located in the Neuse River Basin while the users are located throughout the Trent River, Neuse River, Contentnea
Creek, and Tar River Basins. This water use constitutes an interbasin transfer; however NRWASA has not yet
obtained an IBT certificate.
Many of those commenting have noted that the Neuse Regional Water and Sewer Authority (NRWASA) may also
be in a position to provide water to the Petitioners. Some comments also state that a purchase by Farmville and
Greene County from NRWASA would not create an interbasin transfer; however that is not the case. NCGS §143‐
215.22G defines the Contentnea Creek Basin as a unique sub‐basin to the Neuse Major River Basin (Figure 3). An
interbasin transfer certificate is required for any transfer between designated basins, even if one basin is a sub‐
basin to the other.
Greene County and Farmville first evaluated the purchase of water from NRWASA in a 2004 Preliminary
Engineering Report titled, Alternative Water Supply Evaluation for Greene County and Farmville (McDavid and
Associates). The alternative was also discussed in GUC’s Environmental Assessment, the Petition, and the
supplemental evaluation by ARCADIS that was developed during the public comment period (Appendix 4). In each
of those reports the cost of required contractual commitments, necessary internal improvements, plus a
proportional share of the $144 million facility resulted in a usage rate 3 times higher than GUC’s. Given this
relatively high economic cost and the fact that the environmental impacts of both options are comparable (as
discussed in the previous section), the purchase from NRWASA was not chosen as the selected alternative.
A41
‐36‐
Figure 3.
Designated Interbasin Transfer River Basins
As defined in G.S. §143-215.22G
BASIN NAME BASIN NAME BASIN NAME
1-1 Broad River 7-1 Little Tennessee River 15-1 Tar River
7-2 Tuskasegee River 15-2 Fishing Creek
2-1 Haw River 15-3 Pamlico River & Sound
2-2 Deep River 8-1 Savannah River
2-3 Cape Fear River
2-4 South River 9-1 Lumber River 16-1 Watauga River
2-5 Northeast Cape Fear River 9-2 Big Shoe Heel Creek
2-6 New River 9-3 Waccamaw River 17-1 White Oak River
9-4 Shallotte River
3-1 Catawba River 18-1 Yadkin River
3-2 South Fork Catawba River 10-1 Neuse River 18-2 South Yadkin River
10-2 Contentnea Creek 18-3 Uwharrie River
4-1 Chowan River 10-3 Trent River 18-4 Rocky River
4-2 Meherrin River
11-1 New River
5-1 Nolichucky River
5-2 French Broad River 12-1 Albemarle Sound
5-3 Pigeon River
13-1 Ocoee River
6-1 Hiwassee River
14-1 Roanoke River
A42
Environmental Management Commission
North Carolina Division of Water Resources
‐ 37 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Subtopic C: Feasibility of Water Purchase from City of Wilson
Comment ID # Comment Text
14.5 Section 5 of the IBT Petition "Alternatives to Proposed Transfer" never mentions the City of
Wilson as a viable alternative for both Greene County and Farmville. Wilson had discussions in
2003 with both, had the water available at a reasonable cost, and is in the Neuse Basin.
Staff Response
Similar to the evaluation of a water purchase from NRWASA, the alternative of purchasing water from The City of
Wilson was first evaluated in a 2004 Preliminary Engineering Report titled Alternative Water Supply Evaluation for
Greene County and Farmville (McDavid and Associates). This alternative is further discussed in Appendix 4,
Environmental and Economic Impacts of Water Supply Alternatives (ARCADIS).
Wilson’s surface water source is in the Contentnea Creek Basin; therefore, this sale would not have required an
interbasin transfer certificate for Farmville and Greene County. However, a certificate would have been required
for the Town of Winterville.
One important factor in evaluating a purchase from Wilson is the fact that Wilson required a one time capacity
charge based on $2.50 per gallon per day demand, estimated at $12.5 million for 5 MGD. This capacity charge is in
addition to a usage rate comparable to existing Wilson customers (presently $4.52 per 1,000 gallons for residential
users). Due to the high relative cost of this purchase alternative, comparable environmental impacts to a purchase
from GUC, and the fact that this alternative would have also required an IBT certificate for Winterville, a purchase
from Wilson was not chosen as the selected alternative. Further detail on this option is presented in Appendix 4.
The Hearing Officers recommended no changes be made based on these comments.
A43
Environmental Management Commission
North Carolina Division of Water Resources
‐ 38 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC IV: MITIGATION OF SECONDARY AND CUMULATIVE IMPACTS
The IBT statutes state that an applicant must establish and the Commission must conclude by a preponderance of
the evidence that: (1) the benefits of the proposed transfer outweigh the detriments, and (2) the detriments have
been or will be mitigated to a reasonable degree. The statutes also allow the Commission the ability to include any
special conditions to ensure that detrimental impacts will be mitigated.
The Hearing Officers received the following public comments pertaining to this factor.
Comment ID # Comment Text
4.7 The EA wholly dismisses the need for evaluation of secondary and cumulative impacts from growth
since the IBT is designed to only replace the lost ground water resource due to the CCPCUA. The EA
states that "significant growth in these areas is not a component of this project or a reason for
developing the interbasin transfer request. " IBT Petition, pp 4‐1. DWR questioned this dismissal of
secondary and cumulative impacts associated with growth that is a direct result of the transfer of
water in their comments on the draft EA (EA Response to Comments, pp: 2/12‐2/13, February
1,2008). The comments stated: The document dismisses cumulative and secondary impacts
associated with growth by repeatedly stating that the project is primarily a water replacement project
and significant growth is not a component of this project or a reason for developing the IBT request. It
is true that they are being forced to switch to surface water and that initially the volume of surface
water matches the volume of ground water; however, over time the volume of water increases due
to growth projections that the communities would have supported with an untapped volume of
ground water. On page 4‐2 it states that "these communities will be unable to compensate for the
reduced ground water withdrawals for predicted growth to 2030': There appear to be pockets of
significant growth and, without the additional water, this growth could not be supported. The
Executive Summary states that growth is modest at 1 to 3 percent in some communities. However, :
Section 2.2 gives growth rates of from 11 to 50 percent for Winterville, Greene County had a 25
percent growth rate from '90 to '06; although the overall growth rate of the county may be 1 percent,
pockets of higher growth may occur, e.g. near the Global Transpark. The document does not provide
the percent growth for Greenville, but from the numbers provided it could be 45 percent from '05 to
‘30. Comments to draft EA by DWR (on file with DWR) The applicant responded by saying that the
growth would occur in these communities with or without the IBT, therefore assessing the
environmental impacts is unnecessary. The communities are required to reduce their ground water
withdrawal due to the CCPCUA rules. Without a new source of water, either from the Neuse River
Basin or from GUC, the growth could not be sustained. The applicant dismisses all other alternatives
as viable options, therefore growth would not occur if the IBT were to be denied. Therefore, the
applicant must provide detailed information on the secondary and cumulative impacts associated
with this growth.
4.2 SEPA requires the agency to include a review of methods "proposed to mitigate or avoid significant
adverse environmental impacts" from the proposed transfer. 1 N.C. Admin. Code 25.0502 (3);. The EA
fails to include any meaningful discussion of mitigation measures, instead providing a review of land
use planning regulations and ordinances. Appropriate measures to mitigate, i.e., lessen, the
environmental impacts would include, for example, returning treated wastewater to the source basin,
implementing aggressive water conservation measures, or detailing measures that would be taken to
protect aquatic life in the source basins during times of drought.
4.9 Another example of the inadequacy of the secondary and cumulative impacts review concerns
threatened and endangered species. The EA states that threatened and endangered aquatic species
are present in both the receiving and source basins but does not address the impacts. The EA must
correct its review of cumulative and secondary impacts to include the impacts to these species from
growth that would be induced by the IBT.
1.10 In Greene County the development and growth is exemplified by proposals such as "Cutter Creek."
Cutter Creek is a sprawling golf course retirement community focused upon large, irrigated lots, and
private vehicular transportation to Raleigh and Greenville for employment, cultural opportunities and
health care. It exemplifies an unsustainable community dependent upon subsidies such as water
supply from the Tar River Basin.
3.2 We're not opposed to controlled growth in general but there must be aggressive controls on how
A44
Environmental Management Commission
North Carolina Division of Water Resources
‐ 39 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
much growth and how that associated water will be used.
Staff Response
Section 7 of GUC’s Environmental Assessment is devoted to discussing mitigation. The above comments state that
the mitigation discussion included in the EA is insufficient; however, all of the specific points mentioned in the
comments are addressed in the EA. Comments note that an acceptable discussion of mitigation should include:
1. Returning treated wastewater to the source basin
2. Implementing aggressive water conservation measures
3. Detailing measures to protect aquatic life during drought
These measures, discussed in the EA and previous sections of this staff response, are summarized as follows:
Return of Wastewater
In discussing the alternative of returning wastewater to the source basin, the EA states that the wastewater
collection system for the service area is decentralized (Section 4.4 of the EA). Although there are 3 small WWTPs in
Greene County, most of the County’s residents currently rely on septic systems. The EA estimates the cost of a
centralized collection system, WWTP and discharge line to the Tar River Basin at over $150 million. The EA also
estimates the cost to pump wastewater from the Farmville WWTP in the Contentnea Creek Basin to the Tar River
Basin at $20 million. Town of Winterville has had discussions with GUC concerning future wastewater service, but
there are no immediate plans to proceed with this option. Winterville’s wastewater is currently discharged to the
Contentnea Creek WWTP (Neuse River Basin).
Water Conservation
The CCPCUA rules require that communities implement very specific conservation measures. These measures
include adoption of a conservation‐based rate structure, adoption of a conservation ordinance for irrigation,
implementation of a retrofit program for indoor conservation devices, and the implementation of a public
education program. The rules also require water systems to evaluate the feasibility of water reuse as a means of
conservation. As previously discussed, the hearing officers have included a special condition to the IBT certificate
that full compliance with these requirements be met before the Petitioner may move water under the IBT
certificate.
Water Use During Drought
Greenville Utilities Commission included its Water Shortage Response Plan (effective July 29, 2008) in the
Environmental Assessment. The purpose of this plan is to define a set of triggers and actions to occur during
droughts or other water shortages. The actions range from voluntary water conservation (during a Stage 1 alert) to
requiring commercial and industrial customers to reduce water use by a minimum of 50% (during a Stage 3
Emergency).
Other mitigative measures that are discussed in the EA include:
Existing land use planning and environmental resource protection initiatives
Existing zoning ordinances
Existing open space plans/initiatives
Greenways and riparian buffers
Existing greenway plans
Existing erosion and sedimentation controls
Existing stormwater controls programs and impervious surface limitations (including compliance with
Phase I and II stormwater rules and the Tar Pamlico Stormwater Rule)
Existing floodplain development regulations
Existing water shortage response plan
A45
Environmental Management Commission
North Carolina Division of Water Resources
‐ 40 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
In addition a, a drought management plan is required to be included as a component of the certificate.
As previously discussed in this staff report, approximately 77% of the IBT request could be considered a direct
replacement of water lost due to the CCPCUA rule through 2018. Consequently, it could be interpreted that the
remaining 23% is to sustain growth through 2030. The hearing officers have determined that it would be
appropriate to require the Petitioners to adopt controls to mitigate unforseen impacts, due to this growth, before
they may begin transferring water.
All communities in the Tar Pamlico and Neuse River Major Basins are subject to nutrient management strategies.
Both the Tar Pamlico and Neuse Nutrient Strategies have requirements for wastewater discharges, agriculture,
buffers, and stormwater management. All of the requirements, except those involving the development of a
stormwater program, are applicable on a basin‐wide basis. However, the stormwater program requirements only
apply to those local governments of a certain size, density, or estimated impact. Both Pitt County and Greenville
are required to develop stormwater programs under the Tar Pamlico Nutrient Strategy. Farmville and Greene
County fall below the thresholds for development of a stormwater program under the Neuse Nutrient Strategy.
Similarly, these governments do not fall under the stormwater phase II program due to their population and rural
nature.
The Hearing Officers have determined that an appropriate mitigative measure, above what these communities are
already required to do under the Tar Pamlico and Neuse Nutrient Management strategies, is the implementation
of Phase II post‐construction stormwater controls. The intent of this measure is to control any unforeseeable
impacts due to growth that may occur as a result of the transfer. As previously stated, Pitt County (including
Winterville) and Greenville are already required to develop stormwater programs consistent with the Tar Pamlico
Nutrient Strategy. This certificate requirement would primarily impact Greene County and Farmville. The Hearing
Officers have determined that implementing post‐construction stormwater controls in these systems would serve
to put in effect the most impactful control measures while not being overly burdensome to a small, rural water
system. The certificate condition will read as follows:
No individual unit of local government may receive surface water regulated under this Certificate unless the local
government maintains, throughout its jurisdiction, requirements that are at least as stringent as the Division of
Water Quality’s Phase 2 post‐construction stormwater controls or the post‐construction stormwater controls of
the Universal Stormwater Management Program (“USMP”), for all new development that disturbs more than one
acre of land, including those projects that disturb less than one acre of land but are part of a common plan of
development or sale that disturbs more than one acre of land.
Appendix 5 to this staff response includes a memo detailing which of the above mitigative measure have already
been implemented by each of the Petitioners.
A46
Environmental Management Commission
North Carolina Division of Water Resources
‐ 41 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC V: IMPACTS TO THE TAR RIVER
During the public comment period, a number of comments were submitted on the scope and results of the
modeling analysis performed by the Petitioners for the EA. Additional comments focused on the potential impact
to aquatic life.
Comment ID # Comment Text
6.7 The flows at the Tarboro gage upon which the predicted flows at Greenville were based are not
representative of those that will occur in the future. The analysis in the EA used the flows
recorded at the USGS Tarboro River at Tarboro gage (Gage No. 02083500) from 1931 through
2007 (EA, Appendix B, page 1). The flows recorded at the gage reflect the cumulative impact of
all the withdrawals and discharges upstream of the gage as well as the regulation resulting from
the operation of the Rocky Mount's Tar River Reservoir. Although at this time it is not known
definitively, we suspect that the operation of the reservoir has the largest impact on the gage
readings. The Tar River Reservoir has been in operation since 1971. Thus, the gage record
reflects essentially natural, i.e., unregulated, flows for the period from 1931 thru 1970, and
regulated flows thereafter. This fact was acknowledged in the EA (Appendix B, page 22). The
operating protocol for the reservoir has changed several times since 1971. Rather than including
the reservoir in the hydrologic model explicitly and applying the current operating protocol
consistently over the entire record, including the period prior to 1970, the analysis used the
gage record "as is." The justification for this approach appears to be that because "Reservoirs
such as Rocky Mount's often augment low flows in rivers because they store water from higher
flow periods and release it over extended lower flow periods" (EA, Appendix B, page 22), the
lower unaltered flows in the record prior to 1970 lead to a conservative result. That is, because
there were flows in the record prior to 1970 that are lower than the current minimum flows, the
substitution of the required minimum flows for the lower, unaltered, flows would result in even
less impact than shown. However, the magnitude of flows alone does not prove this hypothesis.
The timing, frequency, and duration of low flows are equally important, and they have not been
considered. The currently‐approved water shortage response plan for the Tar River Reservoir
allows for discharges to be reduced incrementally to 60 cfs during the course of a drought. This
policy has been invoked only three times since the mid‐1990s. Thus, the statement in the EA
that "the hydrologic model reflects the impacts of the Rocky Mount operating rules and
minimum flows that have been in place over the past 36 years" (EA, Appendix B. page 22) is true
for only a very small portion of the record used for the analysis. Also, flows recorded early in the
early stages of the 2007108 event are not representative even though the current water
shortage response plan was in place because the Tar River below Tar River Reservoir gage (Gage
No. 02082506), upon which the release from the reservoir is based, was out of calibration. As a
result, for a period of approximately a month, rather than releasing 60 cfs, as intended, the
actual release was approximately twice that much. The reservoir releases, of course, are
captured by the Tarboro gage. Thus: at least for a portion of the drought of record, the flows
recorded at the Tarboro gage are higher than intended and not representative of system
operations.
18.2 The hydrologic modeling effort used empirical flow data from WSGS gauging stations that
spanned a 76 year period of record. The hydrologic analysis considered carefully the General
Statute provision that all withdrawals and transfers in the source basin not be impacted to the
degree existing uses would be impaired (at the time of the 18T Petition). To meet these
requirements, fourteen modeling scenarios were developed: six modeling scenarios addressed
the hydrologic effects upstream of GUC's raw water intake, and eight modeling scenarios
addressed the hydrologic effects of the proposed transfer downstream of the GUC Wastewater
Treatment Plant (WWTP). The scenarios included current and future (2030) water withdrawal
conditions for no IBT, the average day IBT, the maximum day IBT, and a hypothetical scenario
where twice the proposed transfer was effectively removed from the Tar River.
18.3 The City of Rocky Mount's operating rules were considered and are reflected in the hydrologic
analysis. The analysis was based on actual flows at Tarboro, which reflect approximately 40
years of conditions prior to the existence of the Rocky Mount reservoir and 36 years of data
A47
Environmental Management Commission
North Carolina Division of Water Resources
‐ 42 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
since reservoir operations. In addition, the analysis considered allowed modifications to the
Rocky Mount's Drought Management Plan in 1993,1999,2002, and 2007.
18.4 The results of the hydrologic analysis were presented relative to the flow duration curves
developed for the Tar River. The impact of each scenario was compared against river flows as
low as 80 percent of the 7Q10 (87.2 cfs). The worst‐case modeling (twice the proposed IBT
amount) scenario revealed a 0.8 percent impact in 2030 compared to the 2030 scenario without
an Interbasin transfer. For comparison, the maximum IBT scenario resulted in a 0.5 percent
impact in 2030 compared to the 2030 scenario without an Interbasin transfer. The EA concluded
that the hydrologic analysis calculations demonstrated that the requested IBT amount will have
a negligible impact on the Tar River.
4.27 During the comment extension period, we also had time to further review the hydrologic study
done by Entrix for GUC and to consult with a hydrologist about its validity. After further review,
we are concerned about the validity of the 7Q10 value that was used in the analysis and
whether or not this is a relevant statistic for the purposes of determining flow changes as a
consequence of the IBT over a one year period. We would have liked to see how this value was
derived.
4.28 Furthermore, it appears that the flow duration curves that GUC relied upon to determine no
significant impact do not reveal the temporal nature of what is actually occurring in the river
over the short‐term. Low‐flow values that may occur over a significant period of time (for
example 1‐2 month time period) would be masked by such a long‐term analysis. It would be
more helpful to see the minimum/maximum percent changes in flow over given periods, such as
a one year period.
6.10 Flow duration curves are, at best, an incomplete metric of impact. Flow duration curves present
the fraction of time that flows are above (or below) some value. They are prepared by sorting
the flows and computing the percentile associated with each flow. Thus the lowest flow in the
record is equal to or exceeded 100 percent of the time, the median flow is exceeded 50 percent
of the time, etc. Flow duration curves can be prepared either for the whole year, in which case
all flow data are included in the sort, or, as was done in the EA, for shorter periods, such as a
month. To prepare the flow duration curve for July, for example, if there are 50 years in the
record, there are 31‐ 50 values that go into the July flow duration curve. The problem arises
because flow duration curves do not account for the temporal variability of flows. This is true
even if the curves are prepared for a period shorter than one year. To continue the example
from above, if there are 50 values of 20 cfs in the July data, and every other value is greater
than 100 cfs, the same flow duration curve will result whether the 50 values of 20 cfs occur one
in each year or all in two years. The potential impact to the stream of the two scenarios,
however, could be very different. In order to fully assess the impact of altered streamflow
regimes, one must also examine the frequency and duration of low flow periods. Looked at
another way, based on the flow duration curves, the applicant concludes that flows will be
lower than 109 cfs (the pre‐IBT 7Q10) on average, 4.7 days per year without the IBT and 6.4
days with the maximum IBT (EA, Table 6‐3, page 6‐7). Again, this metric does not tell the whole
story because the frequency, timing, and duration of the extra 127 days (1.7 extra days per year
times 76 years) below 109 cfs are not reported. The impacts to the stream will likely be very
different if all those days occur in one or two years versus being distributed over 20 years. These
comments do not address the appropriateness of using comparisons of the 7Q10 with and
without the IBT as a basis for determining impact. The 7410 is a relevant statistic for
unregulated rivers. Where, as here, the river is regulated, the statistic is much less useful
because the same number can result from very different flow sequences. For example, as noted
above, the pre‐IBT 7Q10 was determined to be 109 cfs. That is, the lowest weekly average flow
in 10 years was 109 cfs. However, the 7Q10 would also be 109 cfs if flows of 109 cfs continued
for three months. Dams, such as Rocky mount's with fixed minimum releases have exactly this
type of effect.
6.6 The EA further explains the decision not to consider impacts on the Tar River Reservoir as
follows: The hydrologic analysis and modeling assumed that interbasin transfers at Greenville
would have no impact on operations of the Rocky Mount reservoir 70 river miles upstream. The
only way that the IBT could affect upstream operations would be if there were to be an
A48
Environmental Management Commission
North Carolina Division of Water Resources
‐ 43 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
approved change in Rocky Mount's permitted withdrawal and operating conditions. GUC has
not made such a request and such as (sic) operational change has not been assumed in the
hydrologic analysis and modeling." (EA Appendix C,page 10112.) However, Rocky Mount was
extremely hard hit by the drought of 2007‐08 and, as a result, is considering a modification to its
water shortage response plan. For Rocky Mount, as for many municipalities in North Carolina,
the drought of 2007108 was an unprecedented event. Whereas Rocky Mount had been able to
negotiate the drought of 2002with relative ease, the event of 2007‐08 was different. The Tar
River Reservoir, Rocky Mount's sole source of water, dropped to10 percent of usable storage.
To avert what appeared to be an impending crisis, in addition to activating the drought
management plan1, emergency connections were made to Wilson and Tarboro. At times, and
with the permission of the Division of Water Resources, releases from the reservoir were cut to
30 cfs, compared to a minimum of 60 cfs allowed in the approved water shortage response
plan. An aerial reconnaissance of the Tar River upstream of the reservoir revealed previously
unknown upstream withdrawals whose aggregate withdrawals exceeded the City's demand.
Thus the storage in the reservoir was falling as if there were two cities the size of Rocky Mount
withdrawing water. As a result of this experience, Rocky Mount intends to update its
probability‐based drought management plan. Thus, the "operational change" that was assumed
in the EA not to be a possibility is exactly the type of change that Rocky Mount is, in fact,
considering. This fact was apparently not known to GUC during preparation of the EA, possibly
because Rocky Mount was not consulted.
6.8 Further, there is no information in the EA as to the timing, frequency, or duration of low flow
occurrences prior to dam construction as compared to the timing, frequency, and duration, post
dam construction, of the periods when the releases from the dam were 80 cfs. It is highly likely
that the impacts to the aquatic environment from, for example, a 30 day period of flows of 20
cfs embedded in a four‐month period in which flows were below 80 cfs are very different from
those associated with a six‐month period of a constant flow of 80 cfs.
6.9 Finally, the period of record analyzed (October I, 1931, through September 30,2007) did not
include the lowest flow 7‐day period in the record, which occurred in October 2007.
20.3 Concerned about climate change
10.1 I have owned riverfront property on the Tar River in Greenville, N.C. for the last ten years. Over
those ten years I have witnessed extreme variation in the size and strength of the water flow in
the Tar River. Frequently in the summer months I have observed the water flow dwindle quite
dramatically. The river, which is sometimes as wide as a six lane highway, has dwindled on at
least one occasion to the size of a creek I could have hopped over. I am not claiming expertise in
these matters, but common sense tells me water should not be diverted from a river that
regularly experiences such wide variations. What has happened before will undoubtedly happen
again, and if water has been diverted when Greenville desperately needs it, then what? Will it
have to be re‐diverted back to the Tar when people in other areas have come to rely on it?
Seems better to find other. more permanent solutions for Farmville, Winterville and Greene
County
11.2 [This] region… recently experienced a reported river flow of only 50 million gallons per day
downstream to Greenville. According to my information the summer use of water from the Tar
River for Greenville alone can amount to 16 million gallons per day. The math is troubling for
the health of communities that depend on the Tar River for their water and for the ecological
health of the river system itself
12.1 I am deeply concerned that 10 years from now the above sea level portions of the Neuse, Tar,
and Roanoke Rivers will only be navigable after a good rain because our public trust waters will
be injected into pipelines and aquifers to be distributed by huge water systems
19.1 It's already hard to navigate the Tar River‐ concerned that it will get worse
20.1 Impact of the IBT may be low now but will increase in 50 years.
20.2 Salt levels in Tar are rising up to Greenville
3.1 We are not in favor of intra‐regional water transfer agreements as they are permanently
divisive. They tend to make enemies of neighbors and they, in this case, stifle the growth
A49
Environmental Management Commission
North Carolina Division of Water Resources
‐ 44 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
potential for eastern Beaufort County by reducing the available water supply to this region.
4.4 In addition, the EA fails to evaluate the costs in terms of lost revenues to source basin water
suppliers that may be expected to impose restrictions on water use for longer time periods as a
result of the proposed transfer of water.
6.1 As a result of the drought of 2007/08, Rocky Mount intends to review and, if necessary, update
its drought management plan. The review will be conducted following the completion of DWR's
Tar River Hydrologic Model, which is anticipated in early 2011. If revised, Rocky Mount will seek
approval of the updated plan from DWR. A revised drought management plan may result in a
low‐flow regime at Tarboro that is different from the one on which the IBT FONSI was based.
6.12 In conversation with our consultant, the GUC's consultants indicated that because some of the
modeling scenarios requested by DWR essentially "double count" demand, this provides a
safety factor that will assure no impact to Rocky Mount. While this assertion may be accurate, it
cannot be established from the analysis in the EA. The best way to insure compliance with the
statute is to use a basin‐wide hydrologic model for the analysis AND to involve others in the
basin in the decision‐making. The updated Tar River Hydrologic Model will be such a basin wide
model and will be developed in consultation with stakeholders throughout the basin. Thus, the
model will form an agreed‐upon basis upon which all parties can evaluate the impacts of the
proposed IBT. Following its completion, Rocky Mount will know whether a modification to its
water shortage response plan is, in fact, needed. In addition, Rocky Mount and other users in
the basin, including those who represent environmental interests, will be able to accurately
evaluate the impacts of the proposed IBT in the context of a basin‐wide water supply plan.
6.2 Rocky Mount is concerned that the analysis done to support the FONSI is not adequate to
determine whether there could be conflicts between its revised drought management plan and
the IBT.
6.5 IBT statute requires that the applicant examine the present and reasonably foreseeable future
detrimental effects on the source river basin. N.C.6.5. 53‐21 5.221(0(2). The City of Rocky Mount
is concerned that the GUC looked only at the potential impacts on an approximately mile reach
of the Tar River below Greenville, as acknowledged in the Environmental Assessment, and not
on the Tar River Reservoir.
18.6 The EA critically evaluated the current and future water uses in the Tar River Basin under the
current hydrologic conditions. Furthermore, the proposed IBT was developed such that GUC has
the flexibility to curtail water during peak demand and fully utilize the ground water resource (in
the form of banked water) to the extent practicable. In effect, we have already placed operating
conditions on ourselves to manage this proposed IBT in the best interest of our customers, our
neighbors, and the environment. We strongly feel that the worst‐case modeling scenario
(effectively twice the proposed Interbasin transfer) fully addresses the ultimate impact to the
Tar River as a result of this proposed transfer.
19.4 Concerned about impact on striped bass and mussels.
2.3 Humans are not the only species in these river basins. I value the wildlife in eastern North
Carolina. The opportunity to paddle these rivers and creeks are activities that I cherish.
Transferring water between basins may have unanticipated and negative impacts on native
species decreasing their abilities to survive.
7.3 And lastly ‐ adversely effecting water resources impacts more than humans. This area has a rich
diversity that has evolved precisely because of the abundance of water. Removing water from
the Tar River Basin can only serve to negatively impact surrounding flora and fauna.
11.1 The potential damage of this proposed transfer from the Tar‐ Pamlico River system includes
wetlands, habitat, the intrusion of salt water upstream, and the loss of a viable water supply
20.4 Concerned about impact to wetlands
18.5 Even though the hydrologic modeling results demonstrated negligible impact on the Tar River,
the tidal influence at our intake provides another opportunity to ameliorate the effect of low
flow. The tidal influence results in a reverse flow direction during low flow periods. This
phenomenon creates a reservoir effect that helps maintain water over our intake pipes. GUC is
in a unique position whereby we have two opportunities to withdraw water from the river
A50
Environmental Management Commission
North Carolina Division of Water Resources
‐ 45 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
where most other water treatment plants have only one opportunity. This tidal effect
phenomenon is part of the reason why we feel confident that we can reliably provide water to
neighboring communities who require regional solutions to solve critical water supply needs.
4.24 The first condition Rocky Mount proposed is that the certificate be revisited upon completion of
the Tar River Hydrologic Model. PTRF and SELC strongly support this recommendation and
suggest that the EMC incorporate similar language as was used in previous IBTs. In the CMU and
Cary/Apex IBT certificates, the EMC included the condition below: "The Commission notes that
future developments may prove the projections and predictions in the EIS to be incorrect and
new information may become available that shows that there are substantial environmental
impacts associated with this transfer. Therefore, to protect water quality and availability and
associate benefits, modification of the terms and conditions of the certificate may be necessary
at a later date." If the EMC moves forward with the GUC IBT, the final certificate should include
similar language triggering a reopening of the certificate based on the Tar River Hydrologic
Model.
6.11 The City of Rocky Mount requests that any IBT certificate issued to the GUC include a condition
allowing the Certificate to be reopened following completion of the Tar River Hydrologic
Modeling and Water Resource Plan if the results indicate that the approved IBT impinges upon
Rocky Mount's ability to modify its water shortage response plan. Rocky Mount is concerned
that, if approved, the demand to transfer water outside the basin could influence the decision
to approve a requested change in the release protocol for the Tar River Reservoir. To guard
against this possibility, in our comments dated December 1, 2009, Rocky Mount proposed
several conditions that might be included in the IBT certificate. Upon further reflection, Rocky
Mount now considers that a condition that would allow, upon the approval of the EMC, the
certificate to be reopened following the completion of the Tar River Hydrologic Model would be
the best option for protecting the interests of all users in the losing basin while still allowing
GUC to address their immediate needs.
Staff Response
The Greenville Utilities Commission performed a hydrologic analysis to evaluate the impact of the interbasin
transfer on the source river basin. This analysis included the development of a long‐term flow record at Greenville,
the generation of flow statistics to characterize the Tar River under both existing and future water use scenarios,
and a spreadsheet‐based hydrologic accounting model.
The hydrologic accounting model simulates water withdrawals and wastewater discharges to predict their effect
on stream flow in the Tar River. The model accounts for all existing and projected withdrawals and discharges on
the Tar River, over 100,000 gpd, from the Rocky Mount Dam to the GUC WWTP discharge. The USGS flow record
developed for the Greenville gage was used as the base flow record. Model simulations included the following
scenarios:
1. Current flows with no IBT.
2. Current flows with 2030 average day IBT.
3. Current flows with 2030 Maximum Withdrawal IBT.
4. Predicted 2030 flows with no IBT.
5. Predicted 2030 flows with 2030 average day IBT.
6. Predicted 2030 flows with 2030 Maximum Withdrawal IBT.
The results of the model show that the effects of the interbasin transfer are negligible at average stream flows and
higher, with a slightly larger impact during low flows. Under the minimum flow of record, the stream flow
becomes negative during both current and 2030 scenarios. A negative stream flow means that the tidal influence
in the lower Tar River pushes freshwater upstream, creating a net upstream flow. Tidal influences were not
simulated in the model.
A51
Environmental Management Commission
North Carolina Division of Water Resources
‐ 46 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
The Division of Water Resources also requested that Greenville Utilities Commission incorporate several changes
to their hydrologic accounting model in 2008 in order to evaluate an even more conservative transfer scenario.
The first change was to reduce the flow record by the amount of GUC’s historic 2002 withdrawals. Since the flow
record would have already accounted for this withdrawal (the gage is downstream of GUC’s intake), this change
creates an even more conservative baseline where the effects of GUC’s existing withdrawals are doubled. The
second change requested by DWR was to reduce GUC’s wastewater discharges on the Tar River by the amount of
the IBT. For many of the modeling scenarios, this change removed the entire volume of GUC’s existing and
projected wastewater discharge from the Tar River flow. Under these more conservative modeling scenarios, the
impact of the IBT was predicted to be below the 7Q10 at 1.8 percent of the time (6.4 days) under existing
conditions and at 2.1 percent of the time (7.7 days) in 2030. These modeling results indicate that the IBT will have
minimal impact on the existing stream flow. Therefore, there are no expected impacts to the wastewater
assimilation capacity of the Tar River Basin. Correspondingly, there are no anticipated impacts to water quality
within the source basin.
The results of the model, as presented in the Petitioner’s Environmental Assessment, are summarized in the
following Table.
Table 3: Summary of Flow Statistics
Greenville Gaging Station (Downstream of WTP
Intake and Upstream of WWTP Discharge) Downstream of Greenville WWTP
Current Scenarios Future 2030 Scenarios Current Scenarios Future 2030 Scenarios
No IBT Avg IBT Max IBT No IBT Avg IBT Max IBT No IBT Avg IBT Max IBT
2x Max
IBT No IBT Avg IBT Max IBT
2X Max
IBT
Flow Statistics (cfs)
Maximum 31,866 31,855 31,849 31,872 31,860 31,854 31,878 31,866 31,860 31,849 31,875 31,863 31,858 31,840
Minimum 24 11 4 20 7 ‐1 38 25 17 4 17 5 ‐3 ‐15
Average 2,524 2,513 2,505 2,525 2,513 2,505 2,537 2,526 2,518 2,506 2,529 2,518 2,509 2,492
Percentiles (cfs)
95th 9,033 9,023 9,014 9,035 9,025 9,016 9,046 9,036 9,027 9,014 9,038 9,028 9,018 9,001
50th 11,398 1,387 1,381 1,397 1,384 1,375 1,410 1,398 1,393 1,381 1,403 1,390 1,380 1,365
5th 229 216 210 228 215 208 242 229 222 210 231 219 211 194
Percent of Time (per year)
7Q10
(109 cfs) 1.3% 1.6% 1.8% 1.4% 1.6% 1.8% 1.0% 1.3% 1.5% 1.8% 1.3% 1.6% 1.7% 2.1%
80% of
7Q10
(87.2 cfs)
0.9% 1.1% 1.2% 0.9% 1.1% 1.3% 0.7% 0.9% 1.0% 1.2% 0.8% 1.1% 1.3% 1.6%
Average Number of Days Per Year
7Q10
(109 cfs) 4.7 5.8 6.4 5 5.9 6.5 3.7 4.6 5.4 6.4 4.7 5.7 6.3 7.7
80% of
7Q10
(87.2 cfs)
3.3 3.9 4.5 3.3 4.1 4.9 2.5 3.2 3.6 4.5 3.1 3.8 4.6 5.8
Due to the large number of comments received on the hydrologic analysis, ARCADIS developed a memo titled
Explanation of Hydrologic Analysis and Result Interpretation. This memo has been included in Appendix 6. The
document performs two additional analyses on the results of the original hydrologic accounting model in order to
provide further clarification.
The first is the application of a statistical analysis. ARCADIS took the flow data for each of the scenarios discussed
above and evaluated them with a statistical test to determine whether there is a “statistically significant”
A52
Environmental Management Commission
North Carolina Division of Water Resources
‐ 47 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
difference. The result is that there is no statistical difference between the scenario distributions. A full description
of the analysis is included in Appendix 6.
Second, ARCADIS performed a frequency‐duration analysis for two of the 2030 scenarios to represent stream flow
with and without the IBT. To perform this analysis, the entire 76 year record was filtered for events where the
flow was less than 300 cfs, 109 cfs (7Q10), and 27 cfs (25% of 7Q10). Those low flow days were then grouped into
25 low flow events where there were at least 40 days of flow less than 300 cfs occurring over a 60‐day span.
ARCADIS then put together a chart comparing the duration of those low flow events with and without the IBT. The
results of the analysis are as follows:
A53
Environmental Management Commission
North Carolina Division of Water Resources
‐ 48 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Table 4: Change in Duration of Low Flow Events
Flow Statistic Average Change in Duration Maximum change in Duration of Event*
< 300 cfs < 5 Days
Event #17 (July 8, 1988‐October 19, 1988) changed from a
total duration of 61 days without IBT to 71 days with
maximum IBT withdrawal.
< 109 cfs (7Q10) < 5 Days
Event #4 (August 10, 1943‐December 24, 1943) changed from
containing 20 days under threshold without IBT to 35 days
under threshold with maximum IBT withdrawal.
Event # 24 (July 26, 2005‐October 21, 2005) changed from
containing 7 days under threshold without IBT to 22 days
under threshold with maximum IBT withdrawal.
< 27 cfs (25% of 7Q10) < 3 Days
Event #10 (July 2, 1968‐November 10, 1968) changed from
containing 13 days under threshold without IBT to 33 days
under threshold with maximum IBT withdrawal.
* Note that an event is defined as a period of time below 300 cfs. Within that event, this chart summarizes the time the stream
flow might have dropped below the identified threshold. For example, within an event that historically lasted 96 days (without
the IBT), the analysis might have predicted an additional 4 days below 300 cfs, 9 days below 109 cfs, and a change in 1 day
below 27 cfs when factoring in the max‐day IBT.
Although each of the modeling analyses that have been performed in support of the Petition indicate a difference
between the IBT and non‐IBT scenarios, it is reasonable to categorize these differences insignificant for the
following reasons:
1. The modeling analysis is conservative. DWR asked the applicant to include a number of very conservative
assumptions so that a “worst case impact” could be identified. These assumptions, as previously
discussed, include reducing GUC’s wastewater discharges on the Tar River by the amount of the IBT. For
many of the modeling scenarios, this change removed the entire volume of GUC’s existing and projected
wastewater discharge from the Tar River. The model also assumes a sustained maximum day transfer (as
opposed to a predicted average day transfer with peaks approaching the max‐day).
2. IBT and State Regulations require a drought management plan. GUC is required to have a Water Shortage
Response Plan (WSRP) containing specific, identifiable triggers that would be put into effect in the event
of drought. Therefore GUC (and the other Petitioners) would likely be under water restrictions during low
flow events. GUC’s WSRP triggers are tied to the stage of water at the intake location and the location of
the salt water wedge.
3. The model did not take into account tidal effects. An important feature of the lower Tar River is that it is
tidally influenced. Since salt water is heavier than freshwater, the salt water wedge creates a dam‐like
effect that pushes freshwater upstream during low flow periods. GUC closely monitors the salt water
wedge since their WTP is not designed to treat saline water. GUC has also noted instances where net
negative downstream flow has been recorded; however, there has been adequate water over the raw
water intake. Due to the tidal influence, the Tar River channel is never depleted. This tidal buffering
effect would also reduce the impact on aquatic life during critical periods.
4. The IBT request will be met with existing infrastructure. GUC has not requested an expansion of their
WTP due to this request. They have sufficient capacity in their existing WTP to meet Farmville, Greene
County, and Winterville’s demand. The direct impact of their withdrawal was previously evaluated in the
environmental documents developed (and approved) for the construction of the water treatment plant.
A54
Environmental Management Commission
North Carolina Division of Water Resources
‐ 49 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
The Hearing Officers have taken into account the number of comments on the modeling analysis. Based on
concerns that future studies may reveal additional impacts to the Tar River Basin, and considering the uncertainty
engendered by the duration of the certificate, the Hearing Officers have recommended a reopener.
The City of Rocky Mount provided detailed comments concerning the possibility that future studies, particularly
DWR’s Tar River Basin Model or the Tar River Basin Plan, might reveal additional impacts to the Tar River. In
response, the hearing officers requested that Rocky Mount and GUC jointly recommend language for the special
condition. While the parties were not able to come to a mutual conclusion, each entity individually recommended
verbiage that was similar to reopeners previously used by the EMC in other IBT Certificates. The most significant
difference is that Rocky Mount proposed that any decision by the Commission to grant or deny a request to
reopen the certificate should be subject to administrative and judicial review according to Chapter 150B of the
General Statutes. However, the Hearing Officers have determined that it would not be appropriate for a condition
of the Certificate to attempt to define any right a party may or may not have in challenging the EMC’s decision.
Therefore the hearing officer’s recommend that the reopener used in previous IBT certificates also be used here.
If the Commission determines that the record on which this Certificate is based is substantially in error or if new
information becomes available, that clearly demonstrates that any Finding of Fact (including those regarding
environmental, hydrologic, or water use impacts) pursuant to G.S. § 143‐215.22I(f) was not or is no longer
supported or is materially incomplete, the Commission may reopen and modify this Certificate to ensure continued
compliance with G.S. ch. 143, art. 21, part 2A. "
A55
Environmental Management Commission
North Carolina Division of Water Resources
‐ 50 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC VI: DIRECT IMPACTS TO RECEIVING BASIN
The following comments express concerns about the potential of increased wastewater flows to impaired and
nutrient sensitive streams in the Contentnea Creek and Neuse River Basins.
Comment ID # Comment Text
14.1 The City of Wilson is concerned about the transfer due to the potential of greater wastewater
flows to the Neuse Basin. Based on current Nitrogen allocations in the Neuse Basin, how will this
area grow in water use without a similar growth in the sewer flows? Will all of this flow then be
pumped back to the Tar River, or land applied, or sent to the Neuse? The City of Wilson is
concerned that potential water quality problems in the Neuse and Contentnea Creek could
further impact point sources upstream of the IBT transfer communities.
4.10 Finally, Contentnea Creek and Little Contentnea Creek are both impaired streams. All of the
communities within the receiving basin that will experience greater wastewater flow due to the
growth precipitated by this IBT discharge their wastewater into these impaired streams. The
Towns of Hookerton and Snow Hill, and the Contentnea Creek wastewater plant have all been
non‐compliant with their NPDES permits within the past year. The EA should provide a
compliance history of each of the wastewater facilities as well as the communities' ability to
handle the increase flow. The EA does state that no wastewater facility will need to increase
their permitted discharge amount, but if the facilities suffer from inflow and infiltration, or
other maintenance problems, these issues would be exacerbated by the increased growth and
flow due to the IBT and should be addressed in the IBT.
Staff Response
Winterville’s wastewater is treated by the Contentnea Metropolitan Sewerage District via the Contentnea Creek
WWTP. This plant is permitted to discharge 2.58 MGD of wastewater to an unnamed tributary to Contentnea
Creek in the Neuse River Basin.
Farmville and the majority of Greene County are located in the Contentnea Creek Basin. Farmville operates a 3.5
MGD WWTP which discharges to this basin. The majority of the wastewater treatment in Greene County is
handled by on‐site septic systems; however, there are three small centralized treatment systems: the Snow Hill
WWTP permitted for 0.5 MGD, the Hookerton WWTP permitted for 0.06 MGD, and the Maury Sanitary Land
District WWTP permitted for 0.225 MGD. All of these facilities discharge to the Contentnea Creek Basin.
The Contentnea Creek WWTP and the Hookerton WWTP were under Special Orders by Consent in 2007 and 2008
for BOD, TSS and fecal coliform violations. Those SOCs resulted in infrastructure repairs. The Contentnea Creek
WWTP has completed the repairs to its collection system. The Hookerton WWTP has begun the construction of an
additional treatment unit. Although these WWTPs have had permit limit violations within the past year, at this
time, neither is in significant non‐compliance with their respective NPDES permit limits. Any future non‐
compliance with the NPDES permit would be handled by the Division of Water Quality in accordance with state
and federal NPDES regulations.
Since none of these facilities will be requesting an expansion (or changes to existing permit limits) to accommodate
additional flows generated by the IBT, the IBT is not expected to cause direct impacts to the receiving basins.
The Hearing Officers recommended no changes be made based on these comments.
A56
Environmental Management Commission
North Carolina Division of Water Resources
‐ 51 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC VII: CONSTRUCTION OF TEMPORARY DAM STRUCTURE
Comment ID # Comment Text
4.13 The EA does not adequately consider the impacts combined with the Greenville Utilities
Emergency Drought Management Planning Project on the Tar River. Additional evidence of the
lack of thoroughness in the environmental review stems from the Petitioner's lack of discussion
of their intention to construct a temporary dam across the Tar River in the vicinity of the
Greenville Utilities Water Treatment Plant. The Petition states that "it is challenging to fully
understand and quantify the flow characteristics for the Tar River at Greenville" and that
"[c]urrent USGS techniques for low‐flow analyses do not provide a means of account for tidal
effect." Petition at 3‐4. Despite these challenges, the applicant should have considered this
related project in its analysis of the probable environmental impacts from the IBT.
4.29 It has also come to our attention that the Greenville Utilities Commission has completed a draft
Environmental Assessment regarding future drought management planning with a preferred
alternative for a temporary dam structure in times of low flow. This EA should be incorporated
into the analysis of the IBT Petition and EA.
Staff Response
The Division has not reviewed or approved an EA for the development of a temporary dam structure on the Tar
River.
The Hearing Officers have chosen to add a reopener clause to the Certificate. The reopener clause states that if
any future information should become available concerning impacts to the Tar River as a result of the IBT, the EMC
may reopen the certificate to include any additional restrictions or requirements that may be necessary to mitigate
the effects.
A57
Environmental Management Commission
North Carolina Division of Water Resources
‐ 52 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC VIII: EXISTING FINANCIAL INVESTMENT
Several of the comments expressed concern that Greenville and Farmville had already begun constructing the
necessary infrastructure to transfer water between basins. These comments were submitted by local
governments, who were concerned that the significant investment not be wasted, as well as from concerned
citizens who felt the investment should not bias the EMC’s decision.
Comment ID # Comment Text
16.1 After an extensive investigation of available alternative water supply sources, Greene County
has entered into contract with GUC to obtain alternative water supply from GUC. In a joint
arrangement with the Town of Farmville, Greene County has invested millions of dollars for the
construction of a delivery system that will deliver up to 5 MGD to Farmville and Greene County.
17.2 Greene County and Farmville have expended a large sum of money to date to implement the
delivery system of water from Greenville to Greene County and Farmville, all in an effort to
comply with the 2002 Central Coastal Plain Capacity Use Area law deadlines of 2008,2013 and
2018. The project is nearing completion and scheduled to be activated in June, 2010.
4.16 Finally, the decisions by the source and receiving basin communities to invest millions of dollars
of public monies for construction of infrastructure, partially completed, for the Tar River to
Neuse River proposed IBT should in no way bias the decision of the EMC.
16.3 The unfunded mandate by the State reducing our dependency on ground water by 25% in 2008,
50% in 2013 and 75% in 2018, places Greene County under an extreme hardship. Every
consideration by the Environmental Management Commission is requested to allow us to
implement the least cost alternative solution, which is the proposed GUC alternative.
Staff Response
This infrastructure does represent a significant investment for Farmville and Greene County and the transmission
lines would continue to be useful even if the EMC were to deny the IBT request. GUC would have the option to
provide these systems with ground water or finished surface water in amounts below the IBT thresholds (GUC can
move up to 2 MGD out of the Tar Basin without receiving an IBT certificate). In the future, the potential exists for
the purchase of water from the planned Aquifer Storage and Recovery system.
The Hearing Officers recommended no changes be made based on these comments.
A58
Environmental Management Commission
North Carolina Division of Water Resources
‐ 53 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC IX: IMPACTS TO AIR QUALITY
Comment ID # Comment Text
4.8 A similar lack of attention plagues the brief discussion of impacts to air quality. In 2009, the
federal government changed the air quality standard for ozone, and in doing so designated 24
counties and parts of 17 others as not meeting this new standard. Pitt County was
recommended as unclassifiable due to a lack of monitoring data. The EA states that DAQ
adopted new ozone standards in 1997 and that DAQ has a monitoring site in Farmville that
recorded no ozone exceedances in 2006. This is outdated information. The EA should include
the new federal ozone standard and an assessment of any state of federal data available for Pitt
County. Again, the EA dismissed the impact of growth on the potential for impacts to air
quality: "No construction activities will occur relative to the proposed project; therefore, no
direct impacts to air quality will occur. Indirect impacts to air quality within the service area
from growth will be minimal. "EA pp 5‐26. The region may be a non‐attainment area for the
new ozone standard. The proposed IBT would facilitate residential and industrial growth in the
receiving basin. Although this growth and the associated increases in vehicular traffic and use of
lawnmowers will lead to complicate the existing air quality problems, this impact is not
discussed.
Staff Response
The Final Environmental Assessment (EA) for the Greenville Utilities Commission IBT was published in October
2008. In November 2008, the Department of Administration issued a cleared letter with the Finding of No
Significant Impact (FONSI). The EA included an air quality impacts discussion using information publicly available in
the fall of 2007. However, in response to the concerns raised in this comment, ARCADIS was able to provide the
following information:
The EA stated that the monitoring site in Farmville did not report any ozone exceedance days in Pitt or
Greene Counties based on the 8‐hour ambient ozone standard of 0.08 parts per million (ppm). The 0.08
ppm ozone standard was adopted in 1997. The monitoring site in Farmville covers a larger region,
including Greene County. In 2008, the Division of Air Quality (DAQ) revised the ozone standard to 0.075
ppm. DAQ is currently reviewing the 2008 standard for a possible revision to an ozone level between 0.060
and 0.070 ppm.
Concurrent with the revision of the ozone standard, DAQ relocated the monitoring site from the Town of
Farmville to the Pitt County Agricultural Center, approximately 14.5 miles from the original Farmville
location. This relocation was completed in early 2008. Due to the distance between the two locations, DAQ
recommended that classification of the area (attainment or non‐attainment) be deferred until three years
of continuous data from a single location became available. Therefore, Pitt and Greene Counties are
currently designated as “unclassifiable”.
The Hearing Officers recommended no changes be made based on this comment.
A59
Environmental Management Commission
North Carolina Division of Water Resources
‐ 54 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC X: AQUIFER STORAGE AND RECOVERY (ASR)
Comment ID # Comment Text
1.8 To meet the commitments in the proposed IBT, GUC would need to expand their current
facilities and would be absolutely dependent upon the Aquifer Storage and Recovery (ASR)
system functioning as designed. The ASR has not been tested. It is a pioneer system in NC. It has
been a troubled project since inception, taking years longer to be in place than was planned. I
would be unwilling to approve creating a dependency on this project.
18.7 our long range water supply planning effort includes the use of an innovative technology,
aquifer storage and recovery (ASR), which will offset future maximum day water demand. The
ASR system, the first in North Carolina, will be operational this spring and we are confident that
this technology, coupled with our water conservation initiatives, will allow us to manage our
water resources even more effectively.
Staff Response
The IBT will not create a dependency on the ASR. GUC’s water sales for Farmville, Winterville, and Greene County
will be managed as described in the IBT Management Strategy. This strategy does not include a discussion the ASR
system. That system is being developed as part of a long‐term planning effort to provide a future water supply.
The IBT is primarily being requested to replace ground water that has been lost due to the Central Coastal Plain
Capacity Use Area rules.
The Hearing Officers recommended no changes be made based on these comments.
A60
Environmental Management Commission
North Carolina Division of Water Resources
‐ 55 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC XI: OTHER COMMENTS
The following general comments have been noted by the hearing officers and are included here as part
of the public record.
Comment ID # Comment Text
1.11 I ask that the Division of Water Resources view this from the perspective of a better management scheme. I
believe it would be much better to manage water resources conservatively within their natural basin.
1.14 … the newly developed and potential for future development of Neuse River supplies is adequate without the
potential problems associated with InterbasinTransfers,
1.5 I think it reasonable for areas with limited resources to recognize those limits and plan not to exceed the
limits available.
1.6 Stream flows and receiving streams will be impacted by the proposed IBT as will the natural characteristics of
the waters affected. These effects and impacts are not necessary and are not even needed except possibly in
the minds eye of municipal officials and self aggrandizing developers in the region.
1.9 Development in Farmville, Winterville, and Greene County promotes rural sprawl. Thus the proposed IBT
promotes rural sprawl. It would be more efficient and conservative of water resources to develop within the
Greenville Urban Area. While it may seem outside the purview of the division whose approval is needed, the
agency can surely not be blind to this problem.
5.4 As in many other communities, the Town supports the desire of the Division of Water Resources for
communities to seek a regional solution to issues such as water capacity. The town already has connection
with Greenville Utilities and bell Arthur Water Corporation. As other communities tie in with the GUC system,
these connections will provide the ability to provide water over a large portion of Pitt County and Greene
county. This further enhances the region's ability to tie into other water systems in the region that could be a
tremendous asset in the times of emergencies or water shortages.
5.5 This project is a true approach to a regional problem that will make eastern NC a stronger area of the state
with increased potential. The City of Greenville is the "hub' of eastern NC with the ability to provide services
on a regional scale. This ability is a real benefit to the region as a while as well as provide for economies o
scale when future needs have to be addressed.
6.4 Please understand that Rocky Mount is not attempting to oppose the requested IBT but does believe that
extension of the comment period and inclusion of the above conditions are necessary to ensure that Rocky
Mount's future water needs are fairly protected.
10.2 In addition, I think the environmental impact from such a drastic measure is essentially unquantifiable before
the action, and may be irreparable after. The Tar River ecosystems are so complex and finely balanced there is
just no telling what the consequences will be. Disturbing the flow of river basins, which have evolved over
millenniums, is a drastic and risky action that may end up causing more problems than it solves. I for one
don't think it's worth the risk.
11.3 I believe this issue is much more than being selfish and not wanting to be a good neighbor and assist other
areas with a limited water supply. Science suggests river systems are best managed within their own basins,
which precludes siphoning water off to other basins. We all must now learn to live in harmony with nature
and within the natural resources available to us, and that means limiting water hungry development where
the water is not available to support it.
16.2 Based upon 2009 statistics from the NC Dept. Of Commerce, Greene County is one of the forty most
distressed counties within NC, thus receiving a Tier 1 designation. Greene County has a population of 21,205
(2008 projection by Office of State Budget Management) and is solely dependent on agriculture. Greene
County has only three incorporated towns, Snow Hill (Pop 1,618)' Walstonburg (Pop. 23 1) and Hookerton
(Pop 485). The annual median household income for Greene County is $32,074 as compared to the Mean
average of $39,184 (2000 census data). Twenty percent of the people in Greene County are classified as
"Poverty". Greene County must have an economically feasible solution for water supply. The proposed
purchase of water from GUC is the most economically and technically feasible solution available.
17.3 The proposed interbasin transfer will not result in significant direct or indirect environmental impacts. Failure
by GUC to obtain an IBT Transfer Certificate will result in extreme hardship on the citizens of Greene County
and the Town of Farmville
19.3 Feels the EA is good but it doesn't address everything.
A61
Environmental Management Commission
North Carolina Division of Water Resources
‐ 56 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
19.5 Bell Arthur is in the Neuse basin so the transfer there (from Neuse WASA) remains in the Neuse (not an IBT by
NRWASA).
21.1 LaGrange purchases water from Farmville and thus relies on this water being made available.
21.2 Neuse WASA is transferring some water in the opposite direction to Bel Arthur (offset of impacts)
A62
Environmental Management Commission
North Carolina Division of Water Resources
‐ 57 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
TOPIC XII: RECOMMENDATIONS TO THE EMC
The following comments are direct recommendations to the EMC on special conditions and proposed
action regarding GUC’s Petition for an interbasin transfer certificate. The hearing officers have reviewed
these recommendations and they are provided here as a reference for the full EMC.
Comment ID # Comment Text
4.1 Although the new requirements do not go into effect for interbasin transfers to supplement ground water
supplies in the fifteen counties designated as the Central Coastal Plain Capacity Use Area under until January
201 1 (H.B. 820 (7)(b) (2007)), it would be shortsighted of the Environmental Management Commission not to
consider the broad policy objectives stated in the amendments in looking at the proposed transfer. Our
comments rely on the requirements set out in N.C. Gen. Stat. 143‐21 5.221 but we urge the EMC to consider
the spirit of the amendments in reviewing the GUC Petition.
4.17 Based on the previous comments, we urge the EMC to deny the request for the proposed IBT at this time. As
noted above, the EMC does not have the necessary information to grant the certificate.
4.18 Given the significant environmental impacts of the proposal, we also encourage the EMC to reconsider the
adequacy of the EA and the associated Finding of No Significant Impact.
4.19 SEPA requires the preparation of an environmental assessment, and, if warranted, an environmental impact
statement ("EIS") for any transfer of surface water that requires the filing of a Petition pursuant to the Surface
Water Transfer Act, N.C. Gen. Stat. 143‐215.221; 113A‐8.1. An EIS is required if the scope and environmental
impact of a planned project is significant. N.C. Admin. Code 25.0501. The EA for the GUC IBT shows that there
will be significant impacts and that an EIS was warranted. Therefore, the EMC should deny the Petition and
require GUC to complete a full and comprehensive environmental review of this project and associated
projects.
4.20 Again, we believe the EA and Petition do not provide enough relevant information on the secondary and
cumulative impacts in both basins for the EMC to be able to make this decision. But, if the IBT is to be granted,
we recommend the following: 1. The EMC should make the IBT a temporary certificate and provide enough
time for the receiving basin communities to identify and make the necessary investments for Neuse Basin
source water. The cross‐connections currently being built to GUC could be used for emergency connections in
the future.2. The EMC should require regional land‐use planning to insure that as growth occurs is does not
exceed the available water supply.3. The EMC should reduce total IBT amount to reflect the stated objectives
of replacing cretaceous aquifer water source of approximately 4 mgd. 4. The EMC should require aggressive
water conservation measures enacted by both source and receiving basins, including but not limited to: Home
fixtures retrofit program, Ordinances for requiring (or incentivizing) cisterns or other rain water harvesting
uses, Separate irrigation meters and higher pricing for irrigation, Comprehensive educational programming
and written information 5. The EMC should require that GUC submit a plan and implement activities for
reducing per capita residential water use by 10% over a 10‐year time period. 6. The EMC should require that
GUC submit a plan and implement for reducing per capita industrial water use by 5% over a 10‐year period.7.
The EMC should require that GUC conduct a feasibility study and create an action plan for water reclamation
projects.8. The EMC should require that the receiving basin wastewater treatments plants remain in
compliance with their NPDES permits 11 of 12 months of the year or face reduction in IBT amount.
4.21 The Surface Water Transfer Law requires the EMC to issue a certificate for the proposed transfer if‐and only if
‐ two conditions are met: the benefits of the proposed transfer must outweigh the detriments, and the
detriments must be mitigated "to a reasonable degree." N.C. Gen. Stat. $ 143‐215.22I(g). The EMC must find
that these conditions are met "by a preponderance of the evidence," ie., a legal standard requiring that the
evidence on which a decision rests be credible, and that the evidence, taken as a whole, shows that the facts
sought‐it to be proved is more probable than not. Given the numerous inadequacies, errors and oversights in
the EA, this standard cannot be met. The EMC should exercise its authority to deny the Petition and certificate
in accordance with N.C. Gen. Stat. $ 143‐2 15.22I(h).
4.22 Based on our previous comments submitted in December, we continue to urge the EMC to deny the request
for the proposed IBT at this time. The EMC does not have the necessary information to grant the certificate.
4.23 We have also had the opportunity to review comments from and confer with the City of Rocky Mount, and
echo the concerns and problems the City raised in its comment letter. If the EMC moves forward with the
Petition, we strongly encourage the state to consider the conditions proposed by the City of Rocky Mount.
A63
Environmental Management Commission
North Carolina Division of Water Resources
‐ 58 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
4.24 The first condition Rocky Mount proposed is that the certificate be revisited upon completion of the Tar River
Hydrologic Model. PTRF and SELC strongly support this recommendation and suggest that the EMC
incorporate similar language as was used in previous IBTs. In the CMU and Cary/Apex IBT certificates, the EMC
included the condition below: "The Commission notes that future developments may prove the projections
and predictions in the EIS to be incorrect and new information may become available that shows that there
are substantial environmental impacts associated with this transfer. Therefore, to protect water quality and
availability and associate benefits, modification of the terms and conditions of the certificate may be
necessary at a later date." If the EMC moves forward with the GUC IBT, the final certificate should include
similar language triggering a reopening of the certificate based on the Tar River Hydrologic Model.
4.26 An additional condition, similar to that included in the Cary/Apex IBT below, should be included to ensure that
any drought management measures and other mitigation measures are properly enacted. The Cary/Apex IBT
certificate included the following: "Prior to transferring water under this certificate, the holders of this
certificate shall work with the Division of Water Resources to develop compliance and monitoring plan subject
to approval by the Division. The plan shall include methodologies and reporting schedules for reporting the
following information: maximum daily transfer amounts, compliance with permit conditions, progress on
mitigation measures, drought management, and reporting. A copy of the approved plan shall be kept on file
with the Division for public inspection. The Division of Water Resources shall have the authority to make
modifications to the compliance and monitoring plan as necessary to assess compliance with the certificate. "
4.6 Furthermore, the applicant suggests that since an IBT certificate would be needed for a NRWSA transfer to
Winterville since the transfer occurs from the Neuse River to the Contentnea Creek sub‐basin, that this
automatically negates this as a viable option. The 2007 changes to the SWTA clearly demonstrate that a
transfer of water within a major river basin (i.e. Neuse to Contentnea sub‐basin) is preferred over a transfer
between major river basins.
5.1 The purpose of this letter is to inform you of the Town of Winterville's official support for Greenville Utilities
Commission's Petition for an interbasin Transfer Certificate. The approval of this Petition is not only important
to the Town of Winterville but to neighboring communities as well.
5.3 The Town believes that the EMC has an obligation to allow Winterville to replace its previously permitted
water supply capacity with a high quality water that is readily available and accessible.
6.11 The City of Rocky Mount requests that any IBT certificate issued to the GUC include a condition allowing the
Certificate to be reopened following completion of the Tar River Hydrologic Modeling and Water Resource
Plan if the results indicate that the approved IBT impinges upon Rocky Mount's ability to modify its water
shortage response plan. Rocky Mount is concerned that, if approved, the demand to transfer water outside
the basin could influence the decision to approve a requested change in the release protocol for the Tar River
Reservoir. To guard against this possibility, in our comments dated December 1, 2009, Rocky Mount proposed
several conditions that might be included in the IBT certificate. Upon further reflection, Rocky Mount now
considers that a condition that would allow, upon the approval of the EMC, the certificate to be reopened
following the completion of the Tar River Hydrologic Model would be the best option for protecting the
interests of all users in the losing basin while still allowing GUC to address their immediate needs.
6.3 Rocky Mount requests that the EMC consider including conditions in the IBT certificate that: 1. Acknowledge
that Rocky Mount's drought management plan will be evaluated based on the normally applicable criteria and
not its potential effect on the requested IBT. 2. Provide that if implementation of Rocky Mount's approved
drought management plan causes flows at Greenville that result in unacceptable impacts (e.g., location of the
salt front) or are insufficient to allow the permitted transfer, the systems that receive the transferred water
will resume ground water pumping until such time as conditions allow resumption of the transfer. The ground
water pumped as a result of these modified operations will be offset by additional transfers during periods of
higher flow in the Tar River over a period of no longer than one year following the resumption of transfers so
that there will be no net change in the amount of the ground water pumped over the long term.. 3. Provide
that if at such time as Greenville applies for an increased withdrawal, there is insufficient water to meet in‐
basin needs, including those of Rocky Mount, the transfer will be reduced in order to accommodate in‐basin
needs.
7.4 I strongly urge that this proposed plan be thoroughly reviewed.
8.4 I support the use of GUC water to Winterville. This proposal would have minimal impact on the environment
and would supply all parties with needed water.
13.1 The City of Oxford supports the request for an interbasin transfer by the Greenville Utility Commission.
A64
Environmental Management Commission
North Carolina Division of Water Resources
‐ 59 ‐ Greenville Utilities Commission,
Town of Farmville, Town of Winterville, and
Greene County
Proposed Interbasin Transfer Certificate
Hearing Officers’ Report‐ November 18, 2010
Comment ID # Comment Text
14.4 We support Rocky Mount's request to extend the comment period for 45 days to complete a revised drought
management plan. This is particularly important due to the existing modest emergency interconnection
capable of transferring 1.9 MGD installed by both communities after the drought of 2007‐2008.
15.1 Greene County is strongly in favor of the Environmental Management Commission issuing the Interbasin
Transfer Certificate to GUC without delay.
16.3 The unfunded mandate by the State reducing our dependency on ground water by 25% in 2008, 50% in 2013
and 75% in 2018, places Greene County under an extreme hardship. Every consideration by the
Environmental Management Commission is requested to allow us to implement the least cost alternative
solution, which is the proposed GUC alternative.
17.4 Request favorable consideration by the Environmental Management Commission in granting the Greenville
Utilities Commission's request for an IBT Certificate permitting the delivery of water from Greenville Utilities
Commission to Greene County and the Town of Farmville (Tar River Basin to Neuse River Basin)
18.8 We have implemented a regional water supply strategy that utilizes our unique geographical advantages. Our
conjunctive use approach to water supply planning has positioned us to be a regional water provider. Our
mission is to protect water resources and provide regional water supply solutions to our customers and to our
neighbors in critical need. We sincerely hope that our regional approach may serve as a model for neighboring
watersheds faced with similar water supply concerns.
A65
Page:
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To: Copies:
Toya Ogallo and Steve Reed
DENR, Division of Water Resources
Kevin Martin and Stan Crowe
Environmental Management Commission
Steve Porter, Greenville Utilities
Randy Emory, Greenville Utilities
Tony Cannon, Greenville Utilities
Ron Elks, Greenville Utilities
Richard Wyche, ARCADIS
From:
Mary Sadler, Hazen and Sawyer
Date: ARCADIS Project No.:
July 21, 2010 NC706015.0030
Subject:
Explanation of IBT Management Strategy
Hearing Officer’s Report Request for Additional Information
Greenville Utilities Commission Interbasin Transfer Certification
Introduction
In June 2010, the Hearing Officers requested more information on the premise behind the development of
the Interbasin Transfer (IBT) Management Strategy for Greenville Utilities. The IBT Management Strategy
was presented in detail in the Final Environmental Assessment (EA) and IBT Petition. This Technical
Memorandum (TM) clarifies the significant elements of the IBT management strategy, such as average
day demand versus maximum day demand, the use of banked water, the definition of average day and
maximum day bulk sales, and the definition of the Approved Base Rate (ABR) relative to actual
groundwater use. This TM references the water demand projections developed in the EA, and will not be
repeated herein.
A key element of the IBT Management Strategy is the Water Purchase Agreements with Greenville
Utilities. These water purchase contracts between Greenville Utilities and each community specify that
Greenville Utilities reserves the right to curtail water if the Greenville Utilities water system is approaching
a maximum day demand. The magnitude of the maximum day demand will determine whether or not
Greenville Utilities has enough excess capacity to sell water. The Purchase Agreements limit water
curtailment to a maximum of 10 percent of the year, or 36 days per year.
Definitions
Approved Base Rate (ABR) – The Central Coastal Plain Capacity Use Area (CCPCUA) rules specify the
use of an ABR as the reference groundwater withdrawal rate for future reductions in groundwater. The
ABR is based on a system’s annual water use in calendar years 1997 or 1999. The total withdrawal for the
selected year is converted into an annual average day value by dividing by 364 days. The new average
annual ABR eliminates the maximum and minimum withdrawals that occurred during that year. The ABR
for Winterville, Farmville, and Greene County are 0.496 million gallons per day (mgd), 1.572 mgd, and
2.96 mgd, respectively
ARCADIS
801 Corporate Center Drive
Suite 300
Raleigh
North Carolina 27607
Tel 919.854.1282
Fax 919.854.5448
Appendix 1 A66
Page:
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Allowable Groundwater Pumping Rate – The allowable groundwater pumping rate is the ABR decreased
by 25 percent in 2008, 25 percent in 2013, and 25 percent in 2018 for a total reduction in water withdrawal
of 75 percent.
Maximum Day Demand – The maximum day demand flow rate, referred to as ‘maximum day’, is the
largest water demand event occurring in a year rate. Maximum day demand projected out over a 20-year
planning period is the capacity at which water systems are permitted (e.g. water treatment plant capacity
and Interbasin transfers). Water systems must provide water to users during high demand events. The
maximum day flow rate occurs once a year, but can be approached two or three times a year.
Peaking Factor – The peaking factor is the ratio of the maximum day demand to the annual average day
demand. Peaking factors typically vary by community, but typically range from 1.4 to over 2.0.
Banked Water – Banked water is the volume of water that can be conserved by not pumping groundwater
at the allowable pumping rate. If the projected demand can be met entirely or in part from another source
of water, e.g. the purchase of finished water from Greenville Utilities, then that excess groundwater may
be conserved, or “banked”, for future use. Banked water will primarily be used when Greenville Utilities
must curtail water to each community to satisfy the system demand for Greenville Utilities. Banked water
may be pumped at a higher rate than the allowable pumping rate as long as the total volume of banked
water is not exceeded.
Banking groundwater is specifically allowed by CCPCUA rules. All of the communities submitted a letter of
intent to bank water to the Division of Water Resources (DWR) in 2003. DWR has approved banking for
Farmville, Winterville, and Greene County. The approval included several provisions for calculating and
reporting the banked amount.
Average Day Bulk Sale of Finished Water – The average day bulk sale of finished water is the projected
water demand less the allowable groundwater pumping rate plus 50 percent of the allowable groundwater
pumping rate. In other words, it was estimated that each community would buy 50 percent more water
from Greenville Utilities on an average day to meet projected demand in order to reduce the groundwater
withdrawal. This strategy allows groundwater to be stored, or banked, for future use.
Maximum Day Bulk Sale of Finished Water – The maximum day bulk sale is the projected water demand
multiplied by the peaking factor less the allowable groundwater pumping rate. The maximum day bulk sale
effectively reduces the overall IBT amount by using groundwater to help meet demand.
Interbasin Transfer – The Interbasin transfer was calculated on an average day and a maximum day
basis. The General Statutes specify that the regulated IBT amount be based on a maximum day,
consistent with permit requirements of water treatment systems across the state. The IBT projections
factor in consumptive use for each community and the return of water to the source basin, if applicable.
The average day IBT projections are based on the average day bulk sale of finished water. The maximum
day IBT projections are based on the maximum day bulk sale of finished water.
Appendix 1 A67
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Normalizing Historic Water Demand
Every community experiences minimum, average, and maximum day water demands throughout the year.
From year to year, the highs and lows in water demand will usually vary with season. The perception is
the maximum day demand occurs only in the hottest months of the year. This perception is not valid every
year. Water systems will experience maximum day demands at any time during the year, including the
coldest months.
In order to illustrate this point, a historic diurnal curve was created for each community. Five to ten years
of daily water production records were compiled for each community. For each day, a factor was
calculated to represent the demand on that day relative to the annual average for that year. The highest
calculated factor will correspond to the maximum day for that year. Likewise, the lowest calculated factor
will correspond to the minimum demand day that year. The calculated factors essentially normalize the
historic diurnal curve such that a demand pattern is created for each community over the period of record.
Maximum and minimum days do not occur on the same day at any time during the historic record for
Greenville Utilities, Farmville, Winterville, or Greene County.
The normalized pattern can be used to create a diurnal demand curve for future projections. The
normalized pattern should only be applied to average day projections (e.g. average day bulk sales or
average day water demands) since the maximum and minimum days are produced using the normalized
diurnal pattern.
Greenville Utilities Sale of Finished Water
Greenville Utilities will sell excess finished water to each community up to the permitted 22.5 mgd water
treatment plant (WTP) capacity. Currently, the annual average for Greenville Utilities has hovered around
10 mgd for the last several years. On an average day basis, Greenville Utilities will be able to sell water to
each community entirely. Greenville Utilities will also be able to sell water to a community if that
community is experiencing a maximum day. The maximum day for each community is not expected to
occur on the same day (per the aforementioned explanation). However, if Greenville Utilities approaches a
maximum day, the Water Purchase Agreements stipulate that Greenville Utilities reserves the right to
curtail water, if necessary, to all of the communities if it is anticipated that WTP capacity may be
exceeded.
To illustrate this concept, the diurnal pattern was applied to the average day bulk purchase for each
community, including Greenville Utilities. Each community’s diurnal bulk sale curve was added
consecutively to the projected demand diurnal curve for Greenville Utilities. Figure 1 provides an
illustration of this concept. Greenville Utilities will be able to provide finished water to each community until
2030. Figure 1 also illustrates that if the combined community rate exceeds the 22.5 mgd WTP capacity,
the use of banked water will be essential for meeting demand, as Greenville Utilities will be required to
curtail water.
Appendix 1 A68
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Explanation of IBT Management Strategy
Figures 2, 3, and 4 were created for Farmville, Greene County, and Winterville, respectively, to illustrate
the IBT Management Strategy for each individual community. Each figure provides an illustration of the
projected average day bulk sale and water demand applied to the diurnal pattern to create projected sale
and demand curves to 2030. The allowable groundwater pumping rate and ABR are also indicated on
each figure. Furthermore, the historic minimum, maximum, and selected peaking factors are also plotted
with respect to the ABR. The IBT projections, with and without groundwater use, are also represented on
each figure.
There are several important points to note, as follows:
1. The ABR multiplied by the peaking factor is a translation of the ABR to a historic maximum day
flow. The ABR is an annual volume that has been normalized to an annual average. The ABR
does not take into account historic peaking factors. Each community has historically pumped a
wide range of peaking factors compared to the ABR.
2. The selected peaking factor used to project maximum day bulk sales and the 2030 IBT amount
represents a decline from historic use. The selected peaking factor for Farmville is 1.7, a
reduction from a maximum historic peaking factor of 2.4. The selected peaking factor for Greene
County is 1.75, a reduction from a historic maximum of 1.98. Winterville’s historic maximum
peaking factor was as high as 2.75, with a selected peaking factor of 1.8.
3. It should be pointed out that smaller water systems tend to exhibit slightly higher peaking factors
than larger utilities. Smaller systems have less buffering in the distribution system (e.g., elevated
storage, large distribution mains, etc.). The selected peaking factors were chosen specifically for
each system based on historic data; however, the peaking factors were also selected with the
understanding that Interbasin transfers require a rigorous evaluation of water conservation in the
form of reduced use, with one example being a reduction in the peaking factor used to determine
maximum day.
4. One primary question that has arisen in the public comment period is how much water is being
replaced by the CCPCUA rules. Prior to the CCPCUA rules, each system could have reasonably
experienced, and met, a maximum day demand with a high peaking factor for short periods of
time. Water systems must provide water to users during high demand events. The ABR
eliminated the ability of each community to provide the maximum day flow to customers.
a. For Farmville, essentially all of the transferred water will replace the groundwater
removed by the CCPCUA rules. The bulk water projections applied to the diurnal
pattern show that Farmville will not begin to exceed the ABR x the selected
peaking factor until approximately 2023. If the historic maximum day peaking
factor is used compared in lieu of the selected peaking factor, then the water
transferred would be considered a total replacement.
b. For Greene County, all of the transferred water will replace the groundwater
removed by the CCPCUA rules. The bulk sale projections do not approach the
ABR x the selected peaking factor until approximately 2028.
c. For Winterville, the 1999 ABR was extremely low compared to the growth the
town has experienced between 2000 and 2008. The IBT calculations for
Appendix 1 A69
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Winterville used a peaking factor that is below the minimum historic peaking
factor and significantly lower than the historic maximum peaking factor. Even
though the transferred water can not necessarily be considered a replacement
due to the CCPCUA rules, the peaking factor Winterville must adhere to is
significantly lower than the historic peak. Consistent with other capacity use
communities, the ability to meet a maximum day demand via a peaking factor is
how the Winterville system was operating for years prior to the CCPCUA rules.
5. Banked water will be used in those instances where Greenville Utilities must curtail water.
6. The IBT calculations are based on a reduction in peaking factor from historic use. Additionally,
the maximum day bulk sale effectively reduces the overall IBT amount by using groundwater to
help meet demand.
Conclusions
The IBT Management Strategy was developed to provide a sustainable water supply solution for Greene
County, Farmville, and Winterville. The CCPCUA rules eliminated the ability of these communities to
provide the maximum day water demand that is required of water systems. Additionally, the IBT
Management Strategy uses each community’s allowable groundwater pumping capacity to help meet
water demands for the maximum day demand, effectively reducing the total amount of the transfer.
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Appendix 1 A74
Appendix 2 A75
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To Copies:
Toya Ogallo and Steve Reed
DENR, Division of Water Resources
Kevin Martin and Stan Crowe
Environmental Management Commission
Steve Porter, Greenville Utilities
Randy Emory, Greenville Utilities
Tony Cannon, Greenville Utilities
Ron Elks, Greenville Utilities
Richard Wyche, ARCADIS
From:
Mary Sadler, Hazen and Sawyer
Date: ARCADIS Project No.:
July 27, 2010 NC706015.0030
Subject:
Summary of Water Conservation Requirements per CCPCUA Rules
Hearing Officer’s Report Request for Additional Information
Greenville Utilities Commission Interbasin Transfer Certification
In June, the Hearing Officer’s requested more information on the status of the water conservation
measures contained in the Central Coastal Plain Capacity Use Area (CCPCUA) Rules for the Town of
Farmville, the Town of Winterville, Greene County, and Greenville Utilities. The six water conservation
points specified in the CCPCUA Rules are as follows:
1. Adoption of water-conservation based rate structure (flat, increasing block, etc.).
2. Implementation of water loss reduction program if unaccounted for water is greater
than 15%.
3. Adoption of a water conservation ordinance for irrigation.
4. Implementation of a retrofit program that makes available indoor water conservation
devices to customers.
5. Implementation of a public education program.
6. Evaluation of the feasibility of water reuse as a means of conservation.
Table 1 provides a matrix table for each community with respect to their progress on each of the six
CCPCUA water conservation requirements. Documentation is provided in the referenced attachments, if
applicable. Table 1 also provides an implementation schedule for any outstanding items.
ARCADIS
801 Corporate Center Drive
Suite 300
Raleigh
North Carolina 27607
Tel 919.854.1282
Fax 919.854.5448
Appendix 3 A76
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2/3
Table 1: Summary of Water Conservation Measures per CCPCUA Rules for Greenville Utilities, Farmville, Greene County, and
Winterville
Water
Conservation
Measure Greenville Utilities Town of Farmville Greene County Town of Winterville
1. Adoption of water-
conservation based
rate structure (flat,
increasing block,
etc.).
Greenville Utilities has a flat
rate structure with an
increasing monthly base rate
per meter size.
See Attachment GUC1.
In 2008, the Town adopted
a water rate structure that
specifies a flat rate for the
first 2,000 gallons, an
increasing rate up to 3,000
gallons, a decline in rate up
to 4,000 gallons, and an
increase in rate over 5,000
gallons.
See Attachment F1.
In 2007, the County
adopted a flat rate
structure for residential
customers.
See Attachment GC1.
The Town is considering an
increasing rate structure that
will have a higher cost for
higher consumption rates.
Schedule for implementation
expected July 2011 (start of
2011-2012 fiscal year).
See Attachment W1.
2. Implementation of
water loss reduction
program if
unaccounted for
water is greater than
15%.
Greenville Utilities performed a
Water Audit in 2009. The Audit
reported a total water loss of
8.7%. Therefore, a water loss
reduction program is not
needed.
See Attachment GUC2.
The Town’s unbilled water
percentage is 7.4%.
Therefore, a water loss
reduction program is not
needed.
See Attachment F2.
PENDING The Town’s unbilled water
percentage is 4%. Therefore,
a water loss reduction
program is not needed.
See Attachment W2.
3. Adoption of a water
conservation
ordinance for
irrigation.
PENDING PENDING PENDING The Town does have
irrigation meters.
The Town expects that an
irrigation ordinance will be in
place by June 30, 2011.
4. Implementation of a
retrofit program that
makes available
indoor water
conservation devices
to customers
PENDING The County passed a
resolution that applies
credits towards a water bills
for the installation of
standard fixtures for low
flow fixtures.
See Attachment F4.
The County passed a
resolution that applies
credits towards a water
bills for the installation of
standard fixtures for low
flow fixtures.
See Attachment GC4.
The Town is considering
elements of water
conservation retrofit programs
around the country.
Winterville also provides
energy audits for residents
upon request.
Work is underway for a more
comprehensive retrofit
program. The Town expects a
retrofit program to be
Appendix 3 A77
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Table 1: Summary of Water Conservation Measures per CCPCUA Rules for Greenville Utilities, Farmville, Greene County, and
Winterville
Water
Conservation
Measure Greenville Utilities Town of Farmville Greene County Town of Winterville
complete by July 2012.
See Attachment W4.
5. Implementation of a
public education
program.
Greenville Utilities has an
extensive public education
program: brochures, billboards,
radio announcements, website
links, etc. Greenville Utilities is
also a member of the “Water,
Use It Wisely” campaign.
Greenville Utilities is also
extremely proactive is getting
the message out during
triggered Stage 1, 2, and 3
water conservation
requirements during drought.
See Attachment GUC5.
The Town has given water
conservation presentations
since 1999.
See Attachment F5.
Conservation information
is displayed on monthly
billing statements.
Information is also
available as posters on
the Water Department
bulletin board.
Greene County adopted
the North Carolina
Plumbing Code in 1999.
See Attachment GC5.
The Town implements a
public information brochure
“Water Conservation Starts at
Home.” This brochure is
mailed to individual
households twice per year
and made available at the
Town Hall, Police Station,
Planning Office, and Library.
The Town has developed a
Winterville Utility
Conservation Program
Proposal. It is expected that
elements of this Program will
be implemented by July 2012.
See Attachment W5.
6. Evaluation of the
feasibility of water
reuse as a means of
conservation.
Greenville Utilities
Commissioned a Reclaimed
Water Feasibility Analysis in
1999. The analysis
recommended a reuse
demonstration project at two
locations. The Report also
provided cost estimates for
implementing reuse
alternatives. GUC has not
implemented any reuse
projects at this time.
See Attachment GUC6.
A 2005 study was
completed that included a
discussion of water reuse
for Farmville and Greene
County. The report
indicated that Farmville
completed a reuse project
in 2003 to pump reclaimed
effluent to a local golf
course for irrigation.
See Attachment F6.
A 2005 study was
completed that included a
discussion of water reuse
for Farmville and Greene
County. The report
identified potential reuse
customer; however, the
existing waste treatment
facilities in Greene County
would require significant
upgrades to achieve reuse
quality water.
See Attachment GC6.
The Town has implemented
to industrial reuse projects in
recent years. The first is the
Winterville Machine Works
Company that uses reclaimed
water as well as internal
recycling. The second facility,
now closed, was the Fullerton
plant that used reclaimed
water in the industrial cooling
process.
See Attachment W6.
Appendix 3 A78
Appendix 3 A79
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Appendix 3 A82
Appendix 3 A83
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Appendix 3 A168
Appendix 3 A169
Appendix 3 A170
Appendix 3 A171
Appendix 3 A172
Appendix 3 A173
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Appendix 3 A175
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Appendix 3 A178
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Appendix 3 A181
Appendix 3 A182
Appendix 3 A183
Appendix 3 A184
Appendix 3 A185
Appendix 3 A186
Appendix 3 A187
Appendix 3 A188
Appendix 3 A189
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To: Copies:
Toya Ogallo and Steve Reed
DENR, Division of Water Resources
Kevin Martin and Stan Crowe
Environmental Management Commission
Steve Porter, Greenville Utilities
Randy Emory, Greenville Utilities
Tony Cannon, Greenville Utilities
Ron Elks, Greenville Utilities
Richard Wyche, ARCADIS
From:
Mary Sadler, Hazen and Sawyer
Date: ARCADIS Project No.:
July 21, 2010 NC706015.0030
Subject:
Environmental and Economic Impacts of Water Supply Alternatives
Hearing Officer’s Report Request for Additional Information
Greenville Utilities Commission Interbasin Transfer Certification
Introduction
In June 2010, the Hearing Officers requested more information on the economic and environmental
impacts of water supply alternatives to the proposed Interbasin transfer (IBT) for Greenville Utilities. This
request was prompted by comments received during the public comment period. The Final Environmental
Assessment (EA) provided an alternative analysis on several water supply options. This Technical
Memorandum (TM) provides more detailed information on the economic and environmental impacts of
water supply alternatives for Greene County, Farmville, and Winterville.
Description of Water Supply Alternatives
Five water supply alternatives were determined to be viable sources for Farmville, Greene County, and
Winterville, as follows:
Alternative 1.A – New 4 million gallons per day (mgd) water treatment plant
(WTP) on Contentnea Creek.
Alternative 1.B – New 13.5 mgd WTP and reservoir on Contentnea Creek.
Alternative 2.A – New surficial aquifer well field and five 2 mgd WTPs.
Alternative 2.B – New surficial aquifer well field and 13.5 mgd nanofiltration WTP.
Alternative 3 – Purchase of finished water from Neuse Regional Water and
Sewer Authority (NRWASA).
Alternative 4 – Purchase of finished water from the City of Wilson.
Alternative 5 – Purchase of finished water from Greenville Utilities.
ARCADIS
801 Corporate Center Drive
Suite 300
Raleigh
North Carolina 27607
Tel 919.854.1282
Fax 919.854.5448
Appendix 4 A190
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2/15
Alternatives 1.A / 1.B and 2.A / 2.B reflect the differences in the water supply project(s) as described by
McDavid and Associates (Preliminary Engineering Report Alternative Water Supply Evaluation for Greene
County and Farmville, 2004) and ARCADIS (Final Environmental Assessment for Greenville Utilities
Commission Interbasin Transfer, 2008). Alternative 1.A, as described by McDavid and Associates, only
considered a surface water source for a capacity equivalent to the safe yield on Contentnea Creek
(e.g., 4 mgd). A reservoir for storage was not considered. Alternative 1.A is presented herein for
consistency with the alternatives as presented in the 2004 Preliminary Engineering Report (PER);
however, this alternative would not be sufficient to meet long-term water supply demands for any of the
three communities. Alternative 1.B (ARCADIS, 2008) provides a surface water supply alternative intended
to achieve long-term water supply demand with a larger water treatment plant and a reservoir.
Alternatives 2.A and 2.B also reflect the differences in the surficial aquifer and treatment alternatives.
Alternative 2.A, per the 2004 PER, assumes that five small water treatment plants would be located in the
vicinity of Farmville and throughout Greene County. This alternative would not serve the Town of
Winterville. Alternative 2.B, per the 2008 ARCADIS Environmental Assessment (EA), assumes one larger
water treatment plant and well field would be centrally located to serve all three communities.
Assumptions Used in Analysis
Tables 2 and 3 provide a summary of the construction costs and expected water use rates for the five
water supply alternatives for Greene County-Farmville and Winterville, respectively. Construction costs in
2004 and 2008 dollars, provided by McDavid and Associates and ARCADIS, respectively, were updated
to 2010 dollars per Engineering News Record (ENR) Construction Cost Indices. Water use rates were
updated from 2004 to 2010 dollars using the Consumer Price Index. In the event that a water use rate was
not provided, a rate was estimated using the water use rates provided by McDavid and Associates. Where
applicable, water use rates were increased proportionally to the estimated construction cost to reflect the
increased cost of larger infrastructure.
Tables 4 and 5 provide a summary of the environmental impacts associated with the water supply
alternatives for Greene County-Farmville and the Town of Winterville, respectively. The information
provided in Tables 4 and 5 were obtained from an analysis of readily available Geologic Information
System (GIS) data. The data review included an analysis of twenty-one potential environmental impacts,
ranging from 100-year floodplain impacts, streams, wetlands, 303d impaired waters, etc. Table 6 provides
a list of the GIS data reviewed for this TM. If applicable, quantification of the environmental impacts was
determined, such as the number of stream crossings and the acres of expected wetland impacts.
A majority of the information pertaining to the water supply alternatives discussed herein was obtained
and compiled from several engineering sources. In a few instances, gaps in information were found
between the different reports and various alternatives. These information gaps were filled based on best
available information.
Appendix 4 A191
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Summary of Environmental and Economic Impacts of Water Supply Alternatives
Table 1 provides a summary and comparison of the economic and environmental impacts of the water
supply alternatives for Greene County-Farmville and Winterville. Tables 2 through 5 should be consulted
for detailed information.
The only alternatives not resulting in an Interbasin transfer are the construction of surficial wells and water
treatment plants (Alternative 2.A / 2.B). However, surficial well fields and treatment may not be viable if the
Division of Water Resources (DWR) were to implement a capacity use rule in this aquifer. All of the other
water supply alternatives result in an Interbasin transfer for Winterville, Greene County, and Farmville
individually or collectively.
The reservoir alternative has the greatest economic and environmental impact. A reservoir in Greene
County would be difficult to construct due to the fairly flat topography. Additionally, this alternative is not
feasible due to the large array of environmental and public issues. A significant amount of private industry
and public land would be affected by this alternative. Construction of a reservoir also results in a high
economic impact due to capital cost and debt service.
The purchase of finished water from the City of Wilson and NRWASA carry a high capital cost and/or debt
service required for implementation. The environmental impacts for these two alternatives are similar.
Furthermore, Winterville would be required to obtain an Interbasin transfer for the City of Wilson water
supply alternative. All three communities would be required to obtain an Interbasin transfer for the
NRWASA water supply alternative.
The purchase of finished water from Greenville Utilities is the selected water supply alternative for several
reasons. This alternative is the most economical in capital cost and debt service. With the exception of the
transmission lines, this alternative uses an existing water treatment plant and intake and therefore
eliminates the need for a larger infrastructure project. The environmental impact of the transmission mains
is similar to the purchase of finished water from the City of Wilson and NRWASA.
Appendix 4 A192
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Table 1: Comparison of Economic and Environmental Impacts of Water Supply alternatives for
Greene County-Farmville and Winterville
Greene County-Farmville Town of Winterville
Alternative 1.A – New 4 mgd WTP on Contentnea Creek
Not a sustainable engineering solution (a 4 mgd water
supply capacity not sufficient for long-term demand).
This water supply alternative is not applicable to the Town
of Winterville. The McDavid and Associates PER (2004)
did not consider Winterville as part of this alternative. Construction of 31 miles of transmission line and WTP.
20 acres of wetlands impacted.
45 stream crossings with one stream noted as an
anadromous fish spawning area.
Alternative 1.B – New 13.5 mgd WTP and Reservoir on Contentnea Creek
Order of magnitude higher in capital cost than other alternatives and would result in
high water use rates to pay down the debt service.
Environmental studies and permitting required for the construction of new reservoir
may require up to 10 years to complete. This option will not meet the near term need
to replace the reductions in groundwater withdrawal as required by CCPCUA Rule
Construction of a reservoir is not a feasible engineering solution due to
environmental impact and fairly flat topography in Greene County.
Construction of 43 miles of transmission line, a water
treatment plant, and 9,500 acre reservoir.
Construction of 55 miles of transmission line, a water
treatment plant, and 9,500 acre reservoir.
Significant impacts to 100-year floodplain, wetlands,
streams, and important forestland.
Significant impacts to 100-year floodplain, wetlands,
streams, and important forestland.
One anadromous fish spawning stream crossing. One anadromous fish spawning stream crossing.
Significant use of resources (>15 mi2 for reservoir). Significant use of resources (>15 mi2 for reservoir).
13 permitted animal operations within the reservoir and
21 additional operations within 2 miles of the reservoir.
13 permitted animal operations within the reservoir and
21 additional operations within 2 miles of the reservoir.
Three threatened and endangered species populations
noted within one mile of the reservoir.
Three threatened and endangered species populations
noted within one mile of the reservoir.
A significant natural heritage area within reservoir. A significant natural heritage area within the reservoir.
1 school, 3 churches, & 1 library in 0.5 mile of reservoir. 1 school, 3 churches, & 1 library in 0.5 mile of reservoir.
Interbasin transfer.
Alternative 2.A – New Surficial Aquifer Well Field and Five 2 mgd WTPs
Higher construction costs than other alternatives. This water supply alternative is not applicable to the Town
of Winterville. The McDavid and Associates PER (2004)
did not consider Winterville as part of this alternative. This alternative would not be viable if DWR were to
implement a capacity use rule in the surficial aquifer
similar to the CCPCUA Rule in the Cretaceous aquifer.
Construction of 43 miles of transmission line, five water
treatment plants, and 20 wells.
23 acres of wetlands impacted.
38 stream crossings with 2 streams noted as
anadromous fish spawning areas.
One threatened and endangered species population
noted adjacent to a corridor.
Alternative 2.B – New Surficial Aquifer Well Field and 13.5 mgd nanofiltration WTP
Significantly higher construction costs than other alternatives.
This alternative would not be viable if DWR were to implement a capacity use rule in
the surficial aquifer similar to the CCPCUA Rule in the Cretaceous aquifer.
Construction of 41 miles of transmission line, a water
treatment plant, and 30 wells.
Construction of 53 miles of transmission line, a water
treatment plant, and 30 wells.
Appendix 4 A193
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Table 1: Comparison of Economic and Environmental Impacts of Water Supply alternatives for
Greene County-Farmville and Winterville
Greene County-Farmville Town of Winterville
26 acres of wetlands impacted. 30 acres of wetlands impacted.
51 stream crossings with 2 streams noted as
anadromous fish spawning areas.
63 stream crossings with 2 streams noted as anadromous
fish spawning areas.
A threatened and endangered species population
noted adjacent to a corridor.
A threatened and endangered species population noted
adjacent to a corridor.
Alternative 3 – Purchase of Finished Water from Neuse Regional Water and Sewer Authority
A water use rate that is three times higher than the alternative to purchase finished
water from Greenville Utilities.
NRWASA members are contractually obligated to purchase a minimum of
75 percent of a member’s 2002 water use in order to pay down the debt service on
the new infrastructure. This obligation applies even if less water is required for a
particular year.
Construction of 21 miles of transmission line. Construction of 26 miles of transmission line.
Interbasin transfer. Interbasin transfer.
13 acres of wetlands impacted. 23 acres of wetlands impacted.
22 stream crossings with one stream noted as an
anadromous fish spawning area.
30 stream crossings with one stream noted as an
anadromous fish spawning area.
A threatened and endangered species population noted
adjacent to a corridor.
Alternative 4 – Purchase of Finished Water from the City of Wilson
Purchasing finished water from the City of Wilson requires a $12.5 million surcharge
and higher water use rates than the alternative to purchase finished water from
Greenville Utilities.
Not an economically feasible alternative for Winterville independently. Winterville
would need to tie-in to Farmville and Greene County infrastructure.
Construction of 75 miles of transmission line. Construction of 87 miles of transmission line.
35 acres of wetlands impacted. Interbasin transfer.
55 stream crossings with 2 streams noted as
anadromous fish spawning areas.
67 stream crossings with 2 streams noted as anadromous
fish spawning areas.
39 acres of wetlands impacted.
A threatened and endangered species population noted
adjacent to a corridor.
Alternative 5 – Purchase of Finished Water from Greenville Utilities
Most economical water supply alternative.
No surcharge rate.
Water use rates reflect the wholesale cost of water with increases tied to the
Consumer Price Index and not debt service payoff.
Use of existing treatment plant and raw water intake.
Construction of 31 miles of transmission line. Construction of a booster pump station.
Interbasin transfer. Interbasin transfer.
21 acres of wetlands impacted.
35 stream crossings with one stream noted as an
anadromous fish spawning area.
Three threatened and endangered species populations
noted adjacent to corridors.
Appendix 4 A194
Page:
6/15
Table 2: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Greene County and Farmville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
1.A New 4.0 mgd Water
Treatment Plant on
Contentnea Creek
$28,260,000 $33,554,000 $1.50 $1.72 1. The 2004 capital cost and rate is from
McDavid and Associates PER dated December
4, 2004.
2. The 2010 usage rate was estimated based on
the Consumer Price Index.
3. McDavid and Associates PER states that a
4 mgd plant capacity is not sufficient to meet
long-term water supply demands.
4. The water treatment plant costs were
estimated by McDavid and Associates at $3.00
per gallon, which is a low estimate for water
plant construction.
1.B New 13.5 mgd Water
Treatment Plant and
Reservoir on
Contentnea Creek
$100,000,000 $100,900,000
$5.18 1. The 2008 capital cost is from ARCADIS Final
EA for GUC Interbasin Transfer, dated
November 2008.
2. Total water treatment plant capacity as stated
in the EA includes the Town of Winterville. Plant
capacity includes 2030 maximum day demand to
meet long-term water supply needs.
3. The Final EA (ARCADIS, 2008) states that
capital costs will most likely exceed stated
estimate, depending on specific factors during
design.
4. The usage rate was increased proportionally
to reflect the cost of larger WTP and reservoir.
2.A New Surficial Aquifer
Well Field and Five
(5) 2 mgd Water
Treatment Plants in
Greene County and
Farmville
$48,163,550
$57,186,000 $1.50 $1.72 1. The 2004 capital cost and rate is from
McDavid and Associates PER dated December
4, 2004.
2. The 2010 usage rate was estimated based on
the Consumer Price Index.
3. The water treatment plant costs were
estimated by McDavid and Associates at $2.00
per gallon, which is a low estimate for water
plant construction.
2.B New Surficial Aquifer
Well Field and 13.5
mgd Nanofiltration
Water Treatment
Plant
$70,000,000 $70,600,000
$2.12 1. The 2008 capital cost is from ARCADIS Final
EA for GUC Interbasin Transfer, dated
November 2008.
2. The rate per 1000 gallons was estimated
based on usage rates provided by McDavid and
Associates and increased proportionally to
reflect the cost of larger WTP.
Appendix 4 A195
Page:
7/15
Table 2: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Greene County and Farmville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
3. Purchase Finished
Water from Neuse
Regional Water and
Sewer Authority
$33,681,000 $39,990,000 $3.03 $3.34
(Expected to be
greater than
$4.00 in fiscal
year 2011)
1. Capital cost reflects the internal improvements
needed to distribute purchased water to existing
elevated storage tanks. The 2004 capital cost
and rate is from McDavid and Associates PER
dated December 4, 2004.
2. The capital cost of the NRWASA treatment
plant and large distribution mains, per the
Certified Bid Tab, is $115 million. City of Kinston
website states total construction cost is at $144
million.
3. The water use rate reflects the debt service
required to pay for the new water treatment plant
and large distribution mains. The debt service for
the construction cost of the tie-in would be an
additional cost to the stated usage rate.
4. NRWASA members are contractually
obligated to an annual 75% minimum purchase
based on 2002 water use. This obligation applies
even if less water is required for a particular
year.
5. The 2010 usage rate was obtained from
NRWSA.
4. Purchase Finished
Water from the City
of Wilson
$25,804,190
$30,638,000 $1.75 $2.19
($12.5 million
surcharge either a
lump sum, factored
into usage rate, or
annual payment of
approximately
$500,000 per year)
1. The 2004 capital cost and rate is from
McDavid and Associates PER dated December
4, 2004.
2. One time capacity charge (connection fee) of
$2.50 per gallon per day demand, equating to a
$12,500,000 surcharge for 5 mgd.
3. Wilson agreed to rates comparable to existing
Wilson customers starting at $1.75 / 1000
gallons. The percent increase between 2005 and
2009 is 125% ($29.78 in 2009 / $23.84 in 2005)
4. The current Wilson residential rate inside the
City limit is $3.37 per ccf, which equates to
$4.52 / 1000 gallons.
5. The usage rate reflects the debt service
required to pay for the new NRWASA water
treatment plant and large distribution mains. The
debt service for the construction cost of the tie-in
would be an additional cost to the stated usage
rate.
Appendix 4 A196
Page:
8/15
Table 2: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Greene County and Farmville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
5. Purchase Finished
Water from the
Greenville Utilities
Commission
$30,695,417 $1.29 $1.48 1. The 2008 capital cost is from ARCADIS Final
EA for GUC Interbasin Transfer, dated
November 2008.
2. The project to purchase water from GUC has
been implemented in three phases: Phase 1A
has been bid (connection from GUC to Pitt
County master meter), Phase 1B is the tie-in to
Farmville's distribution system, and Phase 1C is
the tie-in to Greene County's distribution system.
3. The 2010 usage rate is based on the Water
Purchase Agreements between Greenville
Utilities and Farmville / Greene County. The debt
service for the construction cost of the tie-in
would be an additional cost to the stated usage
rate or could be covered with the existing usage
rate.
4. Usage rate increases are tied to the
Consumer Price Index.
1 Engineering News Record (ENR) construction cost indices: December 2004 = 7380, November 2008 = 8602, and April 2010 = 8677. 2 The Consumer Price Index in 2004 was 188.9. The index in 2010 is 216.741.
Appendix 4 A197
Page:
9/15
Table 3: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Winterville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
1.A New 4.0 mgd Water
Treatment Plant on
Contentnea Creek
N/A N/A N/A N/A N/A 1. This water supply alternative is not applicable
to the Town of Winterville. The McDavid and
Associates PER (2004) stated that a 4 mgd plant
capacity is not sufficient to meet long-term water
supply demands. Additionally, the PER did not
consider Winterville as part of this alternative.
1.B New 13.5 mgd Water
Treatment Plant and
Reservoir on
Contentnea Creek
$100,000,000 $100,900,000
$5.18 1. The 2008 capital cost is from ARCADIS Final
EA for GUC Interbasin Transfer, dated
November 2008.
2. Total water treatment plant capacity as stated
in the EA includes the Town of Winterville. Plant
capacity includes 2030 maximum day demand to
meet long-term water supply needs.
3. The Final EA (ARCADIS, 2008) states that
capital costs will most likely exceed stated
estimate, depending on specific factors during
design.
4. The usage rate cost was increased
proportionally to reflect the cost of larger WTP
and reservoir.
2.A
New Surficial Aquifer
Well Field and Five
(5) 2 mgd Water
Treatment Plants in
Greene County and
Farmville
N/A
N/A
N/A
N/A
N/A
1. This water supply alternative is not applicable
to the Town of Winterville. The McDavid and
Associates PER (2004) did not consider
Winterville as part of this alternative.
2.B New Surficial Aquifer
Well Field and
13.5 mgd
Nanofiltration Water
Treatment Plant
$70,000,000 $70,600,000
$2.12 1. The 2008 capital cost is from ARCADIS Final
EA for GUC Interbasin Transfer, dated
November 2008.
2. The rate per 1000 gallons was estimated
based on usage rates provided by McDavid and
Associates and increased proportionally to
reflect the cost of a larger WTP.
Appendix 4 A198
Page:
10/15
Table 3: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Winterville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
3. Purchase Finished
Water from Neuse
Regional Water and
Sewer Authority
$6,246,000 $3.03 $3.34
(Expected to be
greater than
$4.00 in fiscal
year 2011)
1. Capital costs of a tie-in with Greene County’s
water distribution system were not stated in the
Water Supply Master Plan (Wooten Company,
2001). Therefore, the capital cost for this
alternative was estimated as part of this Hearing
Officer’s request for information.
2. The capital cost of the NRWASA treatment
plant and large distribution mains, per the
Certified Bid Tab, is $115 million. City of Kinston
website states total construction cost is at $144
million.
3. The usage rate reflects the debt service
required to pay for the new NRWASA water
treatment plant and large distribution mains. The
debt service for the construction cost of the tie-in
would be an additional cost to the stated usage
rate.
4. NRWASA members are contractually
obligated to an annual 75% minimum purchase
based on 2002 water use. This obligation applies
even if less water is required for a particular
year.
5. The 2010 usage rate was obtained from
NRWASA.
4. Purchase Finished
Water from the City
of Wilson
$2,883,000 $1.75 $2.19
($12.5 million
surcharge either a
lump sum, factored
into usage rate, or
annual payment of
approximately
$500,000 per year)
1. This alternative was not evaluated in the
Water Supply Master Plan (Wooten, 2001).
However, the alternative would be feasible if a
tie-in were made to Greene County’s distribution
system. The capital cost for this alternative was
estimated as part of this Hearing Officer’s
request for information.
2. One time capacity charge (connection fee) of
$2.50 per gallon per day demand, equating to a
$12,500,000 surcharge for 5 mgd.
3. Wilson agreed to rates comparable to existing
Wilson customers starting at $1.75 / 1000
gallons. The percent increase between 2005 and
2009 is 125% ($29.78 in 2009 / $23.84 in 2005).
4. The current Wilson residential rate inside the
City limit is $3.37 per ccf, which equates to
$4.52 / 1000 gallons.
Appendix 4 A199
Page:
11/15
Table 3: Summary of Water Supply Alternative Capital Cost and Water Use Rates for Winterville
Water Supply
Alternative
Construction
Cost (2004$)
Construction
Cost (2008$)
Construction
Cost (2010$)
Expected Usage
Rate in 2004
(per 1000 gallons
treated)
Expected Usage
Rate in 2010
(per 1000 gallons
treated) Comments
5. The usage rate reflects the debt service
required to pay for the new NRWASA water
treatment plant and large distribution mains. The
debt service for the construction cost of the tie-in
would be an additional cost to the stated usage
rate.
5. Purchase Finished
Water from the
Greenville Utilities
Commission
$200,000
(2001$)
$276,000 $1.29 $1.48 1. The 2001 capital cost is from the Water
Supply Master Plan (Wooten, 2001).
2. The usage rate reflects the debt service
required to pay for the new NRWASA water
treatment plant and large distribution mains. The
debt service for the construction cost of the tie-in
would be an additional cost to the stated usage
rate or could be covered with the existing
Winterville usage rate.
3. The 2010 usage rate is based on the Water
Purchase Agreements between Greenville
Utilities and Farmville / Greene County.
4. Usage rate increases are tied to the
Consumer Price Index.
1 Engineering News Record (ENR) construction cost indices: May 2001= 6288, December 2004 = 7380, November 2008 = 8602, and April 2010 = 8677. 2 The Consumer Price Index in 2004 was 188.9. The index in 2010 is 216.741.
Appendix 4 A200
Page:
12/15
Table 4 Summary of Water Supply Alternative Environmental Impacts for Farmville and Greene County
Water Supply
Alternative In
t
e
r
b
a
s
i
n
T
r
a
n
s
f
e
r
10
0
-
Y
e
a
r
Fl
o
o
d
p
l
a
i
n
I
m
p
a
c
t
s
(a
c
r
e
s
)
We
t
l
a
n
d
s
(
a
c
r
e
s
)
St
r
e
a
m
s
C
r
o
s
s
e
d
(D
W
Q
C
l
a
s
s
i
f
i
e
d
)
St
r
e
a
m
s
C
r
o
s
s
e
d
(D
W
Q
U
n
c
l
a
s
s
i
f
i
e
d
)
Im
p
o
r
t
a
n
t
Fo
r
e
s
t
l
a
n
d
(
a
c
r
e
s
)
30
3
(
d
)
L
i
s
t
e
d
Im
p
a
i
r
e
d
W
a
t
e
r
s
An
a
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r
o
m
o
u
s
F
i
s
h
Sp
a
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A
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Fe
d
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a
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t
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Ow
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St
a
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M
u
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p
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Pa
r
k
s
Hi
g
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Q
u
a
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Ou
t
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t
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Re
s
o
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W
a
t
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s
Ha
z
a
r
d
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s
W
a
s
t
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Fa
c
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l
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s
Hi
s
t
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c
N
a
t
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n
a
l
Re
g
i
s
t
e
r
D
i
s
t
r
i
c
t
s
/
St
r
u
c
t
u
r
e
s
NP
D
E
S
S
i
t
e
s
No
n
-
d
i
s
c
h
a
r
g
e
Sy
s
t
e
m
s
La
n
d
f
i
l
l
s
Pe
r
m
i
t
t
e
d
A
n
i
m
a
l
Op
e
r
a
t
i
o
n
s
Na
t
u
r
a
l
H
e
r
i
t
a
g
e
Oc
c
u
r
r
e
n
c
e
S
i
t
e
s
(T
&
E
s
)
Si
g
n
i
f
i
c
a
n
t
N
a
t
u
r
a
l
He
r
i
t
a
g
e
A
r
e
a
s
Sc
h
o
o
l
s
,
L
i
b
r
a
r
y
’
s
,
or
C
h
u
r
c
h
e
s
La
n
d
M
a
n
a
g
e
d
f
o
r
Co
n
s
e
r
v
a
t
i
o
n
a
n
d
Op
e
n
S
p
a
c
e
a
n
d
Re
c
r
e
a
t
i
o
n
a
l
L
a
n
d
s
Source of
Impacts
1.A
New 4.0 mgd
WTP on
Contentnea
Creek
No 17 20
(20
sites)
8 37 17 Yes
1 stream
Yes
1
stream
No No No Yes
1 within
600 feet of
corridor
No No No No No No No No No 1. Construct
31 miles of
transmission
line.
2. Construct a
WTP.
1.B
New 13.5 mgd
WTP and
Reservoir on
Contentnea
Creek
No 3,745
(100-year
floodplain)
4,398
(floodway)
4,450
(>200
sites)
13 58 1,982 Yes
1 stream
Yes
1
stream
No No No Yes
1 within
600 feet of
corridor
Yes
3 structures
and 1
district
within 2
miles of
reservoir
Yes
1 site
within
reservoir
and 1 site
0.7 mile
upstream
of reservoir
No Yes
1.9
miles
from
reservoir
Yes
34
within 2
miles of
reservoir
Yes
3 within 1
mile of
reservoir
Yes
1 site
Yes
1 school,
3
churches,
1 library
within 0.5
mile of
reservoir
Yes
81
acres of
land
man-
aged for
conser-
vation
1. Construct
43 miles of
transmission
line
2. Construct a
WTP.
3. Construct a
9,518-acre
reservoir.
2.A
New Surficial
Aquifer Well
Field and Five
(5) 2 mgd WTPs
in Greene
County and
Farmville
No 21 23
(21
sites)
8 30 11 Yes
1 stream
Yes
2
streams
No No No Yes
1 within
600 feet of
corridor
Yes
1 structure
and 1
district
adjacent to
corridor
No Yes
1 site
No No Yes
1 within or
adjacent
to corridor
No No No 1. Construct
35 miles of
transmission
line.
2. Install 20 wells
3. Construct five
WTPs.
2.B
New Surficial
Aquifer Well
Field and 13.5
mgd
Nanofiltration
WTP
No 21 26
(29
sites)
9 42 11 Yes
1 stream
Yes
2
streams
No No No Yes
1 within
600 feet of
corridor
Yes
1 structure
and 1
district
adjacent to
corridor
No Yes
1 site
No No Yes
1 within or
adjacent
to corridor
No No No 1. Construct
41 miles of
transmission
line.
2. Install 30 wells.
3. Construct a
WTP.
3. Purchase
Finished Water
from Neuse
Regional Water
and Sewer
Authority
Yes 15 13
(14
sites)
8 14 3 No Yes
1
stream
Yes
1 site
No No Yes
1 within
600 feet of
corridor
No No No No No No No No No 1. Construct
21 miles of
transmission
line.
4. Purchase
Finished Water
from the City of
Wilson
No 35 35
(46
sites)
19 36 13 Yes
1 stream
Yes
2
streams
No No No No 4 NR and 3
state listed
districts
and 4 NR
structures
No No No No No No No No 1. Construct
75 miles of
transmission
line.
5.
Purchase
Finished Water
from the
Greenville
Utilities
Commission
Yes 20 21
(21
sites)
8 27 18 Yes
2
streams
Yes
1
stream
No No No Yes
1 within
600 feet of
corridor
No No No No No Yes
3 within or
adjacent
to corridor
No No No 1. Construct
31 miles of
transmission
line.
Appendix 4 A201
Page:
13/15
Table 5: Summary of Water Supply Alternative Environmental Impacts for Winterville
Water Supply
Alternative In
t
e
r
b
a
s
i
n
T
r
a
n
s
f
e
r
10
0
-
Y
e
a
r
Fl
o
o
d
p
l
a
i
n
I
m
p
a
c
t
s
(a
c
r
e
s
)
We
t
l
a
n
d
s
(
a
c
r
e
s
)
St
r
e
a
m
s
C
r
o
s
s
e
d
(D
W
Q
C
l
a
s
s
i
f
i
e
d
)
St
r
e
a
m
s
C
r
o
s
s
e
d
(D
W
Q
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c
l
a
s
s
i
f
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d
)
Im
p
o
r
t
a
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t
Fo
r
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s
t
l
a
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d
(
a
c
r
e
s
)
30
3
(
d
)
L
i
s
t
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d
Im
p
a
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d
W
a
t
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s
An
a
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o
m
o
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s
F
i
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Sp
a
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M
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y
/
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Re
s
o
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r
c
e
W
a
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s
Ha
z
a
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d
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s
W
a
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t
e
Fa
c
i
l
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t
i
e
s
Hi
s
t
o
r
i
c
N
a
t
i
o
n
a
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Re
g
i
s
t
e
r
D
i
s
t
r
i
c
t
s
/
St
r
u
c
t
u
r
e
s
NP
D
E
S
S
i
t
e
s
No
n
-
d
i
s
c
h
a
r
g
e
Sy
s
t
e
m
s
La
n
d
f
i
l
l
s
Pe
r
m
i
t
t
e
d
A
n
i
m
a
l
Op
e
r
a
t
i
o
n
s
Na
t
u
r
a
l
H
e
r
i
t
a
g
e
Oc
c
u
r
r
e
n
c
e
S
i
t
e
s
(T
&
E
s
)
Si
g
n
i
f
i
c
a
n
t
N
a
t
u
r
a
l
He
r
i
t
a
g
e
A
r
e
a
s
Sc
h
o
o
l
s
,
L
i
b
r
a
r
i
e
s
,
or
C
h
u
r
c
h
e
s
La
n
d
M
a
n
a
g
e
d
f
o
r
Co
n
s
e
r
v
a
t
i
o
n
a
n
d
Op
e
n
S
p
a
c
e
a
n
d
Re
c
r
e
a
t
i
o
n
a
l
L
a
n
d
s
Source of
Impacts
1.A
New 4.0 mgd
WTP on
Contentnea
Creek
N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A
1.B
New 13.5 mgd
WTP and
Reservoir on
Contentnea
Creek
Yes 3,751
(100-year
floodplain)
4,398
(floodway)
4,454
(>200
sites)
15 68 1,984 Yes
3
streams
Yes
1
stream
No No No Yes
1 within
600 feet of
corridor
Yes
4 structures
and 2
districts
within 2
miles of
reservoir or
adjacent to
corridor
Yes
1 site
within
reservoir
and 1 site
0.7 mile
upstream
of reservoir
No Yes
1.9
miles
from
reservoir
Yes
34
within 2
miles of
reservoir
Yes
4 within 1
mile of
reservoir
Yes
1 site
Yes
1 school,
3
churches,
1 library
within 0.5
mile of
reservoir
Yes
81
acres of
land
man-
aged for
conser-
vation
1. Construct
55 miles of
transmission
line.
2. Construct a
WTP.
3. Construct a
9,518-acre
reservoir.
2.A
New Surficial
Aquifer Well
Field and Five
(5) 2 mgd WTPs
in Greene
County and
Farmville
N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A
2.B
New Surficial
Aquifer Well
Field and 13.5
mgd
Nanofiltration
WTP
No 23 30
(27
sites)
11 52 13 Yes
1 stream
Yes
2
streams
No No No Yes
1 within
600 feet of
corridor
Yes
1 structure
and 1
district
adjacent to
corridor
No Yes
1 site
No No Yes
1 within or
adjacent
to corridor
No No No 1. Construct
53 miles of
transmission
line.
2. Install 30 wells.
3. Construct a
WTP.
3. Purchase
Finished Water
from Neuse
Regional Water
and Sewer
Authority
Yes 19 23
(16
sites)
10 20 3 Yes
1 stream
Yes
1
stream
Yes
2
sites
No No Yes
1 within
600 feet of
corridor
No No No No No Yes
1 within or
adjacent
to corridor
No No No 1. Construct
26 miles of
transmission
line.
4. Purchase
Finished Water
from the City of
Wilson
Yes 42 39
(51
sites)
21 46 15 Yes
3
streams
Yes
2
streams
No No No No 5 NR and 3
state listed
districts
and 4 NR
structures
No No No No Yes
1 within or
adjacent
to corridor
No No No 1. Construct
87 miles of
transmission
line.
5.
Purchase
Finished Water
from the
Greenville
Utilities
Commission
Yes No No No No No No No No No No No No No No No No No No No No 1. Construct a
booster pump
station.
Appendix 4 A202
Page:
14/15
Table 6: Summary of GIS Data Used in Analysis
Environmental Concern Data Reviewed
100-year Floodplain GIS data published on 16July2008 by the Federal Emergency Management Agency
(FEMA) titled National Flood Hazard Layer and distributed by FEMA.
303(d) List of Impaired
Waters
Review of the draft 1020 303(d) list, as provided in the NC 2010 Integrated Report
Category 5-303(d) List – EPA Submittal 20100329 and draft GIS data published on
3Feb2010 and distributed by the North Carolina Department of Environment and
Natural Resources (NC DENR) Division of Water Quality (DWQ).
Ambient Water Quality
Monitoring Sites
GIS data published on 13Mar2007 by the NC DENR DWQ, Water Quality Section
titled Ambient Water Quality Monitoring Sites and distributed by the North Carolina
Center for Geographic Information and Analysis (NCCGIA).
Anadromous Fish
Spawning Areas
GIS data published on 1Dec1998 by the NCDENR Division of Marine Fisheries
(DMF) titled afsa and distributed by NCCGIA.
Benthic Monitoring Sites GIS data published on 29Apr2003 by the NCDENR DWQ, Environmental Sciences
Branch titled onemap_prod.SDEADMIN.benthic and distributed by NCCGIA.
Federally Owned Land
(including federally owned
game lands)
GIS data published on 29Mar2006 by the NCCGIA titled Federal Land Ownership
and distributed by NCCGIA.
Fish Community Monitoring
Sites
GIS data published on 31Mar2004 by the NC DENR, DWQ titled
onemap_prod.SDEADMIN.dshcmntysts and distributed by NCCGIA.
Fish Nursery Areas
GIS data published by the NC DENR Division of Marine Fisheries (DMF), Information
and Technology Section on 3Dec2008 titled Protected Areas Fishery Nursery Areas
2005 and distributed by the DMF, Information and Technology Section.
Game Lands
GIS data published on 1June2009 by the North Carolina Wildlife Resources
Commission (NC WRC) titled WRC Gamelands and distributed by the NC WRC and
NCCGIA.
Hazardous Substance
Disposal Site
GIS data published on 1Dec1998 by the NC DENR Division of Waste Management
titled onemap_prod.SDEADMIN.hsds and distributed by NCCGIA.
Hazardous Waste Facilities GIS data published by the NC DENR Division of Waste Management on 1Dec1998
titled Hazardous Waste Facilities and distributed by NCCGIA.
High Quality Outstanding
Resource Waters
(HQW/ORW)
GIS data published by the NC DENR DWQ on 7Jun2007 titled High Quality Water
and Outstanding Resource Water Management Zones, Division of Water Quality and
distributed by NCCGIA.
Historic National Register
Districts
GIS data published by State Historic Preservation Office (SHPO) on 21Aug2002
titled Historic Natl. Register Districts.
Historic National Register
Structures GIS data published by SHPO on 21Aug2002 titled Historic Natl. Register Structures.
Wetlands
GIS data published by the United States Fish and Wildlife Service (US FWS)
National Wetlands Inventory (NWI) on 18May1999 titled
onemap_prod.SDEADMIN.nwi_poly and distributed by NCCGIA.
National Pollution
Discharge Elimination
System (NPDES) Sites
GIS data published by the NC DENR DWQ, Planning Branch on 30Mar2006 titled
onemap_prod.SDEADMIN.npdes and distributed by NCCGIA.
NPDES Non-Discharge
Systems
GIS data published by the NC DENR DWQ, Planning Branch on 10Jul2006 titled
onemap_prod.SDEADMIN.ndsys and distributed by NCCGIA.
Appendix 4 A203
Page:
15/15
Table 6: Summary of GIS Data Used in Analysis
Environmental Concern Data Reviewed
Proposed Critical Habitat
GIS data published by an unknown author on 10Jul2006 titled pcha.
Permitted Animal
Operations
Animal Operation Sites: GIS data published by the NC DENR DWQ, Non-Discharge
Compliance/Enforcement Section on 4Dec2003 titled onemap_test.SDEADMIN.aop
and distributed by NCCGIA.
State Parks GIS data published by the North Carolina Parks and Recreation Department on
Jul2009 titled ncprk0709 and distributed by NCCGIA.
Streams
DWQ classified and unclassified: GIS data published by the NC DENR DWQ on
30Nov2007 titled dwq_classifications_20071130 and distributed by the NC DENR
DWQ.
Water Supply Watersheds GIS data published by the NC DENR DWQ on 1Jul2007 titled Water Supply
Watersheds and distributed by NCCGIA.
Important Forestland GIS data published by the North Carolina Division of Forest Resources (DFR) in
Jan2009 titled forimp0109_fullstate.
Landfills
GIS data published by the United Stated Environmental Protection Agency (US EPA)
Landfill Methane Outreach Program on 4Nov2004 titled
onemap_prod.SDEADMIN.lndfls and distributed by NCCGIA.
Lands Managed for
Conservation and Open
Space
GIS data published by the NCCGIA on 28Feb2002 titled onemap_SDEADMIN.lmcos
and distributed by NCCGIA.
Recreational Lands and
Open Space
GIS data compiled by the NCDENR that contains various layers from varying
sources published on 13Feb2008 titled RecLands_OpenSpace_Shapefiles and
distributed by NCCGIA.
State Owned Lands GIS data published by the North Carolina Department of Administration, State
Property Office on 6May2008 titled State-Owned Lands and distributed by NCCGIA.
Wild and Scenic Rivers
GIS data published by the National Wild and Scenic Rivers System (administered by
the Bureau of Land Management, the National Park Service, the US FWS, and the
United States Forest Service) on 13May2008 titled Wild and Scenic Rivers and
distributed by NCCGIA.
Appendix 4 A204
Page:
1/4
To Copies:
Toya Ogallo and Steve Reed
DENR, Division of Water Resources
Kevin Martin and Stan Crowe
Environmental Management Commission
Steve Porter, Greenville Utilities
Randy Emory, Greenville Utilities
Tony Cannon, Greenville Utilities
Ron Elks, Greenville Utilities
Richard Wyche, ARCADIS
Don Davenport, Greene County
Richard Hicks, Town of Farmville
Van Lewis, McDavid and Associates
Terri Parker-Eakes, Town of Winterville
From:
Mary Sadler, Hazen and Sawyer
Date: ARCADIS Project No.:
July 20, 2010 NC706015.0030
Subject:
Summary of Mitigation for Secondary and Cumulative Impacts
Hearing Officer’s Report Request for Additional Information
Greenville Utilities Commission Interbasin Transfer Certification
In June, the Hearing Officers requested more information on mitigative measures for Greene County and
the Towns of Farmville and Winterville. The Hearing Officers want to verify that mitigation is consistent
between communities so that any secondary and cumulative impacts as a result of the proposed
Interbasin transfer (IBT), albeit minor, are mitigated to a reasonable degree. This Technical Memorandum
(TM) provides a mitigation summary and an update to the Final Environmental Assessment (EA). In
particular, the Hearing Officers are focused on consistent stormwater measures between communities.
Table 1 provides a summary of mitigation for Pitt County, City of Greenville, Town of Farmville, Town of
Winterville, and Greene County. The City of Greenville, Pitt County, and the Town of Winterville currently
comply with the NPDES Phase II stormwater rules in addition to requiring 50-foot riparian buffers on
perennial and intermittent streams. The Town of Farmville and Greene County have not adopted any
stormwater requirements. The Town of Farmville does have a 50-foot riparian buffer requirement on
perennial streams and an impervious surface requirement in their Erosion and Sedimentation Control
Ordinance. Greene County is very rural and currently does not have a zoning ordinance. All of the
communities have similar erosion and sedimentation control programs.
In a June 25, 2010 email update to the Division of Water Resources (DWR), the mitigation issue was put
into perspective for Greene County, in particular. Greene County is ranked 82/100 in population and
86/100 in income. The County is rural and primarily agricultural based. A quick analysis was performed on
impervious surface using land classification data. High intensity and low intensity land classes were
assumed to be 100 percent impervious. This assumption yielded an impervious surface of 0.37 percent of
the total land area in Greene County. Using the published growth rate for Greene County, the resulting
total impervious surface coverage in 2030 would equal to 0.47 percent, assuming that the rate of
ARCADIS
801 Corporate Center Drive
Suite 300
Raleigh
North Carolina 27607
Tel 919.854.1282
Fax 919.854.5448
Appendix 5 A205
Page:
2/4
impervious surface per capita would remain constant until 2030. A question was posed to the Hearing
Officers: Is a tenth of a percentage point difference in impervious surface enough of a growth impact to be
considered significant enough for the implementation of stormwater rules?
In a recent discussion with DWR staff, the Hearing Officers will not approve an IBT Certificate without
stormwater measures for mitigation. A special condition would be included in the IBT Certificate to
address the stormwater issues. In lieu of a specific schedule for stormwater ordinance adoption, the
Hearing Officers will write the condition such that water may be transferred once a stormwater program is
approved by DWR. However, the Hearing Officers have asked that all parties provide verbal assurance of
a reasonable schedule.
Appendix 5 A206
Page:
3/4
Table 1: Summary of Mitigation for City of Greenville, Pitt County, Farmville, Greene County, and Winterville
Mitigation
Measure City of Greenville Pitt County Town of Farmville Greene County Town of Winterville
1. Land Use
Planning 2004 Update to 1992
Horizons Comprehensive
Plan.
2002 Land Use Plan
Update.
2008 Revision to Land
Use Plan.
No comprehensive
land use planning due
to many small towns
and unincorporated
areas.
1997 Land
Development Plan.
Board adopted Pitt
County Greenway Plan
in 2005.
2. Zoning Thirty-two zoning districts.
Includes overlay districts
(water supply watershed,
historic district, and
conservation district).
Open space requirements in
the conservation overlay
district.
County zoning
ordinance applies to
areas outside
corporate or
municipal ETJs.
Eight zoning districts.
Water Supply
Watershed Protection
Overlay.
Zoning Ordinance.
Nineteen zoning districts.
No zoning due to many
small towns and
unincorporated areas.
Zoning Ordinance
adopted 2000 and
amended May 2010.
Seventeen zoning
districts.
3. Riparian
Buffers
Tar Pamlico Riparian Buffer
Rule requiring a 50-foot
riparian buffer on perennial
and intermittent streams.
2006 Riparian Buffer
Protection Ordinance
to enforce Tar
Pamlico and Neuse
Rules for a 50-foot
riparian buffer on
perennial and
intermittent streams.
Zoning Ordinance
requires a 50-foot
vegetative buffer along
all perennial waters.
Subdivision
Regulations require
vegetated buffer strips
of 15 feet along all
watercourses and
wetlands.
50-foot riparian buffer
on perennial and
intermittent streams.
Ordinance is
administered by Pitt
County under an
interlocal agreement
executed October
2008.
4. Erosion and
Sedimentation
Control
Soil Erosion and
Sedimentation Control
Ordinance.
Measures provide protection
from the 25 year storm.
Soil Erosion and
Sedimentation
Control Ordinance.
Requirements similar
to City of Greenville.
Sedimentation and
Erosion Control
Ordinance.
Requirements similar to
City of Greenville and Pitt
County.
Subdivision
Regulations enforce
state requirements for
erosion and
sedimentation control.
Pitt County Erosion
and Sedimentation
Control Ordinance
enforced.
5. Stormwater
Programs 2002 Stormwater Program
that complies with NPDES
Phase II and Tar Pamlico
Stormwater Rules.
Tar Pamlico rules include
Neuse watershed areas in
the ETJ.
Measures enforced via
ordinance.
2004 Stormwater
Ordinance for Nutrient
Control effective to
comply with Tar
Pamlico rules.
Identical program to
City of Greenville.
Compliance not currently
required under Phase II
or Neuse Rules.
Zoning Ordinance
establishes 60 percent
impervious surface for
the neighborhood
business district and
65 percent impervious
None (due to rural
nature of County).
1988 Stormwater
Management Plan
ordinance amended
2001. Complies with NPDES
Phase II Stormwater
rules.
Appendix 5 A207
Page:
4/4
Table 1: Summary of Mitigation for City of Greenville, Pitt County, Farmville, Greene County, and Winterville
Mitigation
Measure City of Greenville Pitt County Town of Farmville Greene County Town of Winterville
surface for R-12 through
R-8. A limit of 75 percent
impervious surface has
been established for high
density residential and
business districts.
6. Floodplain
Regulations Identified flood hazard areas
via FEMA requirements.
Identified flood hazard
areas via FEMA
requirements.
Identified flood hazard
areas via FEMA
requirements.
Identified flood hazard
areas via FEMA
requirements.
Identified flood hazard
areas via FEMA
requirements.
Appendix 5 A208
Page:
1/8
To Copies:
Toya Ogallo and Steve Reed
DENR, Division of Water Resources
Kevin Martin and Stan Crowe
Environmental Management Commission
Steve Porter, Greenville Utilities
Randy Emory, Greenville Utilities
Tony Cannon, Greenville Utilities
Ron Elks, Greenville Utilities
Richard Wyche, ARCADIS
From:
Mary Sadler, Hazen and Sawyer
Date: ARCADIS Project No.:
July 19, 2010 NC706015.0030
Subject:
Explanation of Hydrologic Analysis and Results Interpretation
Hearing Officer’s Report Request for Additional Information
Greenville Utilities Commission Interbasin Transfer Certification
Summary of Hydrologic Modeling in Support of IBT Effort
A hydrologic model was developed for the lower Tar River to predict river flow under current and future
water use scenarios (ENTRIX 2007). The model was designed to evaluate the effect of Greenville Utilities
Commission (GUC) proposed Interbasin transfer (IBT) withdrawals on current and future flow at
Greenville. The model was based on available United States Geological Survey (USGS) flow records from
the Tar River at Tarboro (Gage No. 02083500) and the Tar River at Greenville (Gage No. 02084000). The
flow record at Tarboro provided a long-term record (1931 to 2007) of hydrologic conditions in the river.
This gage represents the majority of the entire drainage area of the basin and therefore was considered
the best available data set for predicting downstream flow at Greenville. Comparatively, the Greenville
gage represents a short period of record (1997 to 2007).
The relationship between the flow record at the Greenville and Tarboro gages was estimated using
hydrologic and statistical methods. This relationship was used to generate a long-term flow record at
Greenville. Tidal influences were not simulated in the model. Days may occur when the tidal influence
creates a net downstream flow of zero or a net upstream flow (“negative” flow).
Model Development
The hydrologic model is a mass balance type model that quantified the relative difference in output flow
associated with and without the proposed IBT at current and future withdrawals and discharges. The
hydrologic mass balance was represented with two modeling locations: the Greenville gage downstream
of GUC’s Water Treatment Plant (WTP) intake and a point downstream of GUC’s Wastewater Treatment
Plant (WWTP) National Pollutant Discharge Elimination System (NPDES) discharge. These two locations
represented a 7.7-mile portion of the Tar River that would be the most influenced by the proposed IBT.
ARCADIS
801 Corporate Center Drive
Suite 300
Raleigh
North Carolina 27607
Tel 919.854.1282
Fax 919.854.5448
Appendix 6 A209
Page:
2/8
The hydrologic model accounts for all documented withdrawals and discharges in the Tar River
downstream of the Rocky Mount Reservoir. The amount of withdrawal and discharge was calculated on a
monthly basis and for two time periods: 2002 and 2030. The 2002 withdrawals were developed using
2002 Local Water Supply Plans (LWSP), GUC withdrawal and discharge data, and registered agricultural
withdrawal data from the Division of Water Resources (DWR). The projected 2030 withdrawals and
discharges were added to the model incrementally and were converted from an annual average to a
monthly average using composite adjustment factors based on historic variability.
Hydrologic Scenarios
Eight different modeling scenarios were developed to reflect a range of existing and proposed conditions
at the upstream and downstream locations in the mass balance. The names of the modeled scenarios
have been altered slightly to provide additional clarification to the original published report, as follows:
Scenario A – Withdrawal and discharge in 2002, no IBT.
Scenario B – Withdrawal and discharge in 2002, average day IBT.
Scenario C – Withdrawal and discharge in 2002, maximum day IBT
Scenario D – Withdrawal and discharge in 2002, 2x maximum day IBT.
Scenario E – Withdrawal and discharge in 2030, no IBT.
Scenario F – Withdrawal and discharge in 2030, average IBT.
Scenario G – Withdrawal and discharge in 2030, maximum day IBT
Scenario H – Withdrawal and discharge in 2030, 2x maximum day IBT.
Statistical Analysis
To clarify the results presented in the original report, an analysis was performed to determine if there was
a statistical difference between the distribution of the upstream data set and the downstream data set for
each scenario. In order to prevent dampening of low flow events due to the large data set, only flow
events defined as less than 300 cubic feet per second (cfs) were used. The non-parametric Kolmogorov-
Smirnov test was used to compare the low flow data set for each scenario at a confidence interval of
95 percent. This non-parametric test was used to compare the cumulative frequency distribution of the low
flow data sets to determine statistically significant differences. Table 1 provides a partial summary of the
results as reported in the original report in addition to the results of the Kolmogoroy-Smirnov test. For the
evaluated scenarios, there are no significant statistical differences between the distributions in the
upstream and downstream low flow data sets.
A frequency-duration analysis was performed on flow less than 300 cfs for the two opposing withdrawal
scenarios: 2030 withdrawal and discharge – no IBT (Scenario E) and 2030 withdrawal and discharge –
maximum day IBT (Scenario G). The entire 76 year record was filtered for all days where the flow was
less than 300 cfs, 109 cfs (7Q10), and 27 cfs (25 percent of 7Q10). The low flow days were then grouped
into 25 low flow events where there were at least 40 days of flow less than 300 cfs that occurred over a
60 day span. A summary of these 25 low flow events is provided in Table 2. Table 2 includes the total
Appendix 6 A210
Page:
3/8
number of days in each event per scenario as well as the difference in the number of low flow days
(e.g. difference in duration) for each event. Conclusions from this analysis are as follows:
1. The average difference in duration between Scenarios E and G at flow less than 300 cfs
was less than 5 days.
2. A maximum of 10 days difference in duration occurred only once at flow less than 300 cfs.
3. A maximum of 15 days difference in duration occurred twice at flow less than 109 cfs.
4. A maximum of 20 days difference in duration occurred once at flow less than 27 cfs.
5. Out of 25 total low flow events, the proposed IBT resulted in only six occurrences where the
number of very low flow days would be longer in duration as a result of the proposed IBT.
Summary
The impact of the proposed IBT on the hydrology of the Tar River will be insignificant. First, there are no
statistically significant differences between the distributions of the upstream and downstream low flow data
sets between scenarios that were developed for the hydrologic mass balance. Second, the frequency-
duration analysis for the two opposing withdrawal scenarios indicates less than a three week difference in
duration, occurring once, on a very low flow event over the 76-year period of record. The additional three
week duration, a rare occurrence, should not be considered a significant impact. During low flow periods,
Greenville Utilities would be withdrawing less water than the maximum day due to their water conservation
ordinance and initiatives. This three week interval would therefore be shorter in duration.
Another important consideration is that the GUC raw water intake is tidally influenced, which will also help
to ameliorate the proposed IBT. The salt water wedge moves fresh water inland (e.g. upstream) as the
tidal wedge pushes into the estuary. Salt water is heavier than fresh water, so the salt water wedge will
move upstream with the highest concentration of salinity at the bottom of the river. This moving wall of salt
water creates a dam-like effect that pushes fresh water upstream. This phenomenon is particularly acute
during low flow periods. GUC closely monitors the salt water wedge, as their WTP is not designed to treat
saline water. Furthermore, GUC’s water conservation tiers are linked to the stage of water at the intake
and the location of the salt water wedge. These conservation tiers are thus directly linked to manifestation
of low flow in the river.
The Tar River channel is never depleted due to tidal influence. Withdrawal in a tidally influenced stream
does not equate to withdrawal in a fresh water stream. In a fresh water stream, a withdrawal is a
permanent subtraction of flow from the system. In a tidally influenced stream, flow is moving back and
forth continuously under the influence of the tides. This tidal buffering effect reduces the aquatic impact
during low flow periods.
Finally, Greenville Utilities is not requesting an increase in permitted withdrawal as part of the proposed
IBT. Rather, Greenville is selling excess water capacity to communities with reduced water supply as a
result of the Central Coastal Plain Capacity Use Area (CCPCUA) rules.
Appendix 6 A211
Page:
4/8
Response to Public Comments
1. Are the flows at the Tarboro gage, which were used to predict the flow at Greenville,
representative of flows that will occur in the future?
The use of the flow record at the Tarboro gage to predict flows at Greenville provided the best
available representation of flow. The Rocky Mount Reservoir operating rules were considered in the
hydrologic analysis and model. The hydrologic analysis was based on actual flow at the Tarboro gage,
reflecting 40 years of data prior to the reservoir and 36 years of reservoir operation data. Reservoirs
often augment low flow in rivers due to storage in higher flow periods and release in extended lower
flow periods. Flow duration curves for the pre-reservoir period of record and post-reservoir period of
record were evaluated to determine if this effect was present in the Tar River. Specific trends were not
observed; therefore, the difference in pre- and post-reservoir low flow was considered negligible.
Furthermore, the hydrologic model reflects the Rocky Mount reservoir operating rules and minimum
flow during the entire 36 year period of record.
2. The impact of the reservoir due to minimum flow is less than unaltered conditions. The
magnitude of flow does not prove this hypothesis. The timing, frequency, and duration of low
flows have not been considered.
A frequency-duration analysis was performed on flow less than 300 cfs for the 2030 withdrawal and
no IBT scenario and the 2030 withdrawal and maximum day IBT scenario. The entire 76 year record
was filtered for all days where the flow was less than 300 cfs, 109 cfs, and 27 cfs. These low flow
days were then grouped into 25 low flow events where there were at least 40 days of flow less than
300 cfs during a 60 day span. Out of 25 total low flow events, the proposed IBT resulted in only six
occurrences where the number of very low flow days would be longer in duration as a result of the
proposed IBT. At flow less than 27 cfs, a maximum of 20 days difference in duration occurred only
once during the 76 year period of record.
In summary, the frequency-duration results indicate that there is less than a three week difference in
duration during a very low flow event as a result of the proposed IBT. The additional three week
duration, a rare occurrence, will not impose a significant impact as a result of the proposed IBT.
3. Concern with the validity of the 7Q10 value as a relevant statistic for comparing flow changes.
Several flow statistics were generated for each modeled scenario to provide a comparison between
the upstream and downstream locations. The 7Q10 flow statistic was used as one of the “yardsticks”
to compare results. The 7Q10 value of 109 cfs was confirmed by the USGS in 2007. However, an
important point to note is that the historical flow record in the Tar River near Greenville (low, medium,
or high) was not being analyzed or debated in this hydrologic modeling effort. Rather, the change in
the flow record as a result of a modeled scenario was being evaluated, e.g. the difference in the flow
between upstream and downstream for the period of record.
Appendix 6 A212
Page: 5/8
Table 1: Summary of Statistical Significance Between Upstream and Downstream Data Sets for Scenarios A, B, D, E, F, and H
Scenario A –
Withdrawal and
Discharge in 2002,
No IBT
Scenario B –
Withdrawal and
Discharge in 2002,
Average Day IBT
Scenario D –
Withdrawal and
Discharge in 2002,
Maximum Day IBT 1
Scenario E –
Withdrawal and
Discharge in 2030,
No IBT
Scenario F –
Withdrawal and
Discharge in 2030,
Average Day IBT
Scenario H –
Withdrawal and
Discharge in 2030,
Maximum Day IBT 1
Percent of Time Per Year Flow is Below Benchmark Flow
Benchmark Up 2 Down 3 Up Down Up Down Up Down Up Down Up Down
109 cfs (7Q10) 1.3% 1.0% 1.6% 1.3% 1.8% 1.8% 1.4% 1.3% 1.6% 1.6% 1.8% 2.1%
87 cfs
(80% of 7Q10) 0.9% 0.7% 1.1% 0.9% 1.2% 1.2% 0.9% 0.8% 1.1% 1.1% 1.3% 1.6%
54 cfs
(50% of 7Q10) 0.3% 0.2% 0.5% 0.3% 0.6% 0.6% 0.3% 0.4% 0.6% 0.5% 0.6% 0.8%
27 cfs
(25% of 7Q10) 0.0% 0.0% 0.2% 0.0% 0.3% 0.3% 0.1% 0.1% 0.2% 0.3% 0.3% 0.5%
Significant
Difference in the
Distribution of
Upstream and
Downstream Flow
below 300 cfs at
α = 0.05? 4
No No No No No No
1 This scenario increases the Greenville withdrawal by the Max IBT amount (as in the 'Max IBT' scenario) and also decreases the Greenville WWTP discharge (not
adjusted for the other IBT scenarios) by the Max IBT amount (effectively removing 2x the Max IBT amount from the Tar River flow). If the calculated discharge was
below zero, the discharge was entered as zero (0). 2 The location at the point “upstream” in the hydrologic mass balance: the Greenville gage downstream of GUC’s water supply intake. 3 The location at the point “downstream” in the hydrologic mass balance: a point downstream of Greenville WWTP discharge. 4 Based on two sample Kolmogorov-Smirnov Test comparing the distribution of flow events below 300 cfs for the period of time modeled at a level of significance of
95%.
Appendix 6 A213
Page: 6/8
Table 2: Summary of Frequency-Duration Analysis for the No IBT Scenario ‘E’ and the Maximum Day IBT Scenario ‘G’ During Low Flow
Events
Event Start Date / End Date Scenario
Days Less
Than 300 cfs
during Event
Difference in
Duration at
< 300 cfs (days)
Days Less
Than 109 cfs
during Event
Difference in
Duration at
< 109 cfs (days)
Days Less
Than 27 cfs
during Event
Difference in
Duration at
< 27 cfs (days)
1 July 14, 1932 Scenario E 1 87 1 41 13 2 10 October 17, 1932 Scenario G 2 88 54 12
2 June 22, 1933 Scenario E 152 8 48 11 10 12 February 1, 1934 Scenario G 160 59 22
3 September 15, 1941 Scenario E 64 4 11 1 0 0 December 4, 1941 Scenario G 68 12 0
4 August 10, 1943 Scenario E 109 5 20 15 0 0 December 24, 1943 Scenario G 114 35 0
5 September 1, 1951 Scenario E 60 2 2 3 0 0 November 2, 1951 Scenario G 62 5 0
6 August 28, 1953 Scenario E 55 3 0 2 0 0 November 8, 1953 Scenario G 58 2 0
7 July 7, 1954 Scenario E 101 7 38 4 0 6 November 21, 1954 Scenario G 108 42 6
8 July 11, 1963 Scenario E 83 4 8 8 0 0 November 6, 1963 Scenario G 87 16 0
9 September 3, 1966 Scenario E 50 6 0 1 0 0 November 27, 1966 Scenario G 56 1 0
10 July 2, 1968 Scenario E 82 1 47 3 13 20 November 10, 1968 Scenario G 83 50 33
11 August 29, 1970 Scenario E 67 2 38 4 0 7 December 14, 1970 Scenario G 69 42 7
Appendix 6 A214
Page: 7/8
Table 2: Summary of Frequency-Duration Analysis for the No IBT Scenario ‘E’ and the Maximum Day IBT Scenario ‘G’ During Low Flow
Events
Event Start Date / End Date Scenario
Days Less
Than 300 cfs
during Event
Difference in
Duration at
< 300 cfs (days)
Days Less
Than 109 cfs
during Event
Difference in
Duration at
< 109 cfs (days)
Days Less
Than 27 cfs
during Event
Difference in
Duration at
< 27 cfs (days)
12 July 7, 1977 Scenario E 57 3 0 0 0 0 October 14, 1977 Scenario G 60 0 0
13 August 7, 1980 Scenario E 95 5 0 2 0 0 November 20, 1980 Scenario G 100 2 0
14 June 28, 1981 Scenario E 122 7 11 4 0 0 December 14, 1981 Scenario G 129 15 0
15 July 30, 1983 Scenario E 71 6 0 0 0 0 November 11, 1983 Scenario G 77 0 0
16 June 11, 1986 Scenario E 46 3 0 2 0 0 August 6, 1986 Scenario G 49 2 0
17 July 8, 1988 Scenario E 61 10 0 0 0 0 October 19, 1988 Scenario G 71 0 0
18 August 1, 1993 Scenario E 116 2 19 12 0 0 November 29, 1993 Scenario G 118 31 0
19 September 10, 1994 Scenario E 56 3 3 2 0 0 November 19, 1994 Scenario G 59 5 0
20 August 6, 1998 Scenario E 64 5 0 0 0 0 November 16, 1998 Scenario G 69 0 0
21 June 5, 1999 Scenario E 51 4 0 1 0 0 August 26, 1999 Scenario G 55 1 0
22 August 21, 2001 Scenario E 46 6 0 0 0 0
October 25, 2001 Scenario G 52 0 0
Appendix 6 A215
Page: 8/8
Table 2: Summary of Frequency-Duration Analysis for the No IBT Scenario ‘E’ and the Maximum Day IBT Scenario ‘G’ During Low Flow
Events
Event Start Date / End Date Scenario
Days Less
Than 300 cfs
during Event
Difference in
Duration at
< 300 cfs (days)
Days Less
Than 109 cfs
during Event
Difference in
Duration at
< 109 cfs (days)
Days Less
Than 27 cfs
during Event
Difference in
Duration at
< 27 cfs (days)
23 April 21, 2002 Scenario E 92 4 34 9 0 0 July 28, 2002 Scenario G 96 43 0
24 July 26, 2005 Scenario E 77 4 7 15 0 0 October 21, 2005 Scenario G 81 22 0
25 May 20, 2007 Scenario E 88 1 32 6 0 12 August 31, 2007 Scenario G 89 38 12
1 Withdrawal and discharge in 2030, no IBT, location downstream of GUC WWTP discharge. 2 Withdrawal and discharge in 2030, maximum day IBT, location downstream of GUC WWTP discharge.
Appendix 6 A216
Appendix 7
Record of Public Comments Received on Greenville
Utilities Commission, Town of Farmville, Town of
Winterville and Greene County’s Petition for an
Interbasin Transfer Certificate
A217
Page 1 of 1
Ogallo, Toya
From: Barney Kane [microbemanager@gmaiI.com]
Sent: Tuesday, January 19,2010 4:37 PM
To: Ogallo, Toya
Subject: Comment on GUC IBT Permit
Attachments: Revised and resubmitted comments of BEK re the GUC 1BT.doc
Dear Ms. Ogallo,
I am attaching my revised comments in opposition to the Permit Request by the Greenville
Utilities Commission for an Interbasin Transfer.
I thank you for considering my comments.
Bernard E. Kane, Jr.
Prof. Emeritus Retired & former member and chair of Greenville Utilities Commission
--
Barney
"Everybody needs beauty as well as bread, places to plan in and pray in, where Nature may heal
and cheer and give strength to body and soul alike." -
John Muir
Appendix 7
1
A218
01/19/2010
Statement of Bernard E. Kane, 1706 Canterbury Road, Greenville, NC 27858
Phone 252-355-6789.
January 19,2010
I am opposed to the GREENVILLE UTILITIES COMMISSION
INTERBASIN TRANSFER CERTlFlCNATlON REQUEST.
It is my belief that the interbasin transfer (IBT) requested is not warranted. It is, in fact,
counter to the best interest of all parties concerned. I also believe the requested transfer
is contrary to contemporary sustainable growth management practices. I believe the
needs presented are exaggerated and that there are better alternatives
1 am generally opposed to interbasin transfers. Historically most such transfers have
resulted in great economic trauma for some populations while selectively offering
transitory benefits to others. More often than not lBTs have resulted in unintended and
unforeseen environmental disasters.
It is my belief, based upon thirty-five years of teaching water supply and wastewater
treatment at East Carolina University, that interbasin transfers should only be approved
for where extraordinary and overwhelming justification is provided such as saving human
lives.
My major and minor points:
m Point # 1
The Approved Base Rate (ABR) used by the NCDWR to determine historical use from
the Cretaceous aquifer in the capacity use area is flawed.
The ABR applied was determined based on historical use at a time when there were no
conservation rates in place, pumping and treatment costs were low, and energy costs for
water production were also low. Thus, these ABR's may be presumed to be based upon
water use patterns that were excessive. There was little reason to limit use or apply
conservation practices. A more realistic (much lower) ABR should have been used
It is therefore also true that the reductions proposed from the artificially high ABR do not
reflect any serious conservation effort. Neither is there serious hardship caused in these
capacity use areas by meeting the per cent reductions required in the early years of the
limitations. Reductions of twenty-five percent could be achieved quite simply.
Reductions of fifty percent represent only a small challenge in conservation and in
planned growth. The seventy-five percent reduction would likely require access to
surface water fiom the Neuse if growth is to be facilitated.
There is no need to transfer water fiom the Tar kver.
Appendix 7
2
A219
Similarly if these high ABRs are used the projections of future needs are dramatically
higher than needed. Offsetting these projected "needs" with the proposed interbasin
transfer would effectively support these former wasteful, luxury, water-use practices.
My point is that these ABRs do not reflect the true base need. Rather they reflect luxury
use patterns that do not warrant the support of the interbasin transfers proposed.
To use these erroneous ABRs as the basis for projected future water "needs" only results
in support of continued wasteful consumption. A more critical, conservation-motivated
analysis is needed in which limits are properly considered and conservation is practiced.
If such analysis were done there would be no basis for the proposed IBT.
Point #2
Water is available from the Neuse for the communities in that basin. In fact if the
proposed IBT were approved water lines from the Tar would pass by lines from the
Neuse providing water to communities in what is partially a turf war for utility growth.
Feigned statements of cooperation and redundancy mask these turf wars including
lawsuits over the right to serve select communities (Bell Arthur Rural Water District vs.
GUC, as an example). NC Water Supply Branch should not facilitate these battles. Let
GUC stay within its own basin and mandated mission to provide for the needs of
Greenville.
Point #3
The data used and the peaking factors applied in the ArcadisIGUC Interbasin
Management Strategy are probably flawed. For one thing there is no way that the
Maximum Daily Demand for 1990 and 1995 for GUC could be "Not Available." The
record keeping at GUC during those years was carefully documented and recorded. It is
hard to imagine why the data are not presented here. I have too much faith in GUC to
believe there was a selective motive for listing them as "NA" and yet these data are too
important for Arcadis to overlook these values. This is puzzlement. NCDWR should ask
for these values and consider them in the determining the proper peaking factors.
Point #4
The peaking factors of 1.7 and 1.8 used for communities in the Capacity Use Areas
(CCAs) contrast dramatically with the 1.5 factor found valid for GUC.
Common sense would support the assumption that the peaking factor applied to
Greenville should be used for the CCA communities as well.
The GUC peaking factor is based upon a larger, more valid, data base and one that likely
reflects the management of water resources that will be needed in the future. The more
rural communities tend to have larger lots and less steady industrial water consumption.
Appendix 7
3
A220
Thus these hlgh peaking factors may be now be supported by the current use patterns. In
the future use will require more conservation and less irrigation. MDDs will need to
more closely approach ADDS as these communities grow and as water resources become
more restricted. Use of these high values of 1.7 and 1.8 for peaking factors is not
reasonable and endorses wasteful use.
Point #5
I can see no valid purpose or reason for GUC to supply water to communities facing
limited water supplies. dn the surface such a statement might seem selfish. In fact it is
likely both reasonable and helpful. It is only in a shortsighted rationale that an interbasin
transfer might be viewed favorably. There are many reasons why GUC should not
supply the water. Some reasons are environmental, some are economic, some are energy
related, and some are moral. The following sub-points explain my position.
Point #5a.
I think it reasonable for areas with limited resources to recognize those limits and plan
not to exceed the limits available. The alternative is an arrogant belief that there is some
duty to push resources hither and yon across landscapes and basins with pumps and
machines thereby disrupting natural systems and causing ripples of unknown but possibly
disastrous consequences.
Point #5b.
Stream flows and receiving streams will be impacted by the proposed IBT as wiH the
natural characteristics of the waters affected. These effects and impacts are not necessary
and are not even needed except possibly in the minds eye of municipal officials and self-
aggrandizing developers in the region.
Point #5c.
Greenville has had a remarkably flat water consumption pattern over the past 15
years. This may seem puzzling considering the growth in Greenville. It is likely
attributed in part to several factors, including good management at the utility,
changes in water use practices at local industries and other more minor practices.
But there are limits to these benefits. It is probable, perhaps even certain, that
Greenville's demand for water will return to the steep growth curves that were
predicted by the consulting engineers in the mid 90's.
If this is true Greenville will be using its current plant capacity in the very near
future. If that is the case, there will be very little excess to commit to other basins.
To meet the commitments in the proposed IBT, GUC would need to expand their
current facilities and would be absolutely dependent upon the Aquifer Storage and
Recovery (ASR) system functioning as designed.
The ASR has not been tested. It is a pioneer system in NC. It has been a troubled
project since inception, taking years longer to be in place than was planned. I would
be unwilling to approve creating a dependency on this project.
Appendix 7
4
A221
Point #5d.
Development in Farmville, Winterville, and Greene Counties promotes rural sprawl.
Thus the proposed IBT promotes rural sprawl. It would be more efficient and
conservative of water resources to develop within the Greenville Urban Area.
While it may seem outside the purview of the division whose approval is needed, the
agency can surely not be blind to this problem.
As an example of this problematic growth consider this. There is no effective
transportation system from these rural areas to major employment centers, to centers for
heath care and to centers of recreational and cultural opportunity other than private
vehicle. If these areas grow, in ten or twenty years there will be serious problems in
transportation alone. There will be extremely limited reserves of fuel in 2030 according
to the US Energy Information Agency.
Point #5e.
Development in Greene County especially highlights points 5e. In Greene County the
development and growth is exemplified by proposals such as "Cutter Creek." Cutter
Creek is a sprawling golf course retirement community focused upon large, irrigated lots,
and private vehicular transportation to Raleigh and Greenville for employment, cultural
opportunities and health care. It exemplifies an unsustainable community dependent
upon subsidies such as water supply from the Tar River Basin.
Point #5f.
The water in the Tar River does not belong to GUC. We must ask for an answer as to
what can be the reason the managers and board have for proposing to extract it, process it
and distribute it elsewhere? Who authorizes thls particular usurpation of the natural
order? It does not serve the tax-payer or the rate-payer of Greenville. I suspect these
good public servants do honestly believe they are extending a Good Samaritan helping
hand. But I question whether they have thought it through properly. I ask that the
Division of Water Resources view this from the perspective of a better management
scheme. I believe it would be much better to manage water resources conservatively
within their natural basin.
Point 6.
There are better alternatives.
First, apply conservation based water supply base requirements needs to the proposed
areas. These should be much lower than the ABRs used in this proposal.
Second, as a matter of principle NCDWR should require vigorous conservation rate
structures and peak demand management in any area receiving an IBT. And the sword
should cut both ways. The area supplying the water should be required to adopt the
same vigorous conservation rates and peak demand management. The reason?
Both would now be sharing the same water resources. It is thus absurd for a utility
Appendix 7
5
A222
to supply water from a common resource and have disparate standard for allocation
and use of that common resource. All users should abide by the same rules.
Finally, the newly developed and potential for future development of Neuse River
supplies is adequate without the potential problems associated with Interbasin
Transfers,
I thank you for considering these comments.
Bernard E. Kane Jr
Appendix 7
6
A223
Page 1 of 1
Ogallo, Toya
From: Reeder, Tom
Sent: Monday, December 07,2009 10:27 AM
To: Ogallo, Toya
Subject: FW: Comment GUC IBT Request
Attachments: NCDWR IBT Comment BEK IBT.doc
fY i
E-mail correspondence to and from this address may be subject to the North Carolina Public
Records Law and may be disclosed to third parties.
From: Barney Kane [mailto:microbemanager@gmail.com]
Sent: Friday, December 04,2009 4:43 PM
To: Reeder, Tom
Cc: toyo.ogallo@ncdener.gov; toya.ogaIlo@ncdenr.gov; toyo.f.ogallo@ncdenr.gov
Subject: Comment GUC IBT Request
Dear Mr. Reeder
Please consider the my attached comments in opposition to the Greenvill Utilities Commissioins
proposed Interbasin Basin Transfer from thr Tar River to the Nuese and Contentnea Creek Sub-
basins.
Thank you,
Bernard E. Kane Jr.
I have tried to send this to toya.f.ogal10 without success.
Appendix 7
7
A224
Statement of Bernard E. Kane, 1706 Canterbury Road, Greenville, NC 27858
Phone 252-355-6789.
I am opposed to the GREENVILLE UTILITIES COMMISSION
INTERBASIN TRANSFER CERTlFlCNATlON REQUEST.
It is my belief that the interbasin transfer (IBT) requested is not warranted. It is, in fact,
counter to the best interest of all parties concerned. I also believe the requested transfer
is contrary to contemporary sustainable growth management practices. I believe the
needs presented are exaggerated and that there are better alternatives
1 am generally opposed to interbasin transfers. Historically most such transfers have
resulted in great economic trauma for some populations while selectively offering
transitory benefits to others. More often than not lBTs have resulted in unintended and
unforeseen environmental disasters.
It is my belief, based upon thirty-five years of teaching water supply and wastewater
treatment at East Carolina University, that interbasin transfers should only be approved
for where extraordinary and overwhelming justification is provided such as saving human
lives.
My major and minor points:
Point # 1
The Approved Base Rate (ABR) used by the NCDWR to determine historical use from
the Creteaceous aquifer in the capacity use area is- flawed. The ABR was determined
based on historical use in a time when there were no conservation rates in place, pumping
and treatment costs were low, and energy costs for water production were also low. Thus
these ABR7s may be presumed to be based upon water use patterns that were excessive
because there was little reason to limit use. A more realistic (lower) ABR should have
been used
It is therefore true that the reductions proposed from the artificiafly high ABR do not
reflect a serious conservation effort nor any hardship in these capacity use areas that
might seem apparent by the per cent reductions required. Similarly, projections of future
needs to be offset by the proposed interbasin transfer result in proposed supplies which
support these former wasteful or luxury water usage practices. My point is that these
ABRs do not reflect the true base need. Rather they reflect luxury use patterns that do
not warrant the support of the interbasin transfers proposed.
To use these erroneous ABRs as the basis for projected future water "needs" only results
in support of continued wasteful consumption. A more critical, conservation motivated
analysis is needed in which limits are properly considered and conservation is practiced.
Appendix 7
8
A225
Point #2
The data used and the peaking factors applied in the ArcadisIGUC Interbasin
Management Strategy are probably flawed. For one thing there is no way that the
Maximum Daily Demand for 1990 and 1995 for GUC could be "Not Available." The
record keeping at GUC during those years was carefully documented and recorded. It is
hard to imagine why the data are not presented here. I have too much faith in GUC to
believe there was a selective motive for listing them as "NA and yet these data are too
important for Arcadis to overlook these values. This is a puzzlement. NCDWR should
ask for these values and consider them in the determining the proper peaking factors.
The peaking factors of 1.7 and 1.8 used for communities in the Capacity Use Areas
(CCAs) contrast dramatically with the 1.5 factor found valid for GUC. I suspect that the
peaking factor applied to Greenville should be used for the CCA communities as well.
The GUC peaking factor is based upon a larger, more valid, data base and one that likely
reflects the management of water resources that will be needed in the future. The more
rural communities tend to have larger lots and less steady industrial water consumption.
Thus these high peaking factors may be supported by the current use patterns. But hture
use will require more conservation and less irrigation. MDDs will need to more closely
approach ADDS as these communities grow and as water resources become more
restricted. Use of these high values for peaking factors in this GUC management strategy
is to endorse wasteful use.
Point #3
I can see no valid purpose or reason for GUC to supply water to communities facing
limited water supplies. In fact there are many reasons why GUC should not supply the
water. Some reasons are environmental, some are economic and some are energy related
and some are moral.
Point #3a.
I think it reasonable for areas with limited resources to recognize those limits and plan
not to exceed the limits available. The alternative is an arrogant belief that there is some
duty to push resources hither and yon across landscapes and basins with pumps and
machines thereby disrupting natural systems and causing ripples of unknown but possibly
disastrous consequences.
Point #3b.
Streamflows and receiving streams will be impacted by the proposed IBT as will the
natural characteristics of the waters affected. These effects and impacts are not necessary
and are not even needed except possibly in the minds eye of municipal officials and self-
aggrandizing developers.
Point #3c.
Appendix 7
9
A226
Development in Fmville, Winterville, and Greene Counties promotes rural sprawl.
Thus the proposed IBT promotes rural sprawl. It would be more efficient and
conservative of water resources to develop within the Greenville Urban Area. It is
particularly important to note there is no effective transportation system from these rural
areas to major employment centers other than private vehicle (which will have limited
access to dwindling reserves of fuel in 2030 according to the US Energy Information
Agency).
Point #3d.
Development in Greene County especially highlights points 3a though 3c. In Greene
County the development and growth is exemplified by proposals such as "Cutter Creek."
Cutter Creek is a sprawling golf course retirement community focused upon large,
irrigated lots, and private vehicular transportation to Raleigh and Greenville for
employment, cultural opportunities and health care. It exemplifies an unsustainable
community dependent upon subsidies such as water supply from the Tar River Basin.
Point #3e.
The water in the Tar River does not belong to GUC. We must ask for an answer as to
what can be the reason the managers and board have for proposing to extract it, process it
and distribute it elsewhere? Who authorizes this particular usurpation of the natural
order? It does not serve the tax-payer or the rate-payer of Greenville. I suspect these
good public servants do honestly believe they are extending a good Samaritan helping
hand. But I question whether they have thought it through properly. I ask that the
Division of Water Resources view this from the perspective of a better management
scheme. I believe it would be much better to manage water resources conservatively
within their natural basin.
Point 4
There are better alternatives.
First, apply conservation based water supply base requirements needs to the proposed
areas. These should be much lower than the ABRs used in this proposal.
Second, as a matter of principle NCDWR should require vigorous conservation rate
structures and peak demand management in any area receiving an IBT. And the sword
should cut both ways. The area supplying the water should be required to adopt the same
vigorous conservation rates and peak demand management. The reason? Both are now
sharing the same water resources.
I thank you for considering these comments.
Bernard E. Kane Jr.
Appendix 7
10
A227
Ogallo, Toya
From:
Sent:
To:
Subject:
Anne Bunnell [anne-bunnell@yahoo.com]
Thursday, January 14,2010 12:48 PM
Ogallo, Toya
Re: IBT
You're welcome.
Anne
----- Original Message ----
From: "Ogallo, Toya" <toya.f.ogallo@ncdenr.gov>
To: Anne Bunnell <anne-bunnell@yahoo.com>
Sent: Thu, January 14, 2010 10:36:52 AM
Subject: RE: IBT
Thank your for your comments!
Toya
Please note that my email address has changed to toya.f.ogallo@ncdenr.gov
Toya F. Ogallo
Environmental Engineer
River Basin Management Section
Division of Water Resources
Phone: (919) 715-0389
Fax : (919) 733-3558
E-mail correspondence to and from this address may be subject to the North Carolina Public
Records Law and may be disclosed to third parties.
----- Original Message-----
From: Anne Bunnell [mailto:anne~bunnell@yahoo.com]
Sent: Tuesday, January 12, 2010 3:43 PM
To: Ogallo, Toya
Subject: IBT
Dear Sir or Madam,
I was present at the Greenville City Council meeting last night when GUC presented its IBT
plan. Although I understand that having a regional water system may in the future to be
beneficial to the human population there are some issues that I think need to be
addressed.
1) According to the map water from GUC and the Tar River is being piped to Snow Hill and
water from Kinston and the Neuse River Basin is being piped to Eastern Pines. The map
itself revealed the flaws in this plan. It doesn't take much to realize that it is
inefficient to pipe water over long distances rather than shorter ones. There is an
increased chance of loss by leakage and an increased need of additional purification for
safety. This also makes economical sense.
2) As the population of eastern North Carolina continues to grow a strain will be placed
on all water resources. It seems logical to promote water conservation practices now. The
reductions in the withdraw1 from underground sources should first be attained by reducing
water usuage rather than by transfering water across miles.
Appendix 7
11
A228
3) Humans are not the only species in these river basins. I value the wildlife in eastern
North Carolina. The opportunity to paddle these rivers and creeks are activities that I
cherish. Transfering water between basins may have unanticpated and negative impacts on
native species decreasing their abilities to survive. Again, it seems that water
conservation efforts should be the first priority, rather than IBTs.
Thank you for reading my comments.
Sincerely yours,
Anne E. Bunnell
Greenville, NC
Appendix 7
12
A229
Page 1 of 2
Ogallo, Toya
From: John and Kathy Schermerhorn [schermsfarm@earthlink.net]
Sent: Tuesday, October 27,2009 3:25 PM
To: Ogallo, Toya
Subject: Tar to Neuse water transfer
From: John and Kathy Scherrnerhorn <schermsfarrn@earthlink.net>
Date: October 27, 2009 2:58:54 PM EDT
To: Tova.F.OaallOQncdenr.aov
Cc: riverkee~erQ~trf.orq, John Chrystal ~imchrvstal@vahoo.com~
Subject: Tar to Neuse water transfer
What an interesting issue you are collecting information and opinions on.
We are not in favor of intra-regional water transfer agreements as they are
permanently divisive. They tend to make enemies of neighbors and they, in this
case, stifle the growth potential for eastern Beaufort County by reducing the
available water supply to this region. As close as eastern Beaufort Co. is to
Greenville, what better place to develop without having to give up water rights.
At times, water transfers are necessary for the true and actual benefit of all - which
has yet to be determined as I understand this Water Transfer Agreement
process. That being said, available water allows for community growth. We're not
opposed to controlled growth in general but there must be aggressive controls on
how much growth and how that associated water will be used. Waste of this life-
giving resource must be a major controlling factor in the issuance of this
agreement. Now is the time to address water waste as a condition of water
transfer. There need to be enforceable building/plumbing permit requirements (as
well as environmental considerations) that aggressively address the use and
potential waste of our water resources for new homes, businesses, industries and
their eventual upgrade improvements. These requirements should (must) be
adopted and enforced by the local and county municipalities paid for by permit
fees. Incorporating an ongoing and far reaching educational process on the
importance of this resource and ways it must be protected and conserved must also
be a part of this transfer agreement.
There are many proven and currently practiced ways of using less water and with
the imaginative minds and talent we have in this region this should not be a
daunting task to undertake. We truly don't need to reinvent the "wheel" but only
take what already exists and refine it to work more efficiently for the benefit of
all. We would like to suggest that these ideas be pursued and adopted by the
Greenville Utilities Commission prior to the allowance of this water transfer
agreement. Additionally, a stepped fee schedule for all water users in GUC's region
must be implemented to aid in the education and reduction of wasted water
resources. A five level fee structure based on amount of water used starting with a
reasonable baseline use and climbing through excessive use needs to be
implemented. The monies generated by the excessive use fees will be accounted for
and expended in areas of education, retrofitting of household and business fixtures
with water conservation fixtures. This can be done through discount programs or
Appendix 7
13
A230
Page 2 of 2
out-right give-a-ways. This program in turn will reduce water waste
and subsequently reduce water bills, putting at least a temporary smile on the end-users
face.
Although not everyone will take kindly to these suggestions, the honest truth is that they
will be implemented out of panicked necessity in the not too distant future as this valued
and necessary resource becomes more scarce, valuable and consequently more costly. By
starting this water saving program now, a model can be developed for other water districts
to follow and improve on, creating needed jobs and allowing conservative water transfer
agreements to be less necessary and when truly needed, positive rather than divisive.
The next issue for consideration is to reduce and or eliminate pollutants from up stream
users as they affect our water and it's potential use to we downstream users. Lots to do!!
John and Kathy Schermerhorn
Beaufort County
schermsfarmQearthlink.net
Appendix 7
14
A231
DEC ? 2UO9
Pamlico-Tar River Foundation Southern Environmentd,&q~~clr~~(rs
P.O. Box 1854, Washington, NC 27889 200 W. Franklin Street, Ste. 330, Chapel Hill, NC 27G6
252-946-7211 919-967-1450
December 4,2009
Toya Ogallo
Division of Water Resources
DENR
16 1 1 Mail Service Center
Raleigh, NC 27699- 16 1 1
Dear Ms. Ogallo,
The Parnlico-Tar River Foundation (PTRF) and Southern Environmental Law Center
(SELC) submit the following comments on the Greenville Utilities Commission's (GUC) petition
for an Interbasin Transfer (IBT) certificate. GUC has requested the IBT certificate to transfer
water from the Tar River Basin to the Contentnea Creek and Neuse River basins. The receiving
communities include the Towns of Farmville, Winterville, and Greene County Regional Water
system, which provides water service to the communities of Snow Hill, Hookerton, Walstonburg
and six other water corporations.
PTRF founded in 198 1, is a grassroots environmental organization representing 1900
members and a licensed member of Waterkeeper Alliance, Inc. Our mission is to enhance and
protect the Pamlico-Tar River watershed through education, advocacy, and research.
SELC is a non-profit legal advocacy group dedicated to protecting the environment of the
South. SELC works with more than 100 partner groups in six southeastern states. SELC has
been actively involved in a variety of efforts to protect and improve water quality in the Pamlico-
Tar River watershed.
I. Background
In 2007, the General Assembly recognized the need to consider more carefully the
impacts of water transfers on the source basin and amended the state interbasin transfer law to
reflect that need. N.C. Gen. Stat. $ 143-21 5.221;. N.C. Gen. Stat. $ 143-21 5.22L(t) states
It is the public policy of the State to maintain, protect, and enhance water quality
within North Carolina. It is the public policy of this State that the reasonably
foreseeable future water needs of a public water system with its service area
located primarily in the receiving river basin are subordinate to the reasonably
foreseeable future water needs of a public water system with its service area
located primarily in the source river basin. Further, it is the public policy of the
State that the cumulative impact of transfers from a source river basin shall not
result in a violation of the antidegradation policy set out in 40 Code of Federal
Appendix 7
15
A232
Regulations 5 13 1.12 and the statewide antidegradation policy adopted pursuant
thereto.
Although the new requirements do not go into effect for interbasin transfers to
supplement ground water supplies in the fifteen counties designated as the Central Coastal Plain
Capacity Use Area under until January 201 1 (H.B. 820 (7)(b) (2007)), it would be shortsighted
of the Environmental Management Commission not to consider the broad policy objectives
stated in the amendments in looking at the proposed transfer. Our comments rely on the
requirements set out in N.C. Gen. Stat. 143-21 5.221 but we urge the EMC to consider the spirit
of the amendments in reviewing the GUC petition.
The receiving communities and the source (GUC) are all regulated under the Central
Coastal Plain Capacity Use Area ("CCPCUA)" rules, initiated in 2002. The rules require the
communities to reduce ground water withdrawals from the cretaceous aquifers by 75% from a
state approved base rate by 201 8. At the present, the receiving communities rely on this
groundwater as their sole source of water supply. The CCPCUA rules also require regulated
communities to implement and provide information on a number of water conservation
measures.
The Division of Water Resources ("DWR) has developed a cretaceous water bank
guidance document that allows communities who choose to reduce groundwater withdrawal
faster than mandated by the rules. This banked water would then be available for use in later
years.
11. Specific Concerns Regarding North Carolina Environmental Policy Act Compliance
The North Carolina Environmental Policy Act ("SEPA") requires the preparation of an
environmental assessment ("EA") or environmental impact statement ("EIS") for any transfer of
surface water that requires the filing of a petition pursuant to the Surface Water Transfer Act,
N.C. Gen. Stat. § 143-21 5.221; 1 13A-8.1. 1 N.C. Admin. Code 25.0502 requires an EA to
include maps and discussion of the following:
(1) need for the proposed activity,
(2) reasonable alternatives to the recommended course of action,
(3) methods proposed to mitigate or avoid significant adverse environmental
impacts, and
. (4) environmental effects of the proposed activity and alternatives.
The FONSJEA for the Greenville Utilities Commission IBT has not met these requirements.
A. The EA provides no meaningful consideration of mitigation measures.
SEPA requires the agency to include a review of methods "proposed to mitigate or avoid
significant adverse environmental impacts" from the proposed transfer. 1 N.C. Admin. Code
25.0502 (3);. The EA fails to include any meaningful discussion of mitigation measures, instead
providing a review of land use planning regulations and ordinances. Appropriate measures to
Appendix 7
16
A233
mitigate, i.e., lessen, the environmental impacts would include, for example, returning treated
wastewater to the source basin, implementing aggressive water conservation measures, or
detailing measures that would be taken to protect aquatic life in the source basins during times of
drought.
B. The EA provides no assessment of the anticipated environmental impacts of
alternatives to the IBT.
Both SEPA and the Surface Water Transfer Act (SWTA) require an evaluation of
alternatives to the proposed transfer. The EA must include "reasonable alternatives to the
recommended course of action." 1 N.C.A.C. 5 25.0502(2). The SWTA requires the EMC to
consider reasonable alternatives to the proposed transfer, including estimated costs and
environmental impacts.
While the EA does identify several alternatives to the proposed IBT, the discussion is
woefully inadequate to the task set forth in the applicable statutes and regulations. The overview
assigns a dollar amount to the financial cost associated with the construction of each alternative.
However, there is no discussion, evaluation, or modeling of environmental impacts, the source
basin. In addition, the EA fails to evaluate the costs in terms of lost revenues to source basin
water suppliers that may be expected to impose restrictions on water use for longer time periods
as a result of the proposed transfer of water. For example, the alternative briefly mentioned in
the EA for the receiving basins to purchase water from the Neuse Regional Water and Sewer
Authority does not provide an analysis of cost, only that the costs would be "prohibitive."
Furthermore, the applicant suggests that since an IBT certificate would be needed for a NRWSA
transfer to Winterville since the transfer occurs from the Neuse River to the Contentnea Creek
sub-basin, that this automatically negates this as a viable option. The 2007 changes to the
SWTA clearly demonstrate that a transfer of water within a major river basin (i.e. Neuse to
Contentnea sub-basin) is preferred over a transfer between major river basins. A more complete
discussion of alternatives, including a thorough review of the comparative environmental
impacts, is required.
C. The EA ignores the cumulative and secondary impacts from growth in the
receiving basin.
The EA wholly dismisses the need for evaluation of secondary and cumulative impacts
from growth since the IBT is designed to only replace the lost groundwater resource due to the
CCPCUA. The EA states that "significant growth in these areas is not a component of this
project or a reason for developing the interbasin transfer request. " IBT Petition, pp 4-1. DWR
questioned this dismissal of secondary and cumulative impacts associated with growth that is a
direct result of the transfer of water in their comments on the draft EA (EA Response to
Comments, pp: 2/12-2/13, February 1,2008). The comments stated:
The document dismisses cumulative and secondary impacts associated with
growth by repeatedly stating that the project is primarily a water replacement
project and significant growth is not a component of this project or a reason for
Appendix 7
17
A234
developing the IBT request. It is true that they are being forced to switch to
surface water and that initially the volume ofsurface water matches the volume of
ground water; however, over time the volume of water increases due to growth
projections that the communities would have supported with an untapped volume
of ground water. On page 4-2 it states that "these communities will be unable to
compensate for the reduced groundwater withdrawals for predicted growth to
2030': There appear to be pockets of signzficant growth and, without the
additional water, this growth could not be supported. The Executive Summary
states that growth is modest at 1 to 3 percent in some communities. However,
: Section 2.2 gives growth rates offrorn I1 to 50 percent for Winterville, Greene
County had a 25 percent growth rate from '90 to '06; although the overall growth
rate of the county may be I percent, pockets ofhigher growth may occur, e.g.
near the Global Transpark. The document does not provide the percent growth
for Greenville, but from the numbers provided it could be 45 percent fiom '05
tot30.
Comments to draft EA by DWR (on file with DWR)
The applicant responded by saying that the growth would occur in these communities
with or without the IBT, therefore assessing the environmental impacts is unnecessary. The
communities are required to reduce their groundwater withdrawal due to the CCPCUA rules.
Without a new source of water, either from the Neuse River Basin or from GUC, the growth
could not be sustained. The applicant dismisses all other alternatives as viable options, therefore
growth would not occur if the IBT were to be denied. Therefore, the applicant must provide
detailed information on the secondary and cumulative impacts associated with this growth.
A similar lack of attention plagues the brief discussion of impacts to air quality. In 2009,
the federal government changed the air quality standard for ozone, and in doing so designated 24
counties and parts of 17 others as not meeting this new standard. Pitt County was recommended
as unclassifiable due to a lack of monitoring data. The EA states that DAQ adopted new ozone
standards in 1997 and that DAQ has a monitoring site in Farmville that recorded no ozone
exceedances in 2006. This is outdated information. The EA should include the new federal ozone
standard and an assessment of any state of federal data available for Pitt County. Again, the EA
dismissed the impact of growth on the potential for impacts to air quality:
"No construction activities will occur relative to the proposedproject; therefore,
no direct impacts to air quality will occur. Indirect impacts to air quality within
the service areafiom growth will be minimal. "
EA pp 5-26. The region may be a non-attainment area for the new ozone standard. The
proposed IBT would facilitate residential and industrial growth in the receiving basin. Although
this growth and the associated increases in vehicular traffic and use of lawnmowers will lead to
complicate the existing air quality problems, this impact is not discussed.
Another example of the inadequacy of the secondary and cumulative impacts review
concerns threatened and endangered species. The EA states that threatened and endangered
Appendix 7
18
A235
aquatic species are present in both the receiving and source basins but does not address the
impacts. The EA must correct its review of cumulative and secondary impacts to include the
impacts to these species from growth that would be induced by the IBT.
Finally, Contentnea Creek and Little Contentnea Creek are both impaired streams. All of
the communities within the receiving basin that will experience greater wastewater flow due to
the growth precipitated by this IBT discharge their wastewater into these impaired streams. The
Towns of Hookerton and Snow Hill, and the Contentnea Creek wastewater plant have all been
non compliant with their NPDES permits within the past year. The EA should provide a
compliance history of each of the wastewater facilities as well as the communities' ability to
handle the increase flow. The EA does state that no wastewater facility will need to increase their
permitted discharge amount, but if the facilities suffer from inflow and infiltration, or other
maintenance problems, these issues would be exacerbated by the increased growth and flow due
to the IBT md should be addressed in the IBT.
D. The EA fails to provide information on water conservation measures
implemented or planned by source and receiving communities.
As noted above, the proposed IBT is not subject to the 2007 session law changes to the
Regulation of Surface Water Transfers Act. Therefore, the proposed IBT was required to conduct
an EA and not an EIS. Under the old rules, an applicant must provide information regarding the
facilities to be used for the water transfer, the proposed uses of the water to be transferred, the
water conservation measures to be used by the applicant and any other information deemed
necessary by the Commission. The EA failed to provide any information (except the short
paragraph below from GUC) regarding the source or receiving communities current and planned
water conservation measures. The only information provided was related to drought management
protocols. Useful data should include information on water rate structures, presence or plans for
retrofit programs, feasibility of reclamation projects, ordinances or incentives for use of cisterns
or other rain water harvesting practices, etc.
'Ydditionally, GUC and its wholesale customers strongly encourage the use of
water saving devices. GUC is a licensed member of the national "Water Use it
Wisely" campaign. The Energy Services and Public Information Ofices
incorporate water conservation messages into all communications. This includes
preparation of fact sheets, television and radio adverfisements, print ads, and
billboards to provide local citizens with water conservation tips."
Furthermore, all communities are required by the CCPCUA rules to adopt water
conservation-based rate structures, implement conservation ordinances for irrigation, provide a
retrofit program for homeowners as well as an educational program and provide information to
the state regarding existing conservation measures and those to be implemented (NCAC 15A 2E
0.0502(d)(5)). Phone conversations with DWR staff reveal that such information has not been
supplied by these communities. Such information is crucial for the EMC to be able to make a
decision on the reasonableness of the IBT and whether or not conditions should be placed on the
certificate if the Petition is granted. The changes in 2007 to the Regulation of Surface Water
Appendix 7
19
A236
Transfers Act clearly reveal that the State is emphasizing the efficient use of water resources.
The petition and EA submitted by GUC provides none of this critical information.
E. The EA does not adequately consider the impacts combined with the Greenville
Utilities Emergency Drought Management Planning Project on the Tar River.
Additional evidence of the lack of thoroughness in the environmental review stems from
the petitioner's lack of discussion of their intention to construct a temporary dam across the Tar
River in the vicinity of the Greenville Utilities Water Treatment Plant. The Petition states that
"it is challenging to fully understand and quantify the flow characteristics for the Tar River at
Greenville" and that "[c]urrent USGS techniques for low-flow analyses do not provide a means
of account for tidal effect." Petition at 3-4. Despite these challenges, the applicant should have
considered this related project in its analysis of the probable environmental impacts from the
IBT.
111. Specific Concerns Regarding the IBT Petition
A. Transfer Amount
Along with our concerns regarding the inadequacies of the EA, we are especially
concerned about the transfer amount requested by the applicant. The stated purpose of the IBT
request in GUC's petition is to aid the receiving communities' compliance with CCPCUA
regulations, which require a 75% reduction in water withdrawals from the cretaceous aquifers
phased over a 1 0-year period.
The amount of groundwater water withdrawal reductions that are required by the
receiving communities are outline in Table 1. The total amount the communities need to replace
this loss of groundwater supply due to CCPCUA rules is 3.771 mgd. Therefore, the proposed
IBT allows for significant growth over the time period evaluated and is incongruent with the
project's stated objective of compliance with CCPCUA rules.
Loss of
Groundwater Source
C'ommunity
Greene County
Table 1. CCPCUA groundwater withdrawal requirements.
* Approved Base Rate
**Amount allowable for withdrawal after compliance with 75% reduction (CCPCUA).
Winterville
Total
The IBT certificate proposes an interbasin transfer of 8.3 mgd for the Towns of Farmville
and Greene County Regional Water authority, as well as an additional 1.0 mgd for emergency
conditions. The second certificate request proposes 4.0 mgd to the Town of Winterville with an
additional 0.2 mgd for emergency conditions. The total transfer requested from the Tar River
ABR"
(mgd)
Farmville 1.572 0.393 1.179
2.96
Allowable
withdrawal by 2018
0.496
tmgd)
0.74
(mgd)"
2.22
0.121
J
0.372
3.771
Appendix 7
20
A237
basin to the Neuse River basin is 12.3 with emergency conditions allowing up to 13.5 mgd. This
amount is well in excess of the stated purpose of the IBT to aid the communities in compliance
with the CCPCUA rules. The IBT does allow for significant growth; growth that would not be
viable without the transfer of water via this IBT.
All of the receiving communities have the option, and appear to be planning, to bank
groundwater by reducing their required 75% reduction prior to the 201 8 deadline. Using the
figures in the EA, we have calculated that with maximum day demands minus the use of
allocated groundwater withdrawal and banked water (assuming equal distribution for 20 years
starting in 201 8), the maximum transfer needs (to meet maximum day demands) is 11.3 mgd.
This also assumes that per capita demand will not change over the time period. Aggressive water
conservation activities that must accompany a transfer awarded could reduce demand upwards of
10% or more, thereby reducing the maximum day water demands of the receiving communities.
At the moment, the Town of Winterville's per capita water use is the lowest of all the
communities at 90 gpcd. Greenville's per capita use is currently at 120 gpcd.l
Greene
Countv
1 Amount 1 11.30 1
Maximum
Demand -
groundwater
withdrawal
(mgd)
4.51
Banked
water Total
(MG)
2700
Daily banked Allocated Maximum
water Demand
availah!e until
2037 (mgd)
Farmville
Winterville
B. Infrastructure Investments
Banked Water
Available per
year until
2037 (MG)
135 0.39
Finally, the decisions by the source and receiving basin communities to invest millions of
dollars of public monies for construction of infrastructure, partially completed, for the Tar River
to Neuse River proposed IBT should in no way bias the decision of the EMC. The commission
may only grant the IBT if the commission determines that the benefits of the proposed transfer
outweigh the detriments and that any detriments are mitigated to a reasonable degree. As noted
throughout the comments, it is clear that the EA and Petition do not provide enough information
for the EMC to make this decision.
Max IBT
1434
449
IV. Recommendations
0.74
Based on the previous comments, we urge the EMC to deny the request for the proposed
IBT at this time. As noted above, the EMC does not have the necessary information to grant the
certificate. Given the significant environmental impacts of the proposal, we also encourage the
EMC to reconsider the adequacy of the EA and the associated Finding of No Significant Impact.
71.7
22.45
Interbasin Transfer Petition: From Tar River to Contentnea and Neuse River Subbasins. April 2009. pp 2-5.
113 5.64
0.196
0.06
0.393
0.123
0.589
0.183
3.96
3.6
3.37
3.42
Appendix 7
21
A238
SEPA requires the preparation of an environmental assessment, and, if warranted, an
environmental impact statement ("EIS") for any transfer of surface water that requires the filing
of a petition pursuant to the Surface Water Transfer Act, N.C. Gen. Stat. 5 143-215.221; tj 113A-
8.1. An EIS is required if the scope and environmental impact of a planned project is significant.
1 N.C. Admin. Code 25.0501. The EA for the GUC IBT shows that there will be significant
impacts and that an EIS was warranted. Therefore, the EMC should deny the petition and
require GUC to complete a full and comprehensive environmental review of this project and
associated projects. At a minimum, GUC and the receiving basin communities should be
instructed to provide the following information:
1) Include information on GUC's drought management planning that has selected a
temporary dam proposal as the preferred alternative for raw water inlet protection during
low flow conditions.
2) Current and planned water conservation measures by both source and receiving basin
communities.
3) Demonstrate compliance with CCPCUA rules regarding required water conservation
activities.
4) Submit an improved alternatives analysis that provides cost estimates for all alternatives
as well as the potential environmental impacts. The EMC should require GUC and the
receiving communities to take a hard look at the Neuse Regional Water and Sewer
Authority alternative. The 2007 law change to the Regulation of Surface Water Transfers
Act gives preference to transfers of waters within a major river basin.
5) Include an analysis of secondary and cumulative environmental impacts due to the
growth that will be possible due to the IBT.
6) Provide more information on the secqndary and cumulative impacts of the proposed IBT
to aquatic resources, including impaired streams and endangered and threatened species
in both the source and receiving basins.
7) Detail the compliance history of the receiving basins wastewater treatment plants and
demonstrate ability to maintain compliance with higher wastewater flows.
The EMC has the authority to grant the petition in whole or part and may grant a
certificate with conditions attached. "The conditions may include mitigation measures proposed
to minimize detrimental effects of the proposed transfer and measures to protect the availability
of water in the source river basin during a drought or other emergency." Again, we believe the
EA and petition do not provide enough relevant information on the secondary and cuinulative
impacts in both basins for the EMC to be able to make this decision. But, if the IBT is to be
granted, we recommend the following:
1. The EMC should make the IBT a temporary certificate and provide enough time
for the receiving basin communities to identify and make the necessary
investments for Neuse Basin source water. The cross-connections currently being
built to GUC could be used for emergency connections in the future.
2. The EMC should require regional land-use planning to insure that as growth
occurs is does not exceed the available water supply.
3. The EMC should reduce total IBT amount to reflect the stated objectives of
replacing cretaceous aquifer water source of approximately 4 mgd.
Appendix 7
22
A239
4. The EMC should require aggressive water conservation measures enacted by both
source and receiving basins, including but not limited to:
Home fixtures retrofit program,
Ordinances for requiring (or incentivizing) cisterns or other rain water
harvesting uses,
Separate irrigation meters and higher pricing for irrigation,
Comprehensive educational programming and written information
5. The EMC should require that GUC submit a plan and implement activities for
reducing per capita residential water use by 10% over a 1 0-year time period.
6. The EMC should require that GUC submit a plan and implement for reducing per
capita industrial water use by 5% over a 10-year period.
7. The EMC should require that GUC conduct a feasibility study and create an
action plan for water,reclamation projects.
8. The EMC should require that the receiving basin wastewater treatments plants
remain in compliance with their NPDES permits 11 of 12 months of the year or
face reduction in IBT amount.
V. Conclusion
The Surface Water Transfer Law requires the EMC to issue a certificate for the proposed
transfer if- and only if - two conditions are met: the benefits of the proposed transfer must
outweigh the detriments, and the detriments must be mitigated "to a reasonable degree." N.C.
Gen. Stat. $ 143-215.22I(g). The EMC must find that these conditions are met "by a
preponderance of the evidence," id., a legal standard requiring that the evidence on which a
decision rests be credible, and that the evidence, taken as a whole, shows that the fact sougl-it to
be proved is more probable than not. Given the numerous inadequacies, errors and oversights in
the EA, this standard cannot be met. The EMC should exercise its authority to deny the petition
and certificate in accordance with N.C. Gen. Stat. $ 143-2 15.22I(h).
We appreciate the opportunity to comment.
Sincerely,
Heather Jacobs Deck
Pamlico-Tar RIVERKEEPER@
Pamlico-Tar River Foundation
IS/ Kay Bond
Kay Bond
Staff Attorney
Southern Environmental Law Center
Appendix 7
23
A240
Ogallo, Toya
From:
Sent:
To:
Cc:
Subject:
Heather [riverkeeper@ptrf.org]
Tuesday, January 19, 2010 4;22 PM
Ogallo, Toya
'Kay Bond'
GUC IBT comments
Attachments: PTRF-SELC supplemental GUC IBT comments.pdf; GUC IBT Final
Comments-PTRF-SELC.pdf
PTRF-SELC GUC IBT Final
pplemental GUC IBlomments-mRF-SE.
Toys,
Please find the attached comments that supplement a letter sent on December 4, 2009. We
have also included that letter for reference.
Thank you,
Heather Jacobs Deck
Pamlico-Tar Riverkeeper
Pamlico-Tar River Foundation
Phone: (252) 946-7211
Cell: (252) 402-5644
Fax: (252) 946-9492
www.ptrf.org
Waterkeeper Alliance Member
Appendix 7
24
A241
Pamlico-Tar River Foundation Southern Environmental Law Center
P.O. Box 1854, Washington, NC 27889 200 W. Franklin Street, Ste. 330, Chapel Hill, NC 27516
252-946-7211 919-967-1450
January 19,20 10
VIA ELECTRONIC MAIL
Toya Ogallo
Division of Water Resources
DENR
16 1 1 Mail Service Center
Raleigh, NC 27699-1 61 1
Dear Ms. Ogallo,
The Pamlico-Tar River Foundation (PTRF) and Southern Environmental Law Center
(SELC) submit the following comments on the Greenville Utilities Commission's (GUC) petition
for an Interbasin Transfer (IBT) certificate. These comments are intended to supplement
comments provided in a letter dated December 4,2009. Our more detailed review of the IBT
Petition and supporting documents in the intervening weeks has strengthened our initial
concerns. Based on our previous comments submitted in December, we continue to urge the
EMC to deny the request for the proposed IBT at this time. The EMC does not have the
necessary information to grant the certificate. However, if the IBT certificate is to be granted we
recommend including several conditions that will mitigate the negative impacts from the
proposed transfer. We have also had the opportunity to review comments from and confer with
the City of Rocky Mount, and echo the concerns and problems the City raised in its comment
letter. If the EMC moves forward with the petition, we strongly encourage the state to consider
the conditions proposed by the City of Rocky Mount.
The City of Rocky Mount has proposed several conditions for Greenville Utilities
Commission's (GUC) petition for an Interbasin Transfer (IBT) certificate. Pursuant to N.C. Gen.
Stat. fj 143-215.221, the Environmental Management Commission can impose conditions on an
IBT certificate and has done so in several other cases, including the Charlotte-Mecklenburg
Utilities IBT fi-om 2002 and the Cary/Apex IBT from 2001.
The first condition Rocky Mount proposed is that the certificate be revisited upon
completion of the Tar River Hydrologic Model. PTRF and SELC strongly support this
recommendation and suggest that the EMC incorporate similar language as was used in previous
IBTs. In the CMU and CaryIApex IBT certificates, the EMC included the condition below:
"The Commission notes that future developments may prove the projections and
predictions in the EIS to be incorrect and new information may become available
that shows that there are substantial environmental impacts associated with this
transfer. Therefore, to protect water quality and availability and associated
benefits, modification of the terms and conditions of the certificate may be
necessary at a later date."
Appendix 7
25
A242
If the EMC moves forward with the GUC IBT, the final certificate should include similar
language triggering a reopening of the certificate based on the Tar River Hydrologic Model.
We also urge the EMC to consider conditions that seek to increase the long-term water
use efficiency by both the receiving and source river basin communities. The IBT petition
includes information on drought management response measures, but fails to include information
on long-term efficiency measures. Conditions to address efficiency could include: - Implementation of regional planning to ensure the most efficient management of the
shared water resources in both the source and receiving communities. - Requirements that GUC and other wastewater facilities in the receiving basins
conduct a feasibility study and action plan for water reclamation 1 reuse projects. - Plan for and implement strong water conservation programs and activities with the
goal of reducing customer water demand, including but not limited to:
o Home fixture retrofit programs
o Requiring or incentivizing water harvesting practices (i.e. cisterns)
o Separate irrigation meters and pricing of irrigation water
o Aggressive public educational campaigns
An additional condition, similar to that included in the CaryIApex IBT below, should be included
to ensure that any drought management measures and other mitigation measures are properly
enacted. The CaryIApex IBT certificate included the following:
"Prior to transferring water under this certificate, the holders of this certificate
shall work with the Division of Water Resources to develop compliance and
monitoringplan subject to approval by the Division. The plan shall include
methodologies and reporting schedules for reporting the following information:
maximum daily transfer amounts, compliance with permit conditions, progress on
mitigation measures, drought management, and reporting. A copy of the
approvedplan shall be kept on file with the Division for public inspection. The
Division of Water Resources shall have the authority to make modiJcations to the
compliance and monitoring plan as necessary to assess compliance with the
certificate. "
During the comment extension period, we also had time to further review the hydrologic
study done by Entrix for GUC and to consult with a hydrologist about its validity. After further
review, we are concerned about the validity of the 7410 value that was used in the analysis and
whether or not this is a relevant statistic for the purposes of determining flow changes as a
consequence of the IBT over a one year period. We would have liked to see how this value was
derived. Furthermore, it appears that the flow duration curves that GUC relied upon to
determine no significant impact do not reveal the temporal nature of what is actually occurring in
the river over the short-term. Low-flow values that may occur over a significant period of time
(for example 1-2 month time period) would be masked by such a long-term analysis. It would be
more helpful to see the minimum/maximum percent changes in flow over given periods, such as
a one year period. In short, with out a summary of all the raw statistics used in the modeling it is
Appendix 7
26
A243
difficult to independently verify the report's conclusions and the validity of the methodology
used.
We appreciate the opportunity to comment.
Sincerely,
Heather Jacobs Deck
Pamlico-Tar RIVERKEEPER@'
Pamlico-Tar River Foundation
IS/ Kay Bond
Kay Bond
Staff Attorney
Southern Environmental Law Center
Appendix 7
27
A244
Page 1 of 1
Ogallo, Toya -
From: Heather [riverkeeper@ptrf.org]
Sent: Wednesday, December 02,2009 5:20 PM
To : scrowe@suddenlink.net; kmartinncemc@hotmail.com
Cc: Ogallo, Toya
Subject: GUC IBT comment period
Attachments: 12-2-09 GUC IBT extension request letter.pdf
Please see the attached letter. It was communicated to me that any request for extension of the written
comment period would have to be made to the hearing officers.
Thank you for your consideration of this request,
Heather Jacobs Deck
Pamlico-Tar Riverkeeper
Pamlico-Tar River Foundation
Phone: (252) 946-721 1
Cell: (252) 402-5644
Fax: (252) 946-9492
~~~.~trf.orq
Waterkeeper Alliance Member
Appendix 7
28
A245
PAMLICO-TAR RIVER FOUNDATION
PO Box 1854, Washington, NC 27889
252-946-7211
December 2,2009
VIA ELECTRONIC MAIL
Kevin Martin
Stan Crowe
Hearing Officers
Environmental Management Commission
Re: Proposed IBT for Greenville Utilities
Dear Mr. Martin and Mr. Crowe,
We understand that the City of Rocky Mount may ask for an extension of the comment period to
pursue further communication with Greenville Utilities to address the concerns of the City. We support
this extension as it will also be difficult for us to provide the best possible comments on this proposed
IBT by this Friday. We need additional time for analysis of several concerns listed below. We would
greatly appreciate receiving a two-week extension of time, i.e., until Friday, December 18,2009 to submit
our comments.
Among the concerns we want to address and need additional time to explore are the hydrologic
model, the wastewater capacities of the receiving basin communities, and the Aquifer Storage and
Recovery program and how it may impact the transfer amounts. It has also come to our attention that the
Greenville Utilities Commission has completed a draft Environmental Assessment regarding future
drought management planning with a preferred alternative for a temporary dam structure in times of low
flow. This EA should be incorporated into the analysis of the IBT EA and petition. Furthermore, we
would like the additional time to continue the dialogue with community members that may be impacted
by this IBT.
Finally, we have concerns with some of the conclusions stated in the EA. For example, the
conclusion that the proposed IBT will have no impact on threatened, rare and endangered species in the
either the receiving or source river basin because of the lack of construction lacks supporting evidence
and does not address potential impacts from increased development (and its attendant construction).
Moreover, there is no mention at all of potential impacts from increased flow or changes in water quality;
nor is there mention of impacts to species of concern in the source basins from decreased flow or changes
in water quality. In addition, the EA fails to provide adequate information on mitigative measures related
to current year-round water conservation measures and planning. The IBT petition similarly excludes this
critical information.
Thank you for your consideration of these preliminary comments and our request for additional
time to submit more complete comments. I look forward to hearing from you.
Sincerely,
Heather Jacobs Deck
Pamlico-Tar RIVERKEEPER
Pamlico-Tar River Foundation
Appendix 7
29
A246
2571 Railroad Street
PO Box 1459
Winterville, NC 28590
December 3, 2009
Toya F. Ogallo, NCDWR
1621 Mail Service Center
Raleigh, North Carolina 27699-1621
Dear Ms. Ogallo:
Phone: (252) 756-2221
Fax: (252) 321-8455
www.wintervillenc.com
The purpose of this letter if to inform you of the Town of Winterville's official support for
Greenville Utilities Commission's Petition for an lnterbasin Transfer Certificate. The approval of
this petition is not only important to the Town of Winterville, but to neighboring communities as
well.
Like many of the jurisdictions in eastern North Carolina, the Town of Winterville is subject to the
Central Coastal Plain Capacity Use Area restrictions. Winterville currently relies on a
combination of groundwater and water purchased from Greenville Utilities for water supply. The
Capacity Use Area restrictions require that the Town reduce its dependency upon groundwater.
In 2008, the Town reduced its use of groundwater by 25% and entered into a water purchase
agreement with Greenville Utilities. The Town will be required to reduce groundwater use by
another 25% in 201 3 and another 25% by 2018.
The Town of Winterville has explored several options as it prepares to meet the reductions
imposed by the Capacity Use Area rules. Winterville has no local source of surface water
available to the Town and has therefore determined that the purchase of water from Greenville
Utilities Commission is the most economical and technically feasible engineering alternative.
The reduction in water supply per the CCPCUA rules places an extreme hardship on the Town
of Winterville. The Town believes that the EMC has an obligation to allow Winterville to replace
its previously permitted water supply capacity with a high quality water that is readily available
and accessible.
The proposed lnterbasin Transfer will allow Winterville to replace the water supply capacity that
has been reduced as a result of the Central Coastal Plain Capacity Use Area Rules. While
understanding why the rules were necessary, the Town of Winterville has few options and
believes the IBT proposal submitted by Greenville Utilities Commission will provide both
communities with high quality water that is readily available and accessible, and will still allow
GUC to meet its future water needs.
As in many other communities, the Town supports the desire of the Division of Water Resources
for communities to seek a regional solution to issues such as water capacity. The Town already
has connections with Greenville Utilities and Bell Arthur Water Corporation. As other
communities tie in with the Greenville Utilities system, these connections will provide the ability
to provide water over a large portion of Pitt County and Greene County. This further enhances
the region's ability to tie into other water systems in the region that could be a tremendous asset
in the times of emergencies or water shortages. This project is a true approach to a regional
Appendix 7
30
A247
Page 2
GUC IBT Support Letter
problem that will make eastern North Carolina a stronger area of the state with increased
potential. The City of GreenviUe is the "hub" of eastern North Carolina with the ability to provide
services on a regional scale. This ability is a real benefit to the region as a whde, as well as
provide for economies of scale when future needs have to be addressed.
The Town of Winterville fully and enthusiasticafly supports the request by Greenville Utilities
Commission for the lnterbasin Transfer Petition. We hope that the Environmental Management
Commission will support this request for the benefit of eastern North Carolina, Greenville
Utilities Commission, and the Town of Winterville.
Sincerely,
Douglas Jackson
Mayor
Cc: Ron Elks, General Manager, Greenville, Utilities Commission
Randy Emory, Director of Water Resources, Greenville Utilities Commission
Bill Whisnant, Town Manager
Terri Parker-Eakes, Assistant Town Manager
Appendix 7
31
A248
December 1,2009
Ms. Toya F. Ogallo
Division of Water Resources
DENR
1 6 1 1 Mail Service Center
Raleigh, NC 27699- 1 6 1 1
Re: Greenville Utilities Commission
IBT Petition
Dear Ms. Ogallo:
I am submitting these comments regarding the above-referenced IBT petition on behalf of
the City of Rocky Mount to express ow concern regarding the uncertainty as to the
impact the requested IBT might have on Rocky Mount's management of the Tar River
Reservoir.
As a result of the drought of 2007/08, Rocky Mount intends to review and, if necessary,
update its drought management plan. The review will be conducted following the
completion of DWR's Tar River Hydrologic Model, which is anticipated in early 201 1.
If revised, Rocky Mount will seek approval of the updated plan from DWR. A revised
drought management plan may result in a low-flow regime at Tarboro that is different
from the one on which the IBT FONSI was based. Rocky Mount is concerned that the
analysis done to support the FONSI is not adequate to determine whether there could be
conflicts between its revised drought management plan and the IBT. Rocky Mount is
attempting to work with the GUC and its consultant to further analyze the potential
interaction between the requested IBT and Rocky Mount's possible future need to reduce
its releases and whether the flows are adequate to accommodate bcth. This analysis has
not been completed. Rocky Mount understands that the comment period closes on
December 4, 2009 and requests that the record be held open for forty-five (45) additional
days so that this analysis can be completed and a further comment can be submitted
based on the results.
Rocky Mount recognizes the possibility that even after hrther analysis the effect of the
IBT on its ability to reduce its releases from the Tar River Reservoir at times low flow
may be uncertain. It is our understanding that further study of instream flows at
Greenville are to be conducted in the near future. In view of this uncertainty and theneed
for additional information, and in order not to unnecessarily delay consideration of the
GUC IBT request, Rocky Mount requests that the EMC consider including condrtions in
the IBT certificate that:
33 1 South Franklin Street Post Office Box 1180 Rocky Mount, North Carolina 27802- 1180
Telephone (252) 972- 1325 Fax (252) 972- 1 173 Website: www. rockymountnc.gov
Appendix 7
32
A249
1. Acknowledge that Rocky Mount's drought management plan will be evaluated
based on the normally applicable criteria and not its potential effect on the
requested IBT.
2. Provide that if implementation of Rocky Mount's approved drought management
plan causes flows at Greenville that result in unacceptable impacts (e.g., location of
the salt front) or are insufficient to allow the permitted transfer, the systems that
receive the transferred water will resume groundwater pumping until such time as
conditions allow resumption of the transfer. The groundwater pumped as a result of
these modified operations will be offset by additional transfers during periods of
higher flow in the Tar River over a period of no longer than one year following the
resumption of transfers so that there will be no net change in the amount of the
groundwater pumped over the long term..
3. Provide that if at such time as Greenville applies for an increased withdrawal, there
is insufficient water to meet in-basin needs, including those of Rocky Mount, the
transfer will be reduced in order to accommodate in-basin needs.
We realize that the above proposed conditions will require rewording, but trust that the
intended meaning is clear. Please understand that Rocky Mount is not attempting to
oppose the requested IBT but does believe that extension of the comment period and
inclusion of the above conditions are necessary to ensure that Rocky Mount's future
water needs are fairly protected.
Please let me know as soon as is feasible whether the comment period will be extended.
Do not hesitate to contact me if you have any questions.
Sincerely,
Peter F. Varney
Assistant. City manager
cc: Stephen W. Raper, City Manager
Wayne Hollowell, Director of Water Resources
Appendix 7
33
A250
- -
MOUNT
NORTH CIROLINA
January 19.201 0
Ms. Toya Ogallo
Division of Water Resources
DENR
161 1 Mail Service Center
Raleigh, NC 27699- 16 1 1
Re: City of Rocky Mount
Comments Regardoing the Greenvillc Iitiiitier C:smmicsic".n'cs IC'C1! !C") IRT Reqtxest
Dear Ms. Ogallo:
Please accept these comments concerning the above-referenced matter. If you or any other
person with the Division of Water Resources would like to discuss these comments, please do
not hesitate to contact me. My telephone number is (252) 972-1 330 and my email address is
peter.varney(~roclcymountnc.~ov.
COMMENTS GREENVILLE WTERBASIN TRANSFER ("IBT") APPLICATION
1. The City of Rocky Mount is concerned that the Environmcnta! Assessment ("EA") does
not examine potential impacts on the Tar River Reservoir. --
The IBT statute requires that the applicant examine the present and reasonably foreseeable future
detrimental effects on the source river basin. N.C.6.5. 53-21 5.221(0(2). The City of Rocky
Mount is concerned that the GUC looked only at the potential impacts on an approximately
eight-mile reach of the Tar River below Greenville, as acknowledged in the Environmental
Assessment ("EA"), and not on the Tar River Resertuir.
"The model was used to evaluate resulting flow in the river at two
locations. The first location was the USGS gage at Greenville, which is
downstream of GUC's water treatment plant intake and water treatment
plant discharge, but is upstream of GUC's wastewater treatment plant
(WWTP) discharge.. .. . .This 7.7-mile portion of the Tar River is the reach
that will have the lowest flows as a result of all upstream withdrawals, and
therefore, may be considered the reach of the Tar River most affected by
the proposed IBT. The second location where flows were evaluated is the
Tar River downstream of the GUC WWTP discharge ..." (EA, Appendix
B, page 1)
33 1 South Franklin Street Post Office Box 1180 Rocky Mount, North Carolina 27802-1180'"
Telephone (252) 972-1 325 Fax (252) 972- 1173 Website: www.rockymo~~iztizc.gov
Appendix 7
34
A251
Ms. Toya Ogallo
Division of Water Resources
January 1 9'20 10
Page 2
2. Rocky Mount's future consideration of operational changes for the Tar hver Reservoir
should be taken into account.
The EA further explains the decision not to consider impacts on the Tar River Reservoir as
follows:
The hydrologic analysis and modeling assumed that interbasin transfers at
Greenville would have no impact on operations of the Rocky Mount
reservoir 70 river miles upstream. The only way th~t ?hc !RT cou!d affect
upstream operations would be if there were to be an approved change in
Rocky Mount's permitted withdrawal and operating conditions. GUC has
not made such a request and such as (sic) operational change has not been
assumed in the hydrologic analysis and modeling." (EA Appendix C,
page 10112.)
However, Rocky Mount was extremely hard hit by the drought of 2007108 and, as a result, is
considering a modification to its water shortage response plan.
For Rocky Mount, as for many municipalities in North Carolina, the drought of 2007108 was an
unprecedented event. Whereas Rocky Mount had been able to negotiate the drought of 2002
with relative ease, the event of 2007108 was different. The Tar River Reservoir, Rocky Mount's
sole source of water, dropped to1 0 percent of usable storage. To avert what appeared to be an
impending crisis, in addition to activating the drought management plan1, emergency
connections were made to Wilson and Tarboro. At times, and with the permission of the
Division of Water Resources, releases from the reservoir were cut to 30 cfs, compared to a
minimum of 60 cfs allowed in the approved water shortage response plan. An aerial
reconnaissance of the Tar River upstream of the reservoir revealed previously unknown upstream
withdrawals whose aggregate withdrawals exceeded the City's demand. Thus the storage in the
reservoir was falling as if there were two cities the size of Rocky Momt withdrawing water.
As a result of this experience, Rocky Mount intends to update its probability-based drought
management plan. Thus, the "operational change" that was assumed in the EA not to be a
possibility is exactly the type of change that Rocky Mount is, in fact, considering. This fact was
apparently not known to GUC during preparation of the EA, possibly because Rocky Mount was
not consulted.
'1n addition to demand restrictions, the plan includes pumping from several abandoned quarries to
supplement flows in the Tar River. 10 cfs were pumped continuously from July 30 through mid-November, during
which time the quarries were pumped down 60 feet.
Appendix 7
35
A252
Ms. Toya Ogallo
Division of Water Resources
January 19,2010
Page 3
Rocky Mount plans to conduct the review of its water shortage response plan after DWR's Tar
River Hydrologic Model is completed. This model will not only have hydrology that includes
the 2007-08 drought, but it will also include the impacts of the other withdrawals in the basin
that had not previously been accounted for. (A comprehensive review of demands, including
agricultural demands, throughout the basin will be a part of the development of this model. It is
likely that even more previously unknown demands will be identified.) The Tar River
Hydrologic Model is expected to be completed in the summer of 201 1.
7 . The impacts of the pro~osd IBT En the notentialto alter t!!e oper~tion of Rocky Moue
Tar River Reservoir cannot be determined from the EA
A. The flows at the Tarboro gage upon which the predicted flows at Greenville were
based are not representative of those that will occur in the future.
The analysis in the EA used the flows recorded at the USGS Tarboro River at Tarboro
gage (Gage No. 02083500) from 193 1 through 2007 (EA, Appendix B, page 1). The
flows recorded at the gage reflect the cumulative impact of all the withdrawals and
discharges upstream of the gage as well as the regulation resulting from the operation of
the Rocky Mount's Tar River Reservoir. Although at this time it is not known
definitively, we suspect that the operation of the reservoir has the largest impact on the
gage readings. The Tar River Reservoir has been in operation since 197 1. Thus, the
gage record reflects essentially natural, i.e., unregulated, flows for the period from 193 1
thru 1970, and regulated flows thereafter. This fact was acknowledged in the EA
(Appendix B, page 22). The operating protocol for the reservoir has changed several
times since 1971. Rather than including the reservoir in the hydrologic model explicitly
and applying the current operating protocol consistently over the entire record, including
the period prior to 1970, the analysis used the gage record "as is." The justification for
this approach appears to be that because "Reservoirs such as Rocky Mount's often
augment low flows in rivers because thev store water from higher flow periods and
release it over extended lower flow periods" (EA, Appendix B, page 22), the lower
unaltered flows in the record prior to 1970 lead to a conservative result. That is, because
there were flows in the record prior to 1970 that are lower than the current minimum
flows, the substitution of the required minimum flows for the lower, unaltered, flows
would result in even less impact than shown. However, the magnitude of flows alone
does not prove this hypothesis. The timing, frequency, and duration of low flows are
equally important, and they have not been considered.
The currently-approved water shortage response plan for the Tar River Reservoir allows
for discharges to be reduced incrementally to 60 cfs during the course of a drought. This
policy has been invoked only three times since the mid-1990s. Thus, the statement in the
EA that "the hydrologic model reflects the impacts of the Rocky Mount operating rules
Appendix 7
36
A253
Ms. Toya Ogallo
Division of Water Resources
January 19,20 10
Page 4
and minimum flows that have been in place over the past 36 years" (EA, Appendix B,
page 22) is true for only a very small portion of the record used for the analysis. Also,
flows recorded early in the early stages of the 2007108 event are not representative even
though the current water shortage response plan was in place because the Tar River
below Tar River Reservoir gage (Gage No. 02082506), upon which the release from the
reservoir is based, was out of calibration. As a result, for a period of approximately a
month, rather than releasing 60 cfs, as intended, the actual release was approximately
twice that much. The reservoir releases, of course, are captured by the Tarboro gage.
Thus: at leas: fir a portior? of the dreught: of record, the flews recorded at tkc Tarboro
gage are higher than intended and not representative of system operations.
Further, there is no information in the EA as to the timing, frequency, or duration of low-
flow occurrences prior to dam construction as compared to the timing, frequency, and
duration, post dam construction, of the periods when the releases from the dam were 80
cfs. It is highly likely that the impacts to the aquatic environment from, for example, a 30
day period of flows of 20 cfs embedded in a four-month period in which flows were
below 80 cfs are very different from those associated with a six-month period of a
constant flow of 80 cfs.
Finally, the period of record analyzed (October I, 193 1, through September 30,2007) did
not include the lowest flow 7-day period in the record, which occurred in October 2007.
B. Flow duration curves are, at best, an incomplete metric of impact.
Flow duration curves present the fraction of time that flows are above (or below) some
value. They are prepared by sorting the flows and computing the percentile associated
with each flow. Thus the lowest flow in the record is equal to or exceeded 100 percent of
the time, the median flow is exceeded 50 percent of the time, etc. Flow duration curves
can be prepared either for the whole year, in which case all flow data are included in the
sort, or, as ws done irr the E.,4, for shorter pzriods, such as a month. To prepre the ficw
duration curve for July, for example, if there are 50 years in the record, there are 3 1 * 50
values that go into the July flow duration curve.
The problem arises because flow duration curves do not account for the temporal
variability of flows. This is true even if the curves are prepared for a period shorter than
one year. To continue the example from above, if there are 50 values of 20 cfs in the July
data, and every other value is greater than 100 cfs, the same flow duration curve will
result whether the 50 values of 20 cfs occur one in each year or all in two years. The
potential impact to the stream of the two scenarios, however, could be very different. In
order to fully assess the impact of altered streamflow regimes, one must also examine the
frequency and duration of low flow periods.
Appendix 7
37
A254
Ms. Toya Ogallo
Division of Water Resources
January 19,201 0
Page 5
Looked at another way, based on the flow duration curves, the applicant concludes that
flows will be lower than 109 cfs (the pre-IBT 7~10~), on average, 4.7 days per year
without the IBT and 6.4 days with the maximum IBT (EA, Table 6-3, page 6-7). Again,
this metric does not tell the whole story because the frequency, timing, and duration of
the extra 127 days (1.7 extra days per year times 76 years) below 109 cfs are not
reported. The impacts to the stream will likely be very different if all those days occur in
one or two years versus being distributed over 20 years.
llese comments do not address the appropriateness of using comparisons of the 74 10
with and without the IBT as a basis for determining impact. The 7410 is a relevant
statistic for unregulated rivers. Where, as here, the river is regulated, the statistic is much
less useful because the same number can result from very different flow sequences. For
example, as noted above, the pre-IBT 741 0 was determined to be 109 cfs. That is, the
lowest weekly average flow in 10 years was 109 cfs. However, the 7Q10 would also be
109 cfs if flows of 109 cfs continued for three months. Dams, such as Rocky Mount's,
with fixed minimum releases have exactly this type of effect.
4. The City of Rocky Mount requests that any IBT certificate issued to the GUC include a
condition allowing the Certificate to be reopened following completion of the Tar River
Hydrologic Modeling and Water Resource Plan if the results indicate that the approved IBT
impinges upon Rocky Mount's ability to modifv its water shortage response plan.
Rocky Mount is concerned that, if approved, the demand to transfer water outside the basin
could influence the decision to approve a requested change in the release protocol for the Tar
River Reservoir. To guard against this possibility, in our comments dated December 1,2009,
Rocky Mount proposed several conditions that might be included in the IBT certificate. Upon
further reflection, Rocky Mount now considers that a condition that would allow, upon the
approval of the EMC, the certificate to be reopened following the completion of the Tar River
Hydrologic Model would be the best option for protecting the interests of a!l users in the losing
basin while still allowing GUC to address their immediate needs.
In conversation with our consultant, the GUC's consultants indicated that because some of the
modeling scenarios requested by DWR essentially "double count3" demand, this provides a
safety factor that will assure no impact to Rocky Mount. While this assertion may be accurate, it
cannot be established from the analysis in the EA. The best way to insure compliance with the
statute is to use a basin-wide hydrologic model for the analysis AND to involve others in the
2~he 7410 is a statistic that represents the lowest 7-day average flow that occurs once in 10 years.
3 In fact, the demands were not double counted in all scenarios because withdrawals were capped at
Greenville's currently-permitted treatment capacity (EA, Table 6-1, page 6-4), which is less than twice the demands.
Appendix 7
38
A255
Ms. Toya Ogallo
Division of Water Resources
January 19,201 0
Page 6
basin in the decision-making. The updated Tar kver Hydrologic Model will be such a basin-
wide model and will be developed in consultation with stakeholders throughout the basin. Thus,
the model will form an agreed-upon basis upon which all parties can evaluate the impacts of the
proposed IBT. Following its completion, Rocky Mount will know whether a modification to its
water shortage response plan is, in fact, needed. In addition, Rocky Mount and other users in the
basin, including those who represent environmental interests, will be able to accurately evaluate
the impacts of the proposed IBT in the context of a basin-wide water supply plan.
Rocky Mount d.oes not oppose or want to delay issumce oJcan IBT Certificate pending
completion of DWR's Tar River Hydrologic Model. However, In the interest of good water
resources management, both for those in the basin as well as those outside, the Certificate should
contain the requested provision that allows users in the basin to request that the EMC reopen the
Certificate, if warranted, once the Tar River Hydrologic Model is complete.
Sincerely,
Peter F. Varney V
Assistant City Manager
cc: Stephen W. Raper, City Manager
Wayne Hollowell, Director of Water Resources
Randall Emory, Director of Water Resources, Greenville Utilities Commission
Appendix 7
39
A256
Page 1 of 1
Ogallo, Toya
From: Laura E. Williamson [laura.williamson@embarqmail.com]
Sent: Wednesday, January 13,2010 5:31 PM
To: Ogallo, Toya
Subject: IBT discussion
As a resident of Greenville, Pitt County I am writing to express my concern re: the proposed IBT, as
presented by GUC.
The population of Eastern North Carolina is likely to grow. Withdrawals from underground sources should
first be addressed by reducing local water usage rather than simply meeting demand by transporting
water over long distances. The latter increases the vulnerability of the water system to leakage and
contamination. While the short-term economics may support the validity of building such an
infrastructure, long-term development of the area and sustainable use of water resources would be better
served by increasing our collective efficiency in water usage. Additionally it would appear that Greenville I Utilities is willing to sell surface water cheaper than Neuse Regional WASA. This, if nothing else, is not a
satisfactory reason for approving IBT.
And lastly - removing adversely effecting water resources impacts more than humans. This area has a
rich diversity that has evolved precisely because of the abundance of water. Removing water from the
Tar River Basin can only serve to negatively impact surrounding flora and fauna.
I strongly urge that this proposed plan be thoroughly reviewed.
Regards - Laura
Laura E. WILLIAMSON
Energy and Climate Change Policy Analyst
3402 Wyneston Road
Greenville - NC 27858
laura.williamson@embarqmail.com
Appendix 7
40
A257
Page 1 of 1
Ogallo, Toya
From: Wayne Caldwell [ewaynecl @embarqmail.com]
Sent: Monday, January 04,2010 12:24 PM
To: Ogallo, Toya
Subject: GUC Interbasin Transfer Request
The transfer of GUC water to Greene County does not make sense since the Neuse Regional
WASA is in the best position to supply those needs and then there is no IBT. Farmville should
likewise get it's water from NR WASA. NR WASA was created to supply these needs but
apparently politics is playing out with the requesters familiarity with GUC and probably lower
cost water. I support the use of GUC water to Winterville. This proposal would have minimal
impact on the environment and would supply all parties with needed water.
Wayne Caldwell
Appendix 7
41
A258
Response to interbasin transfer Page 1 of 1
Ogallo, Toya
-
From: Charles Schwartz [schwartzcf@embarqmail.com]
Sent: Monday, December 14,2009 12:51 PM
To: Ogallo, Toya
Subject: Response to interbasin transfer
Dear Ms. Ogallo,
Thank you for this opportunity to respond to the proposed draft petition for an
interbasin transfer certificate.
I attended a recent public hearing on this matter at Pitt Community College in
Greenville. After listening to the pros and cons of those who spoke, I was convinced
that the citizens of Greenville should be deeply troubled about what is being proposed.
One of the major concerns that a number of individuals identified was that the proposed
transfer appears to be a one-way flow of water from our area. In follow up comments,
it was said that if the water must be given, then a return of the waste water should be
made mandatory as a part of the agreement.
The folks in our region want to be good neighbors. In the event that an existing
neighboring community was experiencing a lack of suitable drinking water, one would
expect assistance to be forthcoming. However, if that neighboring community was
expanding and using water in a manner not consistent with good conservation
practices, then one would expect questions to be raised.
One can observe that new subdivisions are being built around Greenville. Some of
these feature verdant lawns which undoubtedly are sustained and enhanced by
frequent watering and fertilizers. Should scarce water be diverted from the Tar River so
that new sub-divisions can create expansive lawns?
At a minimum, those communities requesting water should require their residents to
use landscaping alternatives as a part of a larger conservation program. There are
lawn substitutes for grass that tolerate light foot traffic and even moderate mowing.
Sincerely,
Charles Schwartz
Appendix 7
42
A259
Carolyn Reed
1 10 Kenilworth Drive
Greenville, N.C. 27858
(252) 353-5781
johncaro2@?mbarclmail.com
~reenae Utilities Commission - Request for an Interbasin Transfer Certif~cate
Thursday, November 5,2009
Goess Student Center, Pitt Community College
Winterville, NC
TO: The North Carolina Environmental Management Commission (EMC)
I have owned riverfront property on the Tar River in Greenville, N.C. for the last
ten years. Over those ten years I have witnessed extreme variation in the size and strength
of the water flow in the Tar River. Frequently in the summer months I have observed the
water flow dwindle quite dramatically. The river, which is sometimes as wide as a six
lane highway, has dwindled on at least one occasion to the size of a creek I could have
hopped over.
I am not claiming expertise in these matters, but common sense tells me water
should not be diverted fiom a river that regularly experiences such wide variations. What
has happened before will undoubtedly happen again, and if water has been diverted when
Greenville desperately needs it, then what? Will it have to be re-diverted back to the Tar,
when people in other areas have come to rely on it? Seems better to find other, more
permanent solutions for Farmville, Winterville and Greene County.
In addition, I think the environmental impact fiom such a drastic measure is
essentially unquantifiable before the action, and may be irreparable after. The Tar River
ecosystems are so complex and finely balanced there is just no telling what the
consequences will be. Disturbing the flow of river basins, which have evolved over
millenniums, is a drastic and risky action that may end up causing more problems than it
solves. I for one don't think it's worth the risk.
Thank you,
Carolyn Reed
Appendix 7
43
A260
James C. Cooke, Jr.
201 Beth Street
Greenville, NC 27858
December 20,2009
Toya F. Ogallo
Division of Water Resources, DENR
161 1 Mail Service Center
Raleigh, NC 27699- 1 6 1 1
Dear Toya:
I am writing to register my comments against the proposed transfer by the Greenville Utilities
Commission of millions of gallons of Tar River water to the Neuse River basin. We have
entered a period of great climate change and uncertainty in which droughts are likely to reduce
river flow in the future as we recently experienced in 2007. Already water is being transferred
from the Roanoke River basin into the Tar River basin, and for water now to be transferred from
the Tar to the Neuse with no return for replenishment defies environmental logic.
Whenever human engineering attempts to tinker with nature there are often unanticipated and
unintended negative consequences. The potential damage of this proposed transfer from the Tar-
Pamlico River system includes wetlands, habitat, the intrusion of salt water upstream, and the
loss of a viable water supply to a region that recently experienced a reported river flow of only
50 million gallons per day downstream to Greenville. According to my information the summer
use of water from the Tar River for Greenville alone can amount to 16 million gallons per day.
The math is troubling for the health of communities that depend on the Tar River for their water
and for the ecological health of the river system itself.
I believe this issue is much more than being selfish and not wanting to be a good neighbor and
assist other areas with a limited water supply. Science suggests river systems are best managed
within their own basins, which precludes siphoning water off to other basins. We all must now
learn to live in harmony with nature and within the natural resources available to us, and that
means limiting water hungry development where the water is not available to support it.
Thank you very much for your kind attention to my comments.
Sincerely,
w James C. Cooke, Jr.
Appendix 7
44
A261
My name is Dave Schwartz and I live and work in Greenville.
I also volunteer with setma1 non-proSlt groups in Eastern
North Carolina promdhq i~s~loe tourism on our wonderPul
rivers and creeks in tk &we, Tar, and Roanoke River
Basins.
The Greenville Utilities Commission has requested from the
State of North Carolina to drain 13.5 million gallons of water
a day from our Tar River calling it, "interbasin water
transfer:" Interbasin water transfer sounds thoughtful,
harmless, and scientific. It is not. Interbasin water transfer
takes water out of a river without returning it. Interbasin
water transfer is a euphemism for "draining from a river."
I am deeply concerned that 10 years from now the above
sea level portions of the Neuse, Tar, and Roanoke Rivers will
only be navigable after a good rain because our public trust
waters will be injected into pipelines and aquifers to be
distributed by huge water systems.
The GUC draining request will remove the water from the
Tar River without returning a drop. Because they will make
money from selling Greenville's water to the communities of
Winterville, Farmville, and Greene County, I do not find it
unreasonable that they could use part of this money to build
another pipeline. This parallel pipeline to the one drawing
from our river would return the treated wastewater from
these communities back to our river and to us, so our
businesses, families, ECU, and visitors can continue
prospering in Greenville. I feel sure the residents of
Greenville would be generous to loan out this valuable
resource as Ions as it is returned.
Appendix 7
45
A262
OfflCE Of MAYOR
October 30, 2009
Mrs. Toya Ogallo
Division of Water Quality
DENR
161 1 Mail Service Center
Raleigh, North Carolina 27699- 16 1 1
Dear Mrs. Ogdlo:
The City of Oxford supports the request for an interbasin transfer by the
Greenville Utility Commission.
yours 'iriJly, w
PO Box ~07 - 300 WiKimsbmo Street - Oxford NC 27565
v: (919) 603-1100 - y: (gig) 603-1107
www. oxfmdnc. urg
Appendix 7
46
A263
December 4,2009
Ms. Toya F. Ogallo
Division of Water Resources
DENR
1611 Mail Service Center
Raleigh, NC 27699-1611
Re: Greenville Utilities Commission
IBT Petition
Dear Ms. Ogallo:
I am submitting these comments regarding the above-referenced IBT Petition on behalf of the City of Wilson to express
our concern regarding the uncertainty as to the impact the requested IBT might have on future wastewater flows to the
Neuse River, and growth in the lower basin downstream of Wilson's wastewater discharge point and into an already
impaired stream, and the potential impact to the City of Rocky Mount, because of our mutual finish water
interconnection.
1) The City of Wilson is concerned about the transfer due to the potential of greater wastewater flows to the
Neuse Basin. Based on current Nitrogen allocations in the Neuse Basin, how will this area grow in water use
without a similar growth in the sewer flows? Will all of this flow then be pumped back to the Tar River, or land
applied, or sent to the Neuse? The City of Wilson is concerned that potential water quality problems in the
Neuse and Contentnea Creek could further impact point sources upstream of the IBT transfer communities.
2) In our opinion, Greenville is asking for a larger IBT than the minimum required. In fact they are requesting an
amount large enough to supply as much as 93% of the maximum daily projected demand for a short term and
151% continuously of the average daily demand. CCPCUA rules only require up to a 75% reduction in the
average daily demand of their permitted amount. Subtracting 75% from the Approved Base rate for Greene
County, Farmville, and Snow Hill would only require 4.45 MGD from GUC to meet the demand for an average
annual day and only 8.5 MGD for a maximum demand day, which is the day that GUC will only be transferring a
minimal amount according to Table 2-3. We do not see the necessity for a request of 8.3 and 9.2 MGD
respectively, and a total of as much as 13.4 MGD since GUC is also requesting to send 111% of the maximum
daily demand to Wintewille and 117% of the maximum daily demand for an emergency thru the year 2030. Even
if you assume the unprecedented growth rates for Greene County, Farmville and Winterville are correct, this
volume of transfer is unnecessary.
Appendix 7
47
A264
At the same time GUC in Table 2-3 stated that they have enough water plant capacity, but only reflect a
minimum withdrawal for the IBT transfer on these same days. Are we to assume that Greenville can run easily at
100% of the plant rated capacity without any issues and that the communities can reliably count on this
minimum amount on the same day when their wells cannot produce this increased demand?
3) We support Rocky Mount's request to extend the comment period for 45 days to complete a revised drought
management plan. This is particularly important due to the existing modest emergency interconnection capable
of transferring 1.9 MGD installed by both communities after the drought of 2007-2008.
4) Section 5 of the IBT Petition "Alternatives to Proposed Transfer" never mentions the City of Wilson as a viable
alternative for both Greene County and Farmville. Wilson had discussions in 2003 with both, had the water
available at a reasonable cost, and is in the Neuse Basin.
We realize that work for the IBT are well under way and funding for the potential IBT is already available.
However, we hope that the Division will take into account all considerations and will fairly protect all the
interests of everyone within the Tar / Pamlico and the Neuse Basins and will at least allow Rocky Mount's study
to be completed before proceeding with authorization. We also hope that IBT amounts will be reduced if the
Division reviews the report and thinks that the amounts of transfer are unnecessary.
Please let us know as soon as possible whether the comment period will be extended. Do not hesitate to contact
me should you have any questions.
Sincerely,
Barry G. Parks
Assistant Director of Public Services / Water Resources
cc: Grant Goings, City Manager
Charles Pittman Ill, Deputy City Manager
Jim Cauley, City Attorney
Appendix 7
48
A265
Commissioners
Bennie Heath - Chairman
Jack Edmondson - Vice Chairman
Denny Garner
Jerry Jones
James T. Shackleford, Jr.
County Manager
Don Davenport
Finance Officer
Shawna Wooten
A PlaceTo Grc>w.The Way To Live.
November 18,2009
Ms. Toya Ogallo
Division of Water Resources
DENR
1611 Mail Service Center
Raleigh, NC 27699-161 1
RE: Greenville Utilities Commission (GUC) - Request for an Interbasin Transfer Certificate
Dear Ms. Ogallo:
Greene County is one of several public water suppliers that the State of North Carolina included in
a capacity use area due to the amount of water that was being drawn from the groundwater
aquifers. The State required water suppliers to reduce their reliance on this groundwater source.
This determination by the State led Greene County and the Town of Farmville to work out an
agreement to purchase potable water from GUC. The sale, use, and disposal of GUC water to
Greene County and Farmvllle creates an interbasin transfer.
Greene County is strongly in favor of the Environmental Management Commission issuing the
Interbasin Transfer Certificate to GUC without delay.
Thank you for your cooperation.
Sincerely,
Don Davenport,
County Manager
xc: Greene County Board of Commissioners
229 Kingold Blvd.. Suite D Snow Hill. NC 28580 (252) 747-3446 FAX (25- 'IVRTBR-
www. m-greene. nc.
7ne mison of Gmne County Government is to sene and improve the lives of a// dtriens by providing llighquality, &-effdve se~cces in an open,
profesy'01~1 and ethical environment
Appendix 7
49
A266
C Commissioners
Bennie Heath - Chairman
Jack Edmondson - Vice Chairman
Denny Gamer
Jerry Jones
James T. Shadeford, Jr.
A PlaccTo Grc>w.The Way To Live. --
December 3,2009
Toya Ogallo
Division of Water Resources
DENR
161 1 Mail Service Center
Raleigh, NC 27699-1 61 1
Toya.F.Ogallo@ncdenr.gov
Subject: Comment - Letter of Support
GUC Request For IBT Certificate
Tar River Basin to Neuse River Basin
Dear Ms. Ogallo:
Greene County submits this letter of support for Greenville Utilities Commission's (hereinafter referred
to as GUC) Petition for an lnterbasin Transfer (IBT) Certificate.
In the past, Greene County's sole source of water supply has been groundwater obtained from the
Cretaceous aquifer. Greene County is under a state mandate (Central Coastal Plain Capacity Use Area
Restrictions implemented August 1,2002) to reduce our dependency upon groundwater by 25% in 2008,50%
in 2013, and 75% in 201 8. After an extensive investigation of available alternative water supply sources,
Greene County has entered into contract with GUC to obtain alternative water supply fiom GUC. In a joint
arrangement with the Town of Farmville, Greene County has invested millions of dollars for the construction
of a delivery system that will deliver up to 5 MGD to Farmville and Greene County. This water supply is
needed to replace the state mandated reductions placed upon our groundwater supply.
Specifically, Greene County request approval of the GUCbs requested IBT Certificate for the following
reasons:
1. The IBT would allow Greene County to replace the water supply capacity being lost by the Central
Coastal Plain Capacity Use Area requirements.
2. Based upon 2009 statistics hm the NC Dept. Of Commerce, Greene County is one of the forty
most distressed counties within NC, thus receiving a Tier 1 designation. Greene County has a
population of 21,205 (2008 projection by Office of State Budget Management) and is solely
dependent on agriculture. Greene County has only three incorporated towns, Snow Hill (Pop
1,618)' Walstonburg (Pop. 23 1) and Hookerton (Pop 485). The annual median household income
for Greene County is $32,074 as compared to the Me average of $39,184 (2000 census data).
Twenty percent of the people in Greene County are classified as "Poverty". Greene County must
have an economically feasible solution for water supply. The proposed purchase of water from
GUC is the most economically and technically feasiblesolution available.
229 Kingold Blvd., Suite D Snow Hill, rW: 28580 (252) 747-3446 FAX (252) 747-3884
www.~.g~e.nc. us
The miaion of Gene County Government is lo sm and improve the lives ofall dIlrem &pm&ing highqwliW, cast-ewve m.cer in an qm,
profesdonal and ethbl mb4vtwnent
Appendix 7
50
A267
.-
6 Commissioners
Bennie Heath - Chairman
Jack Edmondson - Vice Chairman
Denny Garner
Jeny Jones
James T. Shackleford, Jr.
County Manager
Don Davenport
Finance Ofiicer
Shawna Wooten
A PlaceTo Grow-The Way To Live.
3. The unhnded mandate by the State reducing our dependency on groundwater by 25% in 2008,
50% in 2013 and 75% in 2018, places Greene County under an extreme hardship. Every
consideration by the Environmental Management Commission is requested to allow us to
implement the least cost alternative solution, which is the proposed GUC alternative.
4. The purchase of water from GUC, is for water currently permitted for withdrawal fiom the Tar
River. No additional Tar River withdrawal permits by GUC are to be requested or needed to meet
the obligations of GUC to supply water to Gmne County. The contractual agreement between
GUC and Greene County is baed upon a ninety percent (90Y0) avaiMility factor. The contract
gives GUC the right to intmpt or curtail the supply of water to Greene County up to ten percent
(1 0%) of the time, or up to thirty-six (36) days per year. This arrangement allows GUC to curtail
water to Greene County on days of peak demand during which time Gwene County will utilize
their remaining 25% well capstcity to meet their demand. Udcr this agreement GUC will not
need to increase its withdrawal permitting capacity from the Tar River now or in the future as
related to selling water to Greene County.
5. Other alternative water supplies for Greene County are significantly more expensive. Failure of
GUC to obtain an IBT certificate will result in extreme financial hardship for the residents of
Greene County.
Greene County strongly supports the issuance of an IBT Certificate to GUC in accordance with their
petition. We encourage the Environmental Management Commission to support GUC's request and to
approve the granting of the D3T Certificate.
Bennie Heath
Chairman
Greene County Board of Commissioners
229 Kingold Blvd., Suite D Snow Hill, NC 28580 (252) 747-3446 FAX (252) 747-3884
www. co.greene.nc. us
?he m~iision of Gene Ciwnty Eovemment is to serve and improve the lives of all cit~zens by prowdng h@h-qualitVI cost-ef7kfive semtes in an openI
pm~onal and ehwl environment
Appendix 7
51
A268
Enpinem Planners Land Survqim
ORPORATEOFFICE I - -0- ~DmORO 0mcE L (252) 753-2139 Fax (252) 113-7220 (919) 736-7630. Fax (919) 735-7351
E-mail: mai@mcdrvid-inc.com E-mail: rnaigold@mcdsvid-inc.com
3714 N. Main Strcn- P.O. Draw 49 109 E. \Valnut Street P.O. Box 1776
FumviPt, NC 27828 &lckboro, NC 27533
December 3,2009
Toya Ogallo
Division of Water Resources
DENR
16 1 1 Mail Service Center
Lalcigh, NC 27699- 16 1 1
r
I Cubject: Letter of Support
GUC Request For IBT Certificate -1 & ar River Basin to Neuse River Bas
1 Dear Ms. Ogalfo:
On behalfof the Town of Farrnvi!lc and Grctne County, I write this letter in support for the Greenvilk
Utilities Commission'r Petition for an LBT CeM~cate.
Afier many years of investigation and negotiation for an alternative water supply, Greenville Utijities
Commission, Greene County and the Town of Farmville contracted for the transfer ofwater from Greenville
Utilities Commission. The most economically, technically feasible alternative with the lest impact on the
citizens of Farmville and Greene County was to obtain their water supply from Greenville Utilities
Commission. In order to comply with the state Central Capacity Plain Capacity Use regulations timetable,
both Greene County and Farrnville were required to begin the construction of the alternative water supply
delivery system immediately. Greene County and Famville have expended a large sum of money to date
to implement the delivery system of water from Greenville to Greene County and Farmville, all in an effort
to coinply with the 2002 Central Coastal Plain Capacity Use Area law deadlines of 2008,2013 and 2018.
-Tho project is nearing completion and ~ched~lcd to be activated in Jrrne, 2010. % The proposed interbasin transfer will not result in significant direct or indirect environmental impacts.
Failure by GUC to obtain an IBT Transfer Certificate will result in extreme hardship on the citizens ol! -a
Greenc County and the Town of Farmville.
Request favorable consideration by the Environmental Management Commission in granting the
Greenville Utilities Commission's request for an IBT Certificate permitting the delivery of water from
Greenville Utilities Commission to Greene County and the Town of Farmville (Tar River basin to Neuse 1
River ~asine P --
. . *.. Please advise this office of tbe Environmental Management Commission's meeting date, time and
&&da related to addressing of this issue.
-
DtOSAVLOP I
Fm-GC Ph IA - GUC IBT Support ~0InbnkIItJ From Enginsa-006.wpd
Appendix 7
52
A269
Thank you for your consideration of this matter.
- Sincaely.
McDavid Associates, Inc.
Albert V. Lewis, Jr.
Fmville Dffce
cc: Don Davenport
County ~akger ~~ecnth6
: Richard N. Hicks
Town Manager
Town of Fanville
DmSAVUl9 2
Fm-CC Ph I A - GUC ll3T Sueporr Cmmcntl f mm Englnt~rUbb.wpd
Appendix 7
53
A270
Oaallo. Tova
From:
Sent:
To:
Cc:
Subject:
' Randy Emory [EMORYRD@guc.com]
Friday, January 15, 201 0 4: 13 PM
Ogallo, Toya
Tony Cannon; Ron Elks; Randy Emory; Barrett Lasater; Steve Porter; Mary Sadler
GUC IBT Request Comments
Attachments: Toya Ogallo - lnterbasin Transfer Request letter.pdf
=pJ *'*
Toya Ogallo -
Interbasin Trans ...
Toya, please find attached Greenville Utilities comment submittal on our IBT
request.
Please acknowledge that you have received this message. Thanks.
Randall Emory, P.E.
Director of Water Resources
Greenville Utilities Commission
Greenville, N.C.
(252) 551-1554
emoryr@guc.com
Appendix 7
54
A271
Greenville
Utilities
January 15,201 0
Ms. Toya Ogallo
Water Resources Engineer, lnterbasin Transfers
Division of Water Resources
Department of Environment and Natural Resources
161 1 Mail Service Center
Raleigh, NC 27699-161 1
RE: lnterbasin Transfer Request
Greenville Utilities Commission
Dear Ms. Ogallo:
The Greenville Utilities Commission (GUC) is submitting this letter in support of our
lnterbasin Transfer (IBT) request. The lnterbasin Transfer will allow us to provide
long-term regional solutions to the water supply challenges our communities face in
eastern North Carolina. Our long-range planning has positioned us to have the
capability to provide water service to the neighboring communities of Farmville,
Winterville and Greene County, as well as other systems. Our neighbors have been
severely impacted by the Central Coastal Plain Capacity Use Area (CCPCUA) Rule,
which requires them to reduce their groundwater withdrawal by 75 percent in 2018.
The CCPCUA Rule impacts fifteen counties in eastern North Carolina, including Pitt
County.
'The IBT Management Strategy was developed in 2007 as a significant component
of the Environmental Assessment (EA). The IBT Management Strategy is a
balanced, managed approach to the transfer of finished water to our neighboring
communities. The Management Strategy takes into account the use of banked
water, the sale of finished water during off-peak periods, and the reduction of
groundwater supply due to the CCPCUA Rule. The IBT Management Strategy was
constructed to allow GUC and neighboring communities the greatest flexibility in the
purchase of water as well as the curtailment of service during peak water demand
or low flow in the Tar River.
l't I\,\ 1\47 - The second significant component of the EA was the development of the hydrologic
(irk,\ I~S.III,., s( ' analysis of flow conditions in the Tar River. The hydrologic modeling effort used
! empirical flow data from WSGS gauging stations that spanned a 76 year period of
1: record. The hydrologic analysis considered carefully the General Statute provision
,,:I\,.:,,. ., :Ill
Appendix 7
55
A272
Ms. Toya Ogallo
January 15,2010
Page 2
that all withdrawals and transfers in the source basin not be impacted to the degree
existing uses would be impaired (at the time of the 18T petition). To meet these
requirements, fourteen modeling scenarios were developed: six modeling scenarios
addressed the hydrologic effects upstream of GUC's raw water intake, and eight
modeling scenarios addressed the hydrologic effects of the proposed transfer
downstream of the GUC Wastewater Treatment Plant (WWTP). The scenarios
included current and future (2030) water withdrawal conditions for no IBT, the
average day IBT, the maximum day IBT, and a hypothetical scenario where twice
the proposed transfer was effectively removed from the Tar River.
The City of Rocky Mount's operating rules were considered and are reflected in the
hydrologic analysis. The analysis was based on actual flows at Tarboro, which
reflect approximately 40 years of conditions prior to the existence of the Rocky
Mount reservoir and 36 years of data since reservoir operations. In addition, the
analysis considered allowed modifications to the Rocky Mount's Drought
Management Plan in 1993,1999,2002, and 2007.
The results of the hydrologic analysis were presented relative to the flow duration
curves developed for the Tar River. The impact of each scenario was compared
against river flows as low as 80 percent of the 7Q10 (87.2 cfs). The worst-case
modeling (twice the proposed IBT amount) scenario revealed a 0.8 percent impact
in 2030 compared to the 2030 scenario without an lnterbasin transfer. For
comparison, the maximum IBT scenario resulted in a 0.5 percent impact in 2030
compared to the 2030 scenario without an lnterbasin transfer. The EA concluded
that the hydrologic analysis calculations demonstrated that the requested IBT
amount will have a negligible impact on the Tar River.
Even though the hydrologic modeling results demonstrated negligible impact on the
Tar River, the tidal influence at our intake provides another opportunity to
ameliorate the effect of low flow. The tidal influence results in a reverse flow
direction during low flow periods. This phenomenon creates a reservoir effect that
helps maintain water over our intake pipes. GUC is in a unique position whereby
we have two opportunities to withdraw water from the river where most other water
treatment plants have only one opportunity. This tidal effect phenomenon is part of
the reason why we feel confident that we can reliably provide water to neighboring
communities who require regional solutions to solve critical water supply needs.
Appendix 7
56
A273
Ms. Toya Ogallo
January 15,2010
Page 3
The EA critically evaluated the current and future water uses in the Tar River basin
under the current hydrologic conditions. Furthermore, the proposed IBT was
developed such that GUC has the flexibility to curtail water during peak demand and
fully utilize the groundwater resource (in the form of banked water) to the extent
practicable. In effect, we have already placed operating conditions on ourselves to
manage this proposed IBT in the best interest of our customers, our neighbors, and
the environment. We strongly feel that the worst-case modeling scenario
(effectively twice the proposed lnterbasin transfer) fully addresses the ultimate
impact to the Tar River as a result of this proposed transfer.
GUC is not requesting an increase in total water withdrawal or an increase in water
treatment plant capacity as a result of the proposed transfer. Rather, our long-
range water supply planning effort includes the use of an innovative technology,
aquifer storage and recovery (ASR), which will offset future maximum day water
demand. The ASR system, the first in North Carolina, will be operational this spring
and we are confident that this technology, coupled with our water conservation
initiatives, will allow us to manage our water resources even more effectively.
We have implemented a regional water supply strategy that utilizes our unique
geographical advantages. Our conjunctive use approach to water supply planning
has positioned us to be a regional water provider. Our mission is to protect water
resources and provide regional water supply solutions to our customers and to our
neighbors in critical need. We sincerely hope that our regional approach may serve
as a model for neighboring watersheds faced with similar water supply concerns.
Sincerely,
Ronald D. Elks
General ManagerKEO
cc: Randall Emory, P.E., GUC Director of Water Resources
Barrett Lasater, GUC WR Plants Manager
Steve Porter, P.E. GUC WR Systems Engineer
Mary Sadler, P.E. Hazen and Sawyer
Appendix 7
57
A274
Attachment C
Notice of Public Hearings
A275
Attachment C
Notice of Public Hearings
Atttachment C- Page 1
A276
Attachment C
Notice of Public Hearings
Atttachment C- Page 2
A277
Attachment C
Notice of Public Hearings
Atttachment C- Page 3
A278
Attachment C
Notice of Public Hearings
Atttachment C- Page 4
A279
Attachment C
Notice of Public Hearings
Atttachment C- Page 5
A280
Attachment C
Notice of Public Hearings
Atttachment C- Page 6
A281
Attachment C
Notice of Public Hearings
Atttachment C- Page 7
A282
Attachment C
Notice of Public Hearings
Atttachment C- Page 8
A283
Attachment C
Notice of Public Hearings
Atttachment C- Page 9
A284
Attachment C
Notice of Public Hearings
Atttachment C- Page 10
A285
Attachment D
(1) Central Coastal Plain Capacity Use Area Rules 15A NCAC 2E .0500
Attachment D- Page 1
A286
APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
1
TITLE 15A - DEPARTMENT OF ENVIRONMENT1
AND NATURAL RESOURCES23
CHAPTER 2 - ENVIRONMENTAL MANAGEMENT45
SUBCHAPTER 2E - WATER USE REGISTRATION AND ALLOCATION67
SECTION .0100 - AUTHORITY89
.0102 PURPOSE1011
History Note: Authority G.S. 143-215.12; 143-215.14;12
Eff. February 1, 1976;13
Repealed Eff. August 1, 2002.1415
.0103 SCOPE1617
History Note: Authority G.S. 143-215.14;18
Eff. February 1, 1976;19
Repealed Eff. August 1, 2002.2021
.0106 DEFINITIONS22
As used herein, unless the context otherwise requires:23
(1) "Director" means the Director of the Division of Water Resources.24
(2) "Division" means the Division of Water Resources.2526
History Note: Authority G.S. 87-87; 143-215.14; 143-215.21;27
Eff. March 1, 1985;28
Amended Eff. August 1, 2002.2930
.0107 DELEGATION31
(a) The Director is delegated the authority to grant, modify, revoke or deny permits under G.S. 143-215.15 and G.S.32
143-215.16.33
(b) The Director may delegate any permitting function given by the rules of this Subchapter.34
(c) The Director is delegated the authority to assess civil penalties and request the Attorney General to institute civil35
actions under G.S. 143-215.17.36
(d) The Director is delegated the authority to process applications and collect fees for registration of water37
withdrawals and transfers under G.S. 143-215.22H and G.S. 143- 215.3(a)(1b).38
(e) The Director may delegate any water withdrawal or transfer registration processing functions given by the rules39
of this Subchapter.4041
History Note: Filed as a Temporary Amendment Eff. October 14, 1991 for a period of 180 Days to Expire on April42
11, 1992;43
Authority G.S. 143-215.3(a)(1); 143-215.3(a)(4);44
Eff. March 1, 1985;45
Amended Eff. August 1, 2002; September 1, 1994; April 1, 1992.4647
SECTION .0200 - CAPACITY USE AREA NO. 14849
.0201 DECLARATION AND DELINEATION OF50
CAPACITY USE AREA NO. 15152
History Note: Authority G.S. 143-215.13;53
Eff. February 1, 1976;54
Repealed Eff. August 1, 2002.5556
.0202 PERSONS WITHDRAWING GROUNDWATER57
IN CAPACITY USE AREAS5859
Attachment D- Page 2
A287
APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
2
History Note: Authority G.S. 143-215.14; 143-215.15;1
Eff. February 1, 1976;2
Amended Eff. March 1, 1985;3
Repealed Eff. August 1, 2002.45
.0205 ACTIVITIES67
History Note: Authority G.S. 143-215.14; 143-215.20;8
Eff. February 1, 1976;9
Repealed Eff. August 1, 2002.1011
SECTION .0500 - CENTRAL COASTAL PLAIN CAPACITY USE AREA1213
.0501 DECLARATION AND DELINEATION OF CENTRAL COASTAL PLAIN CAPACITY USE AREA14
The area encompassed by the following 15 North Carolina counties and adjoining creeks, streams, and rivers is15
hereby declared and delineated as the Central Coastal Plain Capacity Use Area: Beaufort, Carteret, Craven, Duplin,16
Edgecombe, Greene, Jones, Lenoir, Martin, Onslow, Pamlico, Pitt, Washington, Wayne and Wilson. The17
Environmental Management Commission finds that the use of ground water requires coordination and limited18
regulation in this delineated area for protection of the public interest. The intent of this Section is to protect the long19
term productivity of aquifers within the designated area and to allow the use of ground water for beneficial uses at rates20
which do not exceed the recharge rate of the aquifers within the designated area.2122
History Note: Authority G.S. 143-215.13;23
Eff. August 1, 2002.2425
.0502 WITHDRAWAL PERMITS26
(a) Existing ground water withdrawal permits issued in Capacity Use Area No. 1 (15A NCAC 2E .0200) within the27
Central Coastal Plain Capacity Use Area are reissued under Section .0500 of this Subchapter and are valid until the28
expiration date specified in each permit. Water use permits are no longer required for withdrawals in Hyde and Tyrrell29
Counties as of the effective date of this Rule. Permits are not required for surface water use under Section .0500 of this30
Subchapter in the Central Coastal Plain Capacity Use Area as delineated in Rule .0501 of this Section.31
(b) No person shall withdraw ground water after the effective date of this Rule in excess of 100,000 gallons per day32
by a well, group of wells operated as a system, or sump for any purpose unless such person shall first obtain a water use33
permit from the Director. Existing withdrawals of ground water as of the effective date of this Rule and proposed34
withdrawals previously approved for funding appropriated pursuant to the “Clean Water and Natural Gas Critical Needs35
Bond Act of 1998” or other local, state or federally funded projects as of the effective date of this Rule shall be allowed36
to proceed with construction or to continue to operate under interim status until a permit has been issued or denied by37
the Director, provided that persons withdrawing in excess of 100,000 gallons per day by a well, group of wells operated38
as a system, or sump comply with the following requirements:39
(1) Persons conducting withdrawals in the Capacity Use Area that require a permit shall submit a permit40
application to the Division of Water Resources within 180 days of the effective date of this Rule.41
(2) Persons who have submitted applications shall provide any additional information requested by the Division42
of Water Resources for processing of the permit application within 30 days of the receipt of that request.43
(3) Persons conducting withdrawals in the Capacity Use Area that require a permit shall submit water level and44
water use data on a form supplied by the Division four times a year, within 30 days of the end of March, June,45
September, and December until a permit has been issued or denied by the Division of Water Resources.46
(c) Ground water withdrawals shall be governed by the following standards:47
(1) Adverse impacts of ground water withdrawals shall be avoided or minimized. Adverse impacts include, but48
are not limited to:49
(A) dewatering of aquifers;50
(B) encroachment of salt water;51
(C) land subsidence or sinkhole development;52
(D) declines in aquifer water levels that indicate that aggregate water use exceeds the aquifer replenishment53
rate.54
(2) Adverse impacts on other water users from ground water withdrawals shall be corrected or minimized55
through efficient use of water and development of sustainable water sources.56
(3) In determining the importance and necessity of a proposed withdrawal the efficiency of water use and57
implementation of conservation measures shall be considered.58
Attachment D- Page 3
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Environmental Management Commission May 17, 2001
3
(d) An application for a water use permit must be submitted on a form approved by the Director to the North1
Carolina Division of Water Resources. The application shall describe the purpose or purposes for which water shall be2
used, shall set forth the method and location of withdrawals, shall justify the quantities needed, and shall document3
water conservation measures to be used by the applicant to ensure efficient use of water and avoidance of waste.4
Withdrawal permit applications shall include the following information:5
(1) Location by latitude and longitude of all wells to be used for withdrawal of water.6
(2) Specifications for design and construction of existing and proposed production and monitoring wells7
including:8
(A) Well diameter;9
(B) Total depth of the well;10
(C) Depths of all open hole or screened intervals that will yield water to the well;11
(D) Depth of pump intake(s);12
(E) Size, capacity and type of pump;13
(F) Depth to top of gravel pack;14
(G) Depth measurements shall be within accuracy limits of plus or minus 0.10 feet and referenced to a15
known land surface elevation.16
Exceptions may be made where specific items of information are not critical, as determined by the Director,17
to manage the ground water resource.18
(3) Withdrawal permit applications for use of ground water from the Cretaceous aquifer system shall include19
plans to reduce water use from these aquifers as specified in Rule .0503 of this Section. Withdrawal rates20
from the Cretaceous aquifer system that exceed the approved base rate may be permitted during Phase I of21
Rule .0503 of this Section if the applicant can demonstrate to the Director’s satisfaction a need for the greater22
amount. Cretaceous aquifer system wells shall be identified using the specifications in Rule .0502(d)(1) and23
.0502(d)(2) of this Section and the hydrogeological framework.24
(4) Withdrawal permit applications for dewatering of mines, pits or quarries shall include a dewatering or25
depressurization plan that includes:26
(A) the current withdrawal rate or estimates of the proposed withdrawal rate;27
(B) the location, design and specifications of any sumps, drains or other withdrawal sources including28
wells and trenches;29
(C) the lateral extent and depth of the zone(s) to be dewatered or depressurized;30
(D) a monitoring plan that provides data to delineate the nature and extent of dewatering or31
depressurization;32
(E) certification of all engineering plans and hydrogeological analyses prepared to meet these requirements33
consistent with professional licensing board statutes and rules governing such activities.34
Exceptions may be made where specific items of information are not critical, as determined by the Director,35
to manage the ground water resource.36
(5) Conservation Measures. The applicant shall provide information on existing conservation measures and37
conservation measures to be implemented during the permit period as follows:38
(A) Public water supply systems shall develop and implement a feasible water conservation plan39
incorporating, at a minimum, the following components. Each component shall be described,40
including a timetable for implementing each component that does not already exist.41
(i) Adoption of a water conservation-based rate structure, such as: flat rates, increasing block rates,42
seasonal rates, or quantity-based surcharges.43
(ii) Implementation of a water loss reduction program if unaccounted for water is greater than 1544
percent of the total amount produced, as documented annually using a detailed water audit.45
Water loss reduction programs shall consist of annual water audits, in-field leak detection, and46
leak repair.47
(iii) Adoption of a water conservation ordinance for irrigation, including such measures as: time-of-48
day and day-of-week restrictions on lawn and ornamental irrigation, automatic irrigation system49
shut-off devices or other appropriate measures.50
(iv) Implementation of a retrofit program that makes available indoor water conservation devices to51
customers (such as showerheads, toilet flappers, and faucet aerators).52
(v) Implementation of a public education program (such as water bill inserts, school and civic53
presentations, water treatment plant tours, public services announcements, or other appropriate54
measures).55
(vi) Evaluation of the feasibility of water reuse as a means of conservation, where applicable.56
(B) Users of water for commercial purposes, other than irrigation of crops and forestry stock, shall develop57
and implement a water conservation plan as follows:58
Attachment D- Page 4
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APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
4
(i) an audit of water use by type of activity (for example, process make-up water, non-contact1
cooling water) including existing and potential conservation and reuse measures for each type2
of water use;3
(ii) an implementation schedule for feasible measures identified in the above item for conservation4
and reuse of water at the facility.5
(C) Users of water for irrigation of crops and forestry stock shall provide the following information:6
(i) total acreage with irrigation available;7
(ii) types of crops that may be irrigated;8
(iii) method of irrigation (for example, wells that supply water to canals, ditches or central pivot9
systems or any other irrigation method using ground water);10
(iv) a statement that the applicant uses conservation practice standards for irrigation as defined by11
the Natural Resources Conservation Service.12
(6) If an applicant intends to operate an aquifer storage and recovery program (ASR), the applicant shall provide13
information on the storage zone, including the depth interval of the storage zone, lateral extent of the14
projected storage area, construction details of wells used for injection and withdrawal of water, and15
performance of the ASR program.16
(e) The Director shall issue, modify, revoke, or deny each permit as set forth in G.S. 143-215.15. Permittees may17
apply for permit modifications. Any application submitted by a permittee shall be subject to the public notice and18
comment requirements of G.S. 143-215.15(d).19
(f) Permit duration shall be set by the Director as described in G.S. 143-215.16(a). Permit transferability is20
established in G.S. 143-215.16(b).21
(g) Persons holding a permit shall submit signed water usage and water level reports to the Director not later than 3022
days after the end of each permit reporting period as specified in the permit. Monitoring report requirements may23
include:24
(1) Amounts of daily withdrawal from each well.25
(2) Pumping and static water levels for each supply well as measured with a steel or electric tape, or an26
alternative method as specified in the permit, at time intervals specified in the permit.27
(3) Static water levels in observation wells at time intervals specified in the permit.28
(4) Annual sampling by applicants located in the salt water encroachment zone and chloride concentration29
analysis by a State certified laboratory.30
(5) Any other information the Director determines to be pertinent and necessary to the evaluation of the effects of31
withdrawals.32
(h) Water use permit holders shall not add new wells without prior approval from the Director.33
(i) The Director may require permit holders to construct observation wells to observe water level and water quality34
conditions before and after water withdrawals begin if there is a demonstrated need for aquifer monitoring to assess the35
impact of the withdrawal on the aquifer.36
(j) For all water uses other than dewatering of mines, pits or quarries, withdrawals shall be permitted only from wells37
that are constructed such that the pump intake or intakes are at a shallower depth than the top of the uppermost confined38
aquifer that yields water to the well. Confined aquifer tops are established in the hydrogeological framework. Where39
wells in existence as of the effective date of this Rule are not in compliance with the requirements of this provision, the40
permit shall include a compliance schedule for retrofitting or replacement of non-compliant wells. Withdrawals from41
unconfined aquifers shall not lower the water table by an amount large enough to decrease the effective thickness of the42
unconfined aquifer by more than 50 percent.43
(k) For withdrawals to dewater mines, pits or quarries, the permit shall delimit the extent of the area and depths of44
the aquifer(s) to be dewatered or depressurized. Maximum withdrawal rates and the permissible extent of dewatering or45
depressurization shall be determined by the Director using data provided by the applicant, data related to permits under46
G.S. 74-47, and other publicly available information. Withdrawal rates that do not cause adverse impacts, as defined in47
Rule .0502(c) of this Section, shall be approved.48
(l) Withdrawals of water that cause changes in water quality such that the available uses of the resource are adversely49
affected shall not be permitted. For example, withdrawals shall not be permitted that result in migration of ground50
water that contains more than 250 milligrams per liter chloride into pumping wells that contain chloride at51
concentrations below 250 milligrams per liter.52
(m) General permits may be developed by the Division and issued by the Director for categories of withdrawal that53
involve the same or substantially similar operations, have similar withdrawal characteristics, require the same54
limitations or operating conditions, and require similar monitoring.55
(n) Permitted water users may withdraw and sell or transfer water to other users provided that their permitted56
withdrawal limits are not exceeded.57
(o) A permitted water user may sell or transfer to other users a portion of his permitted withdrawal. To carry out58
such a transfer, the original permittee must request a permit modification to reduce his permitted withdrawal and the59
Attachment D- Page 5
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APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
5
proposed recipient of the transfer must apply for a new or amended withdrawal permit under Section .0500 of this1
Subchapter.2
(p) Where an applicant or a permit holder can demonstrate that compliance with water withdrawal limits established3
under Section .0500 of this Subchapter is not possible because of construction schedules, requirements of other laws, or4
other reasons beyond the control of the applicant or permit holder, and where the applicant or permit holder has made5
good faith efforts to conserve water and to plan the development of other water sources, the Director may issue a6
temporary permit with an alternative schedule to attain compliance with provisions of Section .0500 of this Subchapter,7
as authorized in G.S. 143-215.15(c)(ii).89
History Note: Authority G.S. 143-215.14; 143-215.15; 143-215.16;10
Eff. August 1, 2002.1112
.0503 PRESCRIBED WATER USE REDUCTIONS IN CRETACEOUS AQUIFER ZONES13
Cretaceous aquifer water use shall be reduced in prescribed areas over a 16 year period, starting from approved base14
rates on the effective date of this Rule. The Cretaceous aquifer system zones and the three phases of water use15
reductions are listed as follows:16
(1) Cretaceous aquifer system zones are regions established in the fresh water portion of the Cretaceous aquifer17
system that delimit zones of salt water encroachment, dewatering and declining water levels. These zones are18
designated on the paper and digital map entitled "Central Coastal Plain Capacity Use Area Cretaceous19
Aquifer Zones" (CCPCUA) on file in the Office of the Secretary of State one week prior to the effective date20
of these Rules.21
(2) The reductions specified in Rule .0503 of this Section do not apply to intermittent users.22
(3) If a permittee implements an aquifer storage and recovery program (ASR), reduction requirements shall be23
based on the total net withdrawals. The reductions specified in Rule .0503 of this Section do not apply if the24
volume of water injected into the aquifer is greater than the withdrawal volume. If the withdrawal volume is25
greater than the injected volume, reductions specified in Rule .0503 of this Section apply to the difference26
between the withdrawal volume and the injected volume.27
(4) The reductions specified in Rule .0503 of this Section shall not reduce permitted water use rates below28
100,001 gallons per day.29
(5) Phase definitions:30
(a) Phase I: The six year period extending into the future from the effective date of this Rule.31
(b) Phase II: The five year period extending into the future from six years after the effective date of this32
Rule to 11 years after the effective date of this Rule.33
(c) Phase III: The five year period extending into the future from 11 years after the effective date of this34
Rule to 16 years after the effective date of this Rule.35
(6) Phase reductions:36
(a) Phase I:37
(i) At the end of the Phase I, permittees who are located in the dewatering zone shall reduce annual38
water use from Cretaceous aquifers by 25% from their approved base rate.39
(ii) At the end of the Phase I, permittees who are located in the salt water encroachment zone shall40
reduce annual water use from Cretaceous aquifers by 25% from their approved base rate.41
(iii) At the end of the Phase I, permittees who are located in the declining water level zone shall42
reduce annual water use from Cretaceous aquifers by 10% from their approved base rate.43
(b) Phase II:44
(i) At the end of the Phase II, permittees who are located in the dewatering zone shall reduce annual45
water use from Cretaceous aquifers by 50% from their approved base rate.46
(ii) At the end of the Phase II, permittees who are located in the salt water encroachment zone shall47
reduce annual water use from Cretaceous aquifers by 50% from their approved base rate.48
(iii) At the end of the Phase II, permittees who are located in the declining water level zone shall49
reduce annual water use from Cretaceous aquifers by 20% from their approved base rate.50
(c) Phase III:51
(i) At the end of the Phase III, permittees who are located in the dewatering zone shall reduce52
annual water use from Cretaceous aquifers by 75% from their approved base rate.53
(ii) At the end of the Phase III, permittees who are located in the salt water encroachment zone shall54
reduce annual water use from Cretaceous aquifers by 75% from their approved base rate.55
(iii) At the end of the Phase III, permittees who are located in the declining water level zone shall56
reduce annual water use from Cretaceous aquifers by 30% from their approved base rate.57
Attachment D- Page 6
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APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
6
(7) The CCPCUA Cretaceous Aquifer Zones map shall be updated, if necessary, in the sixth, eleventh, and1
sixteenth years following the effective date of this Rule to account for aquifer water level responses to phased2
withdrawal reductions. The map update shall be based on the following conditions:3
(a) Rate of decline in water levels in the aquifers;4
(b) Rate of increase in water levels in the aquifers;5
(c) Stabilization of water levels in the aquifers;6
(d) Chloride concentrations in the aquifers.7
This aquifer information shall be analyzed on a regional scale and used to develop updated assessments of aquifer8
conditions in the Central Coastal Plain Capacity Use Area. The Environmental Management Commission (EMC) may9
adjust the aquifer zones and the water use reduction percentages for each zone based on the assessment of conditions.10
The EMC shall adopt the updated map and reduction percentage changes after public hearing.11
(8) The reductions specified in Rule .0503 of this Section do not apply to wells exclusively screened or open to12
the Peedee aquifer.13
(9) An applicant may submit documentation supporting the exemption of a well located in the Declining Water14
Level Zone from the withdrawal reductions specified in Rule .0503 of this Section. This documentation must15
include a record of monthly static water levels from that well over at least a three-year period, ending with the16
month when the request for exemption is submitted. The Director may exempt a well from reductions if the17
water level history shows no pattern of decline during this three-year period. A well previously exempted18
from the withdrawal reductions shall become subject to the reductions if water levels begin to show a pattern19
of decline.2021
History Note: Authority G.S. 143-215.15;22
Eff. August 1, 2002.2324
.0504 REQUIREMENTS FOR ENTRY AND INSPECTION25
(a) The Division may enter and inspect property in order to evaluate wells, pumps, metering equipment or other26
withdrawal or measurement devices and records of water withdrawals and water levels, if:27
(1) Persons conduct an activity that the Division believes requires the use of water at quantities that subject the28
person to regulation under these Rules;29
(2) A permittee or applicant has not provided data or information on use of water and wells and other water30
withdrawal facilities as required by these Rules; or31
(3) Water levels and chloride concentrations at the person’s facility, or at nearby facilities or monitoring stations,32
indicate that aquifers may be damaged by overpumping or salt water encroachment, or other adverse affects33
that may be attributed to withdrawal by the person.34
(b) All information submitted to fulfill the requirements of these Rules, or to obtain a permit under these Rules, or35
obtained by inspection under these Rules, shall be treated as Confidential Business Information, if requested by the36
applicant, and found to be such by the Division. Reports defined in Rule .0502(g) of this Section are not considered37
Confidential Business Information.3839
History Note: Authority G.S. 143-215.19;40
Eff. August 1, 2002.4142
.0505 ACCEPTABLE WITHDRAWAL METHODS THAT DO NOT REQUIRE A PERMIT43
(a) As of the effective date of this Rule, any person who is not subject to Rule .0502 of this Section and withdraws44
more than 10,000 gallons per day from surface or ground water in the Central Coastal Plain Capacity Use Area, shall45
register such withdrawals on a form supplied by the Division and comply with the following provisions:46
(1) Construct new wells such that the pump intake or intakes are above the top of the uppermost confined aquifer47
that yields water to the well. Confined aquifer tops are established in the hydrogeological framework.48
(2) Report surface and ground water use to the Division of Water Resources on an annual basis on a form49
supplied by the Division.50
(3) Withdraw water in a manner that does not damage the aquifer or cause salt water encroachment or other51
adverse impacts.52
(b) These requirements do not apply to withdrawals to supply an individual domestic dwelling.53
(c) Agricultural water users may either register water use with the Division of Water Resources as provided in this54
Rule or provide the information to the North Carolina Department of Agriculture and Consumer Services.5556
History Note: Authority G.S. 143-215.14; 143-355(k);57
Eff. August 1, 2002.5859
Attachment D- Page 7
A292
APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
7
.0506 CENTRAL COASTAL PLAIN CAPACITY USE AREA STATUS REPORT1
Within two years of the effective date of this Rule, and at five year intervals thereafter, the Division of Water Resources2
shall publish a status report on the Central Coastal Plain Capacity Use Area. The report shall include the following:3
(1) Compilations of water use data,4
(2) Evaluations of surface and ground water resources,5
(3) Updated information about the hydrogeologic framework in the Central Coastal Plain Capacity Use Area,6
(4) A summary of alternative water sources and water management techniques that may be feasible by7
generalized geographic location, and8
(5) A status report on actions by water users to develop new water sources and to increase water use efficiency.910
History Note: Authority G.S. 143-215.14;11
Eff. August 1, 2002.1213
.0507 DEFINITIONS14
The following is a list of definitions for terms found in Section .0500 of this Subchapter.15
(1) Approved base rate: The larger of a person’s January 1, 1997 through December 31, 1997 or August 1, 199916
through July 31, 2000 annual water use rate from the Cretaceous aquifer system, or an adjusted water use rate17
determined through negotiation with the Division using documentation provided by the applicant of:18
(a) water use reductions made since January 1, 1992,19
(b) use of wells for which funding has been approved or for which plans have been approved by the20
Division of Environmental Health by the effective date of this Rule,21
(c) the portion of a plant nursery operation using low volume micro-irrigation, or22
(d) other relevant information.23
(2) Aquifer: Water-bearing earth materials that are capable of yielding water in usable quantities to a well or24
spring.25
(3) Aquifer storage and recovery program (ASR): Controlled injection of water into an aquifer with the intent to26
store water in the aquifer for subsequent withdrawal and use.27
(4) Confining unit: A geologic formation that does not yield economically practical quantities of water to wells28
or springs. Confining units separate aquifers and slow the movement of ground water.29
(5) Cretaceous aquifer system: A system of aquifers in the North Carolina coastal plain that is comprised of30
water-bearing earth materials deposited during the Cretaceous period of geologic time. The extent of the31
Cretaceous Aquifer System is defined in the hydrogeological framework and includes the Peedee, Black32
Creek, Upper Cape Fear and Lower Cape Fear aquifers.33
(6) Dewatering: Dewatering occurs when aquifer water levels are depressed below the top of a confined aquifer34
or water table declines adversely affect the resource.35
(7) Flat rates: Unit price remains the same regardless of usage within customer class.36
(8) Fresh water: Water containing chloride concentrations equal to or less than 250 milligrams per liter.37
(9) Gravel pack: Sand or gravel sized material inside the well bore and outside the well screen and casing.38
(10) Ground water: Water in pore spaces or void spaces of subsurface sediments or consolidated rock.39
(11) Hydrogeological framework: A three-dimensional representation of aquifers and confining units that is stored40
in Division data bases and may be adjusted by applicant supplied information.41
(12) Increasing block rates: Unit price increases with additional usage.42
(13) Intermittent users: Persons who withdraw ground water less than 60 days per calendar year; or who withdraw43
less than 15 million gallons of ground water in a calendar year; or aquaculture operations licensed under the44
authority of G.S. 106-761 using water for the initial filling of ponds or refilling of ponds no more frequently45
than every five years.46
(14) Observation well: A non-pumping well screened in a particular aquifer where water levels can be measured47
and water samples can be obtained.48
(15) Pumping water level: The depth to ground water in a pumping well as measured from a known land surface49
elevation. Measurements shall be made four hours after pumping begins. Measurements shall be within50
accuracy limits of plus or minus 0.10 feet.51
(16) Quantity based surcharges: Surcharges billed with usage over a certain determined quantity.52
(17) Salt water: Water containing chloride concentrations in excess of 250 milligrams per liter.53
(18) Salt water encroachment: The lateral or vertical migration of salt water toward areas occupied by fresh water.54
This may occur in aquifers due to natural or man-made causes.55
(19) Seasonal rates: Unit prices change according to the season.56
(20) Static water level: The depth to ground water in a non-pumping well as measured from a known land surface57
elevation. Measurements shall be made after pumping has ceased for 12 hours. Measurements shall be58
within accuracy limits of plus or minus 0.10 feet.59
Attachment D- Page 8
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APPROVED RULES
North Carolina Division of Water Resources Central Coastal Plain Capacity Use Area Rules
Environmental Management Commission May 17, 2001
8
(21) Unaccounted for water: The difference between the total water entering the system (produced and purchased)1
and the total metered or otherwise accounted for water usage.2
(22) Water table: The water level in an unconfined aquifer.34
History Note: Authority G.S. 143-215.14;5
Eff. August 1, 2002.6
Attachment D- Page 9
A294
Attachment D
(2) Session Law 2006‐246 Section 9(c) Post‐Construction Practices
Attachment D- Page 10
A295
Senate Bill 1566* Session Law 2006-246 Page 13
propose using any existing State or local program that relates to the minimum measures
to meet, either in whole or in part, the requirements of the minimum measures.
SECTION 8. Exclusions from Post-Construction Practices. – The
post-construction practices required by Section 9 of this act shall not apply to any of the
following:
(1) Development in an area where the requirements of Section 9 of this act
are applicable that is conducted pursuant to one of the following
authorizations, provided that the authorization was obtained prior to
the effective date of the post-construction stormwater control
requirements in the area and the authorization is valid, unexpired,
unrevoked, and not otherwise terminated:
a. A building permit pursuant to G.S. 153A-357 or
G.S. 160A-417.
b. A site-specific development plan as defined by
G.S. 153A-344.1(b)(5) and G.S. 160A-385.1(b)(5).
c. A phased development plan approved pursuant to
G.S. 153A-344.1 for a project located in the unincorporated
area of a county that is subject to the requirements of Section 9
of this act, if the Commission is responsible for implementation
of the requirements of Section 9 of this act, that shows:
1. For the initial or first phase of development, the type and
intensity of use for a specific parcel or parcels, including
at a minimum, the boundaries of the project and a
subdivision plan that has been approved pursuant to
G.S. 153A-330 through G.S. 153A-335.
2. For any subsequent phase of development, sufficient
detail so that implementation of the requirements of
Section 9 of this act to that phase of development would
require a material change in that phase of the plan.
d. A vested right to the development under G.S. 153A-344(b),
153A-344.1, 160A-385(b), or 160A-385.1 issued by a local
government that implements Section 9 of this act.
e. A vested right to the development pursuant to common law.
(2) Redevelopment.
SECTION 9. Post-Construction Practices. –
(a) For post-construction requirements, a program will be deemed compliant for
the areas where it is implementing any of the following programs:
(1) Water Supply Watershed I (WS-I) – 15A NCAC 2B.0212.
(2) Water Supply Watershed II (WS-II) – 15A NCAC 2B.0214.
(3) Water Supply Watershed III (WS-III) – 15A NCAC 2B.0215.
(4) Water Supply Watershed IV (WS-IV) – 15A NCAC 2B.0216.
(5) Freshwater High Quality Waters (HQW) – 15A NCAC 2H.1006.
(6) Freshwater Outstanding Resource Waters (ORW) – 15A NCAC
2H.1007.
Attachment D- Page 11
A296
Page 14 Session Law 2006-246 Senate Bill 1566*
(7) The Neuse River Basin Nutrient Sensitive Waters (NSW) Management
Strategy – 15A NCAC 2B.0235.
(8) The Tar-Pamlico River Basin Nutrient Sensitive (NSW) Management
Strategy – 15A NCAC 2B.0258.
(9) The Randleman Lake Water Supply Watershed Nutrient Management
Strategy – 15A NCAC 2B.0251.
(b) In order to fulfill the post-construction minimum measure program
requirement, a permittee, delegated program, or regulated entity may use the
Department's model ordinance, design its own post-construction practices based on the
Department's guidance on scientific and engineering standards for best management
practices (BMPs), incorporate the post-construction model practices described in this
act, or develop its own comprehensive watershed plan that is determined by the
Department to meet the post-construction stormwater management measure required by
40 Code of Federal Regulations § 122.34(b)(5) (1 July 2003 Edition).
(c) Permittees, delegated programs, and regulated entities must require
stormwater controls for a project that disturbs one acre or more of land, including a
project that disturbs less than one acre of land that is part of a larger common plan of
development or sale. The stormwater controls shall be appropriate to the project's level
of density as follows:
(1) Post-construction model practices for low-density projects. – A project
that is located within one-half mile of and draining to Shellfish
Resource Waters is a low-density project if it contains no more than
twelve percent (12%) built-upon area. A project that is not located
within one-half mile of Shellfish Resource Waters is a low-density
project if it contains no more than twenty-four percent (24%)
built-upon area or no more than two dwelling units per acre.
Low-density projects must use vegetated conveyances to the maximum
extent practicable to transport stormwater runoff from the project.
On-site stormwater treatment devices such as infiltration areas,
bioretention areas, and level spreaders may also be used as added
controls for stormwater runoff. A project with an overall density at or
below the low-density thresholds, but containing areas with a density
greater than the overall project density, may be considered low density
as long as the project meets or exceeds the post-construction model
practices for low-density projects and locates the higher density in
upland areas and away from surface waters and drainageways to the
maximum extent practicable.
(2) Post-construction model practices for high-density projects. – A
project that is located within one-half mile of and draining to Shellfish
Resource Waters is a high-density project if it contains more than
twelve percent (12%) built-upon area. A project that is not located
within one-half mile of Shellfish Resource Waters is a high-density
project if it contains more than twenty-four percent (24%) built-upon
area or more than two dwelling units per acre. High-density projects
Attachment D- Page 12
A297
Senate Bill 1566* Session Law 2006-246 Page 15
must use structural stormwater management systems that will control
and treat runoff from the first one inch of rain unless the project is in a
county that is subject to the Coastal Area Management Act of 1974, in
which case the project must use structural stormwater management
systems that will control and treat runoff from the first one and
one-half inches of rain. In addition, projects that are located within
one-half mile and draining to Shellfish Resource Waters must control
and treat the difference in the stormwater runoff from the
predevelopment and post-development conditions for the one-year, 24-
hour storm. The structural stormwater management system must also
meet the following design standards:
a. Draw down the treatment volume no faster than 48 hours, but
no slower than 120 hours.
b. Discharge the storage volume at a rate equal to or less than the
predevelopment discharge rate for the one-year, 24-hour storm.
c. Remove an eighty-five percent (85%) average annual amount of
Total Suspended Solids.
d. Meet the General Engineering Design Criteria set out in 15A
NCAC 02H .1008(c).
e. Wet detention ponds designed in accordance with the
requirements of subsection (h) of this section may be used for
projects draining to Class SA waters.
(d) Permittees, delegated programs, and regulated entities must require
built-upon areas to be located at least 30 feet landward of all perennial and intermittent
surface waters. For purposes of this section, a surface water shall be present if the
feature is shown on either the most recent version of the soil survey map prepared by
the Natural Resources Conservation Service of the United States Department of
Agriculture or the most recent version of the 1:24,000 scale (7.5 minute) quadrangle
topographic maps prepared by the United States Geologic Survey (USGS). Relief from
this requirement may be allowed when surface waters are not present in accordance
with the provisions of 15A NCAC 02B .0233(3)(a). In addition, an exception to this
requirement may be pursued in accordance with subsection (a) of Section 11 of this act.
(e) Permittees, delegated programs, and regulated entities must implement or
require a fecal coliform reduction program that controls, to the maximum extent
practicable, the sources of fecal coliform. At a minimum, the program shall include the
development and implementation of an oversight program to ensure proper operation
and maintenance of on-site wastewater treatment systems for domestic wastewater. For
municipalities, this program may be coordinated with local county health departments.
(f) Permittees, delegated programs, and regulated entities must impose or require
recorded deed restrictions and protective covenants that ensure development activities
will maintain the project consistent with approved plans.
(g) Permittees, delegated programs, and regulated entities must implement or
require an operation and maintenance plan that ensures the adequate long-term
operation of the structural BMPs required by the program. The operation and
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Attachment D
(3) Regulation of Surface Water Transfers §142‐215.22I
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as required by this subsection.
(e) Any person who is required to register a water transfer or withdrawal under this section and fails
to do so shall pay, in addition to the registration fee required under G.S. 143- 215.3(a)(1a) and G.S.
143-215.3(a)(1b), a late registration fee of five dollars ($5.00) per day for each day the registration is late
up to a maximum of five hundred dollars ($500.00). A person who is required to update a registration
under this section and fails to do so shall pay a fee of five dollars ($5.00) per day for each day the
updated information is late up to a maximum of five hundred dollars ($500.00). A late registration fee
shall not be charged to a farmer who submits a registration that pertains to farming operations. (1991, c.
712, s. 1; 1993, c. 344, s. 1; c. 553, s. 81; 1998-168, s. 3.)
'''' 143-215.22I. Regulation of surface water transfers.
(a) No person, without first securing a certificate from the Commission, may:
(1) Initiate a transfer of 2,000,000 gallons of water or more per day from one river basin to
another.
(2) Increase the amount of an existing transfer of water from one river basin to another by
twenty-five percent (25%) or more above the average daily amount transferred during the year ending
July 1, 1993, if the total transfer including the increase is 2,000,000 gallons or more per day.
(3) Increase an existing transfer of water from one river basin to another above the amount
approved by the Commission in a certificate issued under G.S. 162A-7 prior to July 1, 1993.
(b) Notwithstanding the provisions of subsection (a) of this section, a certificate shall not be required
to transfer water from one river basin to another up to the full capacity of a facility to transfer water from
one basin to another if the facility was existing or under construction on July 1, 1993.
(c) An applicant for a certificate shall petition the Commission for the certificate. The petition shall
be in writing and shall include the following:
(1) A description of the facilities to be used to transfer the water, including the location and
capacity of water intakes, pumps, pipelines, and other facilities.
(2) A description of the proposed uses of the water to be transferred.
(3) The water conservation measures to be used by the applicant to assure efficient use of the
water and avoidance of waste.
(4) Any other information deemed necessary by the Commission for review of the proposed
water transfer.
(d) Upon receipt of the petition, the Commission shall hold a public hearing on the proposed transfer
after giving at least 30 days' written notice of the hearing as follows:
(1) By publishing notice in the North Carolina Register.
(2) By publishing notice in a newspaper of general circulation in the area of the river basin
downstream from the point of withdrawal.
(3) By giving notice by first-class mail to each of the following:
a. A person who has registered under this Part a water withdrawal or transfer from the same
river basin where the water for the proposed transfer would be withdrawn.
b. A person who secured a certificate under this Part for a water transfer from the same river
basin where the water for the proposed transfer would be withdrawn.
c. A person holding a National Pollutant Discharge Elimination System (NPDES)
wastewater discharge permit exceeding 100,000 gallons per day for a discharge located downstream
from the proposed withdrawal point of the proposed transfer.
d. The board of county commissioners of each county that is located entirely or partially
within the river basin that is the source of the proposed transfer.
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e. The governing body of any public water supply system that withdraws water downstream
from the withdrawal point of the proposed transfer.
(e) The notice of the public hearing shall include a nontechnical description of the applicant's request
and a conspicuous statement in bold type as to the effects of the water transfer on the source and
receiving river basins. The notice shall further indicate the procedure to be followed by anyone wishing
to submit comments on the proposed water transfer.
(f) In determining whether a certificate may be issued for the transfer, the Commission shall
specifically consider each of the following items and state in writing its findings of fact with regard to
each item:
(1) The necessity, reasonableness, and beneficial effects of the amount of surface water
proposed to be transferred and its proposed uses.
(2) The present and reasonably foreseeable future detrimental effects on the source river basin,
including present and future effects on public, industrial, and agricultural water supply needs,
wastewater assimilation, water quality, fish and wildlife habitat, hydroelectric power generation,
navigation, and recreation. Local water supply plans that affect the source major river basin shall be used
to evaluate the projected future municipal water needs in the source major river basin.
(2a) The cumulative effect on the source major river basin of any water transfer or consumptive
water use that, at the time the Commission considers the application for a certificate is occurring, is
authorized under this section, or is projected in any local water supply plan that has been submitted to
the Department in accordance with G.S. 143-355(l).
(3) The detrimental effects on the receiving river basin, including effects on water quality,
wastewater assimilation, fish and wildlife habitat, navigation, recreation, and flooding.
(4) Reasonable alternatives to the proposed transfer, including their probable costs, and
environmental impacts.
(5) If applicable to the proposed project, the applicant's present and proposed use of
impoundment storage capacity to store water during high-flow periods for use during low-flow periods
and the applicant's right of withdrawal under G.S. 143-215.44 through G.S. 143-215.50.
(6) If the water to be withdrawn or transferred is stored in a multipurpose reservoir constructed
by the United States Army Corps of Engineers, the purposes and water storage allocations established
for the reservoir at the time the reservoir was authorized by the Congress of the United States.
(7) Any other facts and circumstances that are reasonably necessary to carry out the purposes of
this Part.
(f1) An environmental assessment as defined by G.S. 113A- 9(1) shall be prepared for any petition
for a certificate under this section. The determination of whether an environmental impact statement
shall also be required shall be made in accordance with the provisions of Article 1 of Chapter 113A of
the General Statutes. The applicant who petitions the Commission for a certificate under this section
shall pay the cost of special studies necessary to comply with Article 1 of Chapter 113A of the General
Statutes.
(g) A certificate shall be granted for a water transfer if the applicant establishes and the Commission
concludes by a preponderance of the evidence based upon the findings of fact made under subsection (f)
of this section that: (i) the benefits of the proposed transfer outweigh the detriments of the proposed
transfer, and (ii) the detriments have been or will be mitigated to a reasonable degree. The conditions
necessary to ensure that the detriments are and continue to be mitigated to a reasonable degree shall be
attached to the certificate in accordance with subsection (h) of this section.
(h) The Commission may grant the certificate in whole or in part, or deny the certificate. The
Commission may also grant a certificate with any conditions attached that the Commission believes are
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necessary to achieve the purposes of this Part. The conditions may include mitigation measures proposed
to minimize any detrimental effects of the proposed transfer and measures to protect the availability of
water in the source river basin during a drought or other emergency. The certificate shall include a
drought management plan that specifies how the transfer shall be managed to protect the source river
basin during drought conditions. The certificate shall indicate the maximum amount of water that may
be transferred. No person shall transfer an amount of water that exceeds the amount in the certificate.
(i) In cases where an applicant requests approval to increase a transfer that existed on July 1, 1993,
the Commission shall have authority to approve or disapprove only the amount of the increase. If the
Commission approves the increase, however, the certificate shall be issued for the amount of the existing
transfer plus the requested increase. Certificates for transfers approved by the Commission under G.S.
162A-7 shall remain in effect as approved by the Commission and shall have the same effect as a
certificate issued under this Part.
(j) In the case of water supply problems caused by drought, a pollution incident, temporary failure of
a water plant, or any other temporary condition in which the public health requires a transfer of water,
the Secretary of the Department of Environment and Natural Resources may grant approval for a
temporary transfer. Prior to approving a temporary transfer, the Secretary of the Department of
Environment and Natural Resources shall consult with those parties listed in G.S. 143-215.22I(d)(3) that
are likely to be affected by the proposed transfer. However, the Secretary of the Department of
Environment and Natural Resources shall not be required to satisfy the public notice requirements of this
section or make written findings of fact and conclusions in approving a temporary transfer under this
subsection. If the Secretary of the Department of Environment and Natural Resources approves a
temporary transfer under this subsection, the Secretary shall specify conditions to protect other water
users. A temporary transfer shall not exceed six months in duration, but the approval may be renewed for
a period of six months by the Secretary of the Department of Environment and Natural Resources based
on demonstrated need as set forth in this subsection.
(k) The substantive restrictions and conditions upon surface water transfers authorized in this section
may be imposed pursuant to any federal law that permits the State to certify, restrict, or condition any
new or continuing transfers or related activities licensed, relicensed, or otherwise authorized by the
federal government.
(l) When any transfer for which a certificate was issued under this section equals eighty percent
(80%) of the maximum amount authorized in the certificate, the applicant shall submit to the
Department a detailed plan that specifies how the applicant intends to address future foreseeable water
needs. If the applicant is required to have a local water supply plan, then this plan shall be an amendment
to the local water supply plan required by G.S. 143-355(l). When the transfer equals ninety percent
(90%) of the maximum amount authorized in the certificate, the applicant shall begin implementation of
the plan submitted to the Department.
(m) It is the public policy of the State to maintain, protect, and enhance water quality within North
Carolina. Further, it is the public policy of the State that the cumulative impact of transfers from a source
river basin shall not result in a violation of the antidegradation policy set out in 40 Code of Federal
Regulations ' 131.12 (l July 1997 Edition) and the statewide antidegradation policy adopted pursuant
thereto. (1993, c. 348, s. 1; 1997-443, ss. 11A.119(a), 15.48(c); 1997-524, s. 1; 1998-168, s. 4.)
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Attachment D
(4) North Carolina Administrative Code NCAC 15A NCAC 02E .0401
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SECTION .0400 - REGULATION OF SURFACE WATER TRANSFERS
15A NCAC 02E .0401 APPLICABILITY
(a) Pursuant to G.S. 143-215.22G(3), the amount of a transfer shall be determined by the amount of water moved from the
source basin to the receiving basin, less the amount of the water returned to the source basin.
(b) Pursuant to G.S. 143-215.22G(3)(a) and 143-215.22G(3)(b), and notwithstanding the definition of basin in G.S. 143-
215.22G(1), the following are not transfers:
(1) The discharge point is situated upstream of the withdrawal point such that the water discharged will
naturally flow past the withdrawal point.
(2) The discharge point is situated downstream of the withdrawal point such that water flowing past the
withdrawal point will naturally flow past the discharge point.
(c) The withdrawal of surface water from one river basin by one person and the purchase of all or any part of this water by
another party, resulting in a discharge to another river basin, shall be considered a transfer. The person owning the pipe or
other conveyance that carries the water across the basin boundary shall be responsible for obtaining a certificate from the
Commission. Another person involved in the transfer may assume responsibility for obtaining the certificate, subject to
approval by the Division of Water Resources.
(d) Under G.S. 143-215.22I(b), a certificate is not required to transfer water from one river basin to another up to the full
capacity of a facility to transfer water from one basin to another if the facility was existing or under construction on July 1,
1993. The full capacity of a facility to transfer water shall be determined as the capacity of the combined system of
withdrawal, treatment, transmission, and discharge of water, limited by the element of this system with the least capacity as
existing or under construction on July 1, 1993.
History Note: Authority G.S. 143-215.22G; 143-215.22I; 143B-282(a)(2);
Eff. September 1, 1994.
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