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HomeMy WebLinkAbout4116WIHighPointCDLF_AssessmentPlan_DIN26955_20161021 Golder Associates NC, Inc. 5B Oak Branch Drive Greensboro, NC. 27407 USA Tel: (336) 852-4903 Fax: (336) 852-4904 www.golder.com Engineering Lic. No. C-2862/Geology Lic. No. C-399 Golder, Golder Associates and the GA globe design are trademarks of Golder Associates Corporation October 21, 2016 1239-651616.300 Ms. Jackie Drummond Department of Environmental Quality Division of Waste Management - Solid Waste Section 2090 US Highway 70 Swannanoa, NC 28778 828-296-4706 RE: ASSESSMENT MONITORING NOTIFICATION AND WORK PLAN ADDENDUM WASTE INDUSTRIES OF HIGH POINT C&D LANDFILL, PERMIT NO. 41-16 GUILFORD COUNTY, NORTH CAROLINA Dear Jackie: On behalf of Waste Industries, Golder Associates NC, Inc. (Golder) is submitting the following addendum to the Assessment Monitoring and Assessment Monitoring Work Plan (Plan), that was submitted to the North Carolina Department of Environmental Quality (NC DEQ) on December 7, 2015, and was approved by the NC DEQ on January 28, 2016. This addendum is being submitted due to exceedances of the NC 2L Standard for benzene in the samples from downgradient monitoring wells MW-2 and MW-6 during the second semi-annual water quality monitoring event of 2016. The initial Plan was submitted due to the presence of benzene above the NC 2L Standard in groundwater samples from MW-2. Based on the analytical results from the second semi-annual water quality monitoring event of 2016, Waste Industries will expand the Assessment Monitoring Program at the Waste Industries of High Point C&D Landfill to include MW-6. It is Waste Industries’ intent to comply with the requirements of 15A NCAC 13B. 0545.(a) and (b). 15A NCAC 13B .0545(a)(1) and (b)(1): INSTALLATION OF ADDITIONAL MONITORING POINT: Rule 15A NCAC 13B .0545(a)(1) requires the installation of at least one additional monitoring well or methane gas monitoring well at the facility or compliance boundary. Waste Industries intends to install additional groundwater monitoring wells downgradient of MW-2 and MW-6 prior to the January 2017 routine semi-annual water quality monitoring event, as shown on the attached Drawing 1. The wells will be designated as AMW-1 and AMW-2. Waste Industries is no longer pursuing the option of adding a surface water monitoring point in lieu of a groundwater monitoring well downgradient of MW-2, based on data from pore water samples collected during the second semi-annual water quality monitoring event of 2016. These samples indicate there is limited evidence to support that the stream receives groundwater from the MW-2 location year-round. The pore water results appear to be seasonal, as the February 2016 results supported that the stream receives groundwater from the MW-2 location. Additionally, Waste Industries intends to install a methane monitoring well adjacent to MW-2 and the waste unit to further investigate landfill gas as a source of benzene in groundwater samples from MW-2. Though the headspace of MW-2 is monitored for methane during the quarterly methane monitoring events, the screened interval of MW-2 is typically submerged. Data collected from the proposed methane monitoring well LFG-1 will be used to help determine the appropriate corrective action to address the benzene detections in samples from MW-2. Ms. Jackie Drummond October 21, 2016 Department of Environmental Quality 2 1239-651616.300 NCAC 13B. 0545(a)(2): NOTIFICATION TO ALL PERSONS WHO OWN LAND OR RESIDE ON LAND WITHIN THE CONTAMINATE PLUME: The property adjacent to the northwestern facility boundary near MW-2 is owned by the City of High Point and is utilized as the Kersey Valley Municipal Solid Waste (MSW) Landfill. There are no structures on the adjacent properties within 700 feet of the property line at MW-2 and no known users of groundwater on the adjacent parcel immediately adjacent to MW-2. A review of recent water quality monitoring reports for the Kersey Valley MSW Landfill indicates that benzene has not been detected in samples from compliance groundwater monitoring well MW-15, which is located approximately 200 feet northwest of MW-2. Based on the adjacent land use and because it does not appear that volatile organic compounds (VOCs) occur in groundwater at the property line based on surface water and pore water data, Waste Industries does not intend to notify the adjacent land owner. The property adjacent to the western facility boundary near MW-6 is owned by DH Griffin and is utilized for agricultural purposes. There are no structures on the adjacent properties within 700 feet of the property line at MW-6 and no known users of groundwater on the adjacent parcel immediately adjacent to MW-6. Based on the adjacent land use and because it does not appear that volatile organic compounds (VOCs) occur in groundwater at the property line based on surface water data, Waste Industries does not intend to notify the adjacent land owner. 15A NCAC 13B .0545(a)(3): SUBMISSION OF ASSESSMENT MONITORING WORK PLAN: Waste Industries has submitted an Assessment Monitoring Work Plan as required by Rule and is now providing this addendum to account for the additional NC 2L Standard exceedance of benzene in MW-6. Once approved by the Division of Waste Management, the addendum will be placed in the facility’s operating record, and all appropriate government officials will be notified. In order to comply with 15A NCAC 13B .0545 (b), Waste Industries will also complete the following activities: 15A NCAC 13B. 0545(b)(2): ANALYSIS OF ADDITIONAL PARAMETERS IN GROUNDWATER: Additional groundwater quality parameters will be performed in downgradient monitoring well MW-6 and proposed assessment wells AMW-1 and AMW-2 during the January 2017 event in accordance to NCAC 13B. 0545(b)(2). A subset of the compliance monitoring wells may be analyzed for Assessment Monitoring Parameters as allowed in 15A NCAC 13B .0545 (b) (6) and data support limited impacts at this time, which support the subset of wells proposed for Assessment Monitoring. The additional assessment monitoring parameters will include all of the constituents listed in the Appendix II of 40CFR 258 and the required indicator parameters for C&D landfills (chloride, manganese, sulfate, iron, specific conductance, pH, temperature, alkalinity, total dissolved solids, and tetrahydrofuran). One event for the complete NC Appendix II list is allowed in 15A NCAC 13B .0545 (b) (6) and is supported by the fact that many of the NC Appendix II parameters (e.g., PCBs, pesticides, and herbicides) are unlikely to be present based on the acceptable waste in the facility permit. As required by Rule, for any constituent detected in MW-6, AMW-1, and AMW-2 as a result of analyzing the NC Appendix II parameters, a minimum of four independent samples from the impacted well(s) will be collected and analyzed to establish background for the new constituents. The sampling schedule and list of parameters will proceed as follows: ENON-MECKLENBURG-CECIL (NC083) MW-4D 770 780 760 770 780 790 790 800 810 820 830 840780 76 0 750 8 0 0 7 9 0 8 0 0 8 1 0 820 830 840 8 1 0 81 0 810 810 81 0 810 820 8 1 0 800 800 810 820 840 830 820 830 820 810 7 9 0 80 0 790 790 800 790 8 0 0 8 0 0 800 780 790 780 800 800 800 790 800 810 820 830 770 780 760 770 780 780 820 80 0 81 0 85 0 850 790 800 810 820 830 840 780 770 760 750 740 750 74 0 750 730 7 3 0 7 4 0 7 3 0 73 0 74 0 7 5 0 75 0 74 0 760 770 780 830 840 800 790 810 820 7 5 0 760 7 3 0 7 4 0 770 780 790 780 740 750 770 760 74 0 76 0 7 5 0 770 780 780 79 0 780 770 790 79 0 780 790 800 8 0 0 8 1 0 8 1 0 8 0 0 800 80 0 80 0 7 8 0 7 9 0 7 7 0 7 6 0 740 750 760 750 730 740 7 3 0 7 3 0 730 760 750 740 720 720 7 2 0 7 2 0 730 740 720720 7 4 0 7 3 0 7 5 0 74 0 730 750 76 0 77 0 7 8 0 760 770 7 6 0 7 5 0 813.6 811.4 823.3 811.0799.2 817.6 820.4 823.5 810.9 810.3 810.2 811.8 831.1 832.8 820.0 821.1 816.6 WE 792.9' 795.3 795.1 795.5 801.7 804.2 810.4 849.0 849.3 811.4 809.4 809.7 817.1 811.1 809.6 810.7 826.8 798.3 811.0 820.6 804.3 798.9 810.2 797.9 795.4 810.5 804.6 799.3 795.8 801.7 802.9 802.9 800.9802.1 799.1 784.1 784.9 788.8 803.2 801.8 785.4 784.1 850.6 850.4 833.0 830.8 849.5 777.0 753.0 743.3 752.5 744.5 781.3 770.3 779.7 785.7 768.0 772.3 798.3 789.3 784.3 805.0 813.6 809.3 800.1 803.4 802.0 783.0 792.4 744.2 743.7 WE 741.6' 745.1 743.9 740.3 724.1723.2 801.1 809.1 RIP-RAP RIP-RA P SCALES END UNKNOW 601 763.88 78 0 780 7 7 0 7 6 0 7 5 0 7 4 0 7 3 0 720 7 2 0 750 760 770 740 730 79 0 7 9 0 i1 i2 i3 BH-4 BH-3 BH-2 BH-1 EXISTING O V E R H E A D P O W E R L I N E S MAPPING LIMITS. RECLAMATION FACILITY MAINTENANCEBUILDING FACILITY PROPERTY BOUNDARY SW-2 SW-1 SW-3 SB-3 MW-5 735.75 795.51 737.04 726.89MW-4S MW-3 MW-1 728.12 747.51MW-2 757.62 MW-8 MW-7S MW-6 MW-4D SCALEHOUSE MW-7D 731.80 SW-4 CREEK OP-3 FUTURE DISPOSAL AREAS PHASE 2 DISPOSAL AREA PHASE I DISPOSAL AREA BH-4 AMW-2 AMW-1 LFG-1 BH-5 CONSULTANT DESIGN PREPARED REVIEW APPROVED YYYY-MM-DD TITLE PROJECT No.Rev. PROJECTCLIENT Pa t h : \ \ g r e e n s b o r o \ C A D \ _ 2 0 1 2 \ 1 2 3 9 6 5 1 6 - W I - H i g h P o i n t \ P R O D U C T I O N \ _ F - 2 0 1 6 G W \ | F i l e N a m e : 1 2 3 9 6 5 1 6 1 5 F 0 0 2 . d w g IF T H I S M E A S U R E M E N T D O E S N O T M A T C H W H A T I S S H O W N , T H E S H E E T S I Z E H A S B E E N M O D I F I E D F R O M : A N S I D 0 1 i n 1239651616 PHASE 300 DRAWING 10 2016-10-14 BSD DYR DYR RPK WASTE INDUSTRIES OF HIGH POINT CONSTRUCTION AND DEMOLITION DEBRIS LANDFILL AND RECLAMATION FACILITY GUILFORD COUNTY, NORTH CAROLINA GROUNDWATER CONTOUR MAP JULY 14-15, 2016 0 FEET 200 400 SCALE LEGEND EXISTING 10' CONTOURS EXISTING 2' CONTOURS PROPERTY LINE STREAM TREELINE EXISTING ROAD PROPOSED OR EXISTING LIMITS OF WASTE MONITORING WELL LOCATION AND GROUNDWATER ELEVATION SURFACE WATER MONITORING POINT BARHOLE PROBE METHANE MONITORING LOCATION PROPOSED ASSESSMENT MONITORING WELL LOCATION PROPOSED METHANE MONITORING WELL LOCATION BENCH MARK SEDIMENT BASIN GROUNDWATER SURFACE CONTOURS GROUNDWATER FLOW SEGMENT USED TO CALCULATE GRADIENTi1 MW-3 SW-1 BM-1 SB-1 760 737.04 1. TOPOGRAPHIC CONTOUR INTERVAL = 2 FEET 2. GROUNDWATER SURFACE CONTOUR INTERVAL = 10 FEET 3. GROUNDWATER ELEVATIONS MEASURED ON JULY 14-15, 2016. 4. GROUNDWATER CONTOURS BASED ON LINEAR INTERPOLATION BETWEEN AND EXTRAPOLATION FROM KNOWN DATA, TOPOGRAPHIC CONTOURS AND KNOWN FIELD CONDITIONS. THEREFORE, GROUNDWATER CONTOURS MAY NOT REFLECT ACTUAL CONDITIONS. 5. GROUNDWATER CONTOURS LINES SHOW THE WATER TABLE SHAPE AND ELEVATION. THESE CONTOURS ARE INFERRED LINES FOLLOWING THE GROUNDWATER SURFACE AT A CONSTANT ELEVATION ABOVE SEA LEVEL. THE GROUNDWATER FLOW DIRECTION IS GENERALLY PERPENDICULAR TO THE GROUNDWATER SURFACE CONTOURS, SIMILAR TO THE RELATIONSHIP BETWEEN SURFACE WATER FLOW AND TOPOGRAPHIC CONTOURS. 6. THE GROUNDWATER ELEVATIONS FOR MW-4D AND MW-7D WERE NOT USED IN THE CONSTRUCTION OF GROUNDWATER CONTOURS. 7. DRAWING BASED ON SITE PLAN PLAN PREPARED BY JOYCE ENGINEERING, INC DATED JULY 7, 2004. 8. UPDATED TOPOGRAPHY PROVIDED FROM AERIAL SURVEY PREPARED BY SURVEYING SOLUTIONS, P.C., PHOTOGRAPHY DATE JANUARY 13, 2016. 9. PORE WATER SAMPLE LOCATIONS ARE APPROXIMATE. SITE SITE LOCATION MAP NOTES GOLDER ASSOCIATES NC, INC. PG C-399 WASTE INDUSTRIES USA, INC. AMW-1 LFG-1 BH-1