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2906__DavidsonPhase2_GWMR_DIN28294_20160921
This page intentionally left blank. September 2016 Semi-Annual Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill NC Solid Waste Permit No. 29-06 Prepared for: Davidson County Integrated Solid Waste 1242 Old Highway 29 Thomasville, North Carolina 27360-0024 January 2017 Prepared by: © 2017 Smith Gardner, Inc. This document is intended for the sole use of the client for which it was prepared and for the purpose agreed upon by the client and Smith Gardner, Inc. This page intentionally left blank. This page intentionally left blank. Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Table of Contents Page i Davidson County Phase 2 MSW Landfill NC Solid Waste Permit No. 29-06 September 2016 Groundwater Monitoring Report Table of Contents Page 1.0 INTRODUCTION ......................................................................................................... 1 2.0 SITE GEOLOGY ........................................................................................................... 1 3.0 SAMPLING LOCATIONS ............................................................................................. 1 4.0 SAMPLING PROCEDURES ......................................................................................... 1 5.0 FIELD & LABORATORY RESULTS .............................................................................. 2 5.1 Field Results .............................................................................................................. 2 5.2 Laboratory Analysis ................................................................................................... 2 5.2.1 Inorganic Constituents .................................................................................. 2 5.2.2 Organic Constituents .................................................................................... 3 5.2.3 Surface Water Results .................................................................................. 3 5.2.4 Leachate Analysis ......................................................................................... 3 6.0 STATISTICAL ANALYSIS ............................................................................................ 3 7.0 GROUNDWATER CHARACTERIZATION ...................................................................... 3 8.0 CONCLUSIONS .......................................................................................................... 4 FIGURE Figure 1 Potentiometric Surface Map TABLES Table 1 Groundwater Elevations Table 2 Field Parameters Table 3 Detected Constituents Table 4 Leachate Analytical Data Table 5 Aquifer Conductivity and Velocity Calculations APPENDICES Appendix A Monitoring Well Information Appendix B Laboratory Analytical Report Appendix C Time vs. Concentration Graphs Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Table of Contents Page ii This page intentionally left blank. Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Page 1 1.0 INTRODUCTION Smith Gardner, Inc. (S+G) was contracted by Davidson County to perform semi-annual groundwater monitoring at the Davidson County Phase 2 Lined MSW Landfill, permit number 29-06, as required by 15A NCAC 13B .1600. Sampling was conducted September 21-22, 2016. This report summarizes the event sampling procedures, field and laboratory results and groundwater characterization as required by NC Solid Waste Regulations. Summary tables, a potentiometric map and the laboratory analytical report are also included. 2.0 SITE GEOLOGY The Davidson County Landfill facility is located in the Piedmont Physiographic Province of North Carolina approximately three and a half miles northeast of the City of Lexington, NC. The Geologic Map of North Carolina (USGS, 1985) indicates that the site lies at the western margin of the Carolina Slate Belt; an area of predominantly volcanic and sedimentary rocks of Late Proterozoic to Cambrian age that have been metamorphosed and intruded by numerous igneous plutons. The boundary zone between the Carolina Slate Belt and the adjacent Charlotte Belt is known as the Gold Hill/Silver Hill shear zone. The site vicinity is underlain by volcanic rocks from the Flat Swamp Member of the Cid Formation and metavolcanic rocks of the Battleground Formation. 3.0 SAMPLING LOCATIONS The groundwater network for Phase 2 at Davidson County includes nine monitoring wells (MW- 1, MW-2, MW-3S, MW-4S, MW-5, MW-6S, MW-8, MW-9 and MW-10S), two surface water locations (SW-1 and SW-2) and one leachate sampling point (Leachate). During this event samples were not collected from MW-1 and MW-4S because they were dry. Monitoring wells MW-3D, MW-4D and MW-10D are designated as water level only locations. MW-1 serves as the background well for this site. A trip blank was submitted for quality control purposes. Available well logs are presented in Appendix A. Sampling locations are shown on Figure 1. 4.0 SAMPLING PROCEDURES Sampling procedures followed the protocols set forth in the site’s Water Quality Monitoring Plan1 and the North Carolina Water Quality Monitoring Guidance Document for Solid Waste Facilities (North Carolina Department of Environment and Natural Resources, Division of Waste Management). S+G personnel gauged each well to determine groundwater depth and purged three to five well volumes or until dry. Groundwater elevations are provided in Table 1. 1 Water Quality Monitoring Plan, Davidson County, Phase 2, Areas 1 and 2, Smith Gardner, Inc. January 2013, presented in the Permit to Construct application. Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Page 2 Environment 1, Inc. (NC Laboratory Certification # 10) provided laboratory prepared sample containers for the specified analytical procedures. Sample collection was performed using factory sealed teflon bailers. Groundwater samples were properly preserved, placed on ice and transported to the laboratory facility within the specified hold times for each analysis. Sampling wells and locations were inspected and found to be in good condition and free of obstructions. 5.0 FIELD & LABORATORY RESULTS 5.1 Field Results Temperature, pH, turbidity and specific conductance were measured in the field at the time of sampling via direct read instruments. The field parameter results are summarized in Table 2 and remain consistent with previously reported sampling events. 5.2 Laboratory Analysis Samples were transported to Environment 1, Inc., in Greenville, NC, a North Carolina certified laboratory (NC Wastewater ID #10). Laboratory analysis for groundwater included metals via EPA Test Method 200.8 and Appendix I Volatile Organic Compounds (VOCs) via EPA Test Method 8260B. Leachate samples were also analyzed for BOD, COD, total suspended residue, ammonia nitrogen, nitrate nitrogen, total phosphorus and sulfate via the SWS approved method noted in the laboratory analytical report. Analytical results were compared to the NC Division of Waste Management Solid Waste Section Quantitation Limits (SWSLs); 15A NCAC 2L.0200 (2LStandard) or SWS determined groundwater protection standard (GWP) and Federal Maximum Contaminant Level. Surface water results were compared with the NCAC 2B Standard for Class C waters (2B Standards). Most inorganic constituents were either below the method detection limit (MDL) or were “J-values” indicating a non-quantifiable value, reported by the laboratory as between the MDL and the SWSL. The laboratory results are presented in Appendix B. 5.2.1 Inorganic Constituents Chromium (MW-2, MW-6S and MW-10S) was the only inorganic constituent reported at a concentration above its 2L Standard in samples collected this event.. Two inorganic constituents: cobalt (MW-6S) and vanadium (MW-2, MW-5, and MW-6S) were reported at concentrations above their respective GWP standards in samples collected this event. Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Page 3 These inorganic constituents are naturally occurring in North Carolina and may also have been influenced by high sample turbidity. A summary of inorganic laboratory results is presented in Table 3. 5.2.2 Organic Constituents No organic constituents were detected in samples above their 2L or GWP Standards for the September monitoring event. 5.2.3 Surface Water Results No inorganic or organic constituents were detected above 2B Standards in surface water samples. Surface water results are shown in Table 3. 5.2.4 Leachate Analysis Leachate samples were collected from the leachate collection system. A summary of constituents detected in the leachate is included as Table 4. 6.0 STATISTICAL ANALYSIS No statistical analyses were performed on the analytical data based on the latest version of 15A NCAC 13B.1632 and .1633 effective April 1, 2011. Time vs. concentration graphs are included in Appendix C. 7.0 GROUNDWATER CHARACTERIZATION A potentiometric surface map was prepared from groundwater data from this sampling event. Groundwater flow velocities for this sampling event were calculated for monitoring wells using the equation: V = Ki/n where: K = hydraulic conductivity i = groundwater gradient n = porosity Groundwater velocities in the uppermost aquifer at the Phase 2 MSW Landfill ranged from 0.0118 feet/day (MW-3S) to 0.2210 feet/day (MW-9) and averaging 0.5357 feet/day. Calculations are included in Table 5. Groundwater elevations indicate the flow direction is generally northwest across the site; which is consistent with historically reported ground water flow patterns. The potentiometric surface map is included as Figure 1. Davidson County Phase 2 MSW Landfill September 2016 Groundwater Monitoring Report January 2017 Page 4 8.0 CONCLUSIONS Laboratory results indicate the water quality at the Davidson County Phase 2 Landfill is generally consistent with reported historical detections. Inorganic constituent detections are likely due to natural occurrence and their presence in the soil and rock formations, not impact from the landfill. In general, detected groundwater concentrations at the site have remained stable. The next groundwater monitoring event will be performed in March 2017; results will be reported to NCDEQ in accordance with 15A NCAC 13B.1600 et seq. FIGURES September 2016 Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill NC Solid Waste Permit No. 29-06 This page intentionally left blank. MW-2 TOC=664.06 DTW=12.67 GWE=651.39 MW-1 TOC=734.16 DTW=20.99 GWE=713.17 MW-9 TOC=683.25 DTW=22.45 GWE=660.80 MW-4D TOC=673.54 DTW=NA GWE=NA MW-4S TOC=673.82 DTW=23.46 GWE=650.36 MW-3S TOC=660.73 DTW=11.72 GWE=649.01 MW-3D TOC=660.91 DTW=NA GWE=NA MW-5 TOC=687.31 DTW=31.04 GWE=656.27 MW-7 MW-8 TOC=711.14 DTW=49.12 GWE=662.02 MW-6S TOC=703.25 DTW=37.73 GWE=665.52 MW-6D SW-1 SW-2 SW-3 MW-10D TOC=668.76 DTW=NA GWE=NA MW-10S TOC=668.58 DTW=19 GWE=649.58 G: \ C A D \ D a v i d s o n \ D a v d c o 1 6 - 4 \ s h e e t s \ D A V D C O - B 0 8 2 1 . d w g - 11 / 2 3 / 2 0 1 6 1 : 0 9 P M SM I T H 14 N . B o y l a n A v e n u e , R a l e i g h N C 2 7 6 0 3 NC L I C . N O . C - 0 8 2 8 ( E N G I N E E R I N G ) 91 9 . 8 2 8 . 0 5 7 7 GA R D N E R + DR A W N : AP P R O V E D : PR O J E C T N O : SC A L E : FI L E N A M E : DA T E : FIG U R E N O . PR E P A R E D B Y : PR E P A R E D F O R : © 2016 Smith Gardner, Inc. PO T E N T I O M E T R I C S U R F A C E M A P SE P T E M B E R 2 0 1 6 PH A S E 2 L A N D F I L L DA V I D S O N C O U N T Y , N C C. T . J . B. P . R . AS S H O W N 1 No v 2 0 1 6 DA V D C O 1 6 - 4 DA V D C O - B 0 8 2 1 (APPROX. 1,600 FT SW AT RAILROAD BRIDGE) N35° 50' 39.04" W80° 11' 30.23" (APPROX. 1,400 FT NE AT OLD NC 29 BRIDGE) N35° 51' 14.89" W80° 10' 56.85" N35° 51' 10.41" W80° 10' 35.15" (APPROX. 1,000 NE) AREA 2 MW-1 TOC= DTW= GWE= SW-1 PERIMETER ACCESS ROAD Th i s p a g e i n t e n t i o n a l l y l e f t b l a n k . TABLES September 2016 Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill Solid Waste Permit No. 29-06 This page intentionally left blank. Ta b l e 1 Gr o u n d w a t e r E l e v a t i o n s Da v i d s o n C o u n t y P h a s e 2 L a n d f i l l Se p t e m b e r 2 0 - 2 1 , 2 0 1 6 By: BR Date: 11/7/16 We l l We l l In s t a l l a t i o n Da t e La t i t u d e L o n g i t u d e We l l Di a m e t e r (i n c h e s ) To t a l We l l De p t h (f e e t b g s ) Gr o u n d Su r f a c e El e v a t i o n (f e e t am s l ) TO C El e v a t i o n (f e e t am s l ) De p t h t o Wa t e r * (f e e t ) Gr o u n d w a t e r El e v a t i o n (f e e t ) Screen In t e r v a l (f e e t b g s ) Screen Geology MW - 1 3 / 2 5 / 2 0 0 8 3 5 . 8 5 2 8 9 8 0 . 1 7 6 4 3 2 . 0 2 0 . 0 7 3 0 . 6 5 7 3 4 . 1 6 2 0 . 9 9 7 1 3 . 1 7 1 0 - 2 0 s a n d y s i l t MW - 2 8 / 1 2 / 2 0 0 8 3 5 . 8 4 9 9 4 8 0 . 1 8 3 5 1 2 . 0 1 4 . 5 6 6 1 . 0 5 6 6 4 . 0 6 1 2 . 6 7 6 5 1 . 3 9 9 . 5 - 1 4 . 5 s a n d y s i l t / g r a n i t e MW - 3 S 3 / 2 4 / 2 0 0 8 3 5 . 8 4 9 4 8 8 0 . 1 8 4 8 6 2 . 0 1 8 . 0 6 5 7 . 8 7 6 6 0 . 7 3 1 1 . 7 2 6 4 9 . 0 1 8 - 1 8 c l a y a n d s a n d MW - 3 D 3 / 2 6 / 2 0 0 8 3 5 . 8 4 9 4 8 8 0 . 1 8 4 8 4 2 . 0 4 0 . 5 6 5 8 . 0 8 6 6 0 . 9 1 N A - 3 5 . 5 - 4 0 . 5 g r a n i t e MW - 4 S 3 / 2 4 / 2 0 0 8 3 5 . 8 4 9 5 3 8 0 . 1 8 5 5 9 2 . 0 2 1 . 0 6 7 0 . 7 4 6 7 3 . 8 2 2 3 . 4 6 6 5 0 . 3 6 1 1 - 2 1 s a n d y s i l t w i t h c l a y MW - 4 D 3 / 2 6 / 2 0 0 8 3 5 . 8 4 9 5 2 8 0 . 1 8 5 5 7 2 . 0 3 7 . 0 6 7 0 . 6 0 6 7 3 . 5 4 N A - 3 2 - 3 7 d i o r i t e MW - 5 3 / 2 4 / 2 0 0 8 3 5 . 8 4 8 6 3 8 0 . 1 8 7 1 3 2 . 0 3 8 . 0 6 8 4 . 5 9 6 8 7 . 3 1 3 1 . 0 4 6 5 6 . 2 7 2 8 - 3 8 c l a y e y s i l t MW - 6 S 3 / 2 5 / 2 0 0 8 3 5 . 8 4 6 8 1 8 0 . 1 8 5 2 5 2 . 0 4 0 . 0 7 0 0 . 0 0 7 0 3 . 2 5 3 7 . 7 3 6 6 5 . 5 2 3 0 - 4 0 s a n d y s i l t w i t h g r a v e l MW - 8 3 / 2 4 / 2 0 0 8 3 5 . 8 4 7 3 6 8 0 . 1 8 4 0 4 2 . 0 5 8 . 6 7 0 8 . 2 1 7 1 1 . 1 4 4 9 . 1 2 6 6 2 . 0 2 4 8 . 6 - 5 8 . 6 d i o r i t e MW - 9 8 / 1 2 / 2 0 0 8 3 5 . 8 4 9 0 6 8 0 . 1 8 6 1 4 2 . 0 3 0 . 5 6 8 3 . 6 8 6 8 3 . 2 5 2 2 . 4 5 6 6 0 . 8 0 2 0 . 5 - 3 0 . 5 d i o r i t e MW - 1 0 S 9 / 2 1 / 2 0 0 4 3 5 . 8 5 0 8 3 8 0 . 1 8 3 0 6 2 . 0 2 7 . 0 6 6 5 . 1 7 6 6 8 . 5 8 1 9 . 0 0 6 4 9 . 5 8 1 2 - 2 7 s i l t y s a n d , c l a y & g r a v e l MW - 1 0 D 9 / 2 1 / 2 0 0 4 3 5 . 8 5 0 8 2 8 0 . 1 8 3 0 5 2 . 0 4 4 . 0 6 6 6 . 0 2 6 6 8 . 7 6 N A - 3 6 - 4 4 d i a b a s e No t e : Su r v e y d a t a f r o m M i c h a e l G r e e n a n d A s s o c i a t e s , P . A . am s l = a b o v e m e a n s e a l e v e l bg s = b e l o w g r o u n d s u r f a c e NA = w a t e r l e v e l d a t a n o t a v a i l a b l e We l l c o n s t r u c t i o n i n f o r m a t i o n f r o m w e l l l o g s ( p r o v i d e d i n A p p e n d i x A ) * D e p t h t o w a t e r m e a s u r e d f r o m T o p o f P V C C a s i n g =H : \ P r o j e c t s \ G r o u n d w a t e r M o n i t o r i n g \ 2 . G r o u n d w a t e r M o n i t o r i n g R ep o r t s \ D a v i d s o n \ 2 3 . D a v i d s o n 9 - 1 6 \ P h 2 \ 9 - 1 5 _ P h 2 d a v t a b l e s B R . x l sx Ta b l e 2 Fi e l d P a r a m e t e r s Da v i d s o n C o u n t y P h a s e 2 L a n d f i l l Se p t e m b e r 2 0 - 2 1 , 2 0 1 6 By: BR Date: 11/09/16 pH C o n d u c t i v i t y T e m p e r a t u r e (S t d . U n i t s ) ( u m h o s ) ( C e l s i u s ) MW - 2 6 . 7 7 9 0 1 8 . 3 3 4 . 2 MW - 3 S 6 . 3 0 1 0 0 1 8 . 2 7 . 5 4 MW - 5 6 . 0 7 8 0 1 6 . 3 1 3 6 MW - 6 S 6 . 8 1 1 2 0 1 6 . 6 6 5 . 1 MW - 8 6 . 8 2 1 1 0 1 6 . 2 1 9 . 9 MW - 9 5 . 8 5 1 1 0 1 7 8 . 0 9 MW - 1 0 S 6 . 9 2 1 0 0 1 6 . 5 9 6 . 4 SW - 1 7 . 2 0 1 1 0 2 3 . 4 1 1 SW - 2 7 . 0 3 1 1 0 2 3 . 5 8 . 0 9 No t e : Da t a C o l l e c t e d b y S m i t h G a r d n e r , I n c . p er s o n n e l Tu r b i d i t y (N T U ) We l l Fi e l d P a r a m e t e r s w e r e u n a b l e t o b e c o l l e c t e d f r o m M W - 1 a n d M W - 4 S th i s e v e n t b e c a u s e t h e y w e r e d r y =H : \ P r o j e c t s \ G r o u n d w a t e r M o n i t o r i n g \ 2 . G r o u n d w a t e r M o n i t o r i n g R e p o r t s \ D a v i d s o n \ 2 3 . D a v i d s o n 9 - 1 6 \ P h 2 \ 9 - 1 5 _ P h 2 d a v t a b l e s B R . x l s x Ta b l e 3 De t e c t e d C o n s t i t u e n t s Da v i d s o n C o u n t y L a n d f i l l - P h a s e 2 Se p t e m b e r 2 0 - 2 1 , 2 0 1 6 By: BR Date: 11/09/16 Pa r a m e t e r M D L S W S L 2L o r GW P * MC L 2 B M W - 2 M W - 3 S M W - 5 M W - 6 S M W - 8 M W - 9 M W - 1 0 S S W - 1 S W - 2 In o r g a n i c s An t i m o n y 0 . 0 5 6 1 * 6 6 4 0 < 0 . 0 5 < 0 . 0 5 < 0 . 0 5 < 0 . 0 5 0 . 1 0 J < 0 . 0 5 < 0 . 0 5 0 . 2 5 J 0 . 2 3 J Ar s e n i c 0 . 6 6 1 0 1 0 1 0 1 0 < 0 . 6 6 < 0 . 6 6 < 0 . 6 6 0 . 7 4 J < 0 . 6 6 < 0 . 6 6 < 0 . 6 6 < 0 . 6 6 < 0 . 6 6 Ba r i u m 0 . 0 2 1 0 0 7 0 0 2 0 0 0 2 0 0 0 0 0 2 9 . 5 J 2 9 . 1 J 4 9 . 2 J 3 7 6 2 . 5 J 5 3 . 8 J 5 8 . 8 J 3 3 . 8 J 3 1 . 1 J Be r y l l i u m 0 . 0 4 1 4 * 4 6 . 5 0 . 0 7 J < 0 . 0 4 0 . 1 8 J 0 . 2 9 J < 0 . 0 4 0 . 1 1 J 0 . 2 5 J 0 . 0 3 J 0 . 0 3 J Ca d m i u m 0 . 0 5 1 2 5 2 < 0 . 0 5 < 0 . 0 5 < 0 . 0 5 0 . 1 3 J < 0 . 0 5 1 0 . 0 8 J < 0 . 0 5 < 0 . 0 5 Co b a l t 0 . 0 4 1 0 1 * N E 4 3 . 2 J 0 . 3 2 J 7 . 1 J 15 0. 2 4 J 1 . 9 J 8 . 4 J 0 . 6 2 J 0 . 7 2 J Co p p e r 0 . 0 7 1 0 1 0 0 0 1 3 0 0 7 1 5 0 . 7 1 J 3 6 1 2 2 1 . 5 J 1 5 4 5 2 . 2 J 2 . 2 J Ch r o m i u m , t o t a l 0 . 0 6 1 0 1 0 1 0 0 5 0 17 0. 7 1 J 8 . 4 J 11 2. 1 J 4 . 6 J 35 < 0.06 0 . 3 4 Le a d 0 . 0 6 1 0 1 5 1 5 2 5 1 . 3 J < 0 . 0 6 3 . 9 J 3 . 8 J 0 . 1 1 J 1 . 2 J 2 . 3 J 0 . 1 9 J 0 . 2 4 J Ni c k e l 0 . 0 6 5 0 1 0 0 N E 8 8 5 . 2 J 0 . 6 9 J 1 0 . 8 J 1 1 . 3 J 1 . 1 J 6 . 0 J 1 4 . 2 J 1 . 6 J 3 . 5 J Se l e n i u m 0 . 5 4 1 0 2 0 5 0 5 < 0 . 5 4 0 . 8 7 J < 0 . 5 4 0 . 8 5 J 1 . 1 J < 0 . 5 4 < 0 . 5 4 < 0 . 5 4 < 0 . 5 4 Si l v e r 0 . 0 6 1 0 2 0 1 0 0 0 . 0 6 0 . 0 8 J < 0 . 0 6 < 0 . 0 6 0 . 0 6 J < 0 . 0 6 < 0 . 0 6 0 . 1 5 J < 0 . 0 6 < 0 . 0 6 Th a l l i u m 0 . 0 5 5 . 5 0 . 2 8 * 2 0 . 4 7 < 0 . 0 5 < 0 . 0 5 < 0 . 0 5 0 . 1 6 J < 0 . 0 5 0 . 0 6 J < 0 . 0 5 < 0 . 0 5 < 0 . 0 5 Va n a d i u m 0 . 3 6 2 5 0 . 3 * N E N E 2 1 . 2 J 7 . 1 J 41 5 5 7. 0 J 2 1 . 6 J 39 2.1 J 2 . 2 J Zi n c 1 . 6 1 1 0 1 0 0 0 5 0 0 0 5 0 5 . 7 J 2 . 8 J 4 5 1 1 9 < 1 . 6 1 1 3 3 3 5 . 4 J 5 . 9 J Or g a n i c s Ac e t o n e 9 . 0 6 1 0 0 6 0 0 0 N E 2 0 0 0 < 9 . 0 6 3 8 . 4 J < 9 . 0 6 < 9 . 0 6 < 9 . 0 6 1 1 . 4 J < 9 . 0 6 < 9 . 0 6 < 9 . 0 6 No t e : MD L - M e t h o d D e t e c t i o n L i m i t SW S L - So l i d W a s t e S e c t i o n Q u a n t i t a t i o n L i m i t s MW - 1 a n d M W - 4 S w e r e n o t s a m p l e d t h i s e v e n t b e c a u s e t h e y w e r e d r y . GW P - G r o u n d w a t e r P r o t e c t i o n S t a n da r d ( I n d i c a t e d w i t h a * ) T a b l e u n i t s a r e p r e s e n t e d i n u g / l . 2L - Gr o u n d w a t e r S t a n d a r d s ( 1 5 A N C A C 2 L 0 2 0 0 ) La b d a t a a n a l y s i s b y E n v i r o n m e n t 1 , I n c . r e p o r t d a t e d 1 0 / 3 1 / 2 0 1 6 , I D # 6 0 5 9 A . MC L - Fe d e r a l M a x i m u m C o n t a m i n a n t L i m i t 2B - NC A C 2 B S t a n d a r d f o r C l a s s C w a t e r s Bo l d - Co n s t i t u e n t s d e t e c t e d a b o v e 2 L o r G W P J- La b o r a t o r y d e f i n e d b e t w e e n M D L a n d S W S L < M D L - No t d e t e c t e d a t o r a b o v e M D L NE - St a n d a r d N o t E s t a b l i s h e d H:\ P r o j e c t s \ G r o u n d w a t e r M o n i t o r i n g \ 2 . G r o u n d w a t e r M o n i t o r i n g R e p o rt s \ D a v i d s o n \ 2 3 . D a v i d s o n 9 - 1 6 \ P h2 \ 9 - 1 5 _ P h 2 d a v t a b l e s B R . x l s x Th i s p a g e i n t e n t i o n a l l y l e f t b l a n k . Table 4 Leachate Analytical Data Davidson County Phase 2 Landfill September 21-22, 2016 By: BR Date: 11/08/2016 Parameter Unit Leachate BOD mg/l 24 COD mg/l 1030 Total Suspended Residue mg/l 276 Ammonia Nitrogen as N mg/l 798 Total Phosphorus mg/l 7.52 Antimony ug/l 2.9 J Arsenic ug/l 11 Barium ug/l 188 Beryllium ug/l 0.23 J Cadmium ug/l 1 Cobalt ug/l 24 Total Chromium ug/l 58 Copper ug/l 22 Lead ug/l 2.6 J Nickel ug/l 191 Silver ug/l 0.32 J Vanadium ug/l 46 Zinc ug/l 42 1,2-Dichloropropane ug/l 0.30 J 1,4-Dichlorobenzene ug/l 5.6 2-Butanone ug/l 2.8 J 4-Methyl-2-pentanone ug/l 2.4 J Acetone ug/l 11 J Benzene ug/l 22.8 Chlorobenzene ug/l 1.1 J Ethylbenzene ug/l 29.2 trans-1,2-Dichloroethene ug/l 0.90 J Toluene ug/l 183 Xylenes ug/l 61.4 Note:J-values are laboratory defined between the SWSL and MDL. =H:\Projects\Groundwater Monitoring\2. Groundwater Monitoring Reports\Davidson\23. Davidson 9-16\Ph2\9-15_Ph2 dav tables BR.xlsx This page intentionally left blank. Ta b l e 5 Aq u i f e r C o n d u c t i v i t y a n d V e l o c i t y C a l c u l a t i o n s Da v i d s o n C o u n t y P h a s e 2 L a n d f i l l Se p t e m b e r 2 0 - 2 1 , 2 0 1 6 By: BR Date: 11/08/2016 We l l N u m b e r A q u i f e r Co n d u c t i v i t y (f t / d a y ) Co n d u c t i v i t y (f t / m i n ) As s u m e d Po r o s i t y ( n ) Gr a d i e n t ( I ) Ve l o c i t y (f t / d a y ) MW - 2 Sa n d y S i l t 6. 7 5 E - 0 2 4 . 6 9 E - 0 5 0 . 1 8 0 . 0 6 8 8 0 . 0 2 5 8 MW - 3 s Sa n d 8. 6 0 E - 0 2 5 . 9 7 E - 0 5 0 . 2 0 0 . 0 2 7 5 0 . 0 1 1 8 MW - 5 Cl a y e y S i l t 4. 3 1 E - 0 1 2 . 9 9 E - 0 4 0 . 1 8 0 . 0 4 5 3 0 . 1 0 8 5 MW - 6 s Sa n d a n d G r a v e l 4. 6 4 E - 0 1 3 . 2 2 E - 0 4 0 . 2 2 0 . 0 2 2 6 0 . 0 4 7 7 MW - 8 Di o r i t e 4. 9 0 E - 0 1 3 . 4 0 E - 0 4 0 . 1 0 0 . 0 1 6 0 0 . 0 7 8 4 MW - 9 Di o r i t e 7. 2 0 E - 0 1 5 . 0 0 E - 0 4 0 . 1 0 0 . 0 3 0 7 0 . 2 2 1 0 Av e r a g e : 0 . 5 3 5 7 No t e s : NA = W e l l h a d i n s u f f i c i e n t w a t e r t o p e r f o r m S l u g T e s t , o r i n s u f f i e n e n t d a t a t o c o m p l e t e c a l c u l a t i o n . Po r o s i t y a s s u m e d b a s e d u p o n s o i l t y p e f r o m m o n i t o r i n g w e l l b o r i n g l o g . Ve l o c i t y C a l c u l a t e d b y e q u a t i o n V = K I / n Gr a d i e n t f o r b e d r o c k w e l l s a s s u m e d t o b e t h e s a m e a s f o r u n c o n s o l i d a t e d a q u i f e r i n Gr a d i e n t c a l c u l a t e d f r o m S e p t e m b e r 2 0 1 6 p o t e n t i o m e t r i c s u r f a c e . +H : \ P r o j e c t s \ G r o u n d w a t e r M o n i t o r i n g \ 2 . G r o u n d w a t e r M o n i t o r i n g R e p o r t s \ D a v i d s o n \ 2 3 . D a v i d s o n 9 - 1 6 \ P h 2 \ 9 - 1 5 _ P h 2 d a v t a b l e s B R . x l s x Th i s p a g e i n t e n t i o n a l l y l e f t b l a n k . Appendix A Monitoring Well Information September 2016 – Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill Solid Waste Permit No. 29-06 This page intentionally left blank. FIELD BOREHOLE LOG BOREHOLE NUMBER PROJECT NAME: LOACATION: DRILLING CO: DRILLING METHOD: FIELD PARTY: GEOLOGIST: DATE BEGUN: COMPLETED: TOTAL DEPTH: GROUND SURFACE ELEVATION: Depth (ft) Time Date STATIC WATER LEVEL (BLS) DE P T H BL O W C O U N T SA M P L I N G M E T H O D RE C O V E R Y DR I L L M E T H O D DESCRIPTION LI T H O L O G Y WE L L IN S T A L L A T I O N 0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 15.0 16.0 17.0 18.0 19.0 20.0 21.0 22.0 23.0 24.0 25.0 26.0 27.0 0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 15.0 16.0 17.0 18.0 19.0 20.0 21.0 22.0 23.0 24.0 25.0 26.0 27.0 DE P T H G. N. Richardson & Associates, Inc. 14 North Boylan Avenue, Raleigh NC 27603 (919) 828-0577 Page 1 of 1 TOP OF CASING ELEVATION: PZ-37 HSA Davidson County - Phase 2 Lexington, NC Engineering Tectonics, P.A. R. Barron J. Smyth 9/21/04 9/21/04 27 SS SS SS SS SS 18" 10" 8" 3" 2" HSA SILTY SAND: Dry to moist, tan and black, silty sand granitic sarprolite with Mn staining. CLAYEY SANDY GRAVEL: Moist red brown clayey sandy gravel sarprolite. CLAYEY GRAVEL: Wet clayey gravel saprolite with large quartz grains. Boring terminated at 27 feet below grade. 11,21,37 6,9,15 4,8,28 50/3 50/2 19 2 pm 9/21/04 16.98 10/12/04 4:15 FIELD BOREHOLE LOG BOREHOLE NUMBER PROJECT NAME: LOACATION: DRILLING CO: DRILLING METHOD: FIELD PARTY: GEOLOGIST: DATE BEGUN: COMPLETED: TOTAL DEPTH: GROUND SURFACE ELEVATION: Depth (ft) Time Date STATIC WATER LEVEL (BLS) DE P T H BL O W C O U N T SA M P L I N G M E T H O D RE C O V E R Y DR I L L M E T H O D DESCRIPTION LI T H O L O G Y WE L L IN S T A L L A T I O N 0.0 1.0 2.0 3.0 4.0 5.06.07.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 15.0 16.0 17.018.019.020.0 21.0 22.0 23.0 24.0 25.0 26.0 27.0 28.0 29.0 30.031.032.033.0 34.0 35.0 36.0 37.0 38.0 39.0 40.0 41.0 42.0 43.044.0 0.0 1.0 2.0 3.0 4.0 5.06.07.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 15.0 16.0 17.018.019.020.0 21.0 22.0 23.0 24.0 25.0 26.0 27.0 28.0 29.0 30.031.032.033.0 34.0 35.0 36.0 37.0 38.0 39.0 40.0 41.0 42.0 43.044.0 DE P T H G. N. Richardson & Associates, Inc. 14 North Boylan Avenue, Raleigh NC 27603 (919) 828-0577 Page 1 of 1 TOP OF CASING ELEVATION: PZ-37d HSA Davidson County - Phase 2 Lexington, NC Engineering Tectonics, P.A. R. Barron J. Smyth 9/21/04 10/14/06 44 SS SS SS SS SS 18" 10" 8" 3" 2" HSA AH/RC SILTY SAND: Dry to moist, tan and black, silty sand granitic sarprolite with Mn staining. CLAYEY SANDY GRAVEL: Moist red brown clayey sandy gravel sarprolite. CLAYEY GRAVEL: Wet clayey gravel saprolite with large quartz grains. AR at 30'. Air hammer to 34' to set outer casing in rock. DIABASE: Rock cored from 34' to 44' REC=95%, RQD=39%. Weathered diabase. Boring terminated at 44 feet. 11,21,37 6,9,15 4,8,28 50/3 50/2 Appendix B Laboratory Analytical Report September 2016 Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill NC Solid Waste Permit No. 29-06 This page intentionally left blank. Appendix C Time vs. Concentration Graphs September 2016 Groundwater Monitoring Report Davidson County Phase 2 MSW Landfill NC Solid Waste Permit No. 29-06 This page intentionally left blank. Pa g e 1 Va n a d i u m Mu l t i - W e l l T i m e - S e r i e s G r a p h Sa m p l e D a t e C o n c e n t r a t i o n ( p p b ) 0 10 0 20 0 30 0 40 0 50 0 MW - 5 MW - 6 S MW - 1 0 S 8 / 2 6 / 2 0 0 8 1 0 / 2 1 / 2 0 0 9 1 2 / 1 6 / 2 0 1 0 2 / 1 0 / 2 0 1 2 4 / 6 / 2 0 1 3 6 / 1 / 2 0 1 4 7/27/2015 9/21/2016 Pa g e 1 Co b a l t , t o t a l Ti m e - S e r i e s G r a p h o f M W - 6 S Sa m p l e D a t e C o n c e n t r a t i o n ( p p b ) 050 10 0 15 0 20 0 8 / 2 6 / 2 0 0 8 1 0 / 2 1 / 2 0 0 9 1 2 / 1 6 / 2 0 1 0 2 / 1 0 / 2 0 1 2 4 / 6 / 2 0 1 3 6 / 1 / 2 0 1 4 7/27/2015 9/21/2016 Pa g e 1 Ch r o m i u m , t o t a l Mu l t i - W e l l T i m e - S e r i e s G r a p h Sa m p l e D a t e C o n c e n t r a t i o n ( p p b ) 050 10 0 15 0 20 0 25 0 30 0 MW - 2 MW - 6 S MW - 1 0 S 8 / 2 6 / 2 0 0 8 1 0 / 2 1 / 2 0 0 9 1 2 / 1 6 / 2 0 1 0 2 / 1 0 / 2 0 1 2 4 / 6 / 2 0 1 3 6 / 1 / 2 0 1 4 7/27/2015 9/21/2016 Th i s p a g e i n t e n t i o n a l l y l e f t b l a n k .