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HomeMy WebLinkAbout22034_Fairey Finishing Plant _EMP_2019_12_04NORTH CAROLINA BROWNFIELDS PROGRAM ENVIRONMENTAL MANAGEMENT PLAN This form is to be used to prepare an Environmental Management Plan (EMP) for projects in the North Carolina Brownfields Program at the direction of a Brownfields project manager. The EMP is a typical requirement of a Brownfields Agreement (BFA). Its purpose is to clarify actions to be taken during the demolition and construction at Brownfields properties in an effort to avoid delays in the event of the discovery of new contamination sources or other environmental conditions. The EMP provides a means to document redevelopment plans and environmental data for each applicable environmental medium to inform regulatory -compliant decision -making at the site. As much detail as possible should be included in the EMP, including contingency planning for unknowns. Consult your project manager if you have questions. Prospective Developers and/or their consultants must complete and submit this form and all pertinent attachments, see checklist below, to their Brownfields project manager prior to any earthmoving or other development -related activities that have the potential to disturb soil at the Brownfields Property, including demolition. For the resultant EMP to be valid for use, it must be completed, reviewed by the program, signed by all parties working on the project, and approved by the Brownfields project manager. Failure to comply with the requirements of the EMP could jeopardize project eligibility, or in the event of a completed agreement, because for a reopener So that the EMP provides value in protecting brownfields eligibility and public health, the preparer shall ensure that the following steps have been completed prior to submitting the EMP for review. Any EMP prepared without completing these steps is premature. ® Site sampling and assessment that meets Brownfields' objectives is complete and has been reviewed and approved by the Brownfields Project Manager. ® Specific redevelopment plans, even if conceptual, have been developed for the project, submitted and reviewed by the Brownfields Project Manager. Please submit, along with the completed EMP form, the following attachments, as relevant and applicable to the proposed redevelopment: ® A set of redevelopment plans, including architectural/engineering plans, if available; if not conceptual plans may suffice if updated when detailed plans are drafted. ® A figure overlaying redevelopment plans on a map of the extent of contamination for each media. (sample locations provided in Exhibit 2—please reference Tables i through Table 4) ® Site grading plans that include a cut and fill analysis. ❑ A figure showing the proposed location and depth of impacted soil that would remain on site after construction grading. ❑ Any necessary permits for redevelopment (i.e. demolition, etc.). EMP Version 2, June 2018 ® A detailed construction schedule that includes timing and phases of construction. Appendix A ® Tabulated data summaries for each impacted media (i.e. soil, groundwater, soil gas, etc.) applicable to the proposed redevelopment. Appendix 8 ® Figures with the sampling locations and contamination extents for each impacted media applicable to the proposed redevelopment. Appendix B ❑ A full final grade sampling and analysis plan, if the redevelopment plan is final. ❑ If known, information about each proposed potential borrow soil source, such as aerial photos, historic site maps, historic Sanborn maps, a site history, necessary for brownfields approval. ❑ Information and, analytical data if required, for quarries, or other borrow sources, detailing the type of material proposed for importation to the Brownfields Property. ❑ A work plan for the sampling and analysis of soil to be brought onto the Brownfields Property. Refer to Issue Resolution 15 in Brownfields Program Guidelines. ® A map of the Brownfields Property showing the location of soils proposed for export and sampling data from those areas. Appendix B: Soil boring locations are depicted on Exhibit 3 with proposed cut areas. Table 4 provides analytical data for select depth intervals. ® If a Vapor Mitigation System is required by the Brownfields Program, the Vapor Intrusion Mitigation System (VIMS) plan will be signed and sealed by a NC Professional Engineer. The VIMS Plan may also be submitted under separate cover. VIMS required at the site will be submitted under separate cover. 11 GENERAL INFORMATION Date: August 8, 2019 Brownfields Assigned Project Name: Fairey Finishing Plant Brownfields Project Number: 22034 18 32 Brownfields Property Address; 1604 East Lawson Street, Durham, Durham County, North Carolina Brownfields Property Area (acres): 4.335 acres Is Brownfields Property Subject to RCRA Permit? Yes No If yes enter Permit No.: Not Applicable Is Brownfields Property Subject to a Solid Waste Permit? Yes No EMP Version 2, June 2018 If yes, enter Permit No.: Not Applicable 11 COMMUNICATIONS Prospective Developer (PD): Durham Technical Community College Contact Person: Marshall Fuller, Director Facility Services Phone Numbers: Office: 919-536-7200 x6206 Mobile: 919-943-0187 Email: fullerm@durhamtech.edu Contractor for PD: Contact Person: Matt Woodlief, Bordeaux Construction Company, Inc. Phone Numbers: Office: 919-220-1141 Mobile: 415-377-1337 Email: matt.w@bordeauxconstruction.com Environmental Consultant: Ms. Analee Farrell (Terracon Consultants, Inc.) Phone Numbers: Office: 919-436-2957 Mobile: 919-630-0421 Email: Analee.farrell@terracon.com Brownfields Program Project Manager: Mr. Brad Atkinson Phone Numbers: Office: 919-707-8748 Mobile: n/a Email: brad atkinson@ncdenr.gov Other DENR Program Contacts (if applicable, i.e., UST Section, Inactive Hazardous Site Branch, Hazardous Waste, and Solid Waste): Not Applicable NOTIFICATIONS TO THE BROWNFIELDS PROGRAM Advance Notification Times to Brownfields Project Manager: Check each box to accept minimum notice periods (in calendar days) for each type of on -site task: On -site assessment or remedial activities: 10 days Prior Construction or grading start: 10 days Prior Discovery of stained soil, odors, USTs, buried drums or waste, landfill, or other signs of previously unknown contamination: Within 48 hours Implementation of emergency actions (e.g. dewatering, flood, or soil erosion control measures in area of contamination, venting of explosive environments): Within 48 hours 3 EMP Version 2, June 2018 Installation of Mitigation systems: Within 10 days Other notifications as required by local, state or federal agencies to implement redevelopment activities: (as applicable): Within 30 days 11 REDEVELOPMENT PLANS 1) Type of Redevelopment (check all that apply): ❑Residential ❑Recreational ❑Institutional ❑Commercial ❑Office ❑Retail ❑Industrial ®Other specify: Educational 2) Check the following activities that will be conducted prior to commencing earth -moving activities at the site: ® Review of historic maps (Sanborn Maps, facility maps) ❑ Conducting geophysical surveys to evaluate the location of suspect UST(s), fuel lines, utility lines, etc. ® Interviews with employees/former employees/facility managers/neighbors 3) Summary of Redevelopment Plans (MANDATORY: attach detailed plans or conceptual plans, if detailed plans are not available. EMP review without such information would be premature): Provide brief summary of redevelopment plans, including demolition, removal of building stabs/pavement, grading plans and planned construction of new structures: See attached drawings prepared by O'Brien/Atkins Associates, PA, dated January 28, 2019, for existing site conditions and demolition plans, grading, and proposed redevelopment plans. The site is planned for redevelopment into an educational facility. The planned Applied Sciences Building is a proposed 20,467 square -foot (aerial extent), two-story structure. The remainder of the site will be redeveloped with paved surface parking areas and landscaping/grassed lawns. Redevelopments plans are not yet finalized and will be provided to Brownfields once finalized. 4) Do plans include demolition of structures)?: ❑ Yes ® No n Unknown ❑ If -yes, please check here to confirm that demolition will be conducted in accordance with applicable legal requirements, including without limitation those related to lead and asbestos abatement that are administered by the Health Hazards Control Unit within the Division of Public Health of the North Carolina Department of Health and Hum,n Services. If available, please provide a copy of your demolition permit. 5) Are sediment and erosion control measures required by federal, state, or local regulations? ® Yes ❑ No ❑ Unknown 4 EMP Version 2, June 2018 ® If tq& please check here to confirm that demolition will be conducted in .accordance with applicable legal requirements. If soil disturbance is necessary to install sediment and erosion control measures, they may not begin until this EMP is approved. 6) Which category of risk -based screening level is used or is anticipated to be specified in the Brownfields Agreement? Note: If children frequent the property, residential screening levels shall be cited in the Brownfields Agreement for comparison purposes. ®Residential ❑Non -Residential or Industrial/Commercial 7) Schedule for Redevelopment (attach construction schedule): a) Construction start date: September 2019 b) Anticipated duration (specify activities during each phase): Summer 2021 c) Additional phases planned? ® Yes C1 No If yes, specify the start date and/or activities if known: Unknown Start Date: Unknown Planned Activity: Unknown — based on funding past 2021 d) Provide the planned date of occupancy for new buildings: Summer 2021 CONTAMINATED MEDIA 11 Contaminated Media (attach tabulated data summaries for each impacted media and figure(s) with sample locations): Tabulated data and figures are provided in Appendix B. Part 1. Soil: Part 2. Groundwater: Part 3. Surface Water: Part 4. Sediment: Part 5. Soil Vapor: Part 6. Sub -Slab Soil Vapor: Part 7. Indoor Air: ® Yes ❑ No ❑ Suspected ® Yes ❑ No ❑ Suspected ❑ Yes ® No ❑ Suspected ❑ Yes ® No ❑ Suspected ® Yes ❑ No ❑ Suspected ❑ Yes ❑ No ® Suspected ❑ Yes ❑ No ® Suspected Existing known chemical concentrations, which are discussed in the sections below, were obtained during investigations completed by Terracon in July 2017 and April 2019. Arsenic was detected above its residential and commercial PSRGs at the site; however, the concentrations are considered representative of naturally occurring background levels based on the frequency and magnitude of the detections; as such, arsenic is not considered a contaminant at the site. Hexavalent chromium was detected above its residential PSRG in soil at the site. The following compounds have been detected above their Residential Vapor Intrusion Screening Level (VISLs) in soil vapor at the site: benzene, ethylbenzene, trichloroethene (TCE), and m&p-xylenes. The following compounds have been detected above their Commercial VISLs at the site: 1,3-butadiene and 1,2,4-trimethylbenzene. 5 EMP Version 2, June 2018 PART 1. SOIL — Please fill out the information below, using detailed site plans, if available, or estimate using known areas of contaminated soil and a conceptual redevelopment plan. Provide a figure overlaying new construction onto figure showing contaminated soil and groundwater locations. 1) Known or suspected contaminants in soil (list specific compounds): Soil assessment activities took place at the Brownfields property in July 2017 (7 soil borings) and April 2019 (10 soil borings). The initial July 2017 assessment consisted of collection of grab samples for analysis of volatile organic compounds (VOCs), semi -volatile organic compounds (SVOCs), Resource Conservation and Recovery Act (RCRA) 8 Metals, and total petroleum hydrocarbons diesel range organics (TPH-DRO). Soil samples collected in April 2019 consisted of grab samples for VOCs, and composited soil samples for SVOCs and RCRA 8 metals. The tables below present suspected contaminants in soil and a comparison to Residential and Non -Residential regulatory standards. Since groundwater is proposed for restriction; the Protection -of -Groundwater (PoG) PSRGs are not presented here. Conta Hexa Chro A minant T Sample Location and Sample Date of Interval (ft) Sampling Concentration Exceeding Screening Level Img/kg) Residential PSRG (mg/kg) Non -Residential PSRG (mg/kg) SB-15 (DUP-01) (0-3) SB-17 (0-3) SB-18 (0-3) SS-19 (0-3) 4/3/19 0.32J —1.6 valent SS-20 (0-3) 0.31 li-$ mium SS-21(0-3) SS-22 (0-3) SB-24 (0-3) SS-20(3-6) 4/3/19 0.341-0.55J SB-21(3-6) See Table 5 attached to the EMP for detected concentrations. J: Estimated concentration between the method detection limit and the reporting limit. 2) Depth of known or suspected contaminants (feet): Sample Soil Contaminant Depth (ft bls) Location Hexavalent Variable* 0-3 Chromium *- multiple locations, see tables in Section 1 of "Part 1. Soil" 3) Area of soil disturbed by redevelopment (square feet): Based on existing grading and cut/fill plans, approximately 146,000 square feet of the site will be disturbed. 4) Depths of soil to be excavated (feet): The planned maximum cut depth does not exceed 6 ft bls and the majority of the site will be cut to a depth of less than 2 ft bls. EMP Version 2, June 2018 5) Estimated volume of soil (cubic yards) to be excavated (attach grading plan) Based on the existing grading and cut/fill plans, approximately 5,208 cubic yards of soil will be excavated at the site. Approximately 2,360 cubic yards of fill soils will be required at the site, and it is assumed that cut soil from the site will be utilized as fill material in these areas. As such, approximately 2,848 cubic yards of cut soil might require off -site disposal. Additional soils that may be deemed unsuitable geotechnically for the site that originated from the cut areas may also require export from the site. If the disposal facility requires additional characterization with regard to exported soils, the soil will be sampled in accordance with NCDEQ regulations and the facility's requirements. 6) Estimated volume of excavated soil (cubic yards) anticipated to be impacted by contaminants: Areas likely impacted by contaminants were based on the assumption that material would be removed to the proposed cut depths around the borings presented in the table in the section above. If the impacted depth was below the cut, then the volume is not included. Hexavalent chromium was detected in excess of its residential PSRG in the following soil boring locations collected from the cut areas at depths of 0-3 feet below land surface (ft bls) SB-17, SB-18, and SB-19. Hexavalent chromium was detected in excess of its residential PSRG in soil borings SB-20, SB-21, and SB-22 at depths of 0-3 and 3-6 ft bls. Based on the existing cut/fill plans, it is estimated that approximately 2,848 cubic yards of excavated soil is impacted by hexavalent chromium. 7) Estimated volume of contaminated soil expected to be disposed offsite, if applicable: Based on the existing cut/fill plan, it is estimated that approximately 2,848 cubic yards of contaminated soil will be disposed off -site. Part 1.A. MANAGING ONSITE SOIL If soil is anticipated to be excavated from the Brownfield Property, relocated on the Brownfields Property, or otherwise disturbed during site grading or other redevelopment activities, please provide a grading plan that clearly illustrates areas of cut and fill (approximate areas & volumes are acceptable, if only preliminarydata available). 1) HAZARDOUS WASTE DETERMINATION: a) Does the soil contain a LISTED WASTE as defined in the North Carolina Hazardous Waste Section under 40 CFR Part 261.31-261.35?....................................... ❑Yes ®No ❑ If yes, explain why below, including the level of knowledge regarding processes generating the waste (include pertinent analytical results as needed). ❑ If yes, do the soils exceed the "Contained -Out" levels in Attachment 1 of the North Carolina Contained -In Policy? ................................................. ❑ Yes ® No Not Applicable b) NOTE: IF SOIL MEETS THE DEFINITION OF A LISTED HAZARDOUS WASTE AND EXCEEDS THE CONTAINED -OUT LEVELS IN ATTACHMENT 1 TO THE NORTH CAROLINA CONTAINED - IN POLICY THE SOIL MAY NOT BE RE -USED ON SITE AND MUST BE DISPOSED OF IN ACCORDANCE WITH DEQ HAZARDOUS WASTE SECTION RULES AND REGULATIONS. EMP Version 2, June 2018 c) Does the soil contain a CHARACTERISTIC WASTE? .................................... ❑ Yes ® No If yes, mark reason(s) why below (and include pertinent analytical results). ❑ Ignitability ❑ Corrosivity ❑ Reactivity ❑ Toxicity ❑ TCLP results ❑ Rule of 20 results (20 times total analytical results for an individual hazardous constituent on TCLP list cannot, by test method, exceed regulatory TCLP standard) ❑ If no, explain rationale: d) NOTE: IF SOIL MEETS THE DEFINITION OF A CHARACTERISTIC HAZARDOUS WASTE, THE SOIL MAYNOT BE RE -USED ON SITE AND MUST BE DISPOSED OF IN ACCORDANCE WITH DEQ HAZARDOUS WASTE SECTION RULES AND REGULATIONS. 2) Screening criteria by which soil disposition decisions will be made (e.g., left in place, capped in place with low permeability barrier, removed to onsite location and capped, removed offsite): ❑ Preliminary Health -Based Residential SRGs ❑ Preliminary Health -Based Industrial/Commercial SRGs ® Division of Waste Management Risk Calculator (For Brownfields Properties Only) ❑ Site -specific risk -based cleanup level. Please provide details of methods used for determination/explanation. 3) If known impacted soil is proposed to be reused within the Brownfields Property Boundary, please check the measures that will be utilized to ensure safe placement and documentation of same. Please attach a proposed location diagram/site map. ® Provide documentation of analytical report(s) to Brownfields Project Manager ® Provide documentation of final location, thickness and depth of relocated soil on site map to Brownfields Project Manager once known ❑ Geotextile to mark depth of fill material. Provide description of material: ® Manage soil under impervious cap ® or clean fill ® Describe cap or fill: Cap to consist of impervious hardscape cover (i.e. pavement, concrete, building slabs) or landscaped areas topped by at least one foot of cover soil. ® Confer with NC BF Project Manager if Brownfield Plat must be revised (or re -recorded if actions are Post -Recordation). ❑ GPS the location and provide site map with final location. ❑ Other. Please provide a description of the measure: i3 EMP Version 2, June 2018 4) Please describe the following action(s) to be taken during and following excavation and management of site soils: Management of fugitive dust from site ® Yes, describe the method will include: Monitoring of fugitive dust for constituents of concern (arsenic and hexavalent chromium) will not be conducted at the site beyond typical construction practices. Soils that are dry and have the potential to migrate through air from the site will be managed in accordance with typical construction practices, which will typically take the form of a light application via a water truck of water periodically to moisten soils and reduce airborne dust. ❑ No, explain rationale: Field Screeninaof.site soil ® Yes, describe the field screening method, frequency of field screening, person conducting field screening: Soils will be screened by a Qualified Environmental Professional (QEP) for visible discoloration and/or odors during grading/excavation activities in the area of identified contaminated soil on the central -western portion of the site. If observed, the suspected soils will be screened with a photo -ionization detector (PID) and/or PetroFLAG TPH Analyzer (PF-MTR-01) to identify relative concentration,; and evaluate the need for sampling and laboratory analysis. Additional screening in other areas of the site will not be conducted beyond visual observation for discoloration and/or odors by on -site construction personnel with a QEP on -call as needed during grading activities. Based on extensive sampling conducted across the site and lack of potential sources of contamination, additional screening is not warranted other than the former UST area. ❑ No, explain rationale: Soil Sample Collection ® Yes, describe the sampling method (e.g., in -situ grab, composite, stockpile, etc.): If during grading, impacted soils are discovered, procedures for screening and sampling the soils will be implemented as described in the section for "Contingency for encountering unknown tanks, drums, or other waste materials". Visual observation for discoloration and/or odors will be made by on -site construction personnel with a QEP on -call as needed during grading activities. ❑ No, explain rationale: If soil samples are collected for analysis, please check the applicable chemical analytes: ® Volatile organic compounds (VOCs) by EPA Method 8260 ® Semi -volatile organic compounds (SVOCs) by EPA Method 8270 EMP Version 2, June 2018 ® Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): Specify Analytical Method Number(s): EPA Method 6010D and EPA Method 7471B ❑ Pesticides: Specify Analytical Method Number(s): ❑ PCBs: Specify Analytical Method Number(s): ® Other Constituents & Respective Analytical Method(s) Hexavalent Chromium via EPA Method 7196A will be run on the soil sample with the highest total chromium laboratory result. In the case of soil stockpiles, if the hexavalent chromium analysis of that sample is below the hexavalent chromium PSRG, then the soil in the stockpile is considered to be below the hexavalent chromium PSRG. ® Check to confirm that stockpiling of known or suspected impacted soils will be conducted in accordance with Figure 1 of this EMP. Stockpile methodology should provide erosion control, prohibiting contact between surface water/precipitation and contaminated soil, and preventing contaminated runoff. Explain any variances or provide additional details as needed: Stockpiling of impacted soils at the site is not planned. If soils are stockpiled, they will be stockpiled in accordance with NCDEQ IHSB protocol. ❑ Final grade sampling of exposed native soil (i.e., soil that will not be under buildings or permanent hardscape). Select chemical analyses for final grade samples with check boxes below (Check all thatapply): ❑ Volatile organic compounds (VOCs) by EPA Method 8260 ❑ Semi -volatile organic compounds (SVOCs) by EPA Method 8270 ❑ Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): Specify Analytical Method Number(s): EPA Method 6010D and EPA Method 7471B ❑ Pesticides: Specify Analytical Method Number(s): ❑ PCBs: Specify Analytical Method Number(s): ❑ Other Constituents & Respective Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.): Specrfy Analytical Method Number(s): Please provide a scope of work for final grade sampling, including a diagram of soil sampling locations, number of samples to be collected, and brief sampling methodology. Samples should be collected from 0-2 ft below ground surface, with the exception of VOCs which should be taken from 1-2 ft below ground surface. Alternatively, a work plan for final grade sampling may be submitted under separate cover. ® if final grade sampling was NOT selected please explain rationale: Based on preliminary development plans for the site, exposed soils (not capped under structures or hardscapes) will be limited to landscaped areas of the site. If contaminated soils are encountered in areas of exposed soils, these soils will be managed in accordance with contingency procedures discussed in Part 9 of this EMP. Part 1.B. IMPORTED FILL SOIL NO SOIL MAY BE BROUGHT ONTO THE BROWNFIELDS PROPERTY WITHOUT PRIOR APPROVAL FROM THE BROWNFIELDS PROGRAM. According to the Brownfields IR 15, "Documenting imported soil (by 10 EMP Version 2,lune 2018 sampling, analysis, and reporting in accordance with review and written approval in advance by the Brownfields Program), will safeguard the liability protections provided by the brownfields agreement and is in the best interest of the prospective developer/property owner." Requirements for importing fill: 1) Will fill soil be imported to the site? ................................................ ❑ Yes ❑ No ® Unknown Based on the existing grading and cut/fill plan, if cut soils from the site are deemed to be geotechnically unsuitable for re -use on -site in fill areas, then the site will need imported off -site fill. 2) If yes, what is the estimated volume of fill soil to be imported? Based on the existing grading plan, fill material is not anticipated to be imported to the site. However, if imported fill material is needed, the soil will be characterized based on the requirements outlined in Section 1.B.5. 3) If yes, what is the anticipated depth that fill soil will be placed at the property? (if a range of depths, please list the range.) Not applicable. 4) Provide the source of fill, including: location, site history, nearby environmental concerns, etc. Attach aerial photos, maps, historic Sanborn maps and a borrow source site history: At this time, the site is not anticipated to require imported off -site fill material. If fill material is needed at the site, the soil will be characterized based on the requirements outlined in Section 1.6.5. 5) PRIOR TO ITS PLACEMENT AT THE BROWNFIELDS PROPERTY, provide a plan to analyze fill soil to demonstrate that it meets acceptable standards applicable to the site and can be approved for use atthe Brownfields property. If off -site import fill is needed for the site, Terracon will provide a sampling and analysis plan to be submitted separately to Brownfields and sample for the analytes listed in Section 1.B.6. 6) Please check the applicable chemical analytes for fill soil samples. (Check all that apply): ® Volatile organic compounds (VOCs) by EPA Method 8260 ® Semi -volatile organic compounds (SVOCs) by EPA Method 8270 ® Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): Specify Analytical Method Number(s): EPA Method 6010D and EPA Method 7471B ❑ Pesticides: Specify Analytical Method Number(s): ❑ PCBs: Specify Analytical Method Number(s): ❑ Other Constituents & Respective Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.): Specify Analytical Method Number(s): 7) The scope of work for import fill sampling may be provided below or in a Work Plan submitted separately for DEQ review and approval. Attach specific location maps for in -situ borrow sites. If using a quarry, provide information on the type of material to be brought onto the Brownfields Property. 11 EMP Version 2, June 2018 If off -site import fill is needed for the site, Terracon will provide a sampling and analysis plan to be submitted separately to Brownfields. Part 1.C. EXPORTED SOIL NO SOIL MAY LEAVE THE BROWNFIELDS PROPERTY WITHOUT APPROVAL FROM THE BROWNFIELDS PROGRAM. FAILURE TO OBTAIN APPROVAL MAY VIOLATE A BROWNFIELDS AGREEMENT CAUSING A REOPENER OR JEOPARDIZING ELIGIBILITY IN THE PROGRAM, ENDANGERING LIABILITY PROTECTIONS AND MAKING SAID ACTION POSSIBLY SUBJECT TO ENFORCEMENT. JUSTIFICATIONS PROVIDED BELOW MUST BE APPROVED BY THE PROGRAM IN WRITING PRIOR TO COMPLETING TRANSPORT ACTIVITIES. Please refer to Brownfields IR 15 for additional details. 1) If export from a Brownfields Property is anticipated, please provide details regarding the proposed export actions. Volume of exported soil, depths, location from which soil will be excavated on site, related sampling results, etc. Provide a site map with locations of export and sampling results included. The areas of cut that will be used as on -site fill and those that will be exported off -site are not known at this time. Based on cut/fill analysis, 2,848 cubic yards of cut might require export from the site. 2) To what type of facility will the export Brownfields soil be sent? The off -site disposal facility has not been determined at this time. ® Subtitle D/Municipal Solid Waste Landfill (analytical program to be determined by landfill): If soils are taken to this type of the facility, the required analytical program will be determined by the accepting facility. ® Permitted but Unlined Landfill (i.e. LCID, C&D, etc.) If soils are taken to this type of the facility, the required analytical program will be determined by the accepting facility. ❑ Landfarm or other treatment facility: ❑ Use as fill at another suitable Brownfields Property — determination that a site is suitable will require, at a minimum, that similar concentrations of the same or similar contaminants already exist at both sites, use of impacted soil willnot increase the potential for risk to human health and the environment at the receiving Brownfields property, and thata record of the acceptance of such soil from the property owner of the receiving site is provided to Brownfields. Please provide additional details below. ❑ Use as Beneficial Fill off -site at a non-Brownfields Property - Please provide documentation of approval from the property owner for receipt of fill material. This will also require approval by the DEQ Solid Waste Section. Additional information is provided in IR 15. Please provide additional details below. 3) Additional Details: (if transfer of soil to another property is requested above, please provide details related to the proposed plans). 12 EMP Version 2, June 2018 Not applicable/planned. Part 1.D. MANAGEMENT OF UTILITY TRENCHES ❑ Install liner between native impacted soils and base of utility trench before filling with clean fill (Preferred) ® Last out, first in principle for impacted soils (if soil can safely be reused onsite and is not a hazardous waste), i.e., impacted soils are placed back at approximately the depths they were removed from such that impacted soil is not placed at a greater depth than the original depth from which it was excavated. During initial site grading activities, workers should use appropriate safety personal protective equipment (PPE). The on -site Health and Safety Plan will address potential exposure of workers to COCs. Soils will at times need to be disturbed for the construction of utilities or other structures. With respect to subsurface utility construction at the site, the general rule will be to remove and stockpile soils so that a "last out, first in" process occurs. During excavation, soils in the upper 2 feet should be stockpiled and segregated as the first materials removed. These soils/fill materials will be the last returned to the excavation during backfilling. Soils will typically "bulk" or expand in volume when disturbed by excavation. The contractor will compact these materials into place according to the compaction requirements of the construction design. If no specifications for compacted fill exist, the contractor will tamp the materials in place using the mechanical excavator or equivalent. Utilities or structures will replace a certain volume of soils in these areas, resulting in excess soils as excavation spoils. After the initial grading of the site, the worker and contractor should plan from onset of construction to maintain a cap comprised of either (a) clean fill, or (b) other barrier approved by the NCDEQ for areas that will not be capped with a building, asphalt, or concrete surface. If excess contaminant impacted soils/fill are produced from excavation as spoils which cannot be restored to original depths through the process of "first out, last in", they must be handled with special care. The worker or contractor will work with the Brownfields Project Manager to ensure that, if the soils are contaminated, they are either properly re -used on -site or disposed of off -site. ® Evaluate whether necessary to install barriers in conduits to prevent soil vapor transport, and/or degradation of conduit materials due to direct impact with contaminants? It is not likely that the soil vapor contaminants observed at the site are at high enough concentrations to degrade subsurface utilities. The NCDEQ risk calculator indicates the detected concentrations exceed soil gas to indoor air intrusion risk at the site for residents; however, the risk calculator did not indicate unacceptable risk to non-residential workers at the site. In addition, based on the existing site plans, it does not appear that utility trenches are located in the areas of elevated soil vapor concentrations. As such, vapor barriers are not warranted within utility trenches. ❑ If yes• provide specifications on barrier materials: ® If no. include rationale here: 13 EMP Version 2, June 2018 See above Other comments regarding managing impacted soil in utility trenches: Concerns and methods for environmental handling of soils do not preclude nor modify any of the Occupational Safety and Health Administration (OSHA) requirements for worker safety incumbent upon contractors for regular site safety and trenching/excavation activities. OSHA requirements will dictate adjustments of the soil management methods where necessary. PART 2. GROUNDWATER — Please fill out the information below. 1) What is the depth to groundwater at the Brownfiields Property? Depth to groundwater ranges from approximately 30 to 45 ft bis at the site based on depth to water from former temporary monitoring wells. Groundwater appears to exist under semi -confined conditions; the stabilized depth to groundwater within the temporary monitoring wells ranged from 10.7 to 23.4 ft bls. 2) Is groundwater known to be contaminated by ® onsite ❑ offsite ❑ both ❑ or unknown sources? Describe source(s): Groundwater at the site is currently restricted by a Notice of Residual Petroleum (NORP) due to Leaking Underground Storage Tank (LUST) Incident No. 39154. While concentrations of contaminants of concern were not identified above their 2L Standards during the 2017 LSI, PCE was detected at low concentrations. In addition, low concentrations of VOCs in soil vapor at the site may suggest that groundwater impacts exist elsewhere on site. 3) What is the direction of groundwater flow at the Brownfields Property? Based on surficial topography, inferred groundwater flow is estimated to flow south and/or west. Temporary monitoring wells were not surveyed and therefore a groundwater elevation map was not developed for the site. 4) Will groundwater likely be encountered during planned redevelopment activities? C] Yes No If yes, describe these activities: Not applicable Regardless of the answer; in the event that contaminated groundwater is encountered during redevelopment activities (even if no is checked above), list activities for contingent management of groundwater (e.g., dewateringof groundwater from excavations or foundations, containerizing, offsite disposal, discharge to sanitary sewer, NPDES permit, or sampling procedures): Excavations in areas where groundwater is encountered should be allowed to re -infiltrate for approximately 24 hours (if it does not affect the construction schedule) or remove the groundwater so that construction activities may proceed. If groundwater must be removed from excavations, it will be pumped out via vacuum truck and taken off -site for disposal at a permitted facility. The analytical program for the removed groundwater will be determined by receiving facility. Disposal of water must comply with local, state, and federal laws. Direct discharge requires an NPDES permit and indirect discharge (to the municipal sanitary sewer) must be negotiated with the City or County. If the PD chooses to obtain a discharge permit from the City or County, copies of approval documentation will be provided to the 14 EMP Version 2, June 2018 Brownfields Program before disposal occurs. 5) Are monitoring wells currently present on the Brownfields Property? ................. Dyes IONo If yes, are any monitoring wells routinely monitored through DEQ or other agencies? ..................... .......................... ....... ................................ ...................... ❑Yes ❑No 6) Please check methods to be utilized in the management of known and previously unidentified wells. ❑ Abandonment of site monitoring wells in accordance with all applicable regulations. It is the Brownfields Program's intent to allow proper abandonment of well(s) as specified in the Brownfields Agreement, except if required for active monitoring through another section of DEQ or the EPA. ❑ location of existing monitoring wells marked ❑ Existing monitoring wells protected from disturbance ® Newly identified monitoring wells will be marked and protected from further disturbance until notification to DEQ Brownfields can be made and approval for abandonment is given. 7) Please provide additional details as needed: Please note, disturbance of existing site monitoring wells without anproval by DEQ is not permissible. If monitoring wells are damaged and/or destroyed, DEQ may require that the PD be responsible for replacement of the well. PART 3.5URFACE WATER -Please fill out the information below. 1) Is surface water present at the property? ❑ Yes ® No 2) Attach a map showing the location of surface water at the Brownfields Property. 3) Is surface water at the property known to be contaminated? ❑ Yes ❑ No 4) Will workers or the public be in contact with surface water during planned redevelopment activities? ❑ Yes ❑ No 5) In the event that contaminated surface water is encountered during redevelopment activities, or clean surface water enters open excavations, list activities for management of such events (e.g. flooding, contaminated surface water run-off, stormwater impacts): Workers are unlikely to encounter surface water as water drainage features were not observed on site. Workers may encounter stormwater from rain events. Groundwater is not anticipated to discharge into open excavations. Excavations and trenches shall be graded, bermed, or provided with an equivalent barrier where necessary to help prevent surface water and/or stormwater from entering excavations and/or leaving the site boundaries. Stormwater or water from an unidentified source that collects in 15 EMP Version 2, June 2018 excavation areas will be removed so that construction activities may proceed. The water will be containerized or diverted to an on -site stormwater management basin where the water will be sampled for disposal characterization before it is allowed to leave the site. Based on the types of contaminants documented on the site, water samples will be analyzed for VOCs, SVOCs, RCRA 8 metals, and hexavalent chromium. If containerized water is determined to be above regulatory standards, the Brownfields Project Manager will be contacted, and the water will be disposed in accordance with regulatory requirements. PART 4. SEDIMENT — Please fill out the information below. 1) Are sediment sources present on the property? ❑ Yes ® No 2) If yes, is sediment at the property known to be contaminated: ❑ Yes ❑ No 3) Will workers or the public be in contact with sediment during planned redevelopment activities? ❑ Yes ® No 4) Attach a map showing location of known contaminated sediment at the property. 5) In the event that contaminated sediment is encountered during redevelopment activities, list activities for management of such events (stream bed disturbance): Not Applicable. There are no known current or historical natural drainage features on the site. PART 5. SOIL VAPOR — Please fill out the information below. 1) Do concentrations of volatile organic compounds at the Brownfields property exceed the following vapor intrusion screening levels (current version) in the following media: IHSB Residential Screening Levels: Soil Vapor:...........® Yes ❑ No ❑ Unknown Groundwater:.....❑ Yes ® No ❑ Unknown IHSB Industrial/Commercial Screening Levels: Soil Vapor:...........® Yes ❑ No ❑ Unknown Groundwater:.....❑ Yes ® No ❑ Unknown 2) Attach a map showing the locations of soil vapor contaminants that exceed site screening levels. Sample locations are provided in Exhibit 1—please reference Table 3. 3) If applicable, at what depth(s) is soil vapor known to be contaminated? Soil vapor points were collected at depths of approximately 4 to 5 ft bls across the site. The detected concentrations were entered into the NCDEQ risk calculator, which indicated that the detected concentrations exceed the acceptable residential cumulative non -carcinogenic risk. 4) Will workers encounter contaminated soil vapor during planned redevelopment activities? 16 EMP Version 2, June 2018 ® Yes ❑ No ❑ Unknown 5) In the event that contaminated soil vapor is encountered during redevelopment activities (trenches, manways, basements or other subsurface work,j list activities for management of such contact: Volatile organic compounds (VOCs) have been identified in localized areas within soils, soil vapor and the groundwater beneath the site. During construction, site workers will be made of aware of the possible presence of contaminated soil vapors particularly in trenches and other excavations and they will be made aware of possible indications of vapors. Terracon will conduct periodic vapor screening with real-time field instrumentation during excavation activities. Should elevated vapors being identified, work will be stopped and will not begin again until vapor concentration measurements return to site background levels. PART 6. SUB -SLAB SOIL VAPOR — Please fill out the information below if existing buildings or foundations will be retained in the redevelopment. 1) Are sub -slab soil vapor data available for the Brownfields Property? ❑ Yes ® No ❑ Unknown 2) If data indicate that sub -slab soil vapor concentrations exceed screening levels, attach a map showing the location of these exceedances. 3) At what depth(s) is sub -slab soil vapor known to be contaminated? 00-6 inches ❑Other, please describe: Not applicable. Vapors will be evaluated as discussed in part 5. 4) Will workers encounter contaminated sub -slab soil vapor during planned redevelopment activities? ❑ Yes ❑ No ❑ Unknown 5) In the event that contaminated soil vapor is encountered during redevelopment activities, list activities for management of such contact Volatile organic compounds (VOCs) have been identified in localized areas within soils beneath the site. Vapors will be evaluated, as discussed in Part 5. PART 7. INDOOR AIR — Please fill out the information below. 1) Are indoor air data available for the Brownfields Property? ❑ Yes ® No ❑ Unknown 2) Attach a map showing the location(s) where indoor air contaminants exceed site screening levels. 3) If the structures where indoor air has been documented to exceed risk -based screening levels will not be demolished as part of redevelopment activities, will workers encounter contaminated indoor air during planned redevelopment activities? ❑ Yes ❑ No ❑ Unknown 4) In the event that contaminated indoor air is encountered during redevelopment activities, list activities for management of such contact: Part 8 - VAPOR INTRUSION MITIGATION SYSTEM — Please fill out the information below. Is a vapor intrusion mitigation system (VI MS) proposed for this Brownfields Property? ® Yes ❑ No ❑ Unknown 17 EMP Version 2, June 2018 Based on the NCDEQ risk calculator results, VIMS are proposed for the Applied Sciences Building. If yes, ❑ VIMS Plan Attached or ® VIMS Plan to be submitted separately If submitted separately provide date: Planned July 2019 VIMS Plan shall be signed and sealed by a NC Professional Engineer if no, please provide a brief rationale as to why no vapor mitigation plan is warranted: Part 9 - CONTINGENCY PLAN — encountering unknown tanks, drums, or other waste materials in this section please provide actions that will be taken to identify or manage unknown potential new sources of contamination. During redevelopment activities, it is not uncommon that unknown tanks, drums, fuel lines, landfills, orother waste materials are encountered. Notification to DEQ Brownfields Project Manager, LIST Section, Fire Department, and/or other officials, as necessary and appropriate, is required when new potential source(s) of contamination are discovered. These Notification Requirements were outlined on Page 1 of this EMP. Should potentially impacted materials be identified that are inconsistent with known site impacts, the DEQ Brownfields Project Manager will be notified and a sampling plan will be prepared based on the EMP requirements and site -specific factors. Samples will generally be collected to document the location of the potential impacts. Check the following chemical analysis that are to be conducted on newly identified releases: ® Volatile organic compounds (VOCs) by EPA Method 8260 ® Semi -volatile organic compounds (SVOCs) by EPA Method 8270 ® Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): EPA Method 6010D and EPA Method 7471E ❑ Pesticides: Specify Analytical Method Number(s): ❑ PCBs: Specify Analytical Method Number(s): ® Other Constituents & Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.) Please note, if field observations indicate the need for additional analyses, they should be conducted, even if not listed here. Hexavalent Chromium via EPA Method 7196A will be run on the soil sample with the highest total chromium laboratory result. In the case of soil stockpiles, if the hexavalent chromium analysis of that sample is below the hexavalent chromium PSRG, then the soil in the stockpile is considered to be below the hexavalent chromium PSRG. Please provide details on the proposed methods of managing the following commonly encountered issues during redevelopment of Brownfields Properties. There is a possibility that materials of unknown type (tanks, drums or impacted soils) could be present on the site. The worker and contractor must be able to recognize when conditions change at the site. Field staff must be able to determine if a new discovery of changed chemical conditions has occurred, and if so, if it is significant. If there is question of the significance of a new discovery or changed condition, the environmental manager (Terracon) or equivalent qualified environmental professional should make the 18 EMP Version 2, June 2018 determination. The worker or contractor should be alert during earthwork for the following indications that will trigger the possible identification of a new condition not addressed by previous investigations and evaluation. Underground Storage Tanks: Prior assessment reports have not identified suspected underground storage tanks (USTs) at the site. The worker and contractor should be cognizant of man-made containers or remnants of containers of any material. The presence of whole or crushed drums or containers in excess of one gallon in the soils in combination with odor or unique color changes may be indicative of a changed condition. Should USTs, drums, or similar items be encountered during redevelopment activities, the environmental manager (Analee Farrell) should be contacted immediately, and the identified item should be left as encountered. The NC Brownfields Program project manager will be notified by site's environmental manager. Following notification of the NC Brownfields Program project manager, the UST will be inerted of potential combustible vapors and removed from the ground. The UST will be taken offsite for proper disposal and soil samples will be collected from beneath the UST and analyzed for VOCs (EPA Method 8260B), SVOCs (EPA Method 8270D), and RCRA 8 Metals (EPA Methods 6010D and 7471B). Documentation of the UST removal activities, UST disposal, and sampling results will be provided to the NC Brownfields Program project manager upon receipt by the environmental manager. Sub -Grade Feature/Pit: If during redevelopment activities, an unknown sub -grade feature/pit is encountered, the environmental manager (Analee Farrell) should be notified immediately. The environmental manager will supervise exploratory excavation in and around the feature and soils will be screened for potential impacts. If potential impacts are identified, the NC Brownfields Program project manager will be notified and soil samples will be collected from the area of potential impacts and analyzed for VOCs (EPA Method 8260B), SVOCs (EPA Method 8270D), and RCRA 8 Metals (EPA Methods 6010D and 7471B). The location of the feature will be recorded for future reference. Soil sampling results will be provided to the NC Brownfields Program project manager. Buried Waste Material: If during redevelopment activities, buried waste material is encountered, the environmental manager (Analee Farrell) should be notified immediately, and the identified waste should be left as encountered. The NC Brownfields Program project manager will be notified by site's environmental manager. Following notification of the NC Brownfields Program project manager. The environmental manager will supervise exploratory excavation in and around the waste and soils will be screened for potential impacts. The waste should be segregated from surrounding soils, inventoried and taken offsite for proper disposal. If potential impacts are identified, the NC Brownfields Program project manager will be notified and soil samples will be collected from the area of potential impacts and analyzed for VOCs (EPA Method 8260B), SVOCs (EPA Method 8270D), and RCRA 8 Metals (EPA Methods 6010D and 7471B). The location of the feature will be recorded for future reference. Documentation of the waste removal activities, waste disposal, and sampling results will be provided to the NC Brownfields Program project manager upon receipt by the environmental manager. Re -Use of Impacted Soils On -Site: See Part 1— Soil and Part 1.A — Managing On -site Soil for details regarding the re -use of impacted soil on - site. 19 EMP Version 2, June 2018 If unknown, impacted soil is identified on -site, management on -site can be considered after the project team provides the necessary information, outlined in Part I.A. Item 11, for Brownfields Project Manager approval prior to final placement on -site. If other potential contingency plans are pertinent, please provide other details or scenarios as needed below: If impacted soil is noted at the site, the suspect soils should be isolated as soon as possible from contact and disturbance by rain and wind until screening identification can be made. Construction flagging tape attached to stakes can be used to prevent accidental movement of the soils by earthwork operations. Covering of the soils with plastic sheeting and weight the covering with planks, sandbags, or equivalent should occur. The soils should be screened for volatile and semi -volatile organic compounds. The screening will be conducted by the on -site environmental manager or other qualified environmental professional. The owner or contractor may alternatively go directly to laboratory testing for identification purposes. Screening tests can be conducted on the site and can produce preliminary results quickly. The field test does not produce a precise measurement of the amounts of contaminants found in the soils, but indicates whether contaminants are likely present and warrant further caution and actual measurement. If preliminary screening activities indicate a changed condition may be present, it may be necessary to conduct laboratory testing to determine if contaminants are present in the soil and actually pose a significant risk. Laboratory testing requires time that varies depending on the type of test needed. In general, laboratory testing for VOCs and SVOCs can take approximately 5 to 7 business days unless special arrangements are made with the laboratory for more expensive "RUSH" results. During this time, the suspected impacted soils should be further isolated from worker and public exposure. Special handling and care must be taken in sampling and transporting soils for the laboratory tests to be accurate. The workers in physical contact with suspect impacted soil should have training consistent with 29 OSHA 1910.120. For small volumes, the soil can be placed temporarily in steel open -top drums with bolt -on lids. After sealing, the drum should be clearly labeled with pertinent information such as "Do Not Disturb", sample number, date, and name of sampler. The drums should be placed in an on -site area protected from general traffic. For larger volumes, it can be effective to place the soils into commercial roll -off dumpsters which have been previously washed and cleaned of residues or soils can be stockpiled on plastic sheeting. The containers will not have free -draining bottoms and stockpiles shall be graded, bermed, or provided with an equivalent barrier where necessary to help prevent water run-off. The tops of the containers or stockpiles will then be covered with plastic sheeting and secured against wind and rain. The commercial containers or stockpiles should be placarded with information similar to the notation on drums. POST -REDEVELOPMENT REPORTING ® Check this box to acknowledge that a Redevelopment Summary Report will be required for the project. If the project duration is longer than one year, an annual update is required and will be due by January 31 of each year, or 30 days after each one-year anniversary of the effective date of this EMP (as agreed upon with the Project Manager). These reports will be required for as long as physical redevelopment of the Brownfields Property continues, except that the final Redevelopment Summary 20 EMP Version 2, June 2018 Reportwill be submitted within 90 days aftercompletion of redevelopment. Based on the estimated construction schedule, the first Redevelopment Summary Report it anticipated to be submitted on Ff Br 020 The Redevelopment Summary Report shall include environment -related activities since the last report, with a summary and drawings that describes: L actions taken on the Brownfield; Property; 2. soil gradins and art and fill actions; 3. methodologv(les) employed for field screen;rw.r sampling and laboratory analysis of environmental media; 4. stnckpging, containerizing, decontaminating, treating, handling, laboratory analysis and ultimate disposition of any sal, groundwater or other materials suspected or confirmed to be contaminated with regulated substances; and S. removal of any contaminated sal, water or other contaminated materials (for example, concrete, demolition debris) from the Brownfieids Property (copies of all legally rewired manifests shall be included). ® Check box to aeknowieds a consent to provide a NC licensed P.G. or P.E. sealed, Redevelopment Summary Report in compliance with the site's BrowunfieldsAgreement. APPROVAL 51"GNATIJRES Brownfields Project Number. 22034-18-32 Brows nfields Proms Name: Fahey Finishing Plant Prospective nevelope-. Durham Technical Community College Date: Consultwm Terracon 94uhants Inc DM: � f Printed yi . Michaeffi. Jordan, PG / Senior GeoWIst / Terracon Consultants la Brad Atfdnson Date: 21 EMP Version 2, June 2018 u C L■ ,.1 5 5 4 3 2 RIM ELEV (8C)=34725' ° \ INV IN=326.95' (N) -A4,1_V IN-339.05' (E) INV OU7 `326.85' (S) l \ SSMH—#6488 RlM EIS<=348.93' —327 38' \ INV / UT \/(S) INV OUT=32718' () t��GRA ✓£LS �GJ / SSIi�I #13524 RIM EJ35J.39� _-7N I' OV T= 326 69 Ls � i G�j, I I• i 3 \ \ \ GRATED INLET J�13832 _— RIM ELEV (BC—334.33' /, V OUT=333. (NW) \) I SGRA ✓EL /e1.1:3:7:k1v1Ie11I[elm BB BOTTOM OF BANK BLDG BUILDING BM BOOK OF MAPS BW BARBED WIRE C&G CURB AND GUTTER CLF CHAIN -LINK FENCE CLF W/BW CHAIN -LINK FENCE WITH BARBED WIRE CLF W/RW CHAIN -LINK FENCE WITH RAZOR WIRE CMF CONCRETE MONUMENT FOUND CMP CORRUGATED METAL PIPE CONC CONCRETE CPP CORRUGATED PLASTIC PIPE DB DEED BOOK ELEC ELECTRICAL FFE FINISHED FLOOR ELEVATION HVAC HEATING VENTILATION & AIR CONDITIONING INV INVERT ELEVATION IPF IRON PIPE FOUND LS LANDSCAPING N/F NOW OR FORMERLY OHE OVER HEAD ELECTRICAL PB PLAT BOOK PG PAGE PKF PK NAIL FOUND PL PROPERTY LINE RCP REINFORCED CONCRETE PIPE RD ROOF DRAIN R/W RIGHT-OF-WAY SF SQUAREFEET SSMH SANITARY SEWER MANHOLE STMH STORM DRAIN MANHOLE SW SIDE WALK TB TOP OF BANK TCP TERRA-COTTA PIPE TYP TYPICAL W/ WITH WDF WOODEN FENCE WIF WROUGHT IRON FENCE WRF WIRE FENCE �roaxE�. F GENERAL NOTES: XI 1 1. THIS SITE IS IN THE CAPE FEAR RIVER BASIN. 2. THIS SITE IS NOT IN A WATERSHED OVERLAY DISTRICT. .4�5'CLF 3. THERE ARE NO STEEP SLOPES ON SITE. 4. THERE ARE NO WETLANDS ON SITE. r l 5 NO PORTION OF THE SUBJECT PROPERTY IS IN A SPECIAL FLOOD HAZARD AREA PER FEMA MAP # 372008300J, EFFECTIVE DATE MAY 2, 2006. I I X C- 5. NO NATURAL OR HISTORICAL INVENTORY SITES HAVE BEEN IDENTIFIED ON THIS SITE OR ADJOINING \ PROPERTIES. w 6. UTILITY STATEMENT: THE UNDERGROUND UTILITIES o SHOWN HAVE BEEN LOCATED FROM FIELD SURVEY I I I \ INFORMATION AND EXISTING DRAWINGS. THE SURVEYOR MAKES NO GUARANTEE THAT THE o UNDERGROUND UTILITIES SHOWN COMPRISE ALL °ff SUCH UTILITIES IN THE AREA, EITHER IN SERVICE OR ABANDONED. THE SURVEYOR FURTHER DOES NOT \ o® WARRANT THAT THE UNDERGROUND UTILITIES \ SHOWN ARE IN THE EXACT LOCATION INDICATED 1®, ALTHOUGH HE DOES CERTIFY THAT THEY ARE \ LOCATED AS ACCURATELY AS POSSIBLY FROM INFORMATION AVAILABLE. THE SURVEYOR HAS NOT PHYSICALLY LOCATED THE UNDERGROUND UTILITIES. \ 0 7. A COPY OF THE APPROVED SITE PLAN MUST BE ON SITE AND � AVAILABLE FOR PERIODIC INSPECTION AND USE DURING CONSTRUCTION TO EVALUATE COMPLIANCE WITH THE ri \ / APPROVED SITE PLAN. REQUESTED INSPECTIONS WILL NOT V TAKE PLACE IF THE JOB SITE COPY IS NOT AVAILABLE AND \ RE -INSPECTION FEES WILL BE CHARGED. 8. CITY OF DURHAM STANDARDS AND SPECIFICATIONS ARE TO \ G BE USED. ,■ 9. THIS NOTE SHALL APPLY TO EACH AND EVERY SHEET IN THIS G SET. \ THE ENGINEER DOES NOT GUARANTEE THAT ALL EXISTING II FACILITIES SUCH AS PIPELINES, ELECTRICAL LINES, CONDUIT, TELEPHONE CABLE, SERVICE CONNECTIONS OR OTHER \ FACILITIES ARE SHOWN ON THE PLANS. IT SHALL BE THE /v CONTRACTOR'S RESPONSIBILITY TO HAVE ALL UTILITIES LOCATED BY THEIR RESPECTIVE OWNERS, FIELD MARK THE UTILITY LOCATIONS, AND PROTECT ALL SUCH EXISTING FACILITIES PRIOR TO BEGINNING CONSTRUCTION. THE 4' CONTRACTOR IS FULLY RESPONSIBLE FOR NOTIFYING ALL " UTILITY OWNERS IN ACCORDANCE WITH NC GENERAL STATUTE -CHAPTER 87, ARTICLE 8, THE UNDERGROUND X X ~ DAMAGE PREVENTION ACT. \ INV I /0.5 N INVOCF= N.4B' \ 1 l / I I I I INV OU 40' SW P e ' I \ INLET —THROAT D 8t \\� EL V=37369' 12.C\ J ) � � �� �• � \ 11^RCPae258 � 11 , • � \ � � � SSIBLE U/G lNV/N=3B7.3>� / P / / 1I _---- ----- ♦ �g l l//✓UNION BOX TION/ /-77' I h ORA✓ELS ' ' \ I �V `� / / j' ✓ / ® •i• • 4.s' I r• I� = / I .S I m \ I \ 6B s I �� _�\ , • • . • .t • •. • ` / i I l 1 SWOODSS � X V I a. 30.5" O /� t ' •;• :'• :.t•:-' • .:,' `.,3 ��� I � � ; ml � � � • y A� •s I I II � / \ t \ I • r• •'• • .•:.RETE .t •t i I I III I I n 47' FFE=376.95' NOTES: \ \� ':�`` •':�• :l ';. :: I \ I I II \\� / 3-STORY qp I I I ,:•, / I I I I1. THE EXISTING CONDITIONS INFORMATION WAS NOT P. HAIL WYNN, ✓R 63 r AKE BRICK / METAL BUILDING j I I I PROVIDED OR VERIFIED BY CALYX ENGINEERS AND IS -804- \ \ \ \ ✓ • FFE=376.94' I I / 111111�1 �/ / SHOWN FOR REFERENCE ONLY. \ I 1111 ��\\\� I� � �I \\ � I• II� V 1 1 � GRATED INLET #9688 \ 1 I I \ RIM MAPLEELEV-3B Mg FILLED WITH DEBRIS � •' moo, � I I ( ` '•M �H I I , I \ `l! Ts� _ 11\\\\ / CTAAL/ �^, l < I �m� I \ SYMBOL LEGEND • PROPERTY CORNER FOUND 0 SEWER GREASE TRAP CONC MONUMENT FOUND OS SEWER MANHOLE O BOLLARD SEWER CLEANOUT — SIGN OT TELEPHONE MANHOLE OD STORM DRAINAGE MANHOLE TELEPHONE PEDESTAL ® CATCH BASIN ❑T TELEPHONE HANDHOLE ❑ GRATED INLET © TELEPHONE CALLBOX Mil CURB INLET ® FIBEROPTIC HANDHOLE r" OPEN THROAT CURB INLET Fo FIBEROP11C MANHOLE d FLARED -END SECTION e CABLE TV PEDESTAL RDO ROOF DRAIN 0 CABLE TV MANHOLE * LIGHT POLE ® CABLE TV HANDHOLE E AREA LIGHT � FIRE HYDRANT `a, UTILITY POLE ® WATER MANHOLE `Z, UTILITY POLE WITH DROP ® WATER METER `�t UTILITY POLE WITH LIGHT e WATER VALVE `t, UTILITY POLE LIGHT & DROP ® WELL (POTABLE) \ GUY WIRE / ANCHOR POST INDICATOR VALVE 0 ELECTRIC MANHOLE ❑U UNKNOWN UTILITY HANDHOLE ❑f ELECTRIC TRANSFORMER QU UNKNOWN UTILITY MANHOLE ® ELECTRIC HANDHOLE EVERGREEN TREE d] ELECTRIC METER DECIDUOUS TREE ® TRAFFIC SIGNAL HANDHOLE 0 SPOT ELEVATION M HVAC UNIT ® MAILBOX © GAS METER —2 DESTINATION UNKNOWN m GAS VALVE LINE CONTINUES b GAS TEST STATION GUTTER I 3 � 2 �PHAL \i 30" CURB & GUTTER (TYP" GRAPHIC SCALE 40 0 20 40 80 160 ( IN FEET ) 1 inch = 40 ft. C ■ w� /., W o m U Z W O Q N N Y O y O O L N y L Q CV d L.L n• Q O YO 'm co >v O N _ C H p p p 0 0 c. CL O Q X O '... C CO-� O N COL O 2 o� c m a� m 0 � o rn rn Q w_ a o a6� z Z Z Z Q3 Jai om�:� + Z n �Y 40 W Kzq 9` Gl W � Z 4,u w Ln Z n¢ 0 a w a U U Z h.Il �•,"'1"1111 N I IIr yhCA :o x 7 co • �I •rr�~MIII��I / U►�Hti► w Q 0 w J 0 w U U7 z O N ua Lu 0 V O 0 W H W_ U) M CD o � Q% U -:L, O z Q 9t Cu E w W M � o Z `9 0 cU) ISSUED SETS CONSTRUCTION 03-15-19 DOCUMENTS Drawn By FNM Project No. 2017050 C1 00 EXISTING CONDITIONS X M C M A 5 9 4 3 1 2 00 /00 TIER: URBAN DEVELOPMENT / 0 EXISTING ASPHALT — ZONING:OI / CURRENT USE: PARKING O / ao 0 / od /° O s/ a a EXISTING PARKING O O 00 0 Q a a o 0 O O O=C, 4 / o0 O EXISTING o LANDSCAPING EXISTING UNIT RETAINING WALL 0 O � O fl �F EXISTING TREES EXISTING UNIT EXISTING o RETAINING WALL TREES PROPERTY LINE — i j f PARCEL ID: 118849 0 C LAWSON ST. PROPERTY LINE ° � I • EXISTI G TREES I l SITE OF FUTURE BUILDING Bman } i I I I � LIMITS OF DISTURBANCE CONCRETE WALK o AND STEPS TO maw Mow Mow PARKING LOT ftne BIORETENTION BUILDING A - 11 . .1, i i i i ii . 1 1 1 1 1 1111 1 r TIER .4TATF . ° _ .. TIER: ETA°TE - - - - ----- • General Site Notes 1.The site will be fully compliant with the North Carolina accessibility codes (ansi 117.1 -2009 and chapter 11 of the ncbc) unless and except in areas where an approved statement from a site engineer, surveyor or architect verifies that site conditions exist where the topography of the site is extreme and only alternate methods of compliance are possible. An as -built survey of the site, performed by the design professional or designee, must be submitted to the building inspections department certifying that all site accessibility code requirements such as curb cuts, ramp slopes, sidewalk slopes and widths, and cross slopes meet the requirements of the nc accessibility code prior to co issuance. 2.Construction drawing and site plan approvals for this project are contingent on receiving stormwater approval from ncdeq. Failure to obtain approval from the state shall nullify any previous city of Durham site plan approvals for this project. 3.Fire lane signs reading 'no parking -fire lane', with red letters on white reflective background, and of standard no parking sign characteristics, need to be used. • ` °. •ECOD1,OfC1111� � • I D)`VELOPMENT ZO-NE•a wI • .`zdN INq: IL"(2) '_ u_ •CURRENT USE: „a mI APPLIED TECHNOLOGIES BUILDING A P• 1N DUSTMA•L ,. W Z a a Z J 16 CLASSROOMS. 2,400 SF ADMINISTRATIVE SPACE 39,856 SQ FEET 6/CLASSROOM (96SP) + V300 SF ADMIN SOLID WASTE a U I I 44' HIGH (2,400SFADMIN=85P) 7 104 SPACES 2 STORIES CONTAINMENT ° 2 (1 HIC, 1 VAN)HANDICAP SPACES CAPACITY • a REQUIRED. PROVIDED 5 HIC, 1 VAN PROVIDED; 45 SPACES ADJACENT AND COLLECTION a FREQUENCY WILL BE _ SUFFICIENT TO r PREVENT THE - ILLEGAL PLACEMENT®—Ro—Ro—RD—RoRo—�n—Ro—Rd—Ro—Rn—Ro—Ro _ OF TRASH AND - RECYCLABLES a • • • ❑ -/ � LL� I'M o UJ o L ' BIORETENTION BUILDING A W W in L1Ao� OVERALL LAYOUT PLAN w 0) 1 40' m N 4 � 3 I EXISTING TREES I 9 NIF DURHAM TECHNICAL COMMUNITY COLLEGE PIN# 0830-07-59-1252 DB 1981 PG 919 P B 172 PG 398 AREA: 142,166 SF 1 3.264 AC M 1 n e I LJ 0 Lij� LJ F I� w a o a � i 33.21' l 1 O IORETENTIO I UILDINGA ti I I � I � S - PROPERTY LINE • � r4 ..�.� a. sw 1 EXISTING TREES IMITS OF DISTURBANCE A W - - -- - COOPER STREET 80' PUBLIC RIW W sir O Eel N/F CROCODILE CREEK PROPERTIES, LLC PIN# 0830-07-59-4328 DB 4123 PG 544 PB 165 PG 118 TCH LINE L1101 L1102 1 I NIF DURHAM COUNTY ABC BOARD PIN# 0830-07-59-3047 DB 364 PG 269 P B 364 PG 269 W W w 2 � 1 a CI A FIX Z Q Z w m b a_ �6 2 m x cu E go,) U O d 0 X O O L c6 C6 �,N d LL O H O Q C p p O Q) '0 Y -O C3 O O �.� �o =0LU� -It o ID L M a� 90 O o Ol w J a 0 a z 12 rn rn 3 ��ktins AsS CC er z° ECTUq� s CERT. 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C U c o U -g 0) '� O en [4 .O U a1 N Q ca Q W J S OdCL'Z rnrn3 �Ikyns Ass,, CERT. NO. 171 0 0 P �RrN CAR01.�� R H Ats D A � _ 9�n - X S X = 647 , Iff lll111111411\1 W Q a W J 0 2 Z O U U) d O_ U U) w Lu a W W Imp 0 J m Q V 0 0 oC = L) LU pQ � N W Q, O U) co 0-) I` O 0� ti � Q J N J u r` 4 W � �# W 'r t O Z "2 o cU) ISSUED SETS CONSTRUCTION DOCUMENTS 03/15119 Drawn By: EM Project No. 2017050 Ll 202 SOUTH GRADING PLAN APPENDIX A Activity ID Activity Name � Org Dur Rem Dur % Complete Start Finish 2020 2021 I Aug I Sep I Oct I Nov IDec Jan I Feb I Ma, Apr I May I Jun I Jul I Aug I Sep I Oct I Nov Dec Jan Feb I i I Apr I May I Jun I Jul I Aug I Sep I Oct I Nov I Dec ATS110 EC/Grading Building Pad -Applied tech Building F� Site Work 30 30 0% 8-19-19 93019 - ! ! : I ! 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I I & I 'our SOG -Ai tech Building ----- iiiiiiiiiiiiiiiij 121.18-19 : � � : : � � � : : : � � : : � � � : : : � � __ __ � .... .. - ----------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------- BOG Complete -Applied tech Building * : : � � : : � � � : : : � � : : I I � : : : I I I . . : ------- ! ----------- F ----------- r ----------- r ---------- I ----------- � ----------- � ---------- 11 ----------- Ir ---------- � ----------- � ----------- � ---------- 11 ----------- Ir ---------- : ----------- � ----------- � --------- Ir ---------- �, ---------- � ---------- � ---------- � ---------- Ir ---------- 11 ---------- Ir ---------- I ---------- � ------- I . . -- ---- I ---------- I ---------- I ---------- I ---------- I ---------- � ---------- I --------------- -------------- ! ----------- ! ----------- ! ---------- 11 ----------- 11 ---------- : ----------- ! ----------- � --------- 11 ---------- �, ---------- I ----------�----------� ---------- 11 ---------- �, ---------- 11 ----------I----------� ------- Steel Erection -Applied tech Building iiiiiiiiiiiiiiiiiiiiiI 1-20-20 � ! ---------------- . , 1 . . 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Lot -Applied tech Building 20 20 0% 10-1-19 10-28-19 ATSIM � Storm Drainage -Applied tech Building 25 25 0% 10-29-19 124-19 ATS140 H2O Line -Applied tech Building 30 30 0% 10-29-19 _ 9 — � ATS150 Gas Line -Applied tech Building 30 30 0% 10-29-19 12-11-19 ATS160 Seven Line -Applied tech Building 30 30 ' . 0% 10-29-19 12-11-19 ATSI`70 Power Line -Applied tech Building 30 30 0% 10-29-19 12-11-19 I 0 Stone / C&G / Pavement -Applied tech Building 20 20 Do 63-20 — 630-20 I ATS190 — Sidewalks -Applied tech Building 20 1 20 1 0% 7-1-20 7-29-20 I ATS11 00 Landscaping -Applied tech Building 15 1 15 1 0% - 7-30-20 , 8-19-20 11111M� ATFD10 � Footings -Applied tech Building 20 20 0% 10-1-19 1028-19 � ATFD20 Underground Rough In -Applied tech Building 20 20 0. 10-29-19 .&' - 11-25-19 ATFD30 i Pour BOG -Applied tech Building 15 15 0% I 11-26-19 12-1 19 "9 � SOG Complete -Applied tech Building 0 0 � 0% -,9 12-18-19 ATST10 Steel Erection -Applied tech Building 20 20 0% 12-19-19 � � __ 1-2 0-20 ATST12 Structure Complete -Applied tech Building 0 0 0% . 1-20-20 I ATS 0 Prep & Pour2nd Floor -Applied tech Building 15 15 0% 1-21-20 2-10-20 ATST30 Stair Erection -Applied tech Building 10 10 0 % 2-11-20 I 2-24-20 ATBE10 Frame / Sheet / Exterior Wall s -Applied tech Building mmm 30 30 0% 1-21-20 = 3-2-20 APP Air Bernier- Applied tech Building 15 . 1 . . 3-3-20 3-23-20 I ATBE30 Brick -Applied tech Building 20 20 0. 3-24-20 - 4-20-20 ATBE40 Glass & Glazing -Applied tech Building 30 30 0% 4-21-20 -_ — (T2-20 ATBE42 Building Dry In -Applied tech Building 0 0 Do 6-2-20 — ATBE50 Metal Wall Pa nels, - Applied tech Building 20 20 1 0% - 6-3-20 — 6-30-20 — — ATR1 0 Roofing -Applied tech Building. 15 15 0o/6 3-3-20 3-23-20 4 ATR12 Temp. Dry In -Applied tech Building 0 0 0% — 3:23-20 91 ATFZ20 Set Rrurs -Applied tech Building 5 5 0% 3-24-20 3-30-20 - M XT 0 Roof Screen -Applied tech Building 15 15 0% 3-31-20 0 — I ATR40 Soi Facie -Applied tech Building 20 20 0% 7-1-20 7-29-20 � I Frame We Is - 1 st R Applied -Ilich Building 20 20 0% 2-25-20 �---,�- 3-23-20 Overhead PJI - 1st R Applied Tech Building ' 20 20 0% 3-24-20 4-20-20 ATPJ120 In Wal RA -1st FI Applied Tech Building 20 20 0% 3 -24-20 4-20-20 — ATRI1 30 Drywall Han & Finish - 1st R Applied Tech Building 15 15 0% 6 -3-20 6 -23-20 — " 12 Prime n - m ! paint -1st Fl Applied Tech Building 15 15 0% 6-24-20 7-15-20 ATRI1 50 � i 1 i;rld - 1 st R Applied Tech Building 15 15 0% 7-16-20 8-5-20 ATRI1 60 'Above Ceiling Inspection - 1st R Applied Tech Building � Building Rl 2nd Floor ATRI200 Frame Weis-2nd F! Applied Tech Building I 0 , 0 , 0% , — 8-5-20 20 20 � 0% 3-24-20 4-20-20 ATRIM Overhead PJI - 2nd R Applied Tech Building 20 20 0% 4-21-20 — 5�1 8-20 ATR1220 In Wal RA - 2nd R Applied Tech Building 20 20 0% 0 4-21-20 ------ SA 8-20 — ATR1230 Drywall Hang & Finish - 2nd R Applied Tech Building 15 15 F000 0% 0 6-24-20 7-15-20 ATR1240 Prime Paint-2nd R Applied Tech Building 15 15 0% 7-16-20 — 8-5-20 ATRI250 Grid - 2nd Fl Applied Tech Building PP 15 15 0% 8-6-20 8-26-20 — ATRI260 . Above Ceiling Inspection - 2nd R Applied Tech Building % 8-26-20 11�11111811nes 1151" ATF100 Wail Finites- 1st FI Applied Tech Building 9 4 ATF110 Ceiling Finishes- 1st R Applied Tech Building 25 25 0% 8-27-20 10-1-20 25 25 Do 8-27-20 10-1-20 91 ATF120 - Floor Finishes - 1 st R Applied Tech Building 15 1 15 = 0% - 10-2-20 — 10-22-20 — ATF130 - Casework Install - 1 st R Applied Tech Building 0% 10-23-20 — 11-5-20 — � IiA 12MOO 0 Wail Finishes-2nd Fl Applied Tech Building 25 25 0% 10-2-20 1 1 -&20 � ATF21 0 Ceiling Finishes - 2nd R Applied Tech Building 25 25 0% 10-2-20 1 1 -&20 ATF220 Floor Finishes- 2nd Fl Applied Tech Building15 15 0% 11-6-20 -Finishes-- 11- 0 ATF230 � Casework Install - 2nd R Applied Tech Building 10 10 0% 12-1-20 - 12-14:20 — — .1111M� ATP1 00 GC Punchlist -Applied tech Building 30 �� 0% 12-15-20 — 1-28-21 ATP1 10 Arch Punci -Applied tech Building 5 5 0% 1-29-21 24-21 ATP120 GC Work off Punci -Applied tech Building 75 0 7L0 10 0% 2-5-21 2-1 — ATP1 30 Final Inspection -Applied tech Building 20 20 0% 2-19-21 3-18-21 �!l ATPFC Lolkinl-ivilooliki — I Final Completion -Applied tech Building - = 0 0 0% 3-18-21 * — Start Date: 8-19-19 Finish Date: 11-4-21 Data Date: 8-19-19 Run Date: 4-23-19 1111111111111111111111111 Master Schedule Hammocks 111111111111111111111111 Critical Remaining Work — EC 1111111111111111111111111 Actual Level of Effort * * Milestone PC Actual Work 1111111111111111111111111 GC SC Remaining Work o Mc DURHAM TECH COMMUNITY COLLEGE Construction Schedule 03 - DT Complete Schedule 8-19-19 Upd File: DT Page 1 of 3 C­.. .. ... . ..... 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Our NBNTP Notice To Proceed - Newton Building I 0 1 0 1 0% 1 6-15-20 NBS140 H2O Line Fire Line - Newton Building 1 20 1 20 1 0% 1 6-29-20 1 7-27-20 NBS190 Sidewalks - Newton Building 15 15 0% 7-28-20 8-17-20 NBS1100 Landscaping - Newton Building 15 15 0% 8-18-20 9-8-20 NBFDO4 Owner Move Out -Newton Building 5 1 5 1 0% 63-20' 1 6-12-20 NBFDO6 Asbestos Abatement - Newton Building 10 10 0% 6-15-20 6-26-20 NBFDO8 Interior Demolition - Newton Building 10 10 0% 6-25-20 7-9-20 ii NBFD20 Underground Rough In - Newton Building 8 8 0% 7-2-20 7-14-20 ,1 NBFD30 Prep &Pour SOG-Newton Building 5 5 0% 7-15-20 7-21-20 NBFD40 SOG Complete -Newton Building 0 0 0% 7-21-20 �Al FDO4 Owner Move Out- Newton Building Area B 5 5 0% 6-7-21• 6-11-21 I Al FDO6 Asbestos Abatement- Newton Building Area B 10 10 0% 6-14-21 6-25-21 Al FDO8 Interior Demolition - Newton Building Area B 10 10 0% 6-24-21 7-8-21 Al FD20 Underground Rough In - Newton Building Area B 8 8 0% 7-1-21 7-13-21 Al FD30 Prep &Pour SOG- Newton Building Area B 5 5 0% 7-14-21 7-2a21 dl Al FD40 SOG Complete - Newton Building Area B 0 0 1 0% 7-20-21 NBST10 Steel Erection for Roof Curbs at New Units - Newton Building 1 5 I 5 1 0% 1 7-10-20 7-16-20 Building Env NBBE10 Frame / Sheet @ Front Entrance - Newton Building 10 I 10 I 0% 1 7-15-20 1 7-28-20 NBBE20 I Air Barrier- Newton Building 2 2 0% 7-29-20 1 730-20 NBBE40 Glass & Glazing - Newton Building 5 5 0% 731-20 85-20 NBB Building Dry In - Newton Building 0 0 0% 1 8-6-20 NBR10 Roofing - Newton Building 10 10 0% 0E42 7-17-20 730-20 NBRI100 Frame Weis -Newton Building 10 I 10 I 0% 7-22-20 1 8-4-20 NBRI110 Overhead R/I - Newton Building 10 10 0% 85-20 8-18-20 N3RI120 In Wei RA - Newton Burdirg 10 10 0% 85-20 8-18-20 NBRI130 Drywall Hang & Finish - Newton Building 12 12 0% 8-19-20 94-20 NBRI140 Prime Paint - Newton Building 8 8 0% 9-7-20 9-16-20 NBR1150 Grid - Newton Building 6 6 0% 9-17-20 9-24-20 NBR1160 Above Ceiling Inspection - Newton Building 0 0 0% 9-24-20 NBF100 WeiIFinishes- NewtonBuIcing 10 10 0% 9-25-20 10-8-20 NBF110 Ceiling Finishes - NewtonBuilding 10 10 0% 9-25-20 1O 20 NBF120 Floor Flnishes - Newton Building 10 10 0% 10-7-20 10-20-20 NBF130 Casework Install - Newton Building 5 5 0% 10-14-20 10-20-20 NBP110 Arch Punchlist- Newton Building 1 2 1 2 1 0% 1 11-4-20 1 115-20 NBP120 GC Work of Punchl'st- Newton Building 8 1 8 1 0% 1 11-6-20 1 11-17-20 NBP130 Final Inspection -Newton Building 2 2 0% 11-18-20 11-19-20 NBPFC Final Completion- Newton Building 0 0 0% 11-19-20" A2SI10 EC / Grading - Newton Building Front Facade Front Facade 5 1 5 1 0% 6-15-20 6-19-20 A2NTP Notice To Proceed- Newton Building Font Facade 0 0 0% 1 6-15-20' A2SI90 Sidewalks - Newton Building Front Facade 10 10 0% 6-22-20 75-20 A2SI100 I Landscaping - Newton Building Front Facade 10 I 10 I 0% 1 7-7-20 1 7-20-20 el._._._ I .__....y_ ._..,_..__.._...,.._....____ 11 A2FD20 Underground Rough In - Newton Building Front Facade .- 5 .- 5 - 1. 0% I . ._-„ 7-24-20 I ._„_„ 730-20 A2F11 D30 Prep & Pour SOG-Newton Building Front Facade 1 5 1 5 1 0% 1 731-20 1 8-6-20 A2FD432 SOG Complete - Newton Building Front Facade I 0 1 0 1 0% I I85-20 A2ST10 Steel Erection - Newton Building Front Facade I 10 10 0% 8-7-20 8-20-20 A2BE10 Frame/Sheet/Exterior Walls - NewtonBuldingFrontFacade 10 I 10 I 0% 8-21-20 911-20 A2BE20 Air Barrier- Newton Building Front Facade 2 2 0% 9-7-20 9-8-20 A2BE30 Bride - Newton Building Front Facade 8 8 0% 95-20 9-18-20 A2BE40 Glass & Glazing - Newton Building Front Facade 10 10 0 % 9-21-20 10-2-20 A2BE42 Building ay In - Newton Building Front Facade 0 0 0% 10-2-20 A2BE50 Metal Wall Panels- Newton Bu icing Front Facade 8 8 0% 105-20 10-14-20 A2R10 I Roofing - Newton Building Front Facade 1 5 1 5 1 0% 1 10-15-20 1 10-21-20 EC/Grading - Nevyton Building O 16-26-20 ---- — —— — ---I---------`----- — '—— —————— --------------'---- ----- — — — — --- -------------'-------------- - `- — —— `— — — —— ----`---------`------'- ——— - - - : : : Notice To Proceed- Newlin Building: ♦ ; ; I-------I---------I I--------------- ---- --------'-------- —— —————— — — ---- ------ ------ --------------- —— --- ——— — —————— — — — ; ; I I I I II - - I------ H2O Line-------- I ---------I---------- -I----------------; ; e Fire Line Newton Building O 7-27-20 ; ; ------ ------- --------------T-------- ------- ------- -------- --------r-------- ----- - - ----------------------'----------`- - -------------------'-----------'I-------------------------------'I----------`----------'I-------------------------------------------`----------'-------- 1 Sidewalks 1 Newton ddin 8-1 g 7-20 -I-----------I----------*.- � ' --! 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(µg/L) Chloroform 4.0 1.6J 8.8 70 Tetrachloroethylene <0.27 0.3J <0.27 0.7 RCRA 8 Metals (EPA Method 6020A-B) - (µg/L) Arsenic <0.77 <0.77 2.8 10 Barium 690 270 150 700 Cadmium <0.16 <0.16 <0.16 2 Chromium 6.4 <1.2 <1.2 10 Lead <0.34 <0.34 <0.34 15 Mercury <0.000034 <0.000034 <0.000034 1 Selenium <2.8 <2.8 <2.8 20 Silver <0.21 <0.21 <0.21 20 Semi -Volatile Organic Compounds (EPA Method 8270) - (µg/L) Analytes Not Detected I ND I ND ND Notes: Compounds detected in one or more groundwater samples are shown in the table Concentrations are reported in micrograms per liter (µg/L) NCAC 2L GWQS - North Carolina Administrative Code Subchapter Groundwater Quality Standards (April 1, 2013) Shaded detections exceed their applicable standard and/or screening level Values in BOLD were detected above the method detection limit J: Estimated concentration between the method detection limit and the reporting limit ft bls: feet below land surface NE: Not established ND: Not detected NTU: Nephelometric Turbidity Unit Table 2 Historical Soil Gas Analytical Results Durham Technical Community College 1604 East Lawson Street Durham, Durham County, North Carolina Terracon Project No. 70177290 Northern Parcel Sample ID: Sample Date: Screen (ft bls): SG-01 07/11/17 4 SG-02 07/11/17 4 SG-03 07/11/17 4 SG-04 07/11/17 5 SG-05 07/11/17 4 SG-06 07/11/17 4.5 SG-07 07/11/17 5 SG-08 07/11/17 5 DWM VI-GWSL (Res) DWM VI-GWSL (Non -Res) Volatile Organic Compounds (TO-15) - (µg/m3) Acetone 26.1 24.2 63.1 64.0 120 47.1 20.2 <59.4 216,000 2,720,000 Benzene 119 123 65.2 24.1 138 131 59.2 74.1 120 1,570 1,3-Butadiene 10.4 <8.85 <8.85 9.46 116 2 12.1 463 13.9 175 Carbon disulfide 62.2 44.0 32.0 31.7 124 35.8 78.8 67.7 4,870 61,300 Chloroethane <1.06 1.49 <1.06 <1.06 <1.06 38.2 <1.06 <10.6 69,500 876,000 Chloroform 9.55 4.0 2.35 27.8 18.4 <3.89 5.80 <19.5 40.7 533 Chloromethane <0.826 <0.826 <0.826 <0.826 2.18 142 1.23 <8.26 626 7,880 cis-1,2-Dichloroethene <1.59 <1.59 9.84 <1.59 6.87 4.47 <1.59 <15.9 NE NE Cyclohexane 11.7 8.46 4.68 3.47 16.7 11.5 8.61 <13.8 41,700 526,000 1,4-Dichlorobenzene <24 5.5613 <2.4 <4.81 <4.81 <4.81 <9.62 <24 85.1 11110 1,1-Dichloroethene <1.59 <1.59 2.48 <1.59 <1.59 5.63 <1.59 <15.9 1,390 17,500 Dichlorodifluoromethane <1.98 <1.98 <1.98 2.37 2.08 <3.96 <1.98 <19.8 695 8,760 Ethanol 11.7 3.11 18.9 12.4 18.2 20.8 14.0 34.7 NE NE Ethylbenzene 677 174 457 219 306 172 310 131 374 4,910 4-Ethyltoluene 281 225 278 138 272 82.8 168 51.7 NE NE Heptane 176 181 68.9 31.5 197 97.7 72.3 152 NE NE Isopropyl benzene 105 65.6 70.3 40.1 80.0 27.0 <7.87 <19.7 2,780 35,000 Methylene Chloride 2.1913 1.9813 2.2213 1.4813 <1.39 <2.78 <1.39 <13.9 4,170 52,600 2-Butanone (MEK) 7.50 <7.37 13.1 8.57 40.6 <14.7 <7.37 <73.7 34,800 438,000 4-Methyl-2-pentanone (MIBK) <10.2 <10.2 21.9 <10.2 22.3 <20.5 <40.9 <102 20,900 263,000 Naphthalene <66 7.7713 18.513 15.413 15.613 14.16 <26.4 <66 20.9 263 n-Hexane 87.3 69.8 27.0 29.6 225 231 61.4 355 4,870 61,300 Propene 267 46.8 33.6 222 624 1200 505 5280 20,900 263,000 Styrene <17 <1.7 <1.7 <3.4 <3.4 42.0 <6.81 <17 6,950 87,600 Tetrachloroethene (PCE) 26.2 19.7 32.3 31.9 31.7 54.0 26.1 29.9 278 3,500 Toluene 2520 762 1450 578 886 545 952 512 34,800 438,000 Trichloroethene (TCE) 6.91 6.65 21.8 5.37 45.8 29.4 <8.57 <21.4 13.9 175 Trichlorofluoromethane <2.25 <2.25 <2.25 <2.25 5.55 <4.5 <2.25 <22.5 NE NE 2,2,4-Trimethyl pentane 250 344 85.8 31.4 257 73.9 80.2 97.0 NE NE 1,2,4-Trimethylbenzene 268 866 408 785 280 504 136 48.7 613 1,3,5-Trimethylbenzene 384 271 337 176 324 102 234 49.2 NE NE Vinyl chloride <1.02 1.20 7.96 <1.02 2.41 31.9 <1.02 <10.2 55.9 2,790 m&p-Xylenes 2430 652 1700 829 1300 548 1190 418 695 8,760 o-Xylene 655 431 520 235 600 1871 327 126 695 8,760 Notes: Compounds detected in one or more soil vapor samples shown Concentrations are reported in micrograms per cubic meter (µg/m3) DWM VI-SGSL: NCDEQ DWM Vapor Intrusion - Soil Gas Screening Level (October 2016) Res/Non-Res: Residential/Non-Residential Shaded detections exceed their applicable standard and/or screening level Values in BOLD were detected above the method detection limit J: Estimated concentration between the method detection limit and reporting limit ft bls: feet below land surface NE: Not established B: Analyte found in the associated blank E: Analyte concentration exceeds the labroatory upper limit of the calibration range of the instrument established by the initial calibration (ICAL) Table 3 Historical Soil Analytical Results Durham Technical Community College 1604 East Lawson Street Durham, Durham County, North Carolina Brownfields Project No. 22034-18-32 Terracon Project No. 70197401 Sample ID: Sample Depth (ft bls): SB-08 2-4 SB-09 1.5 3 SB-10 5-6 SB-11 3-4 SB-12 4-5 SB-13 5-6 SB-14 6-7 PSRG (Residential) PSRG (Commercial) Volatile Organic Compounds (EPA Method 8260) - (mg/kg) Analytes Not Detected ND I ND I -- -- -- -- -- - -- Semi-Volatile Organic Compounds (EPA Method 8270) - (mg/kg) Analytes Not Detected ND I ND I -- -- -- -- -- -- I -- Resource Conservation and Recovery Act (RCRA) 8 Metals (EPA Method 602OA-B) - (mg/kg) Arsenic 1.9 0.86 - -- -- -- 0.68 3 Chromium 22 11 - -- -- -- 24,000 100,000 Lead 15 10 - - - 400 800 Mercury 0.0045.11 <0.0028 - -- -- - 2.2 3.13 Selenium <0.14 <0.15 - - - - 78 1,160 Silver 0.044.1 0.028J - - - - 78 1,160 Barium 130 88 - -- -- 3,000 44,000 Cadmium <0.058 <0.06 - -- -- -- 14.2 196 TPH-DRO (EPA Method 8015C) - (mg/kg) NCDEQ Action Level DRO - 7.8 4.7 4.4 5.5 5.3 100 Notes: Samples collected on July 11, 2017 Compounds detected in one or more soil sample are shown in the table Concentrations are reported in milligrams per kilogram (mg/kg) Values in BOLD were detected above the method detection limit Detections in excess of a standard are shaded PSRG - NCDEQ Inactive Hazardous Sites Branch (IHSB) Residential Health Based PSRGs (Oct 2016) PoG - Protection of Groundwater U / R - Unrestricted -Use / Restricted -Use TPH-DRO - total petroleum hydrocarbons diesel range organics ft bls - feet below land surface NE - not established NO - analytes were not detected above the reporting limit J - estimated concentration greater than the method detection limit and less than the practical quantitation limit Table 4 Summary of Soil Analytical Results Durham Technical Community College 1604 East Lawson Street Durham, Durham County, North Carolina Brownfields Project No. 22034-18-32 Terracon Project No. 70197104 Sample ID: Sample Depth (ft bls): SB-15 DUP-01 (SB-15) SB-16 SB-17 SB-18 SB-19 PSRG (Residential) PSRG (Commercial) 1-2 5-6 1-2 1-2 5-6 2-3 5-6 0.5-1.5 5-6 1-2 5-6 Volatile Organic Compounds (EPA Method 8260) - (mg/kg) Acetone 1 <0.019 <0.020 <0.020 <0.020 <0.023 <0.020 <0.028 <0.020 <0.019 <0.019 <0.019 12,000 140,000 Sample ID: Sample Depth (ft bls): SB-15 DUP-01 (SB-15) SB-16 SB-17 SB-18 SB-19 PSRG (Residential) PSRG (Commercial) 0-3 3-6 0-3 0-3 3-6 0-3 3-6 0-3 3 6 0-3 3-6 Semi -Volatile Organic Compounds (EPA Method 8270) - (mg/kg) 3-Nitroaniline <0.03 <0.028 <0.031 <0.029 <0.032 <0.036 <0.031 <0.029 <0.029 <0.033 <0.029 NE NE Benzo(a)anthracene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 1.1 21 Benzo(b)fluoranthene <0.003 <0.0028 <0.0031 0.0012J <0.0032 0.00231 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 1.1 21 Benzo(k)fluoranthene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 11 210 Benzo(a)pyrene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 0.11 2.1 Caprolactam 0.01 BJ 0.0087 BJ <0.015 0.011 BJ 0.0096 BJ <0.017 0.0099 BJ 0.0091 BJ 0.0091 BJ 0.012 BJ 0.009 BJ 6,300 82,000 Chrysene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 110 2,100 Fluoranthene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 480 6,000 Phenanthrene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 NE NE Pyrene <0.003 <0.0028 <0.0031 <0.0029 <0.0032 <0.0036 <0.0031 <0.0029 <0.0029 <0.0033 <0.0029 0.036 0.0045 Resource Conservation and Recovery Act (RCRA) 8 Metals (EPA Method 6010/7470) - (mg/kg) Arsenic 0.57 0.20 J 0.63 1.4 2.0 1.3 0.76 0.83 4.2 1.5 1.8 0.68 3 Barium 54 26 55 83 160 100 62 320 240 62 190 3,100 47,000 Cadmium 0.026 J 0.032 J 0.035 J 0.045 J 0.080 J <0.12 <0.10 0.041 J 0.11 <0.14 0.024 J 14 200 Chromium (III) 11 B 2.1 B 10 B 25 B 43 B 33 B 16 B 21 B 25 B 28 B 34 B 23,000 350,000 Chromium (VI) <1.1 <1.1 0.32 J <1.1 <1.2 0.73 J <1.1 0.35 J <1.1 0.35 J <1.1 0.31 6.5 Lead 9.4 12 9.9 7.1 10 14 5.8 19 17 10 13 400 800 Mercury <0.083 <0.082 <0.089 <0.084 <0.087 <0.095 <0.0089 <0.086 <0.080 <0.099 <0.086 2.3 9.7 Selenium 0.46 J <1.2 <1.4 1.1 J 1.0 J 0.55 J 0.42 J 0.64 J 1.1 <1.4 1.7 78 1,200 Silver <0.23 j <0.23 j <0.26 j <0.22 <0.25 j <0.24 <0.19 <0.25 <0.22 <0.26 <0.21 78 1,200 Notes: Samples collected April 3, 2019 Compounds detected in one or more soil sample are shown in the table Concentrations are reported in milligrams per kilogram (mg/kg) PSRG: North Carolina Department of Environmental Quality (NCDEQ) Preliminary Soil Remediation Goals (February 2018) Detections in excess of a standard are shaded ft bls: feet below land surface NIS: Not sampled / analyzed for NA: Not applicable If chromium (VI) concentrations were detected below the laboratory reporting limt then chromium (III) is reported as total chromium. 1: Estimated concentration between the method detection limit and the reporting limit B: Analyte detected within method blank Page 1 of 2 Table 4 Summary of Soil Analytical Results Durham Technical Community College 1604 East Lawson Street Durham, Durham County, North Carolina Brownfields Project No. 22034-18-32 Terracon Project No. 70197104 Sample ID: Sample Depth (ft bls): SB-20 SB-21 SB-22 SB-23 SB-24 PSRG (Residential) PSRG (Commercial) 1-2 5-6 11-2 3.5-4.5 1-2 1-2 5-6 1-2 5-6 Volatile Organic Compounds (EPA Method 8260) - (mg/kg) Acetone 0.0191 <0.021 <0.017 <0.022 <0.018 <0.019 <0.019 <0.019 <0.026 12,000 140,000 Sample ID: Sample Depth (ft bIs): SB-20 SB-21 SB-22 SB-23 SB-24 PSRG (Residential) PSRG (Commercial) 1 0-3 3-6 0-3 3-6 0-3 0-3 3-6 0-3 3-6 Semi -Volatile Organic Compounds (EPA Method 8270) - (mg/kg) 3-Nitroaniline <0.03 <0.031 <0.03 <0.036 <0.15 <0.31 <0.67 0.036 <0.035 NE NE Benzo(a)anthracene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0017 J <0.0035 1.1 21 Benzo(b)fluoranthene 0.0031 <0.0031 0.0017J <0.0036 <0.015 <0.031 <0.067 0.0029 J <0.0035 1.1 21 Benzo(k)fluoranthene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0011 J <0.0035 11 210 Benzo(a)pyrene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0018 J <0.0035 0.11 2.1 Caprolactam 0.019 B 0.012 BJ 0.011 BJ 0.011 BJ <0.071 <0.15 <0.32 0.012 BJ 0.011 BJ 6,300 82,000 Chrysene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0018 J <0.0035 110 2,100 Fluoranthene 0.0016 J <0.0031 0.0016 J <0.0036 <0.015 <0.031 <0.067 0.0045 <0.0035 480 6,000 Phenanthrene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0019 J <0.0035 NE NE Pyrene <0.003 <0.0031 <0.003 <0.0036 <0.015 <0.031 <0.067 0.0032 <0.0035 0.036 0.0045 Resource Conservation and Recovery Act (RCRA) 8 Metals (EPA Method 6010/7470) - (mg/kg) Arsenic 0.97 1.7 1.5 1.4 0.67 3.1 5.6 1.9 1.4 0.68 3 Barium 51 40 100 270 270 220 530 180 190 3,100 47,000 Cadmium 0.061 J <0.15 0.034 J 0.036 J 0.057 J <0.13 0.094 J 0.043 J 0.085 J 14 200 Chromium (III) 13 B 23 B 33 B 45 B 18 B 45 B 53 B 40 B 38 B 23,000 350,000 Chromium (VI) 0.77 J 0.34 J 1.6 0.55 J 1.1 <1.1 <1.3 0.39 J <1.3 0.31 6.5 Lead 9.7 8.5 12 15 9.2 13 17 14 14 400 800 Mercury <0.089 <0.087 <0.093 <0.098 <0.081 <0.087 <0.093 <0.092 <0.10 2.3 9.7 Selenium <1.4 <1.5 0.641 1.5 1.6 1.7 1.6 0.98 J 0.58 J 78 1,200 Silver 1<0.27 1<0.30 1 <0.22 <0.24 1<0.25 1 <0.24 1<0.26 1 <0.28 <0.29 1 78 1 1,200 Notes: Samples collected April 3, 2019 Compounds detected in one or more soil sample are shown in the table Concentrations are reported in milligrams per kilogram (mg/kg) PSRG: North Carolina Department of Environmental Quality (NCDEQ) Preliminary Soil Remediation Goals (February 2018) Detections in excess of a standard are shaded ft bls: feet below land surface NIS: Not sampled / analyzed for NA: Not applicable If chromium (VI) concentrations were detected below the laboratory reporting limt then chromium (III) is reported as total chromium. J: Estimated concentration between the method detection limit and the reporting limit B: Analyte detected within method blank Page 2 of 2 Figure 1 NCBP Diagram for Temporary Containment of Impacted or Potentially Impacted Soil Cross -Section View 'fop Plastic Cover Sheeting: Underliner: 1 layer, minimum of 10 (1 Layer, minimum: 10 mil thick) mil thick plastic Berm (Straw bales, composted earth, etc) Land Surface 1 1 x Stra v Bale Berm NN'eight a plastic cover used) Contaminated Soils Map View Weight Contaminated Soils L ......... .......... .................. .......... Plastic Sheeting Note- Adapted from NC DEQ UST Section "Guidelines for Ea Situ Petroleum Contaminated ,Soil Remediation" dated December, 1, 2013 26 EMP Version 2, June 2018 $1 SITE J��)ff� �� tiff'j�irrr �/ I ! r; yf—�jiY J � .1\\ yt—]� it y J I}liff�f' `I �ol 7 h� .rr J ] U" kl,'r TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGICAL SURVEY QUADRANGLES INCLUDE: SOUTHWEST DURHAM, NC (1/1/2002) and SOUTHEAST DURHAM, NC (1/1/2002). Project Manager: Project % SITE LOCATION MAP Exhibit ALF 1"=2,0 04 Irerracon Drawn by: ALF scale: 000' Fairey Finishing Plant Checked by: MTJ 70197104 Brownfield Project Number: 22034-18-32 2401 Brentwood Rd Ste 107 1604 East Lawson Street Approved by: MT.I APR 2019 Raleigh, NC 27604-3686 Durham, North Carolina E. LAWSON STREET ,4A 40P R SG-02 1 SB-23 , 1 ' I SG-03 w - 1 SG-05 � I 0 � SB-08 QI 1 1 SG-04 1 — �! SB-22 3tion of former 1, 000-gallon I _ _ SB=14 SG-06 Heating Oil UST SB-21 Q UST Incident No. 39154) s Q TW-03 Q SB-13 SB-10 SB-12 r__� _JJ - : SB-11 SB-19 SB-18 0 SG-07 Piedmont Metalworks (1551 Cooper Street)- V1 1 Legend O April 2019 Soil Boring Locations O Historical Soil Boring Locations A Historical Shallow Soil Gas Points Historical Temporary Monitoring Wells Approximate Site Boundary Former On -site Buildings (Prior to 2015) PM: Project No. MTJ 70197104 Drawn By: Scale: ALF 1 in = 100 ft Checked By: File Path: MTJ 70197104 Approved By:MTJ Date: 4/18/2019 CC Building 8 R { r p 49, COOPER STREET 50 100 � Feet Site Map EXHIBIT NO. 1rerracon FaPFinishing Plant Brownfield Project Number: 22034-18-32 1604 East Lawson Street 2 Durham, North Carolina zao, Breoh eed orlve, sae 107 Raleigh, Nc z soa Phone: (919) 8734211 Fax: (919) 873-9555 is E. LAWSON INV;& F; DTCC Building 8 r117 It � DTCC Building 10 I `?.ub,iIII 1Ax 4 • r •GUILD .:i i� {,3 i Ji Leg@iICI _ - COOPER STREET O April 2019 Soil Boring Locations Approximate Site Boundary A iDTCC Building 4 �,�(Newton Hall) 0 MMM=5 10 Note: The underlaid figure is the preliminary grading plan for site redevelopment. PM: Project No. MTJ 70197104 Drawn By: Scale: ALF 1 in = 100 ft Checked By: File Path: MT 70197104 Approved ByMTJ Date: 2/20/2019 �I Sampling Locations EXHIBIT NO. 1rerracon Proposed Sampling Locations Fairey Finishing Plant Brownfield Project Number: 22034-18-32 1604 East Lawson Street Durham, North Carolina 2401 Brentwood Drive, Suite 107 Raleigh, NC 27604 Phone: (919)873-2211 Fax: (919)873-9666