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HomeMy WebLinkAbout1203_BurkeCDLF_SiteSuitabilityReevaluateRequest_DIN27499_20160829Environmental Engineers, Scientists & Consultants 2211 W. Meadowview Road, Boone Buildiing, Suite 101 Greensboro, NC 27407 tel: 336/ 323-0092 fax: 336/ 323-0093 www.JoyceEngineering.com August 29, 2016 Mr. Perry Sugg Permitting Hydrogeologist Division of Waste Management/Solid Waste Section 1646 Mail Service Center Raleigh, NC 27699-1646 RE: John’s River Waste Management Facility, Permit No. 12-03 C&D Landfill Expansion Conditional Site Suitability – Request for Reevaluation JOYCE Project No. 00277.1701.12, Task No. 01 Dear Perry: On behalf of Burke County, North Carolina, Joyce Engineering (JOYCE) is submitting this request to reevaluate the site suitability of Phases 1B, 2B, and 3 of the C&D landfill expansion at the John’s River Waste Management Facility (Permit No. 12-03). The facility is currently operating in Phase 1A of the C&D expansion, which began accepting waste in September 2014. JOYCE is currently preparing a permit-to-construct application for Phases 2A and 4 of the C&D expansion, which are scheduled to be constructed in 2018. The County has limited capacity to operate in Phase 1A; therefore, they requested that JOYCE revisit the Conditional Site Suitability Approval and present this request to the Section for review. The County wishes to gain site suitability approval for Phases 1B, 2B, and 3 in order to obtain a permit to construct Phase 1B. On February 28, 2014, the NCDEQ Solid Waste Section (the Section) issued a Conditional Site Suitability Determination (DIN 20647) for the John’s River C&D Landfill Expansion. The Section determined the Site Plan Application met the requirements of 15A NCAC 13B.0536 and .0538, and that the proposed Phases 1A, 2A, 4, 5, 6, 7, and 8 were suitable for landfill construction and operation; however, the Section determined that the Phases 1B, 2B, and 3 were not suitable for landfill construction and operation due to a groundwater contaminant plume from the old C&D-over-MSW landfill (old landfill) impinging on these phases. In our conversations with the Section about this issue in late 2013 and early 2014, we agreed to monitor the landfill gas and groundwater plume in the area between the old landfill and the new C&D expansion area for two years; after such time, we could request a reevaluation of site suitability for Phases 1B, 2B, and 3. The groundwater contaminant plume on the northeast side of the old landfill, between the old landfill and the C&D expansion area, was determined to be the result of landfill gas migration. JOYCE submitted an Addendum to the Corrective Action Plan (ACAP) in August Mr. Perry Sugg August 29, 2016 Page 2 of 3 2013 on behalf of Burke County, which added Control of Landfill Gas (LFG) as a remedy for the area between the old landfill and new C&D expansion area. The Section approved the ACAP for immediate implementation on September 5, 2013 (DIN19655). In November 2013, seven passive landfill gas vents (GVs) were installed on the northeast side of the old landfill and JOYCE submitted a Gas Vent Installation and Monitoring Report to the Solid Waste Section on December 12, 2013. JOYCE has conducted quarterly LFG monitoring of the area between the two landfills following the approved ACAP, including the eight GVs, nine temporary gas probes (TGPs), and several piezometers and monitoring wells (PZ-30S, PZ-31, PZ-34, PZ-35, MW-36, and MW-38). Table 1 presents the LFG monitoring data for these locations from April 2014 through August 2016, and Drawing 1 shows the locations of the monitoring points. Unfortunately, one piezometer (PZ-34) and two temporary gas probes (TGP-3 and TGP-6) have been inadvertently destroyed. There have been no exceedances of the LEL and few detections of methane in piezometers PZ-30S, PZ-31, PZ-35, or in temporary gas probes TGP-5, TGP-7, or TGP-8; therefore, there have been no exceedances of the LEL for methane within the footprint of Phases 1B. TGP-4 and TGP-9, which are near the boundary between Phases 2B and 3, have consistently had exceedances of the LEL for methane. Burke County also agreed to monitor several wells and piezometers in the area between the two landfills to evaluate migration of the groundwater plume and its potential impact on Phases 1B, 2B, and 3. Piezometers PZ-36 and PZ-38 were converted to permanent monitoring wells MW-36 and MW-38, respectively, to serve as performance wells for the Control of LFG remedy. MW-38 also serves as a compliance well for Phase 1A. In addition, piezometers PZ-12, PZ 30S, PZ-31, PZ-35 and monitoring well MW-15S are sampled with each semiannual sampling event for the constituents of concern (COCs) associated with the northeastern portion of the groundwater plume. The COCs for the northern portion of the groundwater plume are benzene, 1,4-dichlorobenzene, methylene chloride, tetrachloroethylene, trichloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, and vinyl chloride. The well and piezometer locations are shown on Drawing 1, and Table 2 summarizes the analytical results for COCs from these wells between February 2013 and May 2016. Chart 1 shows the total COCs (the sum of the detected concentrations of all COCs) versus time for these wells. There have been no exceedances of groundwater standards or detections above the solid waste section reporting limits for any of the COCs in PZ-12, PZ-30S, PZ-31, or PZ-35 since July 2013; so the COC plume does not appear to extend very far, if at all, into the footprints of Phases 1B, 2B or 3. Also, the concentrations of total COCs appear to show downward trends in MW-36, MW-15S, and PZ-31, and the concentrations in MW-38 appear stable (see Chart 1). This indicates that the groundwater plume in this area is receding, not expanding. Mr. Perry Sugg August 29, 2016 Page 3 of 3 It is our understanding that nothing in the NC Solid Waste Management Regulations precludes permitting a landfill over an existing groundwater plume; however, we understand the Section’s concern about monitorability. Given that the plume does not extend far under Phases 1B, 2B, or 3, and that the plume appears to be receding, we contend that the existing plume will not prevent adequate monitoring of the proposed new phases. On behalf of Burke County, we request that the Section reevaluate site suitability for Phases 1B, 2B, and 3 of the John’s River C&D Landfill Expansion. Please contact us if you have any questions regarding this request. Sincerely, JOYCE ENGINEERING Van Burbach, Ph.D., P.G. Senior Technical Consultant Attachments: Table 1, Table 2, Chart 1, Drawing 1 cc: Chris Hollifield – General Services Director, Burke County, NC Allen Gaither, NCDEQ-SWS Jackie Drummond, NCDEQ-SWS TA B L E 1 : L a n d f i l l G a s ( L F G ) C o n c e n t r a t i o n s in v i c i n i t y o f P h as e s 1 B , 2 B , a n d 3 4/ 9 / 2 0 1 4 8 / 2 7 / 2 0 1 4 1 0 / 2 2 / 2 0 1 4 3 / 3 0 / 2 0 1 5 5 / 2 1 / 2 0 1 5 7 / 1 6 / 2 0 1 5 1 2 / 9 / 2 0 1 5 2 / 1 9 / 2 0 1 6 5 / 1 7 / 2 0 1 6 8 / 2 3 / 2 0 1 6 GV - 1 5 8 . 0 5 7 . 7 63 . 3 6 1 . 4 5 6 . 4 5 8 . 4 5 9 . 6 6 0 . 0 5 9 . 1 4 8 . 7 GV - 2 5 7 . 9 5 9 . 1 65 . 1 6 2 . 9 5 7 . 4 6 0 . 5 6 0 . 3 6 0 . 1 6 1 . 5 6 0 . 0 GV - 3 5 7 . 9 5 8 . 5 64 . 8 6 2 . 8 5 7 . 3 6 0 . 4 6 0 . 1 6 0 . 2 6 1 . 6 6 0 . 5 GV - 4 6 2 . 5 6 2 . 3 66 . 1 6 2 . 9 5 9 . 8 6 2 . 8 6 1 . 8 6 1 . 2 6 4 . 9 6 1 . 1 GV - 5 5 9 . 9 6 0 . 0 60 . 4 6 2 . 0 5 7 . 3 6 0 . 8 5 9 . 0 5 9 . 4 6 1 . 2 4 3 . 7 GV - 6 2 7 . 9 5 9 . 3 65 . 6 6 3 . 1 5 6 . 8 6 0 . 2 6 0 . 8 6 0 . 2 6 1 . 0 6 0 . 2 GV - 7 1 . 1 4 0 . 5 28 . 5 1 6 . 2 3 4 . 4 3 1 . 1 4 0 . 1 4 1 . 1 4 0 . 1 3 2 . 1 GP - 1 S 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 GP - 1 D 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 GP - 2 S 5 7 . 1 5 6 . 9 62 . 5 6 2 . 0 5 5 . 2 5 6 . 2 5 9 . 9 6 0 . 1 5 8 . 7 5 6 . 3 GP - 2 I 6 0 . 2 5 8 . 1 62 . 8 6 1 . 7 5 5 . 8 5 7 . 9 5 8 . 5 5 8 . 6 5 8 . 6 5 8 . 2 GP - 2 D 5 9 . 8 5 8 . 3 63 . 0 6 1 . 6 5 5 . 9 5 8 . 1 5 7 . 9 5 8 . 1 5 8 . 7 5 6 . 4 GP - 3 S 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 GP - 3 D 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 2 0 . 0 0 . 0 0 . 0 0 . 0 GP - 4 n y i n y i 62 . 2 4 1 . 7 5 5 . 4 5 6 . 2 5 7 . 7 5 2 . 1 5 8 . 5 3 3 . 2 GP - 5 n y i n y i 0. 0 0 . 0 0 . 0 0 . 1 0 . 0 0 . 0 0 . 0 0 . 0 GP - 6 n y i n y i 0. 0 0 . 0 0 . 0 0 . 2 0 . 0 0 . 0 0 . 0 0 . 0 TG P - 1 4 5 . 6 3 1 . 5 23 . 9 3 6 . 4 3 6 . 0 1 9 . 1 2 8 . 7 4 5 . 2 3 0 . 8 1 3 . 3 TG P - 2 3 3 . 7 1 6 . 8 9. 8 2 7 . 7 2 2 . 8 6 . 8 6 . 8 1 6 . 1 1 1 . 4 2 . 7 TG P - 4 3 3 . 3 6 7 . 8 50 . 9 5 4 . 2 6 2 . 2 3 6 . 1 8 3 . 6 3 0 . 3 5 6 . 1 3 4 . 3 TG P - 5 0 . 0 0 . 0 0. 0 0 . 0 0 . 1 0 . 0 0 . 0 0 . 0 0 . 1 0 . 0 TG P - 6 2 9 . 5 2 1 . 7 0. 0 - - - - - - - - - - - - - - - - - TG P - 7 0 . 0 0 . 0 0. 0 0 . 0 0 . 1 0 . 1 0 . 1 0 . 1 0 . 0 0 . 0 TG P - 8 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 TG P - 9 1 0 . 0 1 8 . 7 0. 0 1 4 . 9 1 7 . 6 5 . 2 1 8 . 3 6 . 1 1 1 . 0 9 . 2 TG P - 1 0 0 . 1 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 PZ - 3 0 S 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 PZ - 3 1 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 PZ - 3 5 0 . 0 0 . 0 0. 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 0 . 0 MW - 3 6 0 . 4 5 7 . 6 42 . 6 5 1 . 9 4 2 . 3 4 8 . 5 5 7 . 3 1 6 . 8 2. 5 3 5 . 0 MW - 3 8 0 . 5 0 . 0 2. 2 0 . 0 5 . 0 1 0 . 7 8 . 7 43 . 8 0 . 5 0 . 0 CH 4 = M e t h a n e . G P = G a s P r o b e . M W = M o n i t o i r n g W e l l . n y i = N o t y e t i n s t a l l e d . GV = G a s V e n t . T G P = T e m p o r a r y G a s P r o b e . P Z = P i e z o m e t e r . - - - = N o l o n g e r e x i s t s . CH 4 (% V o l . ) CH 4 (%Vol.) CH 4 (% V o l . ) CH 4 (% V o l . ) Lo c a t i o n o r LF G W e l l I D CH 4 (% V o l . ) CH 4 (% V o l . ) CH 4 (% V o l . ) CH 4 (% V o l . ) CH 4 (% V o l . ) CH 4 (% V o l . ) Bu r k e C o . - J o h n ' s R i v e r L a n d f i l l Pe r m i t # 1 2 - 0 3 Joyce Enginering TABLE 2: Constituents of Concern (COCs) in vicinity of Phases 1B, 2B, and 3 Analyte Sample Date DL SWSL MW-38 MW-36 MW-15S PZ-12 PZ-30S PZ-31 PZ-35 Benzene 18-Feb-13 0.25 1.0 ---8.0 --- --- ND --- ND 18-Jul-13 0.25 1.0 --- --- --- --- ---7.6 --- NC 2L = 1 µg/L (10/23/07) 6-May-14 0.25 1.0 6.5 8.7 4.6 --- ND ND ND 22-Oct-14 0.25 1.0 5.9 8.3 3.3 ND ND ND ND 21-May-15 0.25 1.0 4.9 5.8 2.0 ND ND ND ND 9-Dec-15 0.25 1.0 4.4 5.8 1.2 ND ND ND ND 4-May-16 0.25 1.0 5.4 6.7 1.3 ND ND ND ND 1,4-Dichlorobenzene 18-Feb-13 0.33 1.0 ---18.0 --- --- ND --- ND 18-Jul-13 0.33 1.0 --- --- --- ---6.5 --- NC 2L = 6 µg/L (01/01/10) 6-May-14 0.33 1.0 13.5 10.0 2.3 --- ND ND ND 22-Oct-14 0.33 1.0 12.9 15.2 1.6 ND ND ND ND 21-May-15 0.33 1.0 12.3 18.7 1.4 ND ND ND ND 9-Dec-15 0.33 1.0 12.2 19.6 1.0 ND ND ND ND 4-May-16 0.33 1.0 13.3 16.5 0.9JNDNDNDND 1,1-Dichloroethane 18-Feb-13 0.32 5.0 ---7.9 --- --- ND --- ND 18-Jul-13 0.32 5.0 --- --- --- --- ---11.3 --- NC 2L = 6 µg/L (01/01/10) 6-May-14 0.32 5.0 8.1 11.6 7.1 --- ND ND ND 22-Oct-14 0.32 5.0 6.9 9.0 4.9JNDNDNDND 21-May-15 0.32 5.0 5.5 4.8 J 2.4JNDNDNDND 9-Dec-15 0.32 5.0 7.2 5.9 2.2 J ND ND ND ND 4-May-16 0.32 5.0 6.5 5.9 1.5 J ND ND ND ND 1,2-Dichloroethane 18-Feb-13 0.12 1.0 ---1.0 --- --- ND --- ND 18-Jul-13 0.12 1.0 --- --- --- --- --- 0.54 J --- NC 2L = 0.4 µg/L (01/01/10) 6-May-14 0.12 1.0 ND 0.78 J ND --- ND ND ND 22-Oct-14 0.12 1.0 0.63 J 0.92 J ND ND ND ND ND 21-May-15 0.12 1.0 0.00 0.00 ND ND ND ND ND 9-Dec-15 0.24 1.0 0.70 J 0.66 J ND ND ND ND ND 4-May-16 0.24 1.0 0.74 J 0.92 J ND ND ND ND ND Methylene Chloride 18-Feb-13 0.97 1.0 ---17.9 --- --- ND --- ND 18-Jul-13 0.97 1.0 --- --- --- --- ---16.4 --- NC 2L = 5 µg/L (01/01/10) 6-May-14 0.97 1.0 ND 24.1 16.7 --- ND ND ND 22-Oct-14 0.97 1.0 ND 15.7 1.6 ND ND ND ND 21-May-15 0.97 1.0 ND 9.5 B 4.4 B ND ND ND ND 9-Dec-15 0.97 1.0 ND 11.2 B 2.6 B ND ND ND ND 4-May-16 0.97 1.0 ND 3.1 2.0 ND ND ND ND Tetrachloroethene 18-Feb-13 0.46 1.0 ---5.5 --- --- ND --- ND 18-Jul-13 0.46 1.0 --- --- --- --- ---7.8 --- NC 2L = 0.7 µg/L (10/23/07) 6-May-14 0.46 1.0 ND 7.9 6.9 --- ND ND ND 22-Oct-14 0.46 1.0 ND 7.3 5.2 ND ND ND ND 21-May-15 0.46 1.0 ND 6.0 3.3 ND ND ND ND 9-Dec-15 0.46 1.0 ND 5.0 2.1 ND ND ND ND 4-May-16 0.46 1.0 ND 4.5 2.0 ND ND ND ND Trichloroethene 18-Feb-13 0.47 1.0 ---3.6 --- --- ND --- ND 18-Jul-13 0.47 1.0 --- --- --- --- ---5.8 --- NC 2L = 3 µg/L (01/01/10) 6-May-14 0.47 1.0 2.1 6.0 4.3 --- ND ND ND 22-Oct-14 0.47 1.0 1.8 5.1 3.4 ND ND ND ND 21-May-15 0.47 1.0 0.9 J 3.5 2.1 ND ND ND ND 9-Dec-15 0.47 1.0 2.1 2.9 1.1 ND ND ND ND 4-May-16 0.47 1.0 1.7 3.1 ND ND ND ND Vinyl chloride 18-Feb-13 0.62 1.0 --- 1.2 --- --- ND --- ND 18-Jul-13 0.62 1.0 --- --- --- --- --- ND --- NC 2L = 0.03 µg/L (01/01/10) 6-May-14 0.62 1.0 ND 1.1 ND --- ND ND ND 22-Oct-14 0.62 1.0 ND 0.87 J ND ND ND ND ND 21-May-15 0.62 1.0 ND 0.00 ND ND ND ND ND 9-Dec-15 0.62 1.0 ND 0.80 J ND ND ND ND ND 4-May-16 0.62 1.0 ND 0.80 J ND ND ND ND ND Methane 18-Feb-13 --- --- --- --- --- --- --- (Dissolved Methane) 18-Jul-13 --- --- --- --- --- --- --- 6-May-14 0.66 2.0 4150 348 9940 --- ND ND ND 22-Oct-14 3.30 6.6 6820 8450 13000 ND ND ND ND 21-May-15 0.63 10.0 4900 173 4680 2.0 J 1.5 J 1.7 J 2.0 J 9-Dec-15 0.63 10.0 3112 3780 8550 3.0 J 2.5 J 4.8 J 2.7 J 4-May-16 0.49 10.0 4040 8920 7860 1.6 J 1.6 J 1.8 J 2.3 J Sum of COCs:18-Feb-13 ND 63.10 --- --- ND --- ND (Sum of above constituents, 18-Jul-13 --- --- --- --- --- 55.94 --- excluding methane.) 6-May-14 30.20 70.18 41.90 --- ND ND ND 22-Oct-14 28.13 62.39 20.00 ND ND ND ND 21-May-15 23.62 48.30 15.60 ND ND ND ND 9-Dec-15 26.60 51.86 10.20 ND ND ND ND 4-May-16 27.64 41.52 7.65 ND ND ND ND All concentrations in micrograms per liter (µg/l) = parts per billion. ND = Not Detected above the DL. DL = Laboratory Detection Limit. J = Estimated value - Concentration is less than the SWSL but greater than the DL. SWSL = Solid Waste Section Reporting Limit. B = Blank-Qualified (Concentration suspected to reflect laboratory or field contamination). NC 2L = Groundwater Standard from 15A NCAC 2L.0202. --- = Not reported or not sampled. Values above the NC 2L Standard are bold. Burke Co. - John's River Landfill Permit # 12-03 Joyce Engineering Bu k e  Co . ,  Jo h n ' s  Ri v e r  La n d f i l l Pe r m i t  #1 2 ‐03 Joyce  Engineering 0. 0 0 10 . 0 0 20 . 0 0 30 . 0 0 40 . 0 0 50 . 0 0 60 . 0 0 70 . 0 0 80 . 0 0 F e b ‐ 1 3 M a r ‐ 1 3 A p r ‐ 1 3 M a y ‐ 1 3 J u n ‐ 1 3 J u l ‐ 1 3 A u g ‐ 1 3 S e p ‐ 1 3 O c t ‐ 1 3 N o v ‐ 1 3 D e c ‐ 1 3 J a n ‐ 1 4 F e b ‐ 1 4 M a r ‐ 1 4 A p r ‐ 1 4 M a y ‐ 1 4 J u n ‐ 1 4 J u l ‐ 1 4 A u g ‐ 1 4 S e p ‐ 1 4 O c t ‐ 1 4 N o v ‐ 1 4 D e c ‐ 1 4 J a n ‐ 1 5 F e b ‐ 1 5 M a r ‐ 1 5 A p r ‐ 1 5 M a y ‐ 1 5 J u n ‐ 1 5 J u l ‐ 1 5 A u g ‐ 1 5 S e p ‐ 1 5 O c t ‐ 1 5 N o v ‐ 1 5 D e c ‐ 1 5 Jan‐16 Feb‐16 Mar‐16 Apr‐16 May‐16 C o n c e n t r a t i o n     ( µ g / l ) Ch a r t  1:    To t a l  CO C s  vs .  Ti m e  in  vi c i n i t y  of  Ph a s e s  1B ,  2B ,  & 3 MW ‐38 MW ‐36 MW ‐15S PZ ‐12 PZ ‐30S PZ ‐31 PZ ‐35