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HomeMy WebLinkAboutNC0020737_WASTELOAD ALLOCATION_19890117 NPDES DOCUMENT SCANNING COVER SHEET NPDES Permit: NC0020737 Kings Mountain WWTP Document Type: Permit Issuance Wasteload Allocation Authorization to Construct (AtC) Permit Modification Correspondence 201 Facilities Plan Instream Assessment (6713) Environmental Assessment (EA) Permit History Document Date.: January 17, 1989 This document is printed oa reuse paper-ignore any content on the resrex- a side ' ^ DIVISION OF ENVIRONMENTAL MANAGEMENT January 17, 1989 TO; Jim Reid THROUGH: Randy Dodd y/ (t> FROMn Ruth Clark hoNa SUBJECTn City of Kings Mountain Monitoring Requirements 1,1 O7�7 B"ffalc' Creep (Q???Q4) Cleveland County l have snclnsed a copy of the guidelines used to determine � which parameters should be monitored instream . Since serundary linits were assigned during the winter months, and the model predicts that the dissolved oxygen sag will occur at the discharge point during these months, the monitoring requirements can be relaxed during the winter . The permit has not yet been issued ' and I have recommenned that the winter monitoring requirement oe dropped for all parameters. Ths summer monitoring will remain as ih is written in toe approval form . if you have any questions - please call me at (919 )723-5083. � Instream Self-Monitoring Recommendations General Guidance hAl PDES permiY Where NtQiLd,i.5_chara watrr es r_ oualltY limited, or where there is a question regarding doyns.tream_%,ta_t_¢r g_ualit_y, appropriate instream (i.e. upstream s downstream) monitoring requirements should be assigned_ In general, the following should apply: . Minor Facilities (,!V/ ,�Q,�_ a.) Oxygen-consuming wastes -- monitoring sties: 1 upstream site, 1 downstream site located at or near the predicted dissolved oxygen sagpoint (if unaccessible, it will generally be preferred to choose a point further downstream in order to better examine the impacts when flows are slightly higher than 7Q10 - i_e. annual summer low flow periods) . -- parameters: temperature, DO, conductivity, fecal coliform if waste is domestic or where bacteria are present (on occasion, it may be necessary to n add BODS and NH3-N, and potentially pH) . , '? -- frequency: weekly. during summer period (Apr - Oct) , biweekly during the winter period (Nov - Mar) . b.) toxics In general, effluent biomonitoring may preclude the need for instream monitoring of a specific toxicant. However, if a particular toxic component is expected to be at or very near the standard under actual discharge con- ditions (i.e. not just permitted conditions) , instream monitoring may be appropriate. -- monitoring sites: 1 upstream site, 1 downstream site located at or just below mixpoint of the discharge -- parameters: (dependent on the composition of the discharge) -- frequency: weekly during summer period (Apr - Oct) , bi-weekly during winter period (Nov - Mar)) Major Facilities '� � i»CA a) Oxygen-consuming wastes -- monitoring sites: 1 upstream, 1-3 downstream locations (It is recom- mended that at least one site be established at the. predicted under low flow conditions_ In many cases it may be appropriate to add a- 2nd site downstream of the 1st in order to examine impacts under more.-normal "'"" flow conditions. Finally, where a discharge influences water quality .for a very long distance -- or multiple DO sags are predicted -- 3 downstream monitoring stations may be assigned.) - _ -- parameters: temperature, DO, conductivity, pH, fecal coliform (if waste is domestic. or if bacteria are present) , BOD5, and NH3-N (if nitrogen is discharged - can also include TKN if a large organic nitrogen component is present) , others as deemed appropriate (e.g. phosphorus, etc.) . -- frequency: 3/week during the summer period (Apr - Oct) , gek y during the winter period (Nov - Mar) . � . b) toxics In general, effluent biomonitoring may preclude the need for instream monitoring of a specific toxicant. However, if a particular toxic component is expected to be at or very near the standard under actual discharge con- ditions (i.e. not just permitted conditions) , instream monitoring may be appropriate. -- monitoring sites: 1 upstream site, 1 downstream site located at or just below the mixpoint of the discharge_ -- parameters: (dependent on the composition of the discharge) -- frequency: 3/week during the summer period (Apr - Oct) , weekly during the winter period (Nov - Mar) . AFC DIVISION OF ENVIRONMENTAL MANAGEMENT December 28, 1987 MEMORANDUM TO: Regional Water Qua l ty Supervisors - THRU: Steve Tedder FROM: Trevor Clementll( C SUBJECT: Instream Monitoring Requirements for NPDES Discharges There have been several inquiries from the regional field offices regarding the rationale for changes in the instream monitoring requirements for NPDES discharges of oxygen-consuming waste. The changes were made in an effort to gather the appropriate information that will allow DEM to evaluate the instream impacts attributed to the discharge. As you know, the Division is no longer changing existing permit requirements for oxygen-consuming wastes upon permit renewal unless there is information demonstrating that the existing limits are not protecting water quality standards during low flow conditions. Since DEM cannot always directly monitor all discharges within the state, staff must rely upon the self-monitoring system for this information. Our ultimate objective is to maintain water quality in a given water body to assure that its designated use is protected. Therefore, we are asking the regions to support this objective by placing as much emphasis on reviewing instream data as is put into reviewing effluent data. Quality assurance will be necessar y if DEM is going to place greater reliance on self-monitoring data. Since Technical Support routinely reviews self-monitoring data for every exist- ing discharge whose permit is up for renewal, we can provide the first phase of screening. The regions can assist by following up on situations where Technical Support has a question regarding the validity of the data or the appropriateness of the methods by wh�ch_.the,_data is being collected. In this manner we can work jointly to improve the information received through the self-monitoring program so that it can be used accordingly. Let me=assure you--that the instream data being "requested is benefteial to the Division. Temperature, D.O., fecal coliform, and conductivity parameters provide the minimum amount of data necessary for Technical Support to adequately assess the impacts instream from an oxygen-consuming -waste discharge. Conducti- vity was added to the other parameters as a routine monitoring requirement because it can add valuable insight as to the contribution of the discharge to instream conditions. This information will help us determine whether low D.O. concentrations downstream are due to a slug Of wastewater, typical facility. Operation, or to natural background conditions. r .aremen working with the Facility Performance Unit to streamline these i requirements and to make sure program_ that they coincide with the overall monitoring b A (those proposed of all Official changes (the sent out P posed for rule-making) will for your review: Please let me know if you have any questions 'or ` .comments regarding this matter_ . cc r Hob" DeWeese - - 3, v �3 7 - f elf-1 40 G� z 6 ,/ i _ d VA#- 05WYle x sz JIle LAC { i //uLn c C/uri,v z { 0 f I I I INSTREAM SELF-MONITORING DATA MONTHLY AVERAGES Discharger : r hj or kD 5 /v CK. lotorP Permit No . : NC00 ,20237 Receiving Strum : bgrojoaeee- Sub-basin : gl� 03o8o6-- :Jpstream Location : ove ( , r{rGEDownstream Locationi0/X� m. lelnvr% XhaJe Upstream `1 Downstream ?ATE TEMP D . O . BOD5 COND . TEMP D .O. BOD5 COND -EC-88 ia:V-88 EP-88 03 (?-0 Col a0 _ I•gCt A.UG-83 �3 1.2 I (F ate_ zo 0.0 JUL-Ss a3 gz ao Ou S•o a.� U N-8,, a3 -31 as 7.91 a.G MAY-8 8 Cl I q R.�13 �•8 All R-88 I Q.20 a•IA 17 Q.`kf 0-31 M P,R-88 f7 �c� 2,g5 gr.3z 3.1+1 JAN-88 -- -s7 _1I.R )o.Q iA9 3.0 -87 lz 9ss q,g_ _� -..- .-8 7 B.2 Q.S. �' ,2-- _8.8 i0,I 3.z -- g 7 z2 i9 � �.3 25 - ,t T,_,27 25 G.O -2,3 2. S.lo I.Q Y-8 7 -tom 0,0 zj I g', 1 3.6 PR-87 _IL q.D 22_5 0 9.1 3,1 - -- AR-87 13 ID,I 3,5 �z ro.i_ qlq EB-87 1� 10.3 z.� _ Il lo, 7- 1L D)EC-86 Iro CUP 2.z 1l �+� 2.5 NOV-86 7/4 2,1 21 2.? OCT-86 zl q.2- 2.6 _2z _4' 2A -- AZ,9P-86 7,3 2 '1 ;25 7.7 2.2. `t dG-86 2g_ 5.9 3,1 q.4 W4,0 ,S'�'d-t*L-8 6 �_ S,5 3, rncl�-86 3 T 3,4 23 A.z _3, 1_ -- MAY-86 .ZB _ A R-8 6 .21 Cj.2 2.6 2-1 4.tr 3.1 MAR-86 '_ 10-ki 3.I 1 ) 10.3 3.4 FEB-86 I_ 103 2.^1 i'J IDA 2.) JAN-86 DEC-85 -- -- -- NOV-85 -- -- -- OCT-85 -- 3EP-85 -- AUG-85 JUL-85 JUN-85 MAY-85 APR-85 MAR-85 FEB-85 JAN-85