HomeMy WebLinkAboutNC0024970_Permit Modification_20010309NPDES DOCUHENT SCANNING COVER SHEET
NC0024970
McAlpine Creek WWTP
NPDES Permit:
Document Type:
Permit Issuance
Wasteload Allocation
Authorization to Construct (AtC)
(1Permit
Modification )
�+RrF _..yam_.. r.•i": V+• r
Complete File - Historical
Engineering Alternatives (EAA)
Correspondence
Owner Name Change
Meeting Notes
Instream Assessment (67b)
Speculative Limits
Environmental Assessment (EA)
Document Date:
March 9, 2001
Yids cocument its printed on reuse paper - ignore arty
content on the re-srerree side
StF to of North Carolina
Department of Environment
and Natural Resources
Division of Water Quality
Michael F. Easley, Governor
William G. Ross, Jr., Secretary
Kerr T. Stevens, Director
March 9, 2001
Mr. Barry M. Gullet
CMUD Administrative Division
5100 Brookshire Boulevard
Charlotte, North Carolina 28216
A7A
NC
NORTH CAROLIN
ENVIRONMENT AND
Subject: NPDES Permit Modific
Permit NC0024970
CMUD McAlpine Creek WWTP
Mecklenburg County
Dear Mr. Gullet:
On March 1, 2001, a final permit for the subject facility became effective. On March 6, 2001, you
requested some changes to the subject permit. These changes relate to issues discussed with the Division of
Water Quality (Division) on December 21, 2000. As a result, a compliance schedule has been granted for the
lindane limit and some changes have been made to the language of Special Condition A.(5.).
With respect to the lindane limit that becomes effective March 1, 2002; your facility may request a
modification to this permit to remove the limit after submitting twelve months of data indicating no detection
of that compound. The Division cannot presently establish a quantitation limit for lindane at your
laboratory. However, the Laboratory Services Section of the Division of Water Quality uses a quantitation
limit of 0.01 fig/L.
Please find enclosed the revised permit pages. The revised pages should be inserted into your permit.
The old pages may then be discarded. All other terms and conditions contained in the original permit remain
unchanged and in full effect. This permit modification is issued under the requirements of North Carolina
General Statutes 143-215.1 and the Memorandum of Agreement between North Carolina and the U. S.
Environmental Protection Agency.
If any parts, measurement frequencies or sampling requirements contained in this permit
modification are unacceptable to you, you have the right to an adjudicatory hearing upon written request
within thirty (30) days following receipt of this letter. This request must be a written petition conforming to
Chapter 150B of the North Carolina General Statutes, filed with the Office of Administrative Hearings (6714
Mail Service Center, Raleigh, North Carolina 27699-6714). Unless such demand is made, this decision shall be
final and binding.
If you have any questions concerning this permit modification, please contact Natalie Sierra at (919)
733-5083, extension 551.
cc: Mooresville Regional Office, Water Quality Section
NPDES Unit
Point Source Compliance and Enforcement
1617 Mail Service Center, Raleigh, North Carolina 27699-1617
An Equal Opportunity Affirmative Action Employer
Sincerely,
rr T. Stevens
Telephone (919) 733-5083 FAX (919) 733-0719
VISIT US ON THE INTERNET @ http://h2o.enr.state.nc.us/NPDES
Permit NC0024970
A. (1.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS - FINAL
During the period beginning on the effective date of this permit and lasting until February 28, 2002, the
Permittee is authorized to discharge from outfall 001. Such discharges shall be limited and monitored by the
Permittee as specified below:
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64.0 MGD
Continuous
Recording
1 or E
CBOD, 5-day (20°C)2
April 1- October 31
4.0 mg/L
6.0 mg/L
Daily
Composite
E,
CBOD, 5-day (20°C)2
November 1- March 31
8.0 mg/L
12.0 mg/L
.
Daily
Composite
E,
Total Suspended Residue2
15.0 mg/L
22.5 mg/L
Daily
Composite
E, I
NH3 as N (April 1- October 31)
1.0 mg/L
Daily
Composite
E
NH3 as N (November 1-March 31)
1.9 mg/L
Daily
Composite
E
Dissolved Oxygen3
Daily
Grab
E, U, D
Fecal Coliform
(geometric mean)
200 / 100 ml
400 / 100 ml
•
Daily
Grab
E
Total Residual Chlorine's
17 µg/L
Daily
Grab
E
Temperature (°C)
Daily
Grab
E, U, D
Total Nitrogen (NO2 + NO3 + TKN)
Monthly
Composite
E
Total Phosphorus5
Monthly
Composite
E
Chronic Toxicitys
Quarterly
Composite
E
Conductivity
Daily
:Grab
E, U, D
Chromium
51 µg/L
204 µg/L
:Weekly l '
Composite
E
Lindane
Weekly
'Grab
E
Copper
_
2/Month
Composite
E, U, D
Cyanides
5 µg/L
15 µg/L
Weekly
Grab
E
Lead
26 µgIL
34 µIL
Weekly
Composite
E
Silver
2/Month
Composite
E
Zinc
•
2/Month
Composite
E, U, D
Mercury's
0.012 µg/L
Weekly
Composite
E
Molybdenum
2/Month
Composite
E
Footnotes:
1 Sample Locations: E - Effluent, I - Influent, U - Upstream, D- Downstream. For instream
monitoring requirements, see Part A.(3.).
2The monthly average effluent CBOD5 and total suspended residue concentrations shall not exceed
15% of the respective influent value.
3 The daily average dissolved oxygen effluent concentrations shall not be less than 6.0 mg/L.
4 The daily average limit for total residual chlorine shall be 28 µg/ L.
5 See Part A.(5.). for additional nutrient monitoring information.
6 Whole effluent toxicity shall be measured by Chronic Toxicity (Ceriodaphnia) P/ F at 90 %. Samples
shall be taken quarterly during the months of March, June, September and December. See Part
A.(4.).
7 The Division of Water Quality shall consider all cyanide concentrations reported below 10 ug/L to
be "zero" for permit -compliance purposes only.
8 The quantitation limit for mercury shall be 0.2 ug/1 (0.2 ppb). Levels reported at less than 0.2 ug/1
shall be considered zero for compliance purposes.
The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units.
There shall be no discharge of floating solids or visible foam in other than trace amounts.
Permit NC0024970
A. (2.) EFFLUENT LIMITATIONS AND MONITORING REQUIREMENTS — FINAL
During the period beginning on March 1, 2002 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:
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Flow
64.0 MGD
Continuous
Recording
I or E
CBOD, 5-day (20°C)2
April 1- October 31
4.0 mg/L
6.0 mg/L
Daily
Composite
E, I
CBOD, 5-day (20°C)2
November 1- March 31
8.0 mg/L
12.0 mg/L
Daily
Composite
E,
Total Suspended Residue2
15.0 mg/L
22.5 mg/L
Daily
Composite
E, I
NH3 as N (April 1- October 31)
1.0 mg/L
Daily
Composite
E
NH3 as N (November 1-March 31)
1.9 mg/L
Daily
Composite
E
Dissolved Oxygen3
Daily
Grab
E, U, D
Fecal Coliform
(geometric mean)
200 / 100 ml
400 / 100 ml
Daily
Grab
E
Total Residual Chlorine4
17 µg/L
Daily
Grab
E
Temperature (°C)
.
Daily
Grab
E, U, D
Total Nitrogen (NO2 + NO3 + TKN)
Monthly
Composite
E
Total Phosphorus5
.
Monthly .
Composite
E
Chronic Toxicity
•
Quarterly
Composite
.
E
Conductivity
. Daily .
_ Grab
E, U, D
Chromium • ..
51 µg/L
204 µg/L
Weekly :..
Composite
E
Lindane _ .
0.01 µg/L
Weekly.-:-..
... . Grab
E
Copper :_.
.._ ..
2/Month__.
..Composite
E. U, D
Cyanide? :.
'..
.... 5 µg/L
15 µg/L
Weekly = •
'Grab _• ..
-
E
Lead
•
26 µg/L' .
34jig/L
Weekly
Composite
E
Silver
2/Month
Composite
E
Zinc
2/Month
Composite
E, U, D
Mercurye
0.012 µg1L
Weekly
Composite
E
Molybdenum
2/Month
Composite
. E
Footnotes:
1 Sample Locations: E - Effluent, I - Influent, U - Upstream, D- Downstream. For instream
monitoring requirements, see Part A.(3.).
2 The monthly average effluent CBODS and total suspended residue concentrations shall not exceed
15% of the respective influent value.
3 The daily average dissolved oxygen effluent concentrations shall not be less than 6.0 mg/L.
4 The daily average limit for total residual chlorine shall be 28 µg/L.
s See Part A.(5.). for additional nutrient monitoring information.
6 Whole effluent toxicity shall be measured by Chronic Toxicity (Ceriodaphnia) P/F at 90 %. Samples
shall be taken quarterly during the months of March, June, September and December. See Part
A.(4.).
7 The Division of Water Quality shall consider all cyanide concentrations reported below 10 ug/L to
be "zero" for permit -compliance purposes only.
8 The quantitation limit for mercury shall be 0.2 ug/1 (0.2 ppb). Levels reported at less than 0.2 ug/ 1
shall be considered zero for compliance purposes.
The pH shall not be less than 6.0 standard units nor greater than 9.0 standard units.
There shall be no discharge of floating solids or visible foam in other than trace amounts.
Permit NC0024970
A. (3.) INSTREAM MONITORING REQUIREMENTS
PARAMETERS TO BE SAMPLED
Parameter
Dissolved Oxygen
Temperature
Frequency Type
1/wk (June - September), 1/mo.
(October - May)
1/wk (June - September), 1/mo.
(October - May)
Location
Grab IC, SC2, SC3, SC4,
SC5, LSC1, MC1, MC2
Grab IC1, SC1, SC2, SC3,
SC4, SC5, LSC1, MC1,
MC2
Conductivity
1/wk (June - September), 1/mo.
(October - May)
Grab IC1, SC1, SC2, SC3,
SC4, SC5, LSC1, MC1,
MC2
pH
Ammonia (NH3)
1/wk (June - September), 1/mo.
(October - May)
Grab
Weekly (January - December) Grab
Nitrate/Nitrite (NOX) Weekly (January - December) Grab
Total Kjeldahl Nitrogen Weekly (January - December) Grab
(TKN)
SC5
SC5
SC5
SC5
Total Phosphorus (TP) Weekly (January - December) Grab SC5
Orthophosphate (PO4) Weekly (January - December) Grab SC5
Copper
1 / mo. (January December) Grab IC1, SC1, LSC1, LSC2,
MC1, MC2
Cadmium
Zinc
1/mo. (January - December)
1/mo. (January - December)
Grab
Grab
MC1, MC2
IC1, SC1, LSC1, LSC2,
MC1, MC2
SAMPLE LOCATIONS:
Irwin Creek
1. Upstream of Irwin Creek WWTP (IC1)
Sugar Creek
1. Downstream of the confluence of Irwin and Sugar Creeks at Yorkmont Road (SC1)
2. Downstream of the confluence of Irwin and Sugar Creeks at Arrowwood Road (SC2)
3. Downstream of the confluence of Irwin and Sugar Creeks at Nations Ford Road (SC3)
4. Downstream of the confluence of Irwin and Sugar Creeks at Route 51 (SC4)
5. Downstream of McAlpine and Sugar Creeks confluence at Route 160 (SC5)
Little Sugar Creek
1. Upstream of Sugar Creek WWTP (LSC1)
2. Downstream of Sugar Creek WWTP at Archdale Road (LSC2)
McAlpine Creek
1. Upstream of Discharge (MC1)
2. Downstream of the confluence of McMullen and McAlpine Creeks at SC 2964 (MC2)
Upstream and downstream samples shall be grab samples. Instream sampling should continue to be
coordinated to reduce redundant sampling for the CMUD-McAlpine Creek, Sugar Creek, and Irwin
Creek wastewater treatment facilities. It is recommended that monitoring be conducted during the
same day or on consecutive days.
Instream monitoring requirements for Irwin Creek, Sugar Creek and McAlpine Creek WWTPs are
identical. All instream monitoring data will be submitted with the Discharge Monitoring Report
(DMR) data for McAlpine creek WWTP. Please refer to McAlpine Creek WWTP DMR data for any
instream monitoring data pertaining to Irwin Creek, Sugar Creek and/or McAlpine Creek WWTPs.
Permit NC0024970
A. (4.) CHRONIC TOXICITY PASS/FAIL PERMIT LIMIT
The effluent discharge shall at no time exhibit observable inhibition of reproduction or significant
mortality to Ceriodaphnia dubia at an effluent concentration of 90%.
The permit holder shall perform at a minimum, quarterly monitoring using test procedures
outlined in the "North Carolina Ceriodaphnia Chronic Effluent Bioassay Procedure," Revised
February 1998, or subsequent versions or "North Carolina Phase II Chronic Whole Effluent
Toxicity Test Procedure" (Revised -February 1998) or subsequent versions. The tests will be
performed during the months of March, June, September, and December. Effluent sampling for
this testing shall be performed at the NPDES permitted final effluent discharge below all
treatment processes.
If the test procedure performed as the first test of any single quarter results in a failure or ChV
below the permit limit, then multiple -concentration testing shall be performed at a minimum,
in each of the two following months as described in "North Carolina Phase II Chronic Whole
Effluent Toxicity Test Procedure" (Revised -February 1998) or subsequent versions.
The chronic value for multiple concentration tests will be determined using the geometric mean of the
highest concentration having no detectable impairment of reproduction or survival and the lowest
concentration that does have a detectable impairment of reproduction or survival. The definition of
"detectable impairment," collection methods, exposure regimes, and further statistical methods are
specified in the "North Carolina Phase II Chronic Whole Effluent Toxicity Test Procedure" (Revised -
February 1998) or subsequent versions.
All toxicity testing results required as part of this permit condition will be entered on the Effluent
Discharge Monitoring Form (MR -I) for the months in which tests were performed, using the
.parameter code TGP3B for the pass/fail results .and THP3B for the Chronic Value. Additionally, DWQ
Form AT-3 (original) is to be sent to the following address:
Attention: North Carolina Division pf Water Quality
Environmental Sciences Branch
1621 Mail Service Center
Raleigh, North Carolina 27699-1621
Completed Aquatic Toxicity Test Forms shall be filed with the Environmental Sciences Branch no
later than 30 days after the end of the reporting period for which the report is made.
Test data shall be complete, accurate, include all supporting chemical/physical measurements and
all concentration/response data, and be certified by laboratory supervisor and ORC or approved
designate signature. 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 Branch at the address cited above.
Should the permittee fail to monitor during a month in which toxicity monitoring is required,
monitoring will be required during the following month.
Should any test data from this monitoring requirement 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.
NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum
control organism survival, minimum control organism reproduction, 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.
•
Permit NC0024970
A. ( 5.) NUTRIENT STUDY
The South Carolina Department of Health and Environmental Control (SC DHEC) has
determined that Fishing Creek Reservoir, Cedar Creek Reservoir and Lake Wateree are impaired due
to excessive nutrient loads and algal response to discharges upstream of these lakes. The Catawba
River Basinwide Water Quality Plan (December 1999) states that a TMDL will be developed to address
the causes and sources of impairment in these South Carolina lakes. SC DHEC has proposed the
development of a phosphorus TMDL and is planning to limit phosphorus for all South Carolina
NPDES dischargers with flows greater than 50,000 gallons per day. Significant discharges of
phosphorus have also been linked to the North Carolina portion of the Fishing Creek Reservoir
watershed. Estimates indicate that a significant portion of the total phosphorus load comes from the
Sugar Creek Subbasin. To work towards reduction of this load, CMUD shall provide the Division
with a study that fully investigates the feasibility of reducing total phosphorus (TP) load at this
WWTP. The target TP load should be equivalent to a TP concentration of 1 mg/L at the effluent. This
condition should not be construed as a permit limit. However, a limit may be imposed once the TMDL
has been completed and an implementation plan is developed.
The optimization study should include the following:
• An identification of significant sources of pollution in the system.
• An evaluation of ways in which these sources can be reduced or eliminated.
• The possibility of reducing influent flows to the WWTP to control mass loading to the
stream.
• An assessment of the current treatment processes and ways in which this may be
optimized to achieve a higher level of treatment.
• A plan to optimize the current treatment system to achieve a higher level of nutrient
removal.
• An evaluation of additional treatment units required to achieve higher nutrient removal.
The optimization study should be completed by February 1, 2002, and submitted to the following
address:
•
-Nor-th:Carolina Division of Water Quality E--
Water. Quality Section/NPDES Unit
1617 Mail Service Center
Raleigh, North Carolina 27699-1617