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HomeMy WebLinkAbout18060_Cooper Bussmann_Receptor_SurveyPage 1 of 3 Rev. 06/05/02 General Instructions 1.) 2.) 3.) Site:Former Cooper Bussman Manufacturing Facility Address:210 Dixie TrailCity:GoldsboroCounty:Wayne Section 1 - Property Characteristics Section 2 - Surrounding Properties X North X South X East X West Section 3 - Potential Receptors - include depth to top, construction material and diameter of the utilities, if available Distance Direction Depth X Is a basement or subsurface foundation within 1000 ft of the Property boundary? N Yes 5/26/2016 X Is a school or daycare center within 1000 ft of the Property boundary? N Yes 5/26/2016 0 0 79 No schools or daycares were located within 1,000 ft of the subject property (see maps in Appendix B). The owner of the property at which Mrs Lisas Day Care is shown on the map does not operate a business from her property and has no business signage on the property. 7.73 3.5 0 0 17.39 0 0 79 7.73 3.5 0 0 Applicable to Site (DENR Use Only) Provide Information for the following potential receptors Y/N Field Verified % of property that is open land (concrete/asphalt/gravel) % of property that is grass area % of property that is agricultural crops % of property that is barren Complete and attach map as appropriate Residential; Office & Institutional Residential General Industry Residential; General Business Residential; Office & Institutional Residential BROWNFIELDS AREA RECONNAISSANCE AND RECEPTOR SURVEY GUIDANCE FORM Provide Information for the following potential receptors Current Usage Proposed Usage This form was created to clarify and simplify preparing a receptor survey for a brownfields site. The form was designed to minimize unnecessary delays in processing brownfields applications. This is a guidance document only and Potential Developers may complete and submit their own receptor survey, if they desire. Complete "Property Characteristics" Section and all portions of other sections where an "X" has been placed in the far left column under “Applicable to Site,” as determined by the DEQ Brownfields Project Manager on a site specific basis. The search-radius distances to potential receptors from the Property boundary will be determined by the DEQ Brownfields Project Manager on a site by site basis.Search-radius distances are measured from the site Property Boundary unless otherwise indicated by the DEQ Brownfield’s Project Manager. % of property that is scrub/shrub Size of Property (acres) % of property that is wooded General Industry Residential; General Business % of property that is used for commercial or industrial usage including paved areas Proposed UsageApplicable to Site (DENR Use Only) Surrounding Properties Zoning/Land Use Current Usage 17.39 A map showing "Growth Strategy Areas" has been extracted from the Wayne County Comprehensive Plan. This map, together with a map showing current land use designations, is attached in Appendix A. Not applicable (water table is very shallow in the immediate area). Date Verified Page 2 of 3 Rev. 06/05/02 Distance Direction Depth X Is a sanitary sewer within 1000 ft of the Property boundary? Y Yes 5/26/2016 X Is a septic system/leach field within 1000 ft of the Property boundary? N Yes 5/26/2016 X Is a water line main within 1000 ft of Property boundary?Y Yes 5/26/2016 X Is a natural gas line main within 1000 ft of the Property boundary? Y No 6/13/2016 X Is a buried telephone/cable main within 1000 ft of the Property boundary?Y Yes 5/26/2016 X Is a buried electrical cable main within 1000 ft of Property boundary?N Yes 5/26/2016 Section 4 - Local Water Supply Public:City of Goldsboro Private: Potable Water Supplier Name: Potable Water Supply Source: Distance:Approximately 1 mile Direction: Potable Water Source Intake: Distance:Approximately 3 miles Direction: Section 5 - Water Supply Wells Distance Direction Depth X Is a public water supply well within 1 mile of the Property boundary?N No 6/13/2016 X Is a private water supply well within 1/2 mile of the Property boundary?Y Yes 5/26/2016 X Is an irrigation supply well within 1/2 mile of the Property boundary?Unknown No 6/23/2016 X Is a monitoring well (MW) within 1500 ft of the Property boundary?N No 6/10/2016 Site photographs of potential receptors are included in Appendix E. Sewer lines are available in all areas within 1,000 feet of property (see water and sewer map, Appendix C). Applicable to Site (DENR Use Only) Provide Information for the following potential receptors Y/N Field Verified Date Verified Section 3 - Potential Receptors, continued Complete and attach map as appropriate Y/N Water mains are present on the western side of the property, parallel with S John Street, and on the northern side of the property, parallel with Dixie Trail (see attached water and sewer map, Appendix C).The survey drawing for the site shows an existing gas valve in the road kerb at the entrance to the site from Dixie Trail, near the intersection of Dixie Trail and Shamrock Avenue (Appendix C). Piedmont Natural Gas confirmed that natural gas is supplied to the building at this location, and that natural gas is supplied to adjacent and adjoining properties (telephone call to Piedmont Natural Gas, 06/13/2016). Underground cable utility boxes and markers are present along the northern and western side of the property (see survey drawing in Appendix C). Electricity is delivered to the site via overhead power lines on the northern side of the property, near the intersection of Dixie Trail and Shamrock Avenue (Appendix C) West The Goldsboro Water Treatment Plant North-northwest Neuse River No private water supply wells on the site City of Goldsboro Site photographs of potential receptors are included in Appendix E. Sewer pressurized mains are present on the western side of the property, parallel with S John Street, and on the northern side of the property, parallel with Dixie Trail (see the attached water and sewer map, Appendix C). Field Verified Two water supply wells were identified on adjoining residential properties to the north, across Dixie Trail (211 and 213 Dixie Trail), and at 1807 and 1809 Ball Street approximately 600 ft to the west of the property. The NCDEQ does not have any monitoring wells within 1500 ft of the property in their database (see Groundwater Management Branch Map Interface, Appendix D). Monitoring wells were not observed at A&K Grocery and Gas station approximately 150 ft northwest of the property boundary. Date Verified Complete and attach map as appropriate See the Source Water Assessment Program Report (SWAP) and Public Water Supply Water Sources map, Appendix D. No irrigation wells were reported within one-half mile of the property. According to the Goldsboro Parks & Recreation Department, the Goldsboro Municipal Golf Course to the north of the site does not use irrigation supply wells. Applicable to Site (DENR Use Only)Provide Information for the following potential receptors Page 3 of 3 Rev. 06/05/02 Section 6 - Water Bodies on Property X Is water body naturally developed or man made? X List the uses of the water body X What is the source of the water for the water body X What is the nature of the bottom of the water body (e.g., rocky or concrete bottom, drainage ways or impoundments) X Are there any wetlands present on the property? Site photographs of stormwater drainage ditches on the property are included in Appendix E. Section 7 - Surface Water Body Distance Direction Depth X Are there surface waters located within 1000 ft of the Property boundary? Y Goldsboro Municipal Golf Course Recreation features (golf water hazards) Approximately 790 ft and 990 ft North Unknown Additional water bodies, if needed Section 8 - Additional Requests/ Observations Applicable to Site (DENR Use Only)Provide Information for the following potential receptors Comments Applicable to Site (DENR Use Only) Provide Information for the following potential receptors Comments Applicable to Site (DENR Use Only) Provide Information for the following potential receptors Y/N Name Type Complete and attach map as appropriate Stormwater drainage ditch. Stormwater. No. Primarily grassy drainage ways. There are no permanent water bodies on the property. Stormwater drainage ditches are present on the property and along the boundaries of the property. Shallow, standing water was observed in isolated areas in these ditches on the eastern side and central part of the property. Appendix A Wayne County Comprehensive Plan Adopted March 18, 2008 Re-adopted August 4, 2009 Growth Strategy Map 36 l,l'111i,,,., Cuw1!y On,10,ih S1r,11!.igy I»;,}) ......... __ ..., ____ _ ~Jt":t:.~~~CI'~!.!:"'~"'~ ~;c.~...:.·~~ s.-==.:=:::-.-::==::t:.;::...."'::.-..~' :.1:::s~;;~i:;.~:gr.· :.::'(',~.'!\?;" ... ~~.,~~'.,~~~ .. :".,"~=-:::::.::.=.=-..;:.:..·:.-.:::&:.·::-. :.~.";"'.::.:.,--•.• ::;::~=:~-::.."::-~"-:,---.,:-,,-... -. ..... , ........ _,_ ..... -.,.-... ., ........................... _.,..,,,, ~=:,'::;:~._~~.:.."';" .. ':';".. ;.';;!,';!7;~~::':" C."'-:::.:-... ":':'::'.::..'1"" -11-,-... --. ~-,, .. ,._,.. ........................... .,.. ................. . =~::?!~':i~::.E::=.-~l:?. -1, ....... -.......... ___ .. ,-~ ... -5~~::;l~.;;...:=-:!' ._ ....... ~_ ..................... ,,, ..... _ ... .., Laoend . .._ ............ -- • Sources: Esri, HERE, DeLorme, Intermap, increment P Corp., GEBCO, USGS, FAO, NPS, NRCAN,GeoBase, IGN, Kadaster NL, Ordnance Survey, Esri Japan, METI, Esri China (Hong Kong),swisstopo, MapmyIndia, © OpenStreetMap contributors, and the GIS User Community R-16 Ouue ;Jr:ul Dlxle~TroJI Olx1e.,Ttlll 1-2 1-2 Appendix B Map data ©2016 Google 200 ft Showing results 1 - 1 Mrs Lisas Day Care Day Care Center · Glenhaven Ln Day Care near 210 Dixie Trail, Goldsboro Map data ©2016 Google 1000 ft Showing results 1 - 3 Pathway Christian Academy Private School · S George St Open until 5:00 PM Carver Heights Elementary School Elementary School · Bunche Dr Dillard Middle School 4.0 (7) Middle School · Devereaux St Schools in Goldsboro, NC Appendix C 1000 Ft Buffer 1000 Ft Buffer 1000 Ft Buffer 210 Dixie Trl Legend "Îi Water Sampling Stations !44 Water Service Connections G!.Water Hydrants 'Gate Water Mains Water Lateral Lines ³Ú Sanitary Sewer Pumps $1 Sewer Clean Outs !!2 Sewer Manholes !A Sewer Taps !R Sewer Fittings Sewer Lateral Lines Sewer Pressurized Mains Our Agency Storm Culverts Storm Casings <all other values> CITY OF GOLDSBOROWATER AND SEWER1000 FT BUFFER210 DIXIE TRL ± Designed and Printed By: James Boyette City of Goldsboro Engineering Department Print Date: 5/20/2016 0 150 300 45075FeetProperty Boundry PRESENTED FOR REGISTRATION DATE------------ TIME LOIS J. MOORING REGISTER OF DEEDS WAYNE COUNTY, N.C. BY------------- DEPUTY, ASSISTANT LEGEND I.R.S. IRON ROD SET I.P.F. IRON PIPE FOUND C.M.F. CONCRETE MONUMENT FOUND RATIO OF PRECISION = MINIMUM 1/10,000 NO HORIZONTAL CONTROL WITHIN 2,000 FEET AREA COMPUTED BY D.M.D. METHOD 19·50'47" W 30.90' S 54·00'05" THE STATE OF NORTH CAROLINA COUNTY OF WAYNE I, REVIEW OFFICER OF WAYNE COUNTY, CERTIFY THAT THE MAP OR PLAT TO WHICH THIS CERTIFICATION IS AFFIXED MEETS ALL STATUTORY REQUIREMENTS FOR RECORDING. REVIEW OFFICER 1924 AREA ROAD RIGHT-OF-WAY 17, 159 SQ. FT. OR 0.394 ACRE± EXISTING DITCH :¢: EXISTING ,I) FLAG POLE___/'" EXISTING SIGN \_EXISTING LIGHT IJl.l,L EXISTING CONCRETE FLUME ,, \ \ ,, ,, \\ ,, \\ "X" MARK BOLT HYDRANT EXISTING PA'IEIIENT ELEVATION = 72.96 EXISTING PAVEMENT EX\ST\NG CONCRETE WALK EXISllNG -CLEAN OUT PROPERTY ZONED 1-2 (CITY OF GOLDSBORO) NOTE FLOOD HAZARD THE PROPERTY IS LOCATED WITHIN A 100 YEAR FLOOD HAZARD AREA. FOR FLOOD HAZARD DATA REFER TO FIRM FLOOD INSURANCE RATE MAP NORTH CAROLINA MAP NUMBER 3720258800J EFFECTIVE DATE DECEMBER 2, 2005. EXISTING 15~ CONCRETE PIPE EXISTING CONCRETE FLUME EXISTING CONCRETE WALK EXISTING CONCRETE PAD EXISTING MONITORING 'NELL EXISTING METAL HANDICAP RAL-IP FINISHED FLOOR ELEVATION = 74.89 EXISTING CONCRETE PAD EXISTING HVAC UNIT EXISTING STOOP EXISTING CONCRETE PAO EXISTING DROP INLET~ EXISTING PAVEMENT EXISllNG CONCRETE FLUME I LOCATION MAP \\ \\ \\ \\ \\ \\ \\ \ \ '\ \\ \ \ \\ \\ \\ " \\ \\ \\ \\ \\ \\ \\ \\ \\ \\ \ \ \\ 50 EXISTING PA'IEIIENT EXISTING CONCRETIE WHEEL STOP EXISTING HANDICAP ~GN \\ \ \ \\ \\ \\ \ \\ \\ EXISTING PAVEMENT ~EXISTING DROP INLET ,, \r--EXISTING 18" CONCRETE PIPE \"~ ~ ~\ EXISTING PAVEMENT f---EXISTING CONCRETIE WHEEL STOP SURVEY FOR COUNTY OF WAYNE CITY OF GOLDSBORO GOLDSBORO TOWNSHIP WAYNE COUNTY, N.C. JANUARY 12, 2015 REFERENCE: DEED BOOK 1813 PAGE 482 AREA 7.746 ACRES± 0 25 50 SCALE: 1" 100 50' IT~ I I I f I I I I I I 200 EXISTING BUILDING EXISTING TRANSFORMER INSIDE 4' CHAIN UNK FENCE FINISHED FLOOR ELEVATION = 74.83 EXISTING STOOP EXISTING CONCRETE EXISTING TRANSFORMER EXISTING WATER VAULT ..,,.,,_----EXISTING WATER METER EXISTING BOLLARD EXISTING MONITORING WELL EXISTING 5' CHAIN LINK FENCE EXISllNG CONCRETE EXISTING; MONITORING WEUL I I I I EXISTING CONCRETE PAO EXISTING CONCRETE PAO EXISTING HVAC UNIT EXISTING STOOP EXISTING CONCRETE PAD I/ ;'ff I 8f l UJ1 / ,' § Dfto A-1,if/tt{· Mc,i Book o'°E:fl r fl Tftu1r 1 .Jao;: /icE: I, BOBBY REX KORNEGAY, CERTIFY THAT THIS MAP WAS DRAWN 56? UNDER MY SUPERVISION BY TERRY S. BEASLEY FROM AN ACTUAL SURVEY MADE UNDER MY SUPERVISION AND THAT THE BOUNDARIES ARE AS INDICATED IN THE LEGEND. THAT THE LAND IS OF THE FOLLOWING RECORDED INFORMATION: DEED BOOK 1813 PAGE 482. THAT THE RATIO OF PRECISION IS AS INDICATED IN THE LEGEND. THAT THIS MAP WAS PREPARED IN ACCORDANCE WITH G.S. 47-30 AS AMENDED, WITNESS MY HAND AND SEAL THIS 12TH DAY OF JANUARY, 2015. -...._ BOBBY REX KORNEGAY PROFESSIONAL LAND SURVEYOR NO. L-944 300 EAST WALNUT STREET GOLDSBORO, NORTH CAROLINA 27530 TELEPHONE NO. 919-735-5886 LICENSE NUMBER F-1054 '-. ....._ ....._ '-. '-. ....._ '-. '-. 'f, I, BOBBY REX KORNEGAY, CERTIFY THAT THIS PLAT IS OF A SURVEY OF AN EXISTING PARCEL OR PARCELS OF LAND. EXISTING SIGN I 36.02' i C) I !z! ... '-. "-'-. "-"- I I en I I lL \ I ii li I I I I I a I I I I I I I I I I I I I I s~- I I PAGE 168 I -=---------!:== I I I I I [x I EXISTING BOLLARD I I I I I I I I I I '-. I I I I I (J1 I j 00 "! I "- -[ I I I I I I I I I ~ I I I I I I I I I I I I I I I I :r: " I .... i5 \ " z ;= en x '" I EXISTING CONCRETE FLU~E ~----========= I I ) EXISTING CONCRETE FLUME 0 I I I I I I I I I I L 0 Appendix D Source Water Assessment Program Report for GOLDSBORO, CITY OF Community Water System Introduction: What is a Source Water Assessment? The North Carolina Division of Water Resources, Public Water Supply (PWS) Section is responsible for implementing the Source Water Assessment Program (SWAP) and completing assessments for all public drinking water supplies in the state. The 1996 amendments to the Safe Drinking Water Act provided federal support and required states to conduct assessments of all public water systems. A source water assessment is a qualitative evaluation of the potential of a drinking water source to become contaminated by the identified potential contaminant sources (PCS) within the delineated area. In North Carolina there are more than 10,000 public water supply sources that were assessed by the state. The PWS Section has gathered information for each water supply and developed a process for completing the assessments. This process is summarized in the next few pages and detailed in Section 6 of this report. This report provides a summary of the results for the Source Water Assessment for your drinking water source(s). What is the Source of Your Drinking Water? Everyone wants clean, safe drinking water and we assume this natural resource will always be available to us. However, surface water sources can be threatened by many potential contaminant sources, including permitted wastewater discharges, urban storm water runoff, or other types of non-point source contamination such as runoff produced by agricultural activities and land clearing for development. Your drinking water source(s) is listed in Table 1. Protecting your drinking water from becoming contaminated is a wise investment in public health and your community's future. PWS ID: 04-96-010 2 July 16, 2015 Table 1. Public Water Supply System Information System Name GOLDSBORO, CITY OF City GOLDSBORO PWS ID 04-96-010 Source Name NEUSE RIVER In addition to the sources listed in Table 1 above, this water supply system (GOLDSBORO, CITY OF) has interconnections to allow for the purchase of water from the following water system(s) or "Seller" system(s):  FORK TOWNSHIP  WAYNE WATER DISTRICT A  WAYNE WATER DISTRICT C  WAYNE WATER DISTRICTS  WAYNE WATER DISTRICTS  WAYNE WATER DISTRICTS  WAYNE WATER DISTRICTS  WAYNE WATER DISTRICTS  WAYNE WATER DISTRICTS  FORK TOWNSHIP SANITARY DI Please refer to the Source Water Assessment Program Report for the "Seller" system(s) to review the assessment results for the purchased water supply sources that provide drinking water for this water system (GOLDSBORO, CITY OF). Assessment Report Contents This assessment report includes the following sections: Section 1: Assessment Area Delineation Section 2: Potential Contaminant Source Inventory and Map Section 3: What is a Susceptibility Rating? Section 4: Reviewing Your SWAP Results Section 5: List of Maps, Tables, and Figures for Your Surface Water Source(s) Section 6: North Carolina's SWAP Approach PWS ID: 04-96-010 3 July 16, 2015 Section 1: Assessment Area Delineation The area delineated for your surface water source(s) for this assessment is the water supply watershed. A watershed is a geographic area of land draining to either a stream or lake. Local ordinances dictate the type of development that can take place in some sections of the water supply watershed. In general, the watershed of your surface water source(s) is the area through which contaminants, if released to the environment, can be reasonably expected to move across the land surface following the path of overland flow or shallow subsurface flow and into the surface water body (stream or lake). Section 2: Potential Contaminant Source Inventory and Map The potential contaminant source inventory map shows the delineated area for your surface water source(s). This is the area where potential contaminant sources, if released to the environment, could reasonably be expected to be a risk or a potential for contamination of your drinking water supply. A PCS in this assessment report is a facility or site regulated under a state or federal regulatory program. These facilities are identified in electronic databases that contain location information for each facility. Only databases that include statewide information were used for this source water assessment. Included in this report are: 1) A table of any PCS identified within the delineated assessment area; and 2) A map of the delineated assessment area showing PCSs, roads, jurisdictional boundaries and other pertinent information. It is important to note that the PCSs identified in this report are only potential sources of contamination to your drinking water source. Environmental contamination is not likely to occur if harmful contaminants are managed properly. Section 3: What is a Susceptibility Rating? In North Carolina the susceptibility of any drinking water source is based on two components, a contaminant rating and an inherent vulnerability rating. Your surface water source(s) was assigned a qualitative susceptibility rating of higher, moderate or lower based on the results of the contaminant rating and inherent vulnerability rating process as described in the following paragraphs. Susceptibility Rating The final susceptibility rating for your surface water source(s) is determined by combining the contaminant rating and the inherent vulnerability rating. More detailed information on the susceptibility rating process can be found in Section 6 of this report. Contaminant Rating The contaminant rating for your surface water source(s) was determined based on the number and location of PCSs within the delineated area. Each PCS identified within the delineated area PWS ID: 04-96-010 4 July 16, 2015 was assigned a risk rating of higher, moderate or lower. If a PCS is a facility regulated in an existing environmental program, it will receive a risk rating of higher. The number of PCSs that occur within the delineated area was determined and a contaminant rating of higher, moderate or lower was assigned to your surface water source(s). Inherent Vulnerability Rating The inherent vulnerability rating of your surface water source(s) refers to the geologic characteristics or existing conditions of the surface water source(s) and the delineated assessment area (watershed). These characteristics include water supply watershed classification, surface water source location and the watershed characteristics rating. The watershed classification is based on the size of the watershed, development activities, and allowable waste treatment and disposal practices. The surface water sources are located in streams, large multi-purpose impoundments or small water supply impoundments. The raw water quality rating assessed turbidity and total coliform values over twelve months. The watershed characteristics rating is an assessment of the likelihood that contaminants will follow the path of overland flow or shallow subsurface flow to a surface water source. An inherent vulnerability rating of higher, moderate or lower was assigned to your surface water source(s). PWS ID: 04-96-010 5 July 16, 2015 Table 2. SWAP Results Summary Source Name Inherent Vulnerability Rating Contaminant Rating Susceptibility Rating NEUSE RIVER Higher Moderate Higher It is important to understand that a susceptibility rating of higher does not imply poor water quality. Susceptibility is an indication of a water supply's potential to become contaminated by the identified PCSs within the assessment area. Table 3. Surface Water Source - Information Source Name Watershed Classification Source Location NEUSE RIVER WS-IV Direct Stream Section 4: Reviewing Your SWAP Results Please review the information on your surface water source(s) provided in this report. If you believe any of this information is incorrect, please contact the Public Water Supply Section by e- mail at the following address: SWAP@ncdenr.gov. Or you may submit comments to us at: SWAP Public Water Supply Section 1634 Mail Service Center Raleigh, NC 27699-1634 Or you may contact the Source Water Assessment staff by phone at 919-707-9098. PWS ID: 04-96-010 6 July 16, 2015 Section 5: Maps, Tables and Figures for Your Surface Water Source(s) Maps, tables and figures specific to your surface water source(s) are included in this report in the following pages and are listed below. Map 1. Location Map Map 2. Delineated Area and PCS Map Table 4. Potential Contaminant Source Attributes Table 5. Inherent Vulnerability Rating Table 6. Watershed Characteristics Rating Calculation Figure 1. Land Use / Land Cover Categories Figure 2. Watershed Characteristics Rating Figure 3. Average Annual Precipitation Rating Figure 4. Land Surface Slope Rating Figure 5. Land Use Rating Figure 6. Land Cover Rating Figure 7. Ground Water Contribution Rating PWS ID: 04-96-010 7 July 16, 2015 "WAKEWAKE JOHNSTONJOHNSTON HARNETTHARNETT LEELEE NASHNASH FRANKLINFRANKLIN ORANGEORANGE WAYNEWAYNE DURHAMDURHAM CHATHAMCHATHAM GRANVILLEGRANVILLE PERSONPERSON VANCEVANCE WARRENWARREN SAMPSONSAMPSON WILSONWILSON CUMBERLANDCUMBERLANDMOOREMOORE CASWELLCASWELL DUPLINDUPLINHOKEHOKE HALIFAXHALIFAX Raleigh Durham Cary Sanford Chapel Hill Garner Dunn Apex Smithfield Morrisville Henderson Oxford Erwin Goldsboro ClaytonHolly Springs Carrboro Selma Wake Forest Fuquay-Varina Lillington Pittsboro Hillsborough Angier Zebulon Benson Wendell Coats Louisburg Roxboro Newton Grove Mount Olive Knightdale Creedmoor Spring Lake Falcon Kenly Stem Broadway Momeyer Bailey Spring Hope Rolesville Bunn Pine Level Franklinton Castalia Middlesex Four Oaks Lucama Linden Princeton Micro Youngsville Godwin Kittrell Middleburg Sims Centerville Warrenton PikevilleI-40U S -1 I-85US-158 I-9 5 NC -2 7 U S -1 3 US-64 N C -49 US-15US-421NC-86US-501NC-96NC-58NC-581NC-50N C -5 6 1 U S -4 0 1 NC -4 2 NC-210 NC-55 US-70 US-701NC-39NC-57NC-157NC-98 N C -5 4 NC-43 NC-56 U S -3 0 1NC-751NC- 2 4 2NC-87NC-97 US-117N C-2 22NC- 5 4 NC-50I-95US-158 NC-58NC-27 NC-581US-421NC-210N C -4 2I-40US-15US-70 NC -42 N C -5 5 U S -6 4 I-40NC -9 6 NC-210NC-21 0 NC-39US-301U S -3 0 1NC-39N C- 8 6 N C-87 US-13NC-39 NC-56 I-85 US-401US-158 NC-98 U S -401US-401US-301 NC-581 NC-50 NC-58I-40 US-1I-85US-70I-85NC-96I-40 US-401US-70 NC-50US-401NC-39U S -6 4 US-64 N C-9 6 NC-581NC-42US-401US-70NC-86US-501NC -42 NC-96NC-50NC-55I-9 5 US-70 NC-98 NEUSE RIVER MAP 1. LOCATION MAP © Roads Rivers and Streams Major Hydrology Municipal Boundaries County Boundaries Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 04812Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 8 July 16, 2015 *** ** * * * * * * * * * * * * * * * * *** *** * * * * * * * * * * * * ** * * ** ** * * ** * * * * * * * * * * * * ** ** * * * * * * * ** * * * * ** * * * * * 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 66 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 666 6 6 6 666 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 66 6 6 6 6 6 6 66 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 66 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 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77777777777777777 77777777777777777777777777777 777777777777777 7 777777777777777 77777777777777777777777777777777777777777777777777777777777777777777777 7777 77 7 7 7 7777777 7777 7 77 7 7 7 777 7 777 7 777777 7 77 777 7777777 77777 777777777777777777777777777777777777777777 7777 7 7 777 77777 777777777777777777777 7777 7777777777777 7 77 777 777777 777 7 77777777 77777777777777 777 777777777 7 7777777777777 77 77 777777 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 7 777 7 7 7 7 7 7 7 7 7 7 7 7 8 8 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 "Raleigh Durham Cary Fayetteville Wilson Sanford Goldsboro Red Oak Rocky Mount Burlington Chapel Hill Garner Apex Pinehurst Dunn Smithfield Southern Pines Clinton Morrisville Graham Dortches Henderson Vass Oxford Erwin Aberdeen Mebane Clayton Siler City Hope Mills Holly Springs Carrboro Roxboro Selma Roanoke Rapids Hoffman Yanceyville Wake Forest Fuquay-Varina Raeford Liberty Warsaw Lillington Pittsboro Spring Lake Hillsborough Angier Zebulon Pinebluff Nashville Gaston Carthage Benson Elon College Wade Wendell Coats Louisburg Newton Grove Haw River Mount Olive Knightdale Whispering Pines La Grange Creedmoor Staley Enfield Wagram Falcon Fremont Kenansville Kenly Stem Stovall Stedman Beulaville Norlina Walnut Creek Broadway Momeyer Calypso Faison Roseboro Littleton Magnolia Bailey Cameron Spring Hope Snow Hill Green Level Rolesville Bunn Pine Level Salemburg Taylortown Parkton Franklinton Castalia Middlesex Goldston Four Oaks Warrenton Elm City Lucama Macon Linden Saratoga Middleburg Princeton Micro Pikeville Turkey Black Creek Pink Hill Eureka Youngsville Sharpsburg Autryville Milton Alamance Macclesfield Lumber Bridge Stantonsburg Whitakers Walstonburg Godwin Kittrell Sims Centerville Seven Springs Robbins Pinetops GreeneversI-85I-40 NC-42 US-158 N C -9 6 NC-24I-9 5 NC -2 7 N C -54 US-15U S -1 3 US-64 N C -9 0 2 US-1NC-39N C -4 3NC-49NC-4NC -2 1 0 NC-11NC-41US-421NC-86NC-242N C -7 1 US-501NC-57N C -5 0NC-48NC-58NC-581NC -55 N C -9 1 N C -5 6 1 US-401NC-87NC-22NC-46 US-70 US-701NC-62NC-111NC-53NC-403US-117NC-157NC-98 NC-211NC-56 NC-97 N C-2 0 US-301US-258NC-73 NC-751N C -4 1 1NC-59NC-222NC-241N C -90 3NC-119US-264NC-61N C -15 0 NC-124 N C -70 0 U S -1NC -42 US-158 NC-96I-95NC-87 NC-86NC-55US-64 NC-210 U S -4 0 1 US-401US-70 U S -3 0 1 NC-24 US-301NC-87N C -5 5NC-55US-701U S-421 U S -6 4 NC-58NC-43 US-70 N C- 5 0 NC -5 8 NC-58 I- 4 0 N C -4 9N C -9 6 N C -2 22NC-119I-40US-501I-95NC-86U S-421 I-85 NC- 5 8 N C -403NC-39 U S -158NC-62NC-210I-85US-70 NC- 3 9 US-70US-401I-40 NC-581I-95US-701NC-48NC-49NC-57US -1 5 8 NC- 5 4 US-401NC- 8 6 NC-50U S -1 3 I-9 5 U S -1 3 I-95US-15U S -1NC-96I-95US-1U S -3 0 1 US - 4 0 1 NC-98 N C -6 1 N C -561 I-40 N C- 2 1 1 US -64 U S-4 21I-40NC-42US-70 NC -42 N C -4 2 US-117U S -5 0 1 NC-581NC-210NC- 1 1 1NC-58NC-87NC-39N C-581 NC-97 US-158 NC-50NC-119NC-50N C -4 2 US-401NC-96NC-62NC-39US-64 N C -56 NC-111N C -4 2 US-117US-117NC-210 US-401I-95NC-24 US-421NC-87NC-49NC-11US-158 I-85US-13 N C -4 3 NC-50NC- 2 4 2 US- 7 0 NC-27 U S-13NC-48US-1N C -1 1US-401NC-22NC-98 NEUSE RIVER MAP 2. DELINEATED AREA AND PCS MAP © 6 Animal Operations *CERCLIS Sites )RCRA Gen. / Trans. Facilities <Non Discharge Permits 7 NPDES Permits [National Priority List Sites F PCB Sites (Pollution Incidents +Septage Disposal Sites ,Soil Remediation Sites i Solid Waste Facilities h Tier II Sites 8 RCRA TSD Facilities 9 Old Landfill Sites _UIC Permits G UST Permits Roads Rivers and Streams Major Hydrology Municipal Boundaries Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles PCS Types GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 9 July 16, 2015 Table 4. Potential Contaminant Source Attributes GOLDSBORO, CITY OF PWS ID: 04-96-010, NEUSE RIVER Common Attributes PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County GURMICO CHEMICALS NCN000410293 CERCLIS Sites H 9710 HWY 70 E PRINCETON Unknown JOHNSTON Owen Kornegay Farm AWS510029 Animal Operations H 11754 Brogden Rd Princeton 27569 JOHNSTON Danny Kornegay Farm AWS510030 Animal Operations H 433 Worley Rd Princeton 27569 JOHNSTON Donnie Peedin Farm AWS960005 Animal Operations H 3555 Stevens Mill Rd Goldsboro 27530 WAYNE Craig Farm #2 AWS960006 Animal Operations H Landfill Rd Goldsboro 27530 WAYNE Wake-Kyle Farm AWS960007 Animal Operations H 531 Beaver Dam Rd Goldsboro 27530 WAYNE Ralph Weaver Hog Farms AWS960012 Animal Operations H 494 Stevens Church Rd Goldsboro 27530 WAYNE Bryant Worley Farm AWS960013 Animal Operations H 720 Oakland Church Rd Princeton 27569 WAYNE Leonard Smith Farm AWS960018 Animal Operations H 2906 US 13 S Goldsboro 27530 WAYNE Dexter Jackson 21-26 AWS960030 Animal Operations H 558 Country Club Rd Mount Olive 28365 WAYNE PWS ID: 04-96-010 10 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County P&D Farms, Inc.- Wayne Mills Finishing AWS960031 Animal Operations H 1047 US 13 S Goldsboro 27530 WAYNE Ryan West Farm AWS96004 1 Animal Operations H Mills Loop Rd Goldsboro 27530 WAYNE P & D Nursery AWS960050 Animal Operations H 464 Mills Rd Goldsboro 27530 WAYNE George Hall Farm AWS96006 9 Animal Operations H 188 Parker Rd Mount Olive 28365 WAYNE Billy Jackson & Son Hog AWS960071 Animal Operations H 3871 Stevens Mill Rd Goldsboro 27530 WAYNE Max & Theresa Futrell AWS960078 Animal Operations H 4437 Stevens Mill Rd Goldsboro 27530 WAYNE Pat Herring Farms AWS960082 Animal Operations H 242 Burton Rd Dudley 28333 WAYNE Gerald Hollamon Farm AWS96008 8 Animal Operations H 406 Mills Loop Rd Mount Olive 283657 028 WAYNE Piggybank Sow AWS96009 6 Animal Operations H 907 A B Overman Rd Goldsboro 27530 WAYNE Danny Mitchell Hog Farm AWS960102 Animal Operations H 249 Clayton Rd Princeton 27569 WAYNE Gray Outlaw Farm AWS960112 Animal Operations H 428 Outlaw Rd Dudley 28333 WAYNE Craig Farm #3 AWS960119 Animal Operations H 518 Overman Rd Goldsboro 27530 WAYNE Bobby Grady Farm AWS96012 1 Animal Operations H 5265 US 117 Alternate Mount Olive 28365 WAYNE George Grantham Farm AWS96012 2 Animal Operations H 3222 Stvens Mill Rd Goldsboro 27530 WAYNE Leo Martin Farm AWS96012 5 Animal Operations H 1224 Mills Loop Rd Mount Olive 28365 WAYNE PWS ID: 04-96-010 11 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County Vance Perkins Farms AWS960135 Animal Operations H 2235 Stevens Mill Rd Goldsboro 27530 WAYNE Overman Farm Inc. AWS960139 Animal Operations H 1132 Overman Rd Goldsboro 27530 WAYNE Craig Farms AWS96014 3 Animal Operations H 2552-B Stevens Mill Rd Goldsboro 27530 WAYNE Dexter Jackson 27 & 28 AWS960144 Animal Operations H 479 Cox Pond Rd Mount Olive 28365 WAYNE Williams Farms, Inc. AWS960171 Animal Operations H 2225 Old Grantham Rd Goldsboro 27530 WAYNE Ed Stevens AWS96018 2 Animal Operations H 2973 Old Grantham Rd Goldsboro 27530 WAYNE Owen Jackson Farm AWS960190 Animal Operations H 3350 Old Mt Olive Hwy Mount Olive 28365 WAYNE GLG Farms, LLC Farm AWS960201 Animal Operations H 3096 Stevens Mill Rd Goldsboro 27530 WAYNE Norwood Head Farm AWS960205 Animal Operations H 705 Mills Rd Mount Olive 28365 WAYNE Danny Langley Farm AWS96020 7 Animal Operations H 260 Damon Dr Princeton 275697 055 WAYNE Crop Production Services - Princeton #0242 NCGNE065 6 NPDES Permits H 141 Luby Smith Rd Princeton 27569 WAYNE PERRY RESIDENCE/YOUN G'S AUTO 87538 Pollution Incidents H 4172 US HWY 117 ALTERNATE S. DUDLEY WAYNE CAR GARAGE 87218 Pollution Incidents H HOLLOMAN ROAD DUDLEY WAYNE DR. WILLIAM EASTERL ING RENTAL 14946 Pollution Incidents H 1170 OLD GRANTHAM HIGHWAY GOLDSBO RO WAYNE PWS ID: 04-96-010 12 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County L.D. JACKSON 88078 Pollution Incidents H 1725 OLD SMITHFIELD ROAD GOLDSBORO WAYNE PROGRESS ENERGY NO. 2 FUEL OIL RELEASE 93109 Pollution Incidents H OLD SMITHFIELD ROAD GOLDSBORO WAYNE ORMAND GAS COMPAN Y 6741 Pollution Incidents H E. RAILROAD ST. PRINCETO N JOHNS UNION 76 TRUCKST OP (SPUR FAC) 3221 Pollution Incidents H 9610B HWY 70 EAST PRINCETON JOHNS HANDY MART 5 16485 Pollution Incidents H 752 PINE STREET (& US 70 BUS.) PRINCETO N JOHNS SMITH BROS. OF DUDLEY BULK PLANT 24114 Pollution Incidents H 4471 SOUTH US 117 ALT. HWY. DUDLEY WAYNE HANDY MART #4 38446 Pollution Incidents H 2011 HIGHWAY 70 WEST GOLDSBORO WAYNE E-Z Flow Septic Tanks & Portable Toilets 96-07 SDS H 294 Bennett Road Goldsboro 27530 Wayne Wayne County Landfill 9601- MSWLF-1981 Solid Wase Facilities H 460-B LANDFILL RD. DUDLEY Unkno wn Wayne BellSouth - 21317 4027313 Tier II Sites H HWY 13N GRANTHA M 27530 Wayne Crop Production Services 242 4024727 Tier II Sites H 141 Luby Smith Road Princeton 27569 Wayne AT&T - NC5870 4028021 Tier II Sites H ROUTE 3 SOUTH OF GOLDSBORO POP DUDLEY 28333 Wayne PWS ID: 04-96-010 13 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County Helena Chemical Company 4044726 Tier II Sites H 101 Hinnant Road Goldsboro 27530 Wayne Helena Chemical Company 4047604 Tier II Sites H 101 Hinnant Road Goldsboro 27530 Wayne LEVEL 3 COMMUN ICATIONS- GOLDSBORO- GNHMNCAA 4091509 Tier II Sites H 1677 Old Smithfield Rd Goldsboro 27530-9434 Wayne GRANTH AM 4067113 Tier II Sites H 3667 HIGHWAY 13 SOUTH GOLDSBO RO 27530 Wayne Kelly Springs Road UDS389 Old Landfill Sites H Kelly Springs Road Mount Olive Unknown WAYNE PRINCETON EXCHANGE 00-0-0000032816 UST Sites H 102 SOUTH PEARL STREET PRINCETON Unknown JOHNSTON PRINCET ON FOOD MART 00-0- 0000017036 UST Sites H 106 JONES BLVD W PRINCETO N Unkno wn JOHNSTO N SOUTHER N WAYNE HIGH SCHOOL 00-0- 0000033349 UST Sites H 124 SOUTHERN WAYNE ROAD DUDLEY Unkno wn WAYNE GRANTHAM SCHOOL 00-0-0000033341 UST Sites H 174 GRANTHAM SCHOOL RD GOLDSBORO Unknown WAYNE GRANTHAM SUPPLY & SUPERMARKET 00-0-0000005216 UST Sites H 3388 US 13 SOUTH GOLDSBORO Unknown WAYNE DANNIE'S GAS & GROCER Y 00-0- 0000027577 UST Sites H 3590 US 13 SOUTH GOLDSBO RO Unkno wn WAYNE PWS ID: 04-96-010 14 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County BEST QUALITY FOOD MART 00-0-0000006642 UST Sites H 3885 US HWY 117 SOUTH ALT DUDLEY Unknown WAYNE BEST GAS & GRILL INC 00-0- 0000036552 UST Sites H 4453 US HWY 117 SOUTH ALT DUDLEY Unkno wn WAYNE SMITH BROTHER 'S OF DUDLEY 00-0-0000006555 UST Sites H 4471 HIGHWAY 117 SOUTH/PO BOX 10 DUDLEY Unknown WAYNE NEUSE CORRECTIONAL INSTITUTION 00-0- 0000032081 UST Sites H 701 STEVENS MILL RD GOLDSBO RO Unkno wn WAYNE ROSEWO OD FOOD MART 00-0- 0000006998 UST Sites H 805 ROSEWOOD ROAD GOLDSBO RO Unkno wn WAYNE MARMAC CONV STORE 00-0- 0000033229 UST Sites H SR 1219 - 928 OLD GRANTHAM RD GOLDSBO RO Unkno wn WAYNE Dudley Plywood Plant NCG210168 NPDES Permits H 139 Brewington Rd Dudley 28333 WAYNE Georgia Pacific Wood Products LLC, Dudley Chip-N- Saw Plant NCG210166 NPDES Permits H 2457b Old Mount Olive Hwy Dudley 28333 WAYNE Wayne County Landfill NCG120030 NPDES Permits H 460b S Landfill Rd Dudley 28333 WAYNE Mill Creek Sand and Gravel Mine NCG020882 NPDES Permits H 637 Williford Rd Princeton 27569 JOHNSTON Hinson Mine NCG020613 NPDES Permits H 1239 Stevens Mill Rd Goldsboro 27530 WAYNE Lee Steam Electric Plant NC0003417 NPDES Permits H NCSR 1007 Raleigh 27602 WAYNE PWS ID: 04-96-010 15 July 16, 2015 PCS Name PCS ID PCS Type PCS Risk Rating Street Address City Zip County Fork Township WTP NC0087726 NPDES Permits H 577 NC Hwy 581 S Goldsboro 27533 WAYNE S T Wooten Corporation-Princeton NCG160049 NPDES Permits H 6401 US 70 E Princeton 27569 JOHNSTON W. Ash Street UDS101 Old Landfill Sites H W. Ash Street Goldsboro Unkno wn WAYNE PWS ID: 04-96-010 16 July 16, 2015 Table 4. (Cont.) Potential Contaminant Source Attributes GOLDSBORO, CITY OF PWS ID: 04-96-010, NEUSE RIVER Unique Attributes PCS Name PCS ID Attribute Value Owen Kornegay Farm AWS510029 Operation Type Swine State COC Danny Kornegay Farm AWS510030 Operation Type Swine State COC Donnie Peedin Farm AWS960005 Operation Type Swine State COC Craig Farm #2 AWS960006 Operation Type Swine State COC Wake-Kyle Farm AWS960007 Operation Type Swine State COC Ralph Weaver Hog Farms AWS960012 Operation Type Swine State COC Bryant Worley Farm AWS960013 Operation Type Swine State COC Leonard Smith Farm AWS960018 Operation Type Swine State COC Dexter Jackson 21-26 AWS960030 Operation Type Swine State COC P&D Farms, Inc.- Wayne Mills Finishing AWS960031 Operation Type Swine State COC Ryan West Farm AWS960041 Operation Type Swine State COC P & D Nursery AWS960050 Operation Type Swine State COC George Hall Farm AWS960069 Operation Type Swine State COC Billy Jackson & Son Hog AWS960071 Operation Type Swine State COC Max & Theresa Futrell AWS960078 Operation Type Swine State COC Pat Herring Farms AWS960082 Operation Type Swine State COC Gerald Hollamon Farm AWS960088 Operation Type Swine State COC Piggybank Sow AWS960096 Operation Type Swine State COC Danny Mitchell Hog Farm AWS960102 Operation Type Swine State COC Gray Outlaw Farm AWS960112 Operation Type Swine State COC Craig Farm #3 AWS960119 Operation Type Swine State COC PWS ID: 04-96-010 17 July 16, 2015 PCS Name PCS ID Attribute Value Bobby Grady Farm AWS960121 Operation Type Swine State COC George Grantham Farm AWS960122 Operation Type Swine State COC Leo Martin Farm AWS960125 Operation Type Swine State COC Vance Perkins Farms AWS960135 Operation Type Swine State COC Overman Farm Inc. AWS960139 Operation Type Swine State COC Craig Farms AWS960143 Operation Type Swine State COC Dexter Jackson 27 & 28 AWS960144 Operation Type Swine State COC Williams Farms, Inc. AWS960171 Operation Type Swine State COC Ed Stevens AWS960182 Operation Type Swine State COC Owen Jackson Farm AWS960190 Operation Type Swine State COC GLG Farms, LLC Farm AWS960201 Operation Type Swine State COC Norwood Head Farm AWS960205 Operation Type Swine State COC Danny Langley Farm AWS960207 Operation Type Swine State COC Crop Production Services - Princeton #0242 NCGNE0656 Permit Type Stormwater Discharge, No Exposure Certificate Crop Production Services - Princeton #0242 NCGNE0656 Permit Issued Date 10/20/2009 PERRY RESIDENCE/YOUNG'S AUTO 87538 Pollutant Type GASOLINE/DIESEL/KEROSENE CAR GARAGE 87218 Pollutant Type GASOLINE/DIESEL/KEROSENE DR. WILLIAM EASTERLING RENTAL 14946 Pollutant Type HEATING OIL DR. WILLIAM EASTERLING RENTAL 14946 Site Risk U L.D. JACKSON 88078 Pollutant Type OTHER PETROLEUM PROD. L.D. JACKSON 88078 Site Risk U PROGRESS ENERGY NO. 2 FUEL OIL RELEASE 93109 Pollutant Type OTHER PETROLEUM PROD. ORMAND GAS COMPANY 6741 Pollutant Type GASOLINE/DIESEL/KEROSENE ORMAND GAS COMPANY 6741 Site Risk L PWS ID: 04-96-010 18 July 16, 2015 PCS Name PCS ID Attribute Value ORMAND GAS COMPANY 6741 Site Priority Code 60E UNION 76 TRUCKSTOP (SPUR FAC) 3221 Pollutant Type GASOLINE/DIESEL/KEROSENE UNION 76 TRUCKSTOP (SPUR FAC) 3221 Site Risk H UNION 76 TRUCKSTOP (SPUR FAC) 3221 Site Priority Code 260A HANDY MART 5 16485 Pollutant Type GASOLINE/DIESEL/KEROSENE HANDY MART 5 16485 Site Risk L HANDY MART 5 16485 Site Priority Code 60B SMITH BROS. OF DUDLEY BULK PLANT 24114 Pollutant Type GASOLINE/DIESEL/KEROSENE SMITH BROS. OF DUDLEY BULK PLANT 24114 Site Risk H HANDY MART #4 38446 Pollutant Type GASOLINE/DIESEL/KEROSENE HANDY MART #4 38446 Site Risk U Dudley Plywood Plant NCG210168 Permit Type Timber Products Stormwater Discharge COC Dudley Plywood Plant NCG210168 Permit Issued Date 8/1/2013 Dudley Plywood Plant NCG210168 Permit Expiration Date 7/31/2018 Dudley Plywood Plant NCG210168 Receiving Stream Brooks Swamp (Buck Sw) Georgia Pacific Wood Products LLC, Dudley Chip-N-Saw Plant NCG210166 Permit Type Timber Products Stormwater Discharge COC Georgia Pacific Wood Products LLC, Dudley Chip-N-Saw Plant NCG210166 Permit Issued Date 8/1/2013 Georgia Pacific Wood Products LLC, Dudley Chip-N-Saw Plant NCG210166 Permit Expiration Date 7/31/2018 Georgia Pacific Wood Products LLC, Dudley Chip-N-Saw Plant NCG210166 Receiving Stream Yellow Marsh Branch (Yellow Swamp) (Durham Lake) Wayne County Landfill NCG120030 Permit Type Landfill Stormwater Discharge COC Wayne County Landfill NCG120030 Permit Issued Date 11/1/2012 PWS ID: 04-96-010 19 July 16, 2015 PCS Name PCS ID Attribute Value Wayne County Landfill NCG120030 Permit Expiration Date 10/31/2017 Wayne County Landfill NCG120030 Receiving Stream Edwards Branch Mill Creek Sand and Gravel Mine NCG020882 Permit Type Mining Activities Stormwater Discharge COC Mill Creek Sand and Gravel Mine NCG020882 Permit Issued Date 4/21/2015 Mill Creek Sand and Gravel Mine NCG020882 Permit Expiration Date 6/1/2015 Mill Creek Sand and Gravel Mine NCG020882 Receiving Stream NEUSE RIVER Hinson Mine NCG020613 Permit Type Mining Activities Stormwater Discharge COC Hinson Mine NCG020613 Permit Issued Date 1/1/2010 Hinson Mine NCG020613 Permit Expiration Date 12/31/2014 Hinson Mine NCG020613 Receiving Stream NEUSE RIVER Lee Steam Electric Plant NC0003417 Permit Type Industrial Process & Commercial Wastewater Discharge Lee Steam Electric Plant NC0003417 Permit Issued Date 7/23/2010 Lee Steam Electric Plant NC0003417 Permit Expiration Date 5/31/2013 Lee Steam Electric Plant NC0003417 Receiving Stream NEUSE RIVER Fork Township WTP NC0087726 Permit Type Water Plants and Water Conditioning Discharge Fork Township WTP NC0087726 Permit Issued Date 2/21/2014 Fork Township WTP NC0087726 Permit Expiration Date 5/31/2018 Fork Township WTP NC0087726 Receiving Stream Beaverdam Creek S T Wooten Corporation-Princeton NCG160049 Permit Type Asphalt Paving Mixture Stormwater Discharge COC S T Wooten Corporation- Princeton NCG160049 Permit Issued Date 10/1/2009 S T Wooten Corporation-Princeton NCG160049 Permit Expiration Date 9/30/2014 S T Wooten Corporation- Princeton NCG160049 Receiving Stream Bawdy Creek PWS ID: 04-96-010 20 July 16, 2015 Table 5. Inherent Vulnerability Rating GOLDSBORO, CITY OF PWS ID: 04-96-010, NEUSE RIVER Surface Water Source Characteristics Higher Vulnerability Moderate Vulnerability Lower Vulnerability Watershed Classification Higher Intake Location Higher Raw Water Quality (water plant data) Moderate Watershed Characteristics Rating Moderate Inherent Vulnerability Rating: Higher PWS ID: 04-96-010 21 July 16, 2015 Table 6. Watershed Characteristics Rating Calculation GOLDSBORO, CITY OF PWS ID: 04-96-010 , NEUSE RIVER Watershed Characteristics Rating 32.4 Notes: 1. Watershed Characteristics Rating for each cell (CR): CR = [3 x (precipitation rating)] + [2 x (land surface slope rating)] + [1 x (GW contribution)] + [3 x (land use rating)] + [1 x (land cover rating)] 2. Watershed Characteristics Rating (R) for the entire Assessment Area is the mean of the cell ratings (CR) calculated as: The sum of all cell watershed characteristics ratings (CR) divided by the number of cells (N) within the assessment area: R = (CR) / N 3. The USGS publication “Methods of ranking unsaturated zone and watershed characteristics of public water supplies in North Carolina,” by J. L. Eimers, J. C. Weaver, S. Terziotti, and R. W. Midgette, 1999, provides a detailed discussion of the methods used to determine watershed characteristics ratings. PWS ID: 04-96-010 22 July 16, 2015 FIGURE 1. LAND USE/LAND COVER CATEGORIES ©Water Developed, Open Space Developed, Low Intensity Developed, Medium Intensity Developed, High Intensity Barren Land (Rock, Sand, Clay) Deciduous Forest Evergreen Forest Mixed Forest Shrub/Scrub Grassland, Herbaceous Pasture, Hay Cultivated Crops Woody Wetlands Emergent Herbaceous Wetlands Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 23 July 16, 2015 "NEUSE RIVER FIGURE 2. WATERSHED CHARACTERISTICS RATING © Lower <= 31 Moderate > 31 to 45 Higher > 45 Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 24 July 16, 2015 FIGURE 3. AVERAGE ANNUAL PRECIPITATION RATING © 1 ( <= 40 inches) 2 ( > 40 to 45 inches) 3 ( > 45 to 50 inches) 4 ( > 50 to 55 inches) 5 ( > 55 to 60 inches) 6 ( > 60 to 65 inches) 7 ( > 65 to 70 inches) 8 ( > 70 to 75 inches) 9 ( > 75 to 80 inches) 10 ( > 80 inches) Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 25 July 16, 2015 "NEUSE RIVER FIGURE 4: LAND SURFACE SLOPE RATING © 1 ( <= 2 percent) 3 ( > 2 to 5 percent) 5 ( > 5 to 10 percent) 7 ( > 10 to 20 percent) 9 ( > 20 to 50 percent) 10 ( > 50 percent) Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 26 July 16, 2015 FIGURE 5: LAND USE RATING ©1 Water, Wetlands (Woody and Herbaceous) 2 Barren Land (Rock/Sand/Clay) 3 Forest (Deciduous, Evergreen, Mixed) 4 Grassland/Herbaceous; Shrub/Scrub 5 Pasture/Hay 6 Developed, Open Space 7 Developed, Low Intensity; Cultivated Crops 8 Developed, Medium Intensity 10 Developed, High Intensity Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 27 July 16, 2015 FIGURE 6: LAND COVER RATING ©1 Deciduous, Evergreen and Mixed Forest 3 (Water, Pasture/hay, Woody wetlands, Emergent herbaceous wetlands) 3 Water, Wetlands, Pasture/Hay, Grassland/Herbaceous 5 (Quarries/strip mines/gravel pits, Bare rock/sand, Transitional) 5 Barren Land (Rock, Sand, Clay) 6 Cultivated Crops 7 Developed, Low Intensity 8 Developed, Medium Intensity 10 Developed, High Intensity Watershed Zones Critical Area (NA for WS-I) Protected Area Boundary (WS-IV, V only) Stream Zone Watershed Boundary 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 28 July 16, 2015 FIGURE 7: GROUND WATER CONTRIBUTION RATING ©Assigned Ratings 1 ( <= 10 Unsaturated Zone Rating) 2 ( >= 10 to 20 Unsaturated Zone Rating) 3 ( >= 20 to 30 Unsaturated Zone Rating) 4 ( >= 30 to 40 Unsaturated Zone Rating) 5 ( >= 40 to 50 Unsaturated Zone Rating) 6 ( >= 50 to 60 Unsaturated Zone Rating) 7 ( >= 60 to 70 Unsaturated Zone Rating) 8 ( >= 70 to 80 Unsaturated Zone Rating) 9 ( >= 80 to 90 Unsaturated Zone Rating) 10 ( >= 90 to 100 Unsaturated Zone Rating) Watershed Zones Critical Area (NA for WS-I) Watershed Boundary Protected Area Boundary (WS-IV, V only) Stream Zone 0 6 12 18 Miles GOLDSBORO, CITY OF, PWS ID: 0496010, NEUSE RIVER PWS ID: 04-96-010 29 July 16, 2015 Section 6: North Carolina's SWAP Approach This section of the report is a more detailed description of North Carolina's SWAP approach. This is a summary of Chapter 2 of North Carolina's Source Water Assessment Program Plan. Description of North Carolina’s SWAP Approach To meet the requirements of the 1996 SDWA Amendments, a Source Water Assessment was completed for approximately 9,000 drinking water sources in North Carolina. A delineated area for assessment was established for each drinking water source. An inventory of potential contaminant sources was conducted in each assessment area and finally, a susceptibility rating was assigned to each drinking water source. Because of the scope of this task and the limited time and resources available for completing the work, North Carolina’s SWAP program efforts relies on Geographic Information Systems (GIS) to effectively use information. GIS allows databases to be linked to points on a map (e.g., public water supply sources, streams, geology, land use, roads, permitted waste disposal sites, Superfund sites, etc.) and overlaid on top of one another. Delineation of Assessment Areas for Surface Water Sources For the purpose of performing source water assessments, "delineation" means defining what land area constitutes the area contributing water to a public water supply source. The delineation of the source water assessment areas for surface water sources was done in consideration and collaboration with the Water Supply Watershed Protection (WSWP) Program. During the development of the WSWP program (final state rules adopted in 1992), the state worked with local governments to determine the location of all surface water sources and existing land uses within the water supply watersheds. This information, in conjunction with information on the types and location of wastewater discharges, was used to determine the appropriate Water Supply Watershed Classification for more than 200 surface water sources in the state. The watershed classifications, WS-I, WS-II, WS-III, WS-IV, and WS-V are based on the size of the watershed, development activities, and allowable waste treatment and disposal practices. All surface water sources were located on US Geological Survey 1:24,000 scale topographic maps. The water supply watershed boundaries were delineated (except WS-V waters, which were delineated for the SWAP assessments by the PWS Section), and the boundaries of the Critical Area, and in the case of most WS-IV water supply watersheds Protected Areas (described below) were delineated. For protection of the surface water sources in North Carolina, a segmentation of the water supply watersheds was implemented through the WSWP rules. The entire drainage areas of WS-I water supply watersheds were delineated. These watersheds are all publicly owned and no new development is allowed in these watersheds. These watersheds are very small. Some are located within National Forests. Others are owned by a local government. All WS-II, WS-III and WS-IV water supplies require delineation of a Critical Area which is defined as the area within ½ mile and draining to the normal pool elevation of a water supply reservoir, or ½ mile and draining to a water supply intake in a river. For WS-II and WS-III water supplies, the remainder of the drainage area is subject to the development standards of the PWS ID: 04-96-010 30 July 16, 2015 WSWP rules and are implemented through local land use ordinances. WS-IV water supplies, which are typically portions of major river systems, are segmented in a Critical Area (previously defined) and a Protected Area. The Protected Area is defined as the area within 5 miles and draining to the normal pool elevation of a reservoir or 10 miles upstream and draining to a river intake. In very few instances the WS-IV Protected Area encompasses the entire drainage area due to the size of the watershed. In 1995, the state allowed local governments to request that the 10 mile Protected Area boundary of a WS-IV water supply be measured “run of river” rather than using a 10-mile arc linear measurement. Surface waters that are used by industry to supply their employees with drinking water or waters formerly used as water supply are generally classified as WS-V. The WS-V waters are protected as water supplies and are typically located upstream of and draining to Class WS-IV waters. Land use restrictions do not apply to WS-V waters under the WSWP rules. Please note that for the purpose of the PWS Section’s Source Water Assessments, delineation of WS-IV boundaries may be different from the WSWP Program’s delineation. The PWS Section watershed assessment areas include all land draining to a drinking water source. However, the watersheds defined in accordance with the WSWP rules often exclude land area draining to a source based on municipal or county jurisdictional boundaries. Please refer to the WSWP program website (http://portal.ncdenr.org/web/lr/water-supply-watershed) for information on the regulations associated with their program and the land area affected by their regulations. Delineation of Assessment Areas for Public Water Supply Wells The delineation of source water assessment areas for wells was in accordance with North Carolina’s EPA approved Wellhead Protection Program. The calculated fixed radius method was used to delineate assessment areas around each well in the following areas: piedmont and mountains; the unconfined surficial aquifer of the coastal plain; and in the semi-confined portions of the Castle Hayne aquifer with an estimated recharge rate of 250,000 gallons per day per square mile. The aquifer-source-volume method was used for confined aquifers of the coastal plain. These methods are described below. Well depth is the determining factor for a well to be considered confined. Well depths greater than 70 feet are considered confined. Other assessment area delineation methods may be of interest to a PWS system in an effort to more accurately define the area contributing water to the well. The state will review delineations provided by any PWS system that employs acceptable alternative delineation methods. Resulting alternative delineation areas will be incorporated into the SWAP if the state concludes that the use of the more sophisticated method is appropriate. Calculation of the Contributing Area The first step in delineating the assessment areas is to determine the size of the contributing area to the well. When a well is pumped, it causes groundwater that is flowing through the subsurface to flow toward the well. The surface area surrounding a well that delineates the area in which water entering the groundwater system at the water table eventually flows to the well and discharges is known as the contributing area for the well. In this area, any contaminants released to the environment that reach the water table, can reasonably be expected to move toward and possibly reach the well. The calculated fixed radius method requires the pumping rate (Q) and the recharge rate (W) for the pumping well in order to calculate the size of the contributing area. The contributing area is calculated as follows: PWS ID: 04-96-010 31 July 16, 2015 where: AC = contributing area in square miles, Q = maximum daily pumping rate in gallons per day, and W = average recharge rate in gallons per day per square mile. The maximum daily pumping rate in gallons per day was determined from information on wells obtained from PWS Section sanitary survey inspection forms, Division of Water Resources Local Water Supply plans, and information supplied by system owners/operators. Where no information was available, an estimate of maximum daily pumping rate was assigned based on hydrogeologic characteristics of the aquifer supplying water to the well. Size of the Assessment Area for Wells Using Calculated Fixed Radius Method Estimates of the size of the contributing area can be obtained using the equation given above. However, because of the complex nature of groundwater flow and contaminant transport, it is not possible to define exact contributing area boundaries around each well. Two factors that affect the shape of the contributing area and its position and orientation with respect to a pumping well are the hydraulic gradient and aquifer transmissivity. The variation in aquifer transmissivity is important in determining the shape of the contributing area for a supply well. In areas where the hydraulic gradient and the aquifer transmissivity are essentially the same in all directions, the shape of the contributing area depends primarily on the hydraulic gradient. Where the water table is nearly flat, as near the water-table divide in broad interstream areas of low relief, the contributing area is approximately circular. Where the hydraulic gradient is moderate to steep, the contributing area is approximately elliptical, being oriented in the direction of groundwater movement. Due to limited availability of information on both hydraulic gradient and aquifer transmissivity, the assessment area for each well was doubled. Therefore, the assessment area for each well is twice the size of the calculated contributing area or: W Q = AC W 2Q = A2 = A CSWAP PWS ID: 04-96-010 32 July 16, 2015 Delineation of Assessment Areas for Wells in Confined Aquifers Recharge to confined aquifers is much less than that to the surficial unconfined aquifer where the calculated fixed radius method was used. If the calculated fixed radius method were applied to wells withdrawing water from confined aquifers, the resulting assessment areas would be very large. With the exception of a portion of the Castle Hayne aquifer, the aquifer-source-volume method was used for delineating assessment areas for wells determined to be withdrawing water from highly confined and semi-confined aquifers. “Aquifer source volume” refers to the volume of the source aquifer that supplies the withdrawals from a well for a specified period of time. This factor has been adopted in many states for defining assessment areas for confined aquifers. For the purpose of these assessments, the volume of aquifer that supplies ten years of withdrawals (i.e. the area surrounding a well in which the time of travel to the well is ten years) was used. A ten-year period should be sufficient to provide time to assess the potential impact of any groundwater contamination discovered within an assessment area and for developing appropriate remediation and source water protection strategies for the water supply. For any well in the coastal plain determined to be withdrawing water from a confined aquifer, the table below will be used to determine the size of the assessment area. Table 1. Radii of Assessment Areas for Wells Withdrawing from Confined Aquifers in the Coastal Plain Pumping Rate of Well (Gal. / min.) Radius of Assessment Area (Feet Rounded) 50 1000 100 1000 200 1500 500 2000 1000 3000 2000 3500 PWS ID: 04-96-010 33 July 16, 2015 Delineation of Assessment Areas for Water Supply Sources Classified as GWUDIs Drinking water supplied by a well may include a surface water component. This is defined as Ground Water Under the Direct Influence of Surface Water (GWUDIs). This term is used to indicate that water withdrawn from a well contains a specific indicator or indicators (e.g., giardia) of the presence of a surface water component. The delineated area for a PWS well classified as a GWUDI well will be the combined area of a circle based on the calculated fixed radius method and the resulting upgradient watershed of the intersected surface water. Segmentation of the resulting watersheds was in accordance with the most appropriate water supply watershed classification scheme. Delineation for Water Supply Sources Classified as Springs Springs can be defined as areas where the water table intersects the ground surface. Ground water may have flowed many miles before appearing on the surface to form a particular spring. The delineated area for a drinking water source classified as a spring was defined as the entire watershed area upgradient of the spring. Segmentation of the resulting watersheds was in accordance with the most appropriate water supply watershed classification scheme. Susceptibility Rating Methodology The state determined that the overall susceptibility rating for each drinking water source should be based on two key components, a contaminant rating and an inherent vulnerability rating. Inherent vulnerability refers to the physical characteristics and existing conditions of the watershed or aquifer. A contaminant rating refers to an evaluation of the number and location of potential sources of contamination. The contaminant rating and inherent vulnerability methodologies are explained below. Contaminant Rating Methodology The contaminant rating for each water supply source was determined based on the number and location of potential contaminant sources (PCSs) within the delineated area. The delineated area for the drinking water source encompasses the area where PCSs, if released to the environment, could reasonably be expected to be a risk or a potential for contamination of the drinking water supply. A PCS in this assessment report is a facility or site regulated under a state or federal regulatory program. These facilities are identified in electronic databases that contain location information for each facility. Only databases that include information statewide were used for this source water assessment. Each PCS identified within the delineated area was assigned a risk rating of higher, moderate or lower. The number of PCSs that occur within the delineated area was determined and a Contaminant Rating of higher, moderate or lower was assigned to each drinking water source. PWS ID: 04-96-010 34 July 16, 2015 Contaminant Rating for Ground Water Sources For each ground water source, define an inner Zone A with an area equal to half the area of the delineated assessment area. Using Table 2, determine the number of PCSs that occur within each risk category according to their location, either in Zone A or in the remaining delineated area. Determine the Contaminant Rating of higher, moderate or lower for each well by adding the totals for each risk category. Table 2. Determination of Contaminant Rating for Ground Water Sources Potential Contaminant Sources in : Number of Higher Risk PCSs Cumulative Number of Higher and Moderate Risk PCSs Cumulative Number of Higher, Moderate and Lower Risk PCSs Zone A (the inner 1/2 of the delineated area) (Number of sources ) > 1 Score: (1 or 0) (Number of sources ) > 2 Score: (1 or 0) (Number of sources ) > 4 Score: (1 or 0) Delineated Area (Zone A plus the remaining delineated area) (Number of sources ) > 2 Score: (1 or 0) (Number of sources ) > 4 Score: (1 or 0) (Number of sources ) > 8 Score: (1 or 0) For each category, score “1” if the number of contaminants exceeds the indicated threshold, or score “0” if the number of contaminants is less than the threshold. Total all the scores (1 or 0) for each category. Therefore, the highest possible score is 6. Determine the Contaminant Rating for each well as follows: Higher (6 - 4) Moderate (3 - 2) Lower (< 1) Contaminant Rating for Surface Water Sources Because the WSWP rules prohibit development in these watersheds, the existence of one PCS in the delineated area of a drinking water source located in a WS-I watershed will result in a contaminant rating of higher. Using Table 3 for WS-II and WS-III watersheds, or Table 4 for WS-IV and V watersheds, determine the number of PCSs that occur within each risk category (i.e., lower, moderate or higher risk) and within each delineated assessment area (e.g., critical area, protected area, etc). Determine the Contaminant Rating for each surface water PWS source by summing the totals for each risk category. PWS ID: 04-96-010 35 July 16, 2015 Table 3. Determination of Contaminant Rating for Surface Water Sources in WS - II or III Watersheds Potential Contaminant Sources in : Number of Higher Risk PCSs Cumulative Number of Higher and Moderate Risk PCSs Cumulative Number of Higher, Moderate and Lower Risk PCSs Critical Area (Number of sources ) > 1 Score: (1 or 0) (Number of sources_____) > 5 Score: (1 or 0) (Number of sources ) > 10 Score: (1 or 0) Watershed Area Within 1000 Foot Stream Zone (Number of sources ) > 5 Score: (1 or 0) (Number of sources ) > 10 Score: (1 or 0) (Number of sources ) > 20 Score: (1 or 0) Watershed Area Outside Stream Zone (Number of sources ) > 20 Score: (1 or 0) (Number of sources ) > 40 Score: (1 or 0) (Number of sources ) > 80 Score: (1 or 0) For each category, score “1” if the number of contaminants exceeds the indicated threshold, or score “0” if the number of contaminants is less than the threshold. Total the scores (1 or 0 for each category). Therefore, the highest possible score is a 9. Determine the Contaminant Rating for each surface water source in a Water Supply Watershed II or III as follows: Higher (9 - 6) Moderate (5 - 3) Lower (< 2) PWS ID: 04-96-010 36 July 16, 2015 Table 4. Determination of Contaminant Rating for Surface Water Sources in WS - IV and V Watersheds Potential Contaminant Sources in : Number of Higher Risk PCSs Cumulative Number of Higher and Moderate Risk PCSs Cumulative Number of Higher, Moderate and Lower Risk PCSs Critical Area (Number of sources ) > 1 Score: (1 or 0) (Number of sources ) > 5 Score: (1 or 0) (Number of sources ) > 10 Score: (1 or 0) Protected Area Within 1000 Foot Stream Zone (Number of sources ) > 5 Score: (1 or 0) (Number of sources ) > 10 Score: (1 or 0) (Number of sources ) > 20 Score: (1 or 0) Protected Area Outside Stream Zone (Number of sources ) > 20 Score: (1 or 0) (Number of sources ) > 40 Score: (1 or 0) (Number of sources ) > 80 Score: (1 or 0) Stream Zone from Protected Area to 25 Mile or Watershed Boundary (Number of sources ) > 20 Score: (1 or 0) (Number of sources ) > 40 Score: (1 or 0) (Number of sources ) > 80 Score: (1 or 0) For each category, score “1” if the number of contaminants exceeds indicated threshold. If the number of contaminants is less than the threshold score “0.” Total all the scores (1 or 0 for each category). Therefore, the highest possible score is a 12. Determine the Contaminant Rating for each surface water source in a Water Supply Watershed IV or V as follows: Higher (12 - 9) Moderate (8 - 4) Lower (< 3) PWS ID: 04-96-010 37 July 16, 2015 Inherent Vulnerability Rating Methodology The inherent vulnerability of a well or surface water source refers to the characteristics or existing conditions of the well or surface water source and its delineated assessment area. Several factors were evaluated for both groundwater and surface water sources and included in the inherent vulnerability rating of each public water supply source. Each drinking water source was assigned an inherent vulnerability rating of higher, moderate or lower. Inherent Vulnerability Rating for Wells The characteristics included for assigning an inherent vulnerability rating for wells are aquifer rating, unsaturated zone rating and well integrity/well construction rating. The aquifer rating is an assessment of the water transmitting characteristics of the aquifer. The unsaturated zone rating is an assessment of the likelihood that contaminants from surface and shallow sources will follow the path of aquifer recharge and reach the water table. The well integrity/construction rating is an assessment of the quality of the construction of the well. A brief description of each factor follows: Aquifer Rating The aquifer rating is a qualitative assessment of the water transmitting characteristics of the aquifer. Relative differences in aquifer vulnerability were based on a review of relevant literature, expert opinions, and confirmed with historical data. Factors considered in rating aquifer vulnerability include hydraulic conductivity, degree of confinement, dilution, and sorption potential. The attenuative capacity of the unsaturated zone is not considered in the determination of aquifer ratings. Table 5 summarizes the aquifer-rating scheme used for these assessments. Well depths determined whether a well was considered unconfined, deep confined or shallow confined for these assessments. Wells less than or equal to 70 feet deep were considered to be withdrawing water from an unconfined or surficial aquifer. Wells greater than 70 feet but less than 180 feet deep were considered to be withdrawing water from a shallow confined aquifer. Wells greater than 180 feet deep were considered to be withdrawing water from a deep confined aquifer. PWS ID: 04-96-010 38 July 16, 2015 Table 5. Aquifer Rating Based on Water Transmitting Characteristics Aquifer/Ground Water Source Rating Coastal Plain Aquifers: Deep Confined (e.g., Kinston area) Lower Shallow Confined (e.g., Pamlico Co.) Moderate Unconfined (e.g., Castle Hayne Outcrop area) Higher Piedmont and Mountain Aquifers: Triassic Basins (e.g., Sanford-Durham) Moderate Fractured Rock Aquifers Higher Other: Metamudstones and Meta-argillites of the Carolina Slate Belt Higher Areas with Wells Cased to Less Than 20 Feet Higher Groundwater under the Direct Influence of Surface Water Higher Sand Hills Area Higher Unsaturated Zone Rating The state, in cooperation with the United States Geological Survey (USGS), developed the unsaturated zone rating methodology. The USGS Water-Resources Investigations Report 99-4283, "Methods of Rating Unsaturated Zone and Watershed Characteristics of Public Water Supplies in North Carolina" describes the methodology. The unsaturated zone rating is the combination of selected factors that contribute to the likelihood that contaminants from surface and shallow sources will follow the path of aquifer recharge and reach the water table. Contributing factors, in the form of GIS spatial data layers, include land use/land cover, vertical hydraulic conductance of the unsaturated zone, and land-surface slope. Vertical hydraulic conductance measures the capacity of the unsaturated zone to transmit water from land surface to water table. Land-surface slope and land cover influences the amount of precipitation that infiltrates into the subsurface. Land use describes the activities that take place on the surface or in the shallow subsurface and the type of contaminants that may be present as a result of those activities (i.e., "non-point source" potential contaminant sources). PWS ID: 04-96-010 39 July 16, 2015 Well Integrity/Construction Rating The integrity of well construction can vary widely, depending on details such as casing depth, grouting depth, well materials and driller knowledge. However, these details are not always available for assigning SWAP assessment ratings. In 1994 and 1999 there were important rule changes that greatly improve the quality of the well construction standards. Therefore, the SWAP assessments use well construction and approval dates as a surrogate to construction details to assign a well construction / integrity rating. For wells that construction and approval date is not available, the well construction/integrity rating defaults to Higher. Table 6 summarizes the characteristics evaluated and rated for the inherent vulnerability for each PWS well. Each well was assigned an inherent vulnerability rating of higher, moderate or lower: Table 6. Inherent Vulnerability Rating of Wells Inherent Vulnerability Factors Higher Vulnerability Moderate Vulnerability Lower Vulnerability Aquifer Rating 10 5 - 1 Unsaturated Zone Rating 10 5 1 Well Integrity/Construction Rating 5 3 1 Totals 25-18 17-15 14-1 Inherent Vulnerability Rating for Surface Water Sources The inherent vulnerability of a surface water source refers to the characteristics and existing conditions of the source and the delineated assessment area (watershed). The characteristics included for assigning an inherent vulnerability rating are water supply watershed classification, surface water source location, raw water quality, and the watershed characteristics rating. The watershed classification is based on the size of the watershed, development activities, and allowable waste treatment and disposal practices. The surface water sources were characterized based on whether they are located in streams, large multi-purpose reservoirs, or small water supply reservoirs. The raw water quality rating is based on recorded turbidity and total coliform values over a twelve month period. The watershed characteristics rating is an assessment of the likelihood that contaminants will follow the path of overland flow or shallow subsurface flow to a surface water source. A description of each factor follows: PWS ID: 04-96-010 40 July 16, 2015 Watershed Classification In North Carolina, all surface water sources are located in water supply watersheds that are classified as either WS-I, II, III, IV, or V. The Water Supply Watershed Protection rules required that all local governments having land use jurisdiction within water supply watersheds adopt and implement water supply watershed protection ordinances, maps and a management plan. All of these ordinances are in place and have been deemed to be in compliance with the statutory requirements. The inherent vulnerability ratings for watershed classification are based on differences between watershed classes, including size of the watershed, development activities, and allowable waste treatment and disposal practices. Surface Water Source Location All surface water sources are located in streams, large multi-purpose reservoirs (Class 3), or small water supply reservoirs (Class 1 or 2). The inherent vulnerability ratings for surface water source location are based on differences between the reaction time for a water plant in the case of a contamination event or spill in a stream versus a reservoir and includes the allowable activities on surface water reservoirs (i.e., single use versus multiple uses allowed). Raw Water Quality The likelihood of the presence of Cryptosporidium and other water-borne microorganisms increases when turbidity is high. Therefore, turbidity and total coliform bacteria are good indicators of raw water quality. The Area Wide Optimization Program (AWOP) within the PWS Section has developed a ranking system for surface water treatment plants based primarily on these two parameters. This ranking system, with some minor modifications, has been adopted by SWAP in order to assign a raw water quality rating to each surface water source. The AWOP ranking system is based on the treatment plant’s raw, settled and finished water turbidity and coliform levels along with violations of MCLs and treatment techniques. Raw, settled and finished water samples are collected daily and compiled in a monthly report, commonly referred to as a MOR (monthly operating report). The AWOP ranking system first totals the number of months in a year that specific levels of turbidity and coliform are exceeded and/or the number of months certain violations occur. The monthly totals are then multiplied by a weighting factor to balance the relative importance of these parameters. These numbers are then totaled for the year and are considered the water treatment plant’s total score. Because the purpose of SWAP is to assess sources of drinking water supply and not how well water plants treat their water, SWAP only uses the raw water scores for turbidity and coliform from the AWOP ranking system. The total raw water quality scores were divided into three categories of vulnerability: Higher, Moderate and Lower. The AWOP ranking system is for surface water treatment plants and not individual surface water sources. Therefore, in the case where more than one source is used by a treatment plant, the plant’s raw water quality rating was initially assigned to all of the plant’s sources. Upon review by the regional office staff some of the ratings were then adjusted based on their extensive knowledge of the surface water sources in their area. PWS ID: 04-96-010 41 July 16, 2015 Watershed Characteristics Rating The state determined the watershed characteristics ratings of each surface water source in cooperation with the USGS. The USGS Water-Resources Investigations Report 99-4283, "Methods of Rating Unsaturated Zone and Watershed Characteristics of Public Water Supplies in North Carolina" describes this methodology. The watershed characteristics ratings were based on the combination of selected factors that may contribute to the likelihood that contaminants follow the path of overland flow and reach the surface water source. Contributing factors, in the form of GIS spatial data layers, include average annual precipitation, land cover, land use, land-surface slope and groundwater contribution. Precipitation is the source of water transported overland to a stream or lake. Land-surface slope and land cover influence the amount of precipitation that infiltrates into the subsurface. Land use describes the activities that take place on the surface or in the shallow subsurface and the type of contaminants that may be present as a result of those activities (i.e., non-point source potential contaminant sources). Ground-water contribution is the effect of ground water on surface-water quantity and quality. For these assessments the ground-water contribution is derived from the unsaturated zone rating described in the ground water inherent vulnerability section of this report. Table 7 includes the characteristics that were evaluated and rated for the inherent vulnerability for each surface water source: Table 7. Inherent Vulnerability of Surface Water Sources Surface Water Source Characteristics Higher Vulnerability Moderate Vulnerability Lower Vulnerability Watershed Classification WS-IV, WS-V 10 WS-III, WS-II 5 WS-I 1 Intake Location Direct Stream 8 Class 3 Reservoirs 4 Class 1 and 2 Reservoirs 2 Raw Water Quality (water plant data) 5 3 1 Watershed Characteristics Rating 10 5 1 Totals 33 - 21 20 - 13 12 - 5 PWS ID: 04-96-010 42 July 16, 2015 Susceptibility Rating Methodology The state assigned a susceptibility rating for each drinking water source that was based on two components, a contaminant rating and an inherent vulnerability rating. Using the results of the evaluations of contaminant rating and inherent vulnerability rating for each public drinking water source, a susceptibility rating of higher, moderate or lower was assigned to each source according to the table below: Table 8. Susceptibility Rating for Public Water Supply Sources by Combining the Inherent Vulnerability and Contaminant Ratings. Contaminant Rating Inherent Vulnerability Rating Higher Moderate Lower Higher H H M Moderate H M M Lower M M L '~ SWAPlnfo 2.0 __±__ [ T I 210 dixie trail Mar-Mac Genoa 0 0.5 lmi DOWNLOAD CSV Incident PWS Sources Get SWAP Reports SWAP Data Info Tool Instructions Contacts Goldsboro Web town Sa Airboro Gol o No features found. PCS Locations Wellhead Protection Are ... Legend All PWS Sources All PWS Sources 2015 Surface Water Community • Surface Water Non-Transient Non-Community Ground Water Community Ground Water Non-Transient Non-Community Ground Water Transient Non-Community Ground Water Adjacent ® Divider Page !!2 Copyright:© 2013 Esri, DeLorme, NAVTEQ, TomTom, NC OneMap, NC Centerfor Geographic Information and Analysis, NC 911 Board Public Water Supply Water Sources 210 Dixie Trail 0 1 2 3 40.5 Miles ³ Divider Page ra •1 • '<nil • " ' 1<> / SO!IDHil ?' c: p:,n ~t.11 • M,n lffUV 11.fVl'W • 11-l ., I C> C.11h1 .. l•u111 :, T l•..tal•1 I " " ,/. ((r,, .. .. b ff ,c;r ; 'l •' I \-b .,,} 'ii r, < ,..,, "''~ -tt ,._"'J "' Ct, .. = } " ------() Appendix E PHOTOGRAPHIC LOG Client Name: Wayne County Development Alliance Site Location: Former Cooper Bussman Manufacturing Facility; Goldsboro, North Carolina Project No. 201455 Photo No. 1 Date: 10/13/15 Direction of Photo: East-southeast Description: Foreground, left to right in the photograph: water valve, stormwater drainage ditch, fire hydrant, storm sewer manhole (right); background: overhead powerline and water vault at the base of the powerline at the entrance to the subject property. Photo No. 2 Date: 10/13/15 Direction of Photo: East Description: Stormwater drainage ditch, telephone pedestal, and telephone panel on the northwesters side of the subject property. PHOTOGRAPHIC LOG Client Name: Wayne County Development Alliance Site Location: Former Cooper Bussman Manufacturing Facility; Goldsboro, North Carolina Project No. 201455 Photo No. 3 Date: 10/13/15 Direction of Photo: Northwest Description: Stormwater drop inlet in the parking lot of the property that discharges into the drainage ditch on the northwestern side of the subject property site via a concrete pipe. Photo No. 4 Date: 10/13/15 Direction of Photo: Southeast Description: Standing water in a stormwater drainage ditch on the northern side of the property. A blue-colored sheen was observed on the surface of the water. PHOTOGRAPHIC LOG Client Name: Wayne County Development Alliance Site Location: Former Cooper Bussman Manufacturing Facility; Goldsboro, North Carolina Project No. 201455 Photo No. 5 Date: 10/13/15 Direction of Photo: East Description: Storm sewer manhole (foreground) and underground telecommunications cable (background, opposite the entrance road) on Dixie Trail. Photo No. 6 Date: 10/13/15 Direction of Photo: East Description: Stormwater drop inlet and stormwater ditch on Dixie Trail. Stormwater ditches and drop inlets are common in the residential neighborhoods within 1,000 ft of the subject property to the north and west. PHOTOGRAPHIC LOG Client Name: Wayne County Development Alliance Site Location: Former Cooper Bussman Manufacturing Facility; Goldsboro, North Carolina Project No. 201455 Photo No. 7 Date: 10/13/15 Direction of Photo: North Description: A private water supply well observed on the residential property located at 213 Dixie Trail, across from the subject property. Private water supply wells were observed on three other residential properties within a half-mile of the subject property. Photo No. 8 Date: 10/13/15 Direction of Photo: Southeast Description: Roadside stormwater drop inlet on Shamrock Avenue to the north of the subject property. PHOTOGRAPHIC LOG Client Name: Wayne County Development Alliance Site Location: Former Cooper Bussman Manufacturing Facility; Goldsboro, North Carolina Project No. 201455 Photo No. 9 Date: 10/13/15 Direction of Photo: West Description: Stormwater drop inlet, drainage ditch, and overhead powerlines and telephone lines on Ball Street, in the residential neighborhood to the west of the subject property Photo No. 10 Date: 10/13/15 Direction of Photo: Northeast Description: Storm sewer manhole and kerbside stormwater drop inlet on Henry Street, south of the subject property. Overhead lines can be seen from the road to the house in the background of the photograph.