Loading...
HomeMy WebLinkAboutNC0040011_Wasteload Allocation_19870807NPDES DOCUWENT SCANNING COVER SHEET NC0040011 Yanceyville WWTP NPDES Permit: Document Type: Permit Issuance :` Wasteload Allocation M Authorization to Construct (AtC) Permit Modification Complete File - Historical Engineering Alternatives (EAA) Correspondence Owner Name Change Instream Assessment (67b) Speculative Limits Environmental Assessment (EA) Document Date: August 7, 1987 This document is printed on reuse paper - ignore any content on the reirerse side Brief of WLA Analysis Previous WLA's 1977: Recieved limits of 20 and 6 fora flow of 0.125 mgd. Discharge to Jail House Branch; a tributary to Country Line Creek. 1981: In -stream assessment based on influent / effluent efficiency and flow increase to 0.2 mgd. Modeling analysis of the Jail House Branch outfall indicated instream DO problems. New modeling analysis performed with correction in flow statistics from the 1977 model. Final WLA for flow increse recommended limits of 18 (21) and 7 (12) summer (winter) limits. A time of travel study accompanies this analysis; it addresses 'an enormous amount of algae' below the outfall of the oxidation pond. A second WLA was finalized in 1981 which included a proposal for the outfall to reloacte to Country Line Creek. Limits recommended for Jail House Br were 12 (16) and 2 (5), and those recommended for Country Line Creek were 30 / 30. 1982: Facility must have been struggling to meet SOC requirments, therefore numerous instream assessments took place with small incremental flow increases. Their discharge point to Jail House Branch created many documented DO problems, but no strong evidence of relocation existed to date in the WLA files. 1984: Facility relocated to Country Line Creek and with a discharge of 0.200 mgd the facility recieved 30 / 30 limits. 1986: Relocation of plant not yet complete. Various SOC's and instream assessments took place. Sa C (7 A-NAL.ci eECi 1k1(J i a,L Tr+rc2 jervN t FE2 `5 00TE 5 : rRNc \Ill VA.1T) / / �C 0,14 �(�v=3 -7Q (0 = p. o Crc O' c4( 1,v sec- Ovj oTA L Ste. co PfoAs't?ei tow = C).11Ae1 QM = 0.4 cS; 7Qto = 0.0 C415 Rfetr•LCC.) 6.100 r Mt,b 07JJ3 'Ma-b Iotkl •13C5 tA“,-D t• 5 (1 Li 0-) lob tan, = 50 �'►" Z — 7c.9,J 1.1 Cos *.5 (Zo� _ �00 Dov) 0.0 kris:/1 Zo = 2. A•t 0 R2 CREE((C 2,1f5 v,� 1 50 �rS. 1 ;7 C49 sple7 TABLE 1. Summary of SOC Wasteflows for Yanceyville WWTP Pre-SOC Previously Approved SOC Current SOC Request Flow (MGD) 0.10000 . 0.02467 0.00565 TOTAL 0.13032 TABLE 2. Model Results Reflecting Discharge to Jailhouse Branch Design Wasteflow BOD5 D.O. Min. (mg/I) D.O. Min. (mg/1) (MGD) (mg/1) Jailhouse Branch Country Line Cr. Pre-SOC 0.1000 140 0.0 4.3 SOC 0.1303 140 0.0 3.3 Pre-SOC 0.1000 100 0.0 5.0 SOC 0.1303 100 0.0 4.2 TABLE 3. Model Results Reflecting Discharge to Country Line Creek Design Wasteflow BODE D.O. Min. (mg/I) (MGD) (mg/1) Country Line Cr. Pre-SOC 0.1000 140 3.9 SOC 0.1303 140 2.8 Pre-SOC 0.1000 100 4.7 SOC 0.1303 100 3.8 ' . Appendix A t ;NEX78/MY _ . 08/07/E. COMPLIANCE EVALUATION ANALYSIS REPORT PERMIT--NC0040011 PIPE~-001 REPORT PERIOD: 8507 ~8606 LOC---E 7ACILITY~~YANCEYV%LLE SAN. DISTRICT WWTP DESIGN FLOW-- °2000 CLASS-- -OCAT%ON--YAMCEYV%LLE REGION/(*t'OUNTY-~04 CASWELL 50050 00310 00530 00610 31818 50060 00300 40NTH Q/MGD BOD RESITSS NH3+NH4- FEC COLI CHLORINE DO ' '35/07 "1366 62^00 108.5F 3^96 17.9 .165 4.79 ]5/08 .1372 41.00 88.5 4.45 6.3 .i22 6.98 35/09 .1190 54.00 5i.5 8.4i 3i.9 .i68 6.93 35/10 .1083 49.00 47.0 12-7.26 2.0 .234 6.4O 35/11 .1173 50.00 57.0 12.66 2.O .200 7.37 ^ 35/12 .1865 38.50F 34.OF 7.65F 2.0 ^255 8.i2 36/01 .i102 94.50F 49.O21.�9F i54.9 .2i9 5.9 F 5 -3 6 02 .1087 78.00F 33.OF 28^2iF 16.5 .18M 4.22 �6/03 .1i05 94.00F 53.0F 25.31F 2.O .195 3.9O 36/84 ^1195 92.00F 142.8F 16^20F 2.0 .177 7.24 ]605 .1O73 55.50F 64.5F 8.48F 2.0 .205 7.69 ]6/06 .i055 67.50F 80.oF 9.59F 2.0 .i92 6.67 \VERACE .ii55 64.66 67^3 i3.O� 2O.i .i92 6.35 IAXIMUM .i800 117.00 18O.0 26.62 12O0111),.1) .4O0 9.00 1INIMUM .i0OO 29.00 26.O 1.91 2.O TRACE 2.O0 IT M�D M�/L M�/L M�/L �/iO0ML MC |N flow. a minimum 0.0. of 0.0 mg/I is predicted to occur in Jailhouse Branch and a secondary sag of 4.3 mg/I is predicted to occur in Country Line Creek. With the total SOC flow added, the secondary sag in Country Line Creek is expected to drop to 3.3 mg/I. Given the predicted impacts. 1 have trouble justifying the need for a BODE limit of 140 mg/I when self -monitoring data for the last year show no monthly average exceeding 95 mg/1 (see Appendix A). A second set of model runs were completed using waste concentrations of 100 mg/I of B0D6 (see Table 2). The results show a substantial improvement in the secondary sag. However, the pre- dicted impact to D.O. from the total SOC flow is still greater than the criterion for no significant impact. Results for the model runs reflecting a direct discharge to Country Line Creek are shown in Table 3. This change should eliminate the occurrence of an anaerobic zone below the outfalt. However, the D.O. sag in Country Line creek is expected to reach slightly lower levels than with the outfalt on Jailhouse Branch. The predicted change in the D.O. minimum from the total SOC flow is 1.1 mg/1, which is substantially higher than the 0.5 mg/I criterion. Lowering the allowable B0D6 concentration to 100 mg/1 reduces the predicted net change to 0.9 mg/1 and increases the minimum expected D.O. by 1.0 mg/l. cc: 1. Page Benton Kent Wiggins Gray Hauser