HomeMy WebLinkAboutNC0027626_Fact Sheet_20230606Page 1 of 7
FACT SHEET
RENEWAL – NPDES PERMIT
NC0027626 – WPCS Grade WW-1 [wetlands]
(Reclassified from Grade WW-2 for this renewal)
Table 1 - Basic Information for Permit Renewal
Permit Writer/Date Joe R. Corporon, P.G. 06Jun2023
Permit Number NC0027626
Permittee North Carolina Department of Public Safety
Facility Name / WWTP Class Caledonia Correctional Institution WWTP /
WPCS WW-1 [downgraded from Grade WPCS -2]
Facility Contacts
Nainesh (Nash) Patel, PE, PEM
Environmental Engineering Manager
919-324-1283 [nainesh.patel@dac.nc.gov]
Basin Name/Sub-basin number Roanoke River / 03-02-08
Receiving Stream Roanoke River [Index 23-(26)]
Stream Classification / IWC Class C / Winter 7Q10 = 1,000 cfs
Summer 7Q10 = 1,500 cfs
Does permit need Daily Max NH3 limits? Not needed. Monitor and Report only.
Does permit need TRC limits/language? No. Existing
Does permit have WET testing? Yes – TGE6C Acute @ 90% effluent concentration
Does permit have Special Conditions? Yes. Electronic Reporting
Does permit have instream monitoring? No.
Is the stream impaired (on 303(d) list)? No
Any obvious compliance concerns?
No. During last permit cycle, fecal coliform Daily
Max geometric mean exceeded on 12Jul2022 and
08Jun2021; one (1) NOV for frequency violation for
MBAS. Request to discontinue Fecal monitoring
denied.
Any permit mods since last permit? No
Current expiration date March 31, 2023
New expiration date March 31, 2028
Comments received on Draft Permit?
Facility / Treatment System Narrative: North Carolina Stated Department of Public Safety
(NCDPS) houses medium and minimum-security offenders. Caledonia Correctional Institution
WWTP is used to treat wastewater generated by the Prison facility. Adding to domestic
wastewater, the prison WWTP receives wastewater from a cannery operated by the prison.
The WWTP consists of Primary
lagoons, wetlands treatment, and a
Chlorination/ Dechlorination
disinfection system.
Wetlands System – Effluent consists of
50% domestic and 50% industrial.
Page 2 of 7
Receiving Stream – Discharge from said treatment works at the location specified on the attached
map into the Roanoke River, HUC Code: 030101070204, Stream Index 23-(26), classified C
waters in the Roanoke River Basin. Roanoke Streamflow: 7Q10w =1,000 cfs; 7Q10s = 1,500 cfs;
7Q10 Ave = 6,000 cfs [BIMS]; effluent discharge IWC = 0.052%.
Compliance History / Data Review - Jan2021- Jun2023
PARAM VIOL DATE UNITS LIMIT CALC
VALUE VIOL TYPE ACTION UPDATED BY
04/30/2023 Late/Missing GW-59 None bimsprod.cron
04/02/2023 Late/Missing GW-59 None bimsprod.cron
03/02/2023 Late/Missing GW-59 None bimsprod.cron
01/30/2023 Late/Missing GW-59 None bimsprod.cron
12/31/2022 Late/Missing GW-59 None bimsprod.cron
11/30/2022 Late/Missing GW-59 None bimsprod.cron
10/31/2022 Late/Missing GW-59 None bimsprod.cron
09/30/2022 Late/Missing GW-59 None bimsprod.cron
08/30/2022 Late/Missing GW-59 None bimsprod.cron
07/31/2022 Late/Missing GW-59 None bimsprod.cron
Fecal 07/12/2022 #/100ml 400 816 Daily Maximum Proceed to NOV cheng.zhang
06/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
05/31/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
04/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
04/02/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
03/02/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
01/30/2022 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
12/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
11/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
10/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
09/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
MBAS 09/30/2021 mg/l Frequency Violation Proceed to NOV alys.hannum
08/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
07/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
06/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
Fecal 06/08/2021 #/100ml 400 921 Daily Maximum Proceed to NOV alys.hannum
05/31/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
04/30/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
04/02/2021 Late/Missing GW-59 No Action, Invalid Permit alys.hannum
Because Fecal coliform detected in the past year, Permittee’s request to discontinue Fecal monitoring is
denied.
Summary of Changes and Rationale for Renewal
1. As requested by the Permittee for renewal, down-graded the current wetlands WWTP from Class
WPCS-2 to WPCS Class11, as approved on 27Apr2023 by NC Operator Certification Unit
(OCU) and Raleigh Regional Office (RRO).
2. Instream Monitoring for Total Nitrogen (TN) and Total Phosphorus (TP) – relaxed monitoring
from Monthly to Quarterly.
3. Lastly, we resorted your effluent monitoring table by Measurement Frequency, most-
often to least-often sampled [see Table A. (1.)].
Page 3 of 7
PROPOSED SCHEDULE FOR PERMIT ISSUANCE
Draft Permit to Public Notice: June 13, 2023
[Tentative] Permit Scheduled to Issue: July 24, 2023
[Tentative] Effective date September 1, 2023
NPDES DIVISION CONTACT
If you have questions about any of the above information, or on the attached permit, please email
Joe R. Corporon, P.G. [joe.corporon@ncdenr.gov].
NAME: DATE: 06JUN2023
NPDES Implementation of Instream Dissolved Metals Standards – Freshwater
Standards
The NC 2007-2015 Water Quality Standard (WQS) Triennial Review was approved by the NC
Environmental Management Commission (EMC) on November 13, 2014. The US EPA subsequently
approved the WQS revisions on April 6, 2016, with some exceptions. Therefore, metal limits in draft
permits out to public notice after April 6, 2016 must be calculated to protect the new standards - as
approved.
Table 2. NC Dissolved Metals Water Quality Standards/Aquatic Life Protection
Parameter Acute FW, µg/l
(Dissolved)
Chronic FW, µg/l
(Dissolved)
Acute SW, µg/l
(Dissolved)
Chronic SW, µg/l
(Dissolved)
Arsenic 340 150 69 36
Beryllium 65 6.5 --- ---
Cadmium Calculation Calculation 40 8.8
Chromium III Calculation Calculation --- ---
Chromium VI 16 11 1100 50
Copper Calculation Calculation 4.8 3.1
Lead Calculation Calculation 210 8.1
Nickel Calculation Calculation 74 8.2
Silver Calculation 0.06 1.9 0.1
Zinc Calculation Calculation 90 81
Table 2 Notes:
1. FW= Freshwater, SW= Saltwater
2. Calculation = Hardness dependent standard
Page 4 of 7
3. Only the aquatic life standards listed above are expressed in dissolved form. Aquatic life
standards for Mercury and selenium are still expressed as Total Recoverable Metals due to
bioaccumulative concerns (as are all human health standards for all metals). It is still necessary
to evaluate total recoverable aquatic life and human health standards listed in 15A NCAC
2B.0200 (e.g., arsenic at 10 µg/l for human health protection; cyanide at 5 µg/L and fluoride at
1.8 mg/L for aquatic life protection).
Table 3. Dissolved Freshwater Standards for Hardness-Dependent Metals
The Water Effects Ratio (WER) is equal to one unless determined otherwise under 15A NCAC
02B .0211 Subparagraph (11)(d)
Metal NC Dissolved Standard, µg/l
Cadmium, Acute WER*{1.136672-[ln hardness](0.041838)} ∙ e^{0.9151 [ln hardness]-
3.1485}
Cadmium, Acute Trout
waters
WER*{1.136672-[ln hardness](0.041838)} ∙ e^{0.9151[ln hardness]-
3.6236}
Cadmium, Chronic WER*{1.101672-[ln hardness](0.041838)} ∙ e^{0.7998[ln hardness]-
4.4451}
Chromium III, Acute WER*0.316 ∙ e^{0.8190[ln hardness]+3.7256}
Chromium III, Chronic WER*0.860 ∙ e^{0.8190[ln hardness]+0.6848}
Copper, Acute WER*0.960 ∙ e^{0.9422[ln hardness]-1.700}
Copper, Chronic WER*0.960 ∙ e^{0.8545[ln hardness]-1.702}
Lead, Acute WER*{1.46203-[ln hardness](0.145712)} ∙ e^{1.273[ln hardness]-1.460}
Lead, Chronic WER*{1.46203-[ln hardness](0.145712)} ∙ e^{1.273[ln hardness]-4.705}
Nickel, Acute WER*0.998 ∙ e^{0.8460[ln hardness]+2.255}
Nickel, Chronic WER*0.997 ∙ e^{0.8460[ln hardness]+0.0584}
Silver, Acute WER*0.85 ∙ e^{1.72[ln hardness]-6.59}
Silver, Chronic Not applicable
Zinc, Acute WER*0.978 ∙ e^{0.8473[ln hardness]+0.884}
Zinc, Chronic WER*0.986 ∙ e^{0.8473[ln hardness]+0.884}
General Information on the Reasonable Potential Analysis (RPA)
The RPA process itself did not change as the result of the new metals standards. However, application of
the dissolved and hardness-dependent standards requires additional consideration in order to establish the
numeric standard for each metal of concern of each individual discharge.
The hardness-based standards require some knowledge of the effluent and instream (upstream) hardness
and so must be calculated case-by-case for each discharge.
Metals limits must be expressed as ‘total recoverable’ metals in accordance with 40 CFR 122.45(c). The
discharge-specific standards must be converted to the equivalent total values for use in the RPA
calculations. We will generally rely on default translator values developed for each metal (more on that
below), but it is also possible to consider case-specific translators developed in accordance with
established methodology.
Page 5 of 7
RPA Permitting Guidance/WQBELs for Hardness-Dependent Metals - Freshwater
The RPA is designed to predict the maximum likely effluent concentrations for each metal of concern,
based on recent effluent data, and calculate the allowable effluent concentrations, based on applicable
standards and the critical low-flow values for the receiving stream.
If the maximum predicted value is greater than the maximum allowed value (chronic or acute), the
discharge has reasonable potential to exceed the standard, which warrants a permit limit in most cases. If
monitoring for a particular pollutant indicates that the pollutant is not present (i.e. consistently below
detection level), then the Division may remove the monitoring requirement in the reissued permit.
1. To perform a RPA on the Freshwater hardness-dependent metals the Permit Writer compiles the
following information:
• Critical low flow of the receiving stream, 7Q10 (the spreadsheet automatically calculates
the 1Q10 using the formula 1Q10 = 0.843 (s7Q10, cfs) 0.993
• Effluent hardness and upstream hardness, site-specific data is preferred
• Permitted flow
• Receiving stream classification
2. In order to establish the numeric standard for each hardness-dependent metal of concern and for
each individual discharge, the Permit Writer must first determine what effluent and instream
(upstream) hardness values to use in the equations.
The permit writer reviews DMR’s, Effluent Pollutant Scans, and Toxicity Test results for any
hardness data and contacts the Permittee to see if any additional data is available for instream
hardness values, upstream of the discharge.
If no hardness data is available, the permit writer may choose to do an initial evaluation using a
default hardness of 25 mg/L (CaCO3 or (Ca + Mg)). Minimum and maximum limits on the
hardness value used for water quality calculations are 25 mg/L and 400 mg/L, respectively.
If the use of a default hardness value results in a hardness-dependent metal showing reasonable
potential, the permit writer contacts the Permittee and requests 5 site-specific effluent and
upstream hardness samples over a period of one week. The RPA is rerun using the new data.
The overall hardness value used in the water quality calculations is calculated as follows:
Combined Hardness (chronic)
= (Permitted Flow, cfs *Avg. Effluent Hardness, mg/L) x (s7Q10, cfs *Avg. Upstream Hardness, mg/L)
(Permitted Flow, cfs + s7Q10, cfs)
The Combined Hardness for acute is the same but the calculation uses the 1Q10 flow.
3. The permit writer converts the numeric standard for each metal of concern to a total recoverable
metal, using the EPA Default Partition Coefficients (DPCs) or site-specific translators, if any
have been developed using federally approved methodology.
4. The numeric standard for each metal of concern is divided by the default partition coefficient (or
site-specific translator) to obtain a Total Recoverable Metal at ambient conditions.
In some cases, where an EPA default partition coefficient translator does not exist (ie. silver), the
dissolved numeric standard for each metal of concern is divided by the EPA conversion factor to
obtain a Total Recoverable Metal at ambient conditions. This method presumes that the metal is
dissolved to the same extent as it was during EPA’s criteria development for metals. For more
information on conversion factors see the June, 1996 EPA Translator Guidance Document.
Page 6 of 7
5. The RPA spreadsheet uses a mass balance equation to determine the total allowable concentration
(permit limits) for each pollutant using the following equation:
Ca = (s7Q10 + Qw) (Cwqs) – (s7Q10) (Cb)
Qw
Where: Ca = allowable effluent concentration (µg/L or mg/L)
Cwqs = NC Water Quality Standard or federal criteria (µg/L or mg/L)
Cb = background concentration: assume zero for all toxicants except NH3* (µg/L or mg/L)
Qw = permitted effluent flow (cfs, match s7Q10)
s7Q10 = summer low flow used to protect aquatic life from chronic toxicity and human
health through the consumption of water, fish, and shellfish from noncarcinogens (cfs)
* Discussions are on-going with EPA on how best to address background concentrations
Flows other than s7Q10 may be incorporated as applicable:
1Q10 = used in the equation to protect aquatic life from acute toxicity
QA = used in the equation to protect human health through the consumption of water,
fish, and shellfish from carcinogens
30Q2 = used in the equation to protect aesthetic quality
6. The permit writer enters the most recent 2-3 years of effluent data for each pollutant of concern.
Data entered must have been taken within four and one-half years prior to the date of the permit
application (40 CFR 122.21). The RPA spreadsheet estimates the 95th percentile upper
concentration of each pollutant. The Predicted Max concentrations are compared to the Total
allowable concentrations to determine if a permit limit is necessary. If the predicted max exceeds
the acute or chronic Total allowable concentrations, the discharge is considered to show
reasonable potential to violate the water quality standard, and a permit limit (Total allowable
concentration) is included in the permit in accordance with the U.S. EPA Technical Support
Document for Water Quality-Based Toxics Control published in 1991.
7. When appropriate, permit writers develop facility specific compliance schedules in accordance
with the EPA Headquarters Memo dated May 10, 2007 from James Hanlon to Alexis Strauss on
40 CFR 122.47 Compliance Schedule Requirements.
8. The Total Chromium NC WQS was removed and replaced with trivalent chromium and
hexavalent chromium Water Quality Standards. As a cost savings measure, total chromium data
results may be used as a conservative surrogate in cases where there are no analytical results
based on chromium III or VI. In these cases, the projected maximum concentration (95th %) for
total chromium will be compared against water quality standards for chromium III and chromium
VI.
9. Effluent hardness sampling and instream hardness sampling, upstream of the discharge, are
inserted into all permits with facilities monitoring for hardness-dependent metals to ensure the
accuracy of the permit limits and to build a more robust hardness dataset.
10. Hardness and flow values used in the Reasonable Potential Analysis for this permit included:
Table 4
Parameter Value Comments (Data Source)
Average Effluent Hardness (mg/L)
[Total as, CaCO3 or (Ca+Mg)] N/A No metals monitored
Average Upstream Hardness (mg/L)
[Total as, CaCO3 or (Ca+Mg)] N/A
7Q10 summer (cfs) 8.9 N/A
1Q10 (cfs) ~ N/A
Page 7 of 7
Permitted Flow (MGD) 0.500 N/A
ROY COOPER
STA1Fy" Governor
ihrik,.
r? 'y• MICHAEL S. REGAN
5j Secretaryieli,
LINDA CULPEPPER
00'"-'
Director
NORTH CAROLINA
Environmental Quality
February 6,2019
Mr.Kenneth G.Hart
Facility Engineering Specialist
North Carolina Department of Public Safety
4216 Mail Service Center
Raleigh,NC,27699-4216
Subject: Draft NPDES Permit NC0027626
Caledonia Correctional Institution WWTP
Halifax County
Grade II Biological WPCS
Dear Mr.Hart:
The Division has reviewed your request to renew the subject permit. Please review this draft carefully to ensure
your thorough understanding of the information,conditions,and requirements it contains.
The draft permit includes the following significant changes from the existing permit:
eDMR requirements have been added.
Regulatory citations have been added.
Facility Grade has been updated and added to the permit.
With this notification,the Division will solicit public comment on this draft permit by publishing a notice in
newspapers having circulation in the general Halifax County area,per EPA requirements.Please provide your
comments,if any,to me no later than 30 days after receiving this draft permit.
Following the 30-day public comment period,the Division will review all pertinent comments and take
appropriate action prior to issuing a final permit.If you have questions concerning the draft,please contact me at
919-707-3622, or via e-mail [Anjali.Orlando@ncdenr.gov].
Sincerely,
44446.7746....„
Anjali Orlando
Compliance&Expedited Permitting Unit
cc: NPDES Files
Raleigh Regional Office
State of North Carolina I Environmental Quality I Water Resources
1617 Mail Service Center I Raleigh,NC 27699-1617
919 807 6300 919-807-6389 FAX
hops://deq.nc.gov/about/divisions/water-resources/water-resources-permits/wastewater-branch/npdes-wastewater-permits
Permit NC0027626
STATE OF NORTH CAROLINA
DEPARTMENT OF ENVIRONMENTAL QUALITY
DIVISION OF WATER RESOURCES
PERMIT
TO DISCHARGE WASTEWATER UNDER THE
NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM
In compliance with the provisions of North Carolina General Statute 143-215.1,other lawful standards and
regulations promulgated and adopted by the North Carolina Environmental Management Commission,and the
Federal Water Pollution Control Act, as amended,
North Carolina Department of Correction
is hereby authorized to discharge wastewater from a facility located at the
Caledonia Correctional Institution WWTP
2787 Caledonia Drive
NE of Tillery
Halifax County
to receiving waters designated as the Roanoke River in the Roanoke River Basin
in accordance with efflueni limitations, monitoring requirements, and other conditions set forth in Parts I, II, III
and IV hereof.
This permit shall become effective
This permit and authorization to discharge shall expire at midnight on March 31,2023. _
Signed this day
Linda Culpepper
Director,Division of Water Resources
By Authority of the Environmental Management Commission
Page 1 of 6
Permit NC0027626
SUPPLEMENT TO PERMIT COVER SHEET
All previous NPDES Permits issued to this facility,whether for operation or discharge,are hereby superseded
and,as of this issuance,any previously issued permit describing this treatment facility or bearing this number is
no longer effective.Therefore,the exclusive authority to operate and discharge from this facility arises under the
permit conditions,requirements,terms,and provisions described herein.
The North Carolina Department of Correction is hereby authorized to:
1. Continue to operate an existing 0.500 MGD extended aeration wastewater treatment plant consisting of
the following treatment components:
Influent headwork's with coarse bar screen and fine rotary screens
Influent pump station
Wetlands treatment system
Chlorination/Dechlorination disinfection system
Magnetic flow meter
g
2. This facility is located at the Caledonia Correctional Institution,2787 Caledonia Drive,Tillery,NC,27887
in Halifax County.
3. Discharge from said treatment works at the location specified on the attached map into the Roanoke River,
classified C waters in the Roanoke River Basin.
Page 2 of 6
Permit NC0027626
Part I.
A. (1.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS
15A NCAC 02B .0400 et seq., 02B .0500 et seq.] Grade II Biological Water Pollution Control
System [15A NCAC 08G.0302]
During the period beginning on the effective date of this permit and lasting until expiration, the Permittee is
authorized to discharge from outfall 001. Such discharges shall be limited and monitored) by the Permittee as
specified below:
EFFLUENT - MONITORING REQUIREMENTS
CHARACTERISTICS
Monthly Daily Measurement
Sample Type Sample Location
Average Maximum Frequency
50050-Flow
0.500 MGD Continuous Recorder Influent or Effluent
50060-
2
Total Residual
28 µg/L Weekly Grab EffluentChlorine
00010-Temperature(°C) Weekly Grab Effluent
C0310-BOD,5-day(20°C)
30.0 mg/L 45.0 mg/L 2/Month Composite Effluent
C0530-Total Suspended
90.0 mg/L 135.0 mg/L 2/Month Composite EffluentSolids
C0610-NH3 as N
2/Month Composite Effluent
00556- Oil&Grease 30.0 mg/L 60.0 mglL 2/Month Grab Effluent
31616-Fecal Coliform
200/100 ml 400/100 ml 2/Month Grab
Effluent
geometric mean)
38260—Surfactants(MBAS) 2/Month Composite Effluent
00400-pH Between6.0- 9.0 s.u. 2/Month Grab Effluent
C0600-Total Nitrogen Monthly 'Composite Effluent
NO2+NO3+TKN)
C0665—Total Phosphorus Monthly Composite Effluent
TGE6C- Acute Toxicity3 Quarterly Composite Effluent
Footnotes:
1. The permittee shall begin submitting discharge monitoring reports electronically using the Division's eDMR
application system [see A. (4.)]
2. The Division shall consider all effluent TRC values reported below 50 ug/L to be in compliance with the
permit.However,the Permittee shall continue to record and submit all values reported by a North Carolina
certified laboratory(including field certified),even if these values fall below 50 ug/L.
3. Acute Toxicity(fathead minnow)Pass/Fail at 90% [See A. (3.)].
There shall be no discharge of floating solids or visible foam in other than trace amounts.
Page 3 of 6
Permit NC0027626
A. (3.) ACUTE TOXICITY PASS/FAIL PERMIT LIMIT(QRTRLY)
15A NCAC 02B.0200 et seq.]
The permittee shall conduct acute toxicity tests on a quarterly basis using protocols defined in the North
Carolina Procedure Document entitled"Pass/Fail Methodology for Determining Acute Toxicity in A Single
Effluent Concentration"(Revised-July 1992 or subsequent versions).The monitoring shall be performed as a
Fathead Minnow(Pimephales promelas)24-hour static test.The effluent concentration at which there may be at
no time significant acute mortality is 90% (defined as treatment two in the procedure document).Effluent
samples for self-monitoring purposes must be obtained during representative effluent discharge below all waste.
treatment.The tests will be performed during the months of January,April,July and October.
All toxicity testing results required as part of this permit condition will be entered on the Effluent Discharge
Monitoring Form(MR-1)for the month in which it was performed,using the parameter code TGE6C.
Additionally,DWQ Form AT-2(original)is to be sent to the following address:
Attention: NC DENR/DWQ/Environmental Sciences Section
1621 Mail Service Center
Raleigh,North Carolina,27699-1621
Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Section no later than 30
days after the end of the reporting period for which the report is made.
Test data shall be complete and accurate and include all supporting chemical/physical measurements performed
in association with the toxicity tests,as well as all dose/response data.Total residual chlorine of the effluent
toxicity sample must be measured and reported if chlorine is employed for disinfection of the waste stream.
Should there be no discharge of flow from the facility during a month in which toxicity monitoring is required,
the permittee will complete the information located at the top of the aquatic toxicity(AT)test form indicating
the facility name,permit number,pipe number, county,and the month/year of the report with the notation of
No Flow"in the comment area of the form. The report shall be submitted to the Environmental Sciences
Section at the address cited above.
Should any single quarterly monitoring indicate a failure,to meet specified limits,then monthly
monitoring will begin immediately until such time that a single test is passed.Upon passing,this monthly
test requirement will revert to quarterly in the months specified above.
Should the permittee fail to monitor during a month in which-toxicity monitoring is required,then monthly
monitoring will begin immediately until such time that a single test is passed.Upon passing,this monthly test
requirement will revert to quarterly in the months specified above.
Should any test data from either these monitoring requirements or tests performed by the North Carolina
Division of Water Quality indicate potential impacts to the receiving stream,this permit may be re-opened and
modified to include alternate monitoring requirements or limits.
If the Permittee monitors any pollutant more frequently than required by this permit,the results of such
monitoring shall be included in the calculation&reporting of the data submitted on the DMR&all AT Forms
submitted.
NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum control organism
survival and appropriate environmental controls, shall constitute an invalid test and will require immediate
follow-up testing to be completed no later than the last day of the month following the month of the initial
monitoring.
Page 4 of 6
Permit NC0027626
A. (4.) ELECTRONIC REPORTING OF DISCHARGE MONITORING REPORTS
NCGS 143-215.1 (b)]
Proposed federal regulations require electronic submittal of all discharge monitoring reports(DMRs)and
specify that,if a state does not establish a system to receive such submittals,then permittees must submit DMRs
electronically to the Environmental Protection Agency(EPA). The Division anticipates that these regulations
will be adopted and is beginning implementation in late 2013.
NOTE: This special condition supplements or supersedes the following sections within Part II of this permit
Standard Conditions for NPDES Permits):
Section B. (11.) Signatory Requirements
Section D. (2.)Reporting
Section D. (6.)Records Retention
Section E. (5.) Monitoring Reports
1. Reporting [Supersedes Section D. (2.) and Section E. (5.)(a)],
The permittee shall begin reporting discharge monitoring data electronically using the NC DWR's
Electronic Discharge Monitoring Report(eDMR)internet application.
Monitoring results obtained during the previous month(s)shall be summarized for each month and
submitted electronically using eDMR. The eDMR system allows permitted facilities to enter monitoring
data and submit DMRs electronically using the internet. Until such time that the state's eDMR application
is compliant with EPA's Cross-Media Electronic Reporting Regulation(CROMERR),permittees will be
required to submit all discharge monitoring data to the state electronically using eDMR and will be required
to complete the eDMR submission by printing, signing,and submitting one signed original and a copy of the
computer-printed eDMR to the following address:
NC DENR/Division of Water Resources/Information Processing Unit
ATTENTION: Central Files/eDMR
1617 Mail SerTrice Center
Raleigh,NC 27699-1617
If a permitteeis unable to use the eDMR system due to a demonstrated hardship or due to the facility being
physically-located in an area where less than 10 percent of the households have broadband access,then a
temporary waiver from the NPDES electronic reporting requirements may be granted and discharge
monitoring data may be submitted on paper DMR forms(MR 1, 1.1,2,3)or alternative forms approved by
the Director. Duplicate signed copies shall be submitted to the mailing address above.
Requests for temporary waivers from the NPDES electronic reporting requirements must be submitted in
writing to the Division for written approval at least sixty(60)days prior to the date the facility would be
required under this permit to begin using eDMR. Temporary waivers shall be valid for twelve(12)months
and shall thereupon expire. At such time,DMRs shall be submitted electronically to the Division unless the
permittee re-applies for and is granted a new temporary waiver by the Division.
Information on eDMR and application for a temporary waiver from the NPDES electronic reporting
requirements is found on the following web page:
http://portal.ncdenr.org/web/wq/admin/bog/ipu/edmr
Page 5 of 6
Permit NC0027626
Regardless of the submission method,the first DMR is due on the last day of the month following the
issuance of the permit or in the case of a new facility,on the last day of the month following the
commencement of discharge.
2. Signatory Requirements [Supplements Section B.(11.) (b) and supersedes Section B.(11.) (d)1
All eDMRs submitted to the permit issuing authority shall be signed by a person described in Part II,
Section B.(11.)(a) or by a duly authorized representative of that person as described in Part II, Section B.
11.)(b). A person,and not a position,must be delegated signatory authority for eDMR reporting purposes.
For eDMR submissions,the person signing and submitting the DMR must obtain an eDMR user account
and login credentials to access the eDMR system. For more information on North Carolina's eDMR
system,registering for eDMR and obtaining an eDMR user account,please visit the following web page:
http://portal.ncdenr.org/web/wq/admin/bog/ipu/edmr
Certification. Any person submitting an electronic DMR using the state's eDMR system shall make the
following certification [40 CFR 122.22]. NO OTHER STATEMENTS OF CERTIFICATION WILL BE
ACCEPTED:
I certify, under penalty of law, that this document and all attachments were prepared under my direction or
supervision in accordance with a system designed to assure that qualified personnel properly gather and
evaluate the information submitted. Based on my inquiry of the person or persons who manage the system,
or those persons directly responsible for gathering the information, the information submitted is, to the best
of my knowledge and belief true, accurate, and complete..1 am aware that there are significant penalties for
submitting false information, including the possibility offines and imprisonment for knowing violations."
3. Records Retention [Supplements Section D. (6.)1
The permittee shall retain records of all Discharge Monitoring Reports,including eDMR submissions.
These records or copies shall be maintained for a period of at least 3 years from the date of the report. This
period may be extended by request of the Director at any time [40 CFR 122.41].
Page 6 of 6
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N.C. Department of Correction
FacilityCaledoniaCorrectionalInstitutionWWTPAif OW
Latitude: 36° 18'51" N State Grid: Boones Crossroads Location
Longitude: 77°26'06" W Stream Class: C not to scale
Receiving Stream: Roanoke River Drainage Basin: Roanoke River Basin
Permitted Flow: 0.500 MGD Sub-Basin: 03-02-08
North
NPDES Permit No. NC0027626
1 V Halifax County