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HomeMy WebLinkAbout20161268_Eval of Impacts of PWS GW Wells_20120208Evaluation of Impacts to Public Water Supply Groundwater Wells US 17 Corridor Study, NCDOT TIP Project U -4751 & R -3300 New Hanover and Pender Counties February 8, 2012 Introduction State Transportation Improvement Program (STIP) projects U -4751 and R -3300 involve the construction of Military Cutoff Road Extension in New Hanover County and the US 17 Hampstead Bypass in New Hanover and Pender Counties. Because the projects may share a common terminus, they are being evaluated together in a single environmental document. A Draft Environmental Impact Statement (DEIS) for the project was signed by the North Carolina Department of Transportation (NCDOT) and the US Army Corps of Engineers on July 28, 2011. In their November 15, 2011 review of the DEIS and at NCDOT's December 15, 2011 agency coordination meeting (Concurrence Point 3 informational merger meeting), EPA expressed concerns and indicated further review of the potential effects of the project on the local public water supply is warranted. To further evaluate potential impacts to groundwater from the proposed project, the following analysis incorporated a review of existing literature and communications with representatives from the Cape Fear Public Utility Authority and the Public Water Supply Section of the NC Department of Environment and Natural Resources. The intent of the review is to determine if the proposed project is likely to result in impacts to the quantity or quality of the Cape Fear Public Utility Authority's groundwater public water supply system. Project Description For project U -4751, NCDOT proposes to extend Military Cutoff Road as a six -lane divided roadway on new location from its current terminus at US 17 (Market Street) in Wilmington north to an interchange with the US 17 Wilmington Bypass Qohn Jay Burney Jr. Freeway). Limited and full control of access is proposed. For project R -3300, NCDOT proposes to construct the US 17 Hampstead Bypass as a freeway on new location. The US 17 Hampstead Bypass may connect to the proposed Military Cutoff Road Extension at the existing US 17 Wilmington Bypass and extend to existing US 17 north of Hampstead. Full control of access is proposed for the US 17 Hampstead Bypass. The project area is shown in Figure 1. The current detailed study alternatives are shown in Figure 2. The purpose of the US 17 Corridor Study project is to improve the traffic carrying capacity and safety of the US 17 and Market Street corridor in the project area. Because of its location within a wellhead protection area, the Military Cutoff Road Extension project is the focus of this review. Military Cutoff Road Extension Alternatives M1 and M2 are new location alternatives extending Military Cutoff Road from Market Street to the US 17 Wilmington Bypass. The City of Wilmington adopted an official transportation corridor map for the proposed extension of Military Cutoff Road on August 8 2005 Alternative M1 follows the adopted corridor map alignment Alternative M 1 begins at a proposed interchange at Military Cutotf Road and Market Street The alternative extends north through vacant County property between the two sections of Ogden Park and residential areas Alternative M1 turns northwest and ends near Plantation Road and Crooked Pine Road at a proposed interchange with the US 17 Wilmington Bypass approximately midway between 140 and Market Street • Alternative M2 begins at a proposed interchange at Military Cutoff Road and Market Street Alternative M2 follows the Alternative M1 alignment for approximatelj two miles Alternatn e M2 then turns northeast and extends through mostly undeveloped property to a proposed interchange with the US 17 Wilmington Bypass approximately one mile west of Market Street Military Cutoff Road Extension incorporates two typical sections • From the proposed interchange at Market Street to approximately 0 9 mile north of Torchwood Boulevard Six lanes (three in each direction) with a 30 foot median and curb and gutter Two 12 foot inside lanes and one 14 foot outside lane (to accommodate bicycles) with two foot curb and gutter and a ten foot berm are proposed in each direction From approximately 0 9 mile north of Tonbwood Boulevard to the proposed interchange at the US 17 LYlilmzngton Bypass Six 12 foot lanes (three in each direction)rwith 14 foot outside shoulders (12 foot paved) A 46 foot median is proposed A variable right of way width of 150 feet to 350 feet is proposed for Military Cutoff Road Extension Pubhc Water Supply The Cape Fear Public Utility Authority (CFPUA) provides water for New Hanover County from several sources including surface water groundwater and purchases from other systems Their 2010 Integrated Water Resources Master Plan indicates that total demand represented 28 percent of the total available water supply (all sources) in 2010 Future demand including the sale of water to other systems is projected to represent 25 percent of the available supply in 2030 and 39 percent of the available supply in 2060 The CFPUA has several existing and proposed well sites associated with their groundwater nanofiltration water treatment plant (WTP) which was brought on line in 2009 and distributes water to portions of northern New Hanover County The WTP is located adjacent to proposed Military Cutoff Road Extension Alternatives M1 and M2 where they share an ahgnment Just north of Torchwood Boulevard The alignment shown on the official transportation corridor map for the proposed extension of Military Cutoff Road adopted in 2005 was a factor in the selection of the CFPUA well sites (personal communication Gary McSmith CFPUA) Roads are commonly found within wellhead protection areas across the state Existing state rules and regulations are relied on to manage risks associated with transportation infrastructure located within wellhead protection areas managed through the non regulatory approach (personal communication Gale Johnson NCDENR PWS) According to the U.S. Geologic Survey, the principal groundwater supply aquifers in New Hanover County — the surficial, Castle Hayne and Peedee — were formed from the late Cretaceous to Quarternary aged geologic formations. Approximately 30 percent of all freshwater used in New Hanover County in 2005 was supplied from these three aquifers. The CFPUA groundwater nanofiltration WTP wells draw from the Castle Hayne and Peedee aquifers. The NC Division of Water Resources website states that aquifer systems are hydraulically connected materials (sands, limestone, and fractured rock) that provide water through a properly constructed well open to those materials. In the coastal plain, an aquifer is typically composed of one to several layers of eastward thickening, permeable sands or limestone split by discontinuous, clay -rich materials. Confining units, consisting of clay -rich sediments, exist above and below an aquifer. These confining units are more continuous clay layers and separate the aquifers. The surficial or unconfined aquifer overlies all the confined aquifers in the coastal plain. The Peedee and Castle Hayne aquifers form regional aquifers. 7,�� � w..nl ^te.. ..11 n.•. • teedx - . 14Y trwbo.l_N • e , urn ew.r.. Ili ; , • S , Peedee Aquifer The Castle Hayne aquifer is widely used in the eastern portions of the coastal plain at elevations of 65 to -1,103 feet, averaging -144 feet. The Castle Hayne aquifer ranges from 6 to 1,105 feet thick and averages 164 feet thick. The aquifer is composed of limestone, sandy limestone, and sand and is considered a semi - confined aquifer. It is the most productive aquifer in North Carolina. Wells typically yield 200 -500 gallons per minute, but can exceed 2,000 gallons per minute. In addition to supplying some industrial and agricultural usages, a number of municipal well fields are supplied by the Castle Hayne aquifer. These municipal areas include the City of Wilmington, New Hanover beach towns, the New Hanover County water system, Topsail Island, and Surf City. 3 The Peedee aquifer is present in the central to southeastern portion of the coastal plain at elevations of 114 to -1,849 feet, averaging -164 feet. The Peedee aquifer ranges from 2 to 1,001 feet thick and averages 141 feet thick. The aquifer is composed of fine to medium sand and is considered a confined aquifer. Wells typically yield up to 200 gallons per minute. The pink area shown in the figure to the left shows the salty extent of the Peedee aquifer. The green area shows the fresh extent and the yellow area is the transitional area between the salty and fresh water. �} Iltrr�n j tin e.r.tf^.M cdtez• ,••eyrrtrlki trv:k -,.r' .� tdpeabt ...r t,^ Na.nine ^ •ryrrell llz•ir ar. v • Glrerr o - Lrtir • • ' k ,i Castle Hayne Aquifer Wellhead Protection Area The proposed Military Cutoff Road Extension project is located within the wellhead protection area established for the public water supply wells operated by the CFPUA. The NC Wellliead Protection Guidebook states that a wellhead protection area is the part of the landscape, both above and below ground, which contributes water that will eventually reach the well. By identifying the contributing area for the well, strategies can be established to manage certain activities to significantly reduce the chance the well might be contaminated. CFPUA's wellhead protection area was established during the preparation of their Wellhead Protection Plan. Each well was assigned an individual wellhead protection radius to identify the area to be managed to reduce the likelihood of contamination of the well. Methods to determine radii for wells withdrawing from the semi - confined Castle Hayne aquifer and the confined Peedee aquifer differed based on information provided by the North Carolina's approved Wellhead Protection Program. Because there was considerable overlap when the wellhead protection areas were identified, the outer boundary of the areas were smoothed and enlarged to encompass an area approximately equal to the combined areas of each individual wellhead protection area (see Figure 3). Figure 4 shows the location of the proposed project in relation to CFPUA's Wellhead Protection Area 1 and existing CFPUA well sites. With the exception of a portion of the proposed interchange at Market Street for both alternatives and the northern quadrants of the Alternative M1 interchange at the US 17 Wilmington Bypass, both Military Cutoff Road Extension Alternatives are located within the wellhead protection area. A portion of Hampstead Bypass Alternative U, where it travels along the existing US 17 Wilmington Bypass, is also located in the wellhead protection area. Wellhead Protection Area 1 is approximately 7,712 acres in size. The well sites shown in Figure 4 are depicted with a 100 -foot buffer around the wellhead. Regulations for public water supply wells stipulate that the area within 100 feet of a well be owned or controlled by the person supplying the water (15A NCAC 18C .0203). The buffer allows the water supplier to protect the well lot from potential sources of pollution and construct landscape features for drainage and diversion of pollution. Table 1 lists the existing CFPUA wells in the project area. The table identifies the aquifer each well draws from and the distance from the wellhead to the proposed Military- Cutoff Road Extension slope stake boundary. The wellheads located closest to Military Cutoff Road Extension at Site B (Well IDs 22 and B -CH) are positioned at a higher elevation than the proposed roadway grade. In addition to the existing wells, CFPUA has plans to expand its infrastructure and add new wells in the future. These "future" well sites are depicted by an "X" on Figure 5. Military Cutoff Road Extension Alternative M2 would cross existing and proposed water lines associated with the proposed expansion area. The CFPUA indicates that future well sites were selected based on aquifer access, anticipated yields, and because the area is undeveloped, which protects the well heads from contamination. 4 Table 1. Summary of CFPIrA Wells in the Vicinity of Nlilitan' Cutoff Road Fxtension (NICRE) Well I o_._ CAM Well 1 I;J Well Depth I Aquifer WHPP I Radius Yield /___) Closest MCRE Alternative Distance from Well -head to MC;ZL Slope II P 1 GU Peedee 2,000 600 M1, Nu 807 Q 16 175 Peedee 3,000 500 M1, M2 1,855 B 22 170 Peedee 3,000 640 M1, M2 126 A 23 170 Peedee 3,000 600 Nil, M2 1,490 M 28 175 Peedee 25000 750 Ml, M2 544 N 29 175 Peedee 2,000 750 M1, M2 781 O 30 175 Peedee 2,000 570 M1, M2 1,006 k A -CH 95 Castle Hayne 2,965 600 Ml, M2 1,490 B B -CH 80 Castle Hayne 3,097 640 M1, M2 126 C C -CH 105 Castle Hayne 2,406 600 M2 1,402 C C -PD 168 Peedee 3,000 570 M2 1,379 F F -CH 105 Castle Hayne 2,273 600 M2 764 F F -PD 170 Peedee 3,000 570 M2 770 G G -CH 90 Castle Hayne 2,440 500 M2 523 G G -PD 173 Peedee 3,000 570 M2 546 H H -CH 100 Castle Hayne 2,471 600 M2 184 H H -PD 175 Peedee 3,000 570 M2 159 1 I -CH 95 Castle Hayne 2,206 400 M2 2,109 1 I -PD 175 Peedee 3,000 570 M2 2,081 J J -CH 100 Castle Hayne 2,493 600 M2 546 J J -PD 175 Peedee 3,000 570 M2 573 K K -CH 100 Castle Hayne 2,713 200 M1, M2 1,187 K K -PD 175 Peedee 3,000 600 M1, M2 1,141 L L -CH 85 Castle Hayne 3,054 500 M2 810 L L -PD 170 Peedee 3,000 640 M2 790 Wellhead Protection Plan The CFPI'A developed a Wellhead Protection Plan (WHPP) in coordination with the NC Department of Environment and Natural Resources' Public Water Supply Section. The CFPUA finalized its plan in December 2009. The purpose of the WHPP is to manage the land areas surrounding the wells in order to prevent contamination of the public water supply. The CFPUA's WHPP is non - regulatory and identifies strategies to manage the wellhead protection area for their northern water system. In addition to delineating the wellhead protection area, the WHPP identifies potential contamination sources, establishes wellhead protection area management actions, describes an emergency contingency plan for alternative water supply sources, describes an emergency response plan for incidents that may impact water quality, and outlines a public education program. A potential contaminant source (PCS) is any substance or activity that could adversely affect the quality of the drinking water supply. The PCS inventory is a complete listing, including mapped locations, of past and present land use activities within the wellhead protection area that threaten groundwater quality. The CFPUA identified potential contaminant sources using guidance provided in the NC Wellhead Protection Guidebook. Ranking criteria were applied to each potential contaminant source to identify overall risk to wells. A risk ranking of "lower ", "moderate" or "higher" was established for potential contaminant sources by totaling points assigned under several criteria including proximity, quantity, relative tonicity and likelihood of occurrence (see Table 2). Potential contaminant sources with a combined ranking between 0 and 7 were considered a lower risk while those with a combined ranking of 10 or higher were considered a higher risk. Fable 2. Cape Fear Public Utility Authority Risk Criteria Major roads are included under the "likelihood of occurrence" category as a higher risk. No existing or proposed roads were included in the list of identified potential contaminant sources in the WHPP. The NC Wellhead Protection Guidebook includes freeways /state highways as a moderate risk. The Cape Fear Public Utility Authority 2011 Annual Report includes information on their Emergency Management Plan: The Cape Fear Public Utility Authority abides by state and federal emergency management regulations, for all- hazards mitigation, preparedness, response and recovery. The program coordinator develops, maintains, and trains Authority employees on the Emergency Response Plan and its associated Incident Action Plans. Proactively working to meet EPA's seventeen National Incident Management System roxnn ` to Re attve Likelihood 0f—] Well Quantity lik Toxicity Occurrence bower (1 pt.) > 1,500 feet < 100 gal. Grease Car Wash < 100 lbs. Chloride Cemetery Funeral home Mini- storage Substation Moderate (2 pts.) 750 -1,500 ft. 100 -2,000 gal. Pertoleum AST 100 — 2,000 lbs. Fertilizers Auto Repair Sewage Lift Station Bacteria Pesticide/ herbicide/ fertilizer appl. / storage UST (gas station Higher (3 pts.) < 750 feet > 2,000 gal. Pesticides Chemical Storage > 2,000 lbs. Herbicides Cleaners Metals Industry Solvents Major Road Railroad Major roads are included under the "likelihood of occurrence" category as a higher risk. No existing or proposed roads were included in the list of identified potential contaminant sources in the WHPP. The NC Wellhead Protection Guidebook includes freeways /state highways as a moderate risk. The Cape Fear Public Utility Authority 2011 Annual Report includes information on their Emergency Management Plan: The Cape Fear Public Utility Authority abides by state and federal emergency management regulations, for all- hazards mitigation, preparedness, response and recovery. The program coordinator develops, maintains, and trains Authority employees on the Emergency Response Plan and its associated Incident Action Plans. Proactively working to meet EPA's seventeen National Incident Management System (NIMS) compliance objectives for the water sector; staff continues to refine emergency preparedness by planning, and implementing standardized response and industry best practice measure as recommended by EPA, FENLA, and North Carolina regulatory agencies. The Authority also participates on the New Hanover County Local Emergency Planning Committee, which plans for hazardous materials response incidents within the community. We have also been active in planning and participating in community - wide drills and exercises with our state, county and city emergency response partners. Evaluation of Potential Impacts Potential impacts to the CFPUA public water supple could occur through actions that would limit the availability of the water the system provides or actions that compromise the safety of the water supply through contamination. Impacts to the supply of water could result from direct impacts to system infrastructure or through actions that limit groundwater recharge. Impervious surfaces, such as roads, increase the amount of runoff during rainfall events and could both reduce groundwater recharge and increase pollutant loadings. Other potential impacts to groundwater quality are accidental spills and wrecks on the proposed roadway. If a contaminant reaches groundwater within the well system's contribution area, the contaminant can move with the groundwater into the well. If the contributing area for the well is identified and management strategies are set in place to manage certain activities, the possibility that the well might become contaminated can be substantially reduced. As previously noted, the CFPUA has delineated a wellhead protection area for their northern water supply and developed management strategies in a wellhead protection plan. Because the Peedee aquifer is semi- confined and Castle Hayne aquifer is confined, they are less likely to experience water quality impacts than surface waters or surficial aquifers (personal communication, Gale Johnson, NCDENR PWS). [dater Supply At the time of completion of the DEIS for the project, it was expected that Alternative M1 would cross two CFPUA well sites and Alternative M2 would cross four existing well sites and a proposed well site. CFPUA estimated that a loss of access to the future sites could result in a reduction of up to six million gallons per day of anticipated future water supply. The alignments of both Alternatives M1 and M2 have been modified since completion of the DEIS. Neither alternative will cross any existing or future CFPUA well sites. Although both Military Cutoff Road Extension alternatives would cross potable and raw water lines, any impacted water lines would be relocated as part of the project and returned to service. The project will not decrease the capacity of the existing and planned water supply infrastructure. The NC Division of Water Resources water budget for the NC Coastal Plain indicates a very small percentage of rainfall infiltrates into the confined aquifer system. Most rainfall is lost to evapotranspiration, runoff, or infiltrates into the shallow ground water system that then discharges to local rivers and streams. Using the impact boundary (slope stake + 25 feet), Military Cutoff Road Extension Alternative M1 would encompass approximately 286 acres and Alternative M2 would 7 encompass approximately 303 acres. Based on the size and confined natures of the Castle Hayne and Peedee aquifers and CFPUA data on available water supply versus demand, the proposed project is not expected to affect the recharge of the aquifers or the amount of water available for withdrawals from existing public water supply system wells.. Water Quality Accidental Spills Accidental spills due to traffic accidents or other causes probably represent the greatest potential impact of the proposed project on the water supply wells. The potential for an accidental spill in the Well Head Protection Area is probably not greater with construction of the project, as several major roadways, including the US 17 Wilmington Bypass and Market Street, already exist in the Well Head Protection Area. The concern with this project is that a major roadway will now be closer to some wellheads than current conditions. Even though the project is constructing a major roadway close to wells, contaminants from a spill likely could be contained and removed before reaching the aquifers the wells are drawing from, due to the semi- confined and confined natures of the aquifers. The Contingency Plan component of the WHPP identifies emergency agencies to be contacted in the event of a major oil or chemical spill. It includes both short -term (less than 48 hours) and long -term plans to determine if contamination has occurred and identifies alternate water sources to be used until it has been determined the system is free of contamination and in compliance with standards governing public water supplies. Stormwater Runoff As noted previously, there are two typical sections associated with the proposed Military Cutoff Road Extension project. The first typical section includes curb and gutter and as such would incorporate a stormwater conveyance system. The second typical section includes a shoulder section, which would incorporate vegetated ditches to convey runoff. The NC Wellhead Protection Guidebook ranks stormwater discharges as a higher -risk potential contaminant source. Literature indicates that highway stormwater does occasionally contaminate groundwater with minor amounts of metals and petroleum compounds. These chemicals are typically present at extremely low concentrations and tend to be localized around the right of way. In addition, the application of road salt and de -icing chemicals can be a concern to groundwater quality, particularly in areas that have appreciable snowfall or use surficial aquifers as a water supply source. The NC Wellhead Protection Guidebook ranks road salt storage areas as a higher risk but does not address the application of road salts during winter weather. The NCDOT Division 3 Maintenance Engineer indicates road salt applications occur infrequently in the project area. The average annual snowfall (including pellets and ice) in Wilmington over the last 50 years is two inches. The Division plans for one application of road salt to major arterials used for commerce at approximately 250 pounds per lane -mile per year. 8 Stormwater ponds included in the CFPUA WHPP are assessed as lower -risk potential contaminant sources. Military Cutoff Road Extension Alternatives M1 and M2 may affect four ponds judged to have the appearance of stormwater ponds during surface water delineations for the project. Two of those ponds, BPE and BPF, are located in the CFPUA's wellhead protection area. The proposed project is expected to impact 0.75 acre of pond BPE. Pond BPE is a stormwater pond permitted by the NC Division of Water Quality ( NCDWQ) in February 2007. Pond BPE is associated with a high density subdivision development, West Bay Phase V. The WHPP does not include a data sheet for the West Bay Phase V stormwater pond, likely because it was not constructed at the time of the potential contaminant source review. A data sheet is included in the WHPP for a West Bay Phase IV stormwater pond, which is not impacted by the project. Estimated impacts to pond BPF are 0.41 acre. The pond was evaluated during the review of potential contaminant sources for the CFPUA WHPP and is listed on the data sheet as a stormwater pond for Courtney Pines, Phase III. The NCDWQ issued a stormwater permit for a low density development with a curb outlet system for the Courtney Pines Phase III development in July 2004. The permit does not cite requirements for the construction or maintenance of a stormwater pond for the low density development. NCDOT will likely be required to replace any stormwater storage capacity lost due to project impacts to permitted ponds. It is not expected that project effects to these ponds will adversely affect the water supply. Due to the semi - confined and confined natures of the aquifers in this area, very little of the runoff from the proposed roadway would reach the aquifers. Avoidance and Minimization of Potential Impacts The CFPUA has identified their wellhead protection area and adopted a wellhead protection plan. The wellhead protection plan includes an emergency contingency plan addressing the steps to be taken should a major oil or chemical spill occur. For soil or groundwater contamination incidents occurring within the wellhead protection area, CFPUA will contact State agencies responsible for oversight to track compliance with the activities and the schedule of remediation efforts. NCDOT will coordinate with the Cape Fear Public Utility Authority on the potential inclusion of a sign on Military Cutoff Road Extension notifying drivers they are travelling through a water supply area. If CFPUA is in favor of erecting such a sign, it could include the instruction "Spill Response Dial 911" in case of accidental highway oil or chemical spills. 0 The Military Cutoff Road Extension design has been revised so that a minimum distance of 100 feet is maintained between the slope stake limits and existing wellheads. No wells would be isolated or relocated as a result of the project. Any impacted water lines would be relocated as part of the project. Appropriate measures will be taken to avoid spillage of construction materials and control runoff. Such measures will include an erosion and sedimentation control plan, provisions for disposal and handling of waste materials and storage, stormwater management measures, and appropriate road maintenance measures. NCDOT's Best Management Practicer, for Protection of Su�Oce Wlaters (BMP -PSW) and Sedimentation Control guidelines will be enforced during the construction stages of the project. Summary and Conclusion It is not uncommon to find roads within wellhead protection areas. The proposed Military Cutoff Road Extension project is located within the wellhead protection area established for the public water supply wells operated by the Cape Fear Public Utility Authority. Military Cutoff Road Extension will be located a minimum of 100 feet away from existing wellheads and in most cases, much greater distances. The CFPUA was aware of the proposed project during the construction of the nanofiltration groundwater water treatment plant and located wells with the Military Cutoff Road Extension official transportation corridor map alignment in mind. Groundwater supplying the CFPUA wells originates from both the confined Peedee aquifer and the semi- confined Castle Hayne aquifer. The geologic nature of these aquifers affords a level of protection not associated with surficial aquifers or surface water supply sources. Impacts to the availability of the water supply are not anticipated as a result of the proposed project. The project is not expected to decrease the capacity of the existing and planned water supply infrastructure or the source aquifers. The CFPUA maintains a Wellhead Protection Plan to manage the land areas surrounding their wells in order to prevent contamination of the public water supply. The plan includes emergency response and contingency plans for incidents that may impact water quality. Stormwater runoff associated with the proposed Military Cutoff Road Extension will be directed to grassed swales or a stormwater conveyance system and away from wellheads. The proposed project is not expected to result in impacts to the quantity or quality of the CFPUA's groundwater water supply wells. iii] Literature Review and References Cape Fear Public Utility Authority, Wilmington, NC. • Wellhead Protection Plan for Cape Fear Public Utility Authority P WS ID # 04 -65 -232, December 2009. • Final Well Head Protection Plan, Individual Well Head Radii Location Map (Preliminary Drawings), August 2009. • Proposed Well Head Protection Plan, Individual Well Head Radii Location Map (Preliminary Drawings), June 2009. • Figure 1: Raw Waterlines and Well Sites (Preliminary Drawing). Cape Fear Public Utility Authority website (www.cfpua.org). * 2010 Water Quality Report * 2011 Annual Report * Capacity Management Program Johnson, Gale. NCDENR Public Water Supply. Personal communication, January 23, 2012. McCormick Rankin Corporation, Highway 69 Route Planning Study, February 2008 (www. highway6 9. ca / highway69 / n o rth to 5 22) . McSmith, Gary. Cape Fear Public Utility Authority. Personal communication, January 23, 2012. NC Department of Environment and Natural Resources, Division of Water Resources (www.ncwater.org/ Education _and_Technical_Assistance / Ground_Water). • Basic Hydrogeology, Ground Water, Aquifers & Confining Beds. • North Carolina Aquifers, Castle -Hayne and PeeDee Aquifer Maps. • Local Water Supply Plans, System Information, CFPUA — Wilmington (www.ncwater.org/ Water _ Supply_ Planning /Local_ Water _Supply_Plan /). NCDENR, Public Water Supply Section (PWS), Source Water Assessment Program (SWAP) (www.ncwater.org/pws/swap/). • Approved Local Wellhead Protection Plans (10/25/2011) in North Carolina. • Learn about Your Drinking Water Source. • NC Wellhead Protection Guidebook. • Source Water Assessment and Protection in North Carolina. • Sources of Potential Groundwater Contamination. • Source Water Assessment Program. • NC SWAPinfo Viewer (swap.deh.enr. state .nc.us /swap_app /viewer.htm). North Carolina General Assembly Statues (www.ncga.state.nc.us) • NC General Statutes Article 10 Chapter 130A, North Carolina Drinking Water Act. • NC General Statutes Article 21 Chapter 143, Water and Air Resources. NC High Country Council of Governments, Final High Country Water Resource Plan, 2010 (WWW.reglond.org/plann'mg/FINAL—WATER—RESOURCE—PLAN.pd�. 11 National Groundwater Association, Numerical Investigation of Road Salt Impact on an Urban Well, M.L. Bester, E.O. Frind, J.W. Molson, and D.L. Rudolph, 2005 (info.ngwa.org /gwol/ pdf /061681221.pdf . NOAA, National Climate Data Center (lwf.ncdc.noaa.gov /oa /climate %online /ccd /snowfall.html). State of California, Public Utilities Commission, Memorandum, Potential Groundwater Impacts from Proposed Southern California Edison, July 2009 (www.cpuc.ca.gov /Environment/ info /esa /sjxvl /O_comments /O18.pdf). SRF Consulting Group, Inc. April 2004, Study Report for Analysis of Highway Storm Water Runoff Impacts to Potable Groundwater Aquifers, St. Croix River Crossing (www.dot.state.mn.us/ metro /projects / s tcroix / pdfs / sdeis /Tech %20Memos /Groundwater/ Groundwater.pdf) . Surface Transportation Board, Port MacKenzie Rail Extension Final Environmental Impact Statement, March 2011 (www.stbportmacraileis.com /pdf /final /individual_Chapters/ 4_3_Groundwater.pdo. US Department of Transportation, Federal Railroad Administration. • Environmental Assessment, Memphis Regional Intermodal Facility, July 2010. • Administrative Action, Finding of No Significant Impact, Norfolk Southern Railway Company, Memphis Regional Intermodal Facility. US Geological Survey, Scientific Investigations Reports, Effects of Highway Deicing Chemicals on Shallow Unconsolidated Aquifers in Ohio — Final Report, August 2004 (pubs.usgs.gov /sir /2004/ 5150 /pdf /SIR2004_5150.pdo. US Geological Survey, NC Water Science Center, Distribution of Transmissivity and Yield of the Surficial, Castle Hayne and Peedee Aquifers in Northern New Hanover County, NC (pubs.usgs.gov/of/2011/1205/). U.S. Department of Agriculture, Forest Service, Technology & Development Program, Measuring Effects of Roads on Groundwater: Five Case Studies, January 1999 (www.stream.fs.fed.us /water- road/w-r- pdf /groudwatercases.pdo. US Government Printing Office, 42 USC 300g -,1 National Drinking Water Regulations (www.gpo.gov/ fdsys /pkg/USCODE- 2010- title42 /pdf /USCODE- 2010- tide42- chap6A- subchapZII- partB- sec300g- 1.pdf . US Environmental Protection Agency (www.epa.gov). • Safe Drinking Water Act (www.epa.gov /lawsregs /laws /sdwa.html). • Safe Drinking Water Act Enforcement (xww.epa.gov /compliance /civil /sdwa /). 33 U.S.0 1251 et seq., Federal Water Pollution Control Act, (epw.senate.gov /water.pd�. World Bank Technical Paper No. 376, Edited by Koji Tsunokawa and Christopher Hoban, Roads and the Environment. A Handbook (siteresources .worldbank.org /INTTRANSPORT/ Resources/ 336291- 1107880869673 /covertoc.pdf). 12 41.__._____ w _` \ 53✓ T 7E wus, 50 Fnneenea 11 \ IS a He ne S 1 HII 1 ronul 1 Hove n r 1 <110 5 wttwi + 1 \ cane, "a o 3 \150 — Saint P� t Helena 3 ID H•-lly Rea X. 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