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HomeMy WebLinkAboutDERR-2024-006608Facilities | Environmental | Geotechnical | Materials i Cover Page Materials Management Plan Lonestar Properties LLC – Former Anderson Auto Wrecking Site, 2890 South State Street, Spanish Fork, Utah County, Utah Voluntary Cleanup Program Site #C127 March 28, 2024 | Terracon Project No. 61237032 Prepared for: Utah Department of Environmental Quality/ Division Of Environmental Response and Remediation Voluntary Cleanup Program (VCP) Facilities | Environmental | Geotechnical | Materials ii Table Of Contents List of Acronyms and Abbreviations .............................................................. ii 1.0 Introduction ..................................................................................... 1 2.0 Site Information and Background ........................................................... 1 3.0 Materials Management Procedures ........................................................ 2 3.1 General Materials Management Procedures ........................................................... 2 3.2 Waste Characterization .................................................................................... 2 3.3 Waste Disposal ............................................................................................. 3 4.0 Quality Assurance ............................................................................. 4 5.0 Contingency Plan .............................................................................. 5 List of Acronyms and Abbreviations ACM Asbestos Containing Material DERR Division of Environmental Response and Remediation DWQ Division of Water Quality HASP Health and Safety Plan LUST Leaking Underground Storage Tank MMP Materials Management Plan OSHA Occupational Safety and Health Administration PCBs Polychlorinated Biphenyls PPE Personal Protective Equipment QAPP Quality Assurance Project Plan SVOCs Semi-Volatile Organic Compounds TCLP Toxicity Characteristic Leaching Procedure TPH Total Petroleum Hydrocarbons UDEQ Utah Department of Environmental Quality UST Underground Storage Tank VOCs Volatile Organic Compounds Materials Management Plan Former Anderson Auto Wrecking Site | Spanish Fork, Utah March 28, 2024 | Terracon Project No. 61237032 Facilities | Environmental | Geotechnical | Materials 1 1.0 Introduction Lonestar Properties LLC (Lonestar) is in the process of redeveloping the property located at 2890 South State Street, Spanish Fork, Utah. The site has been enrolled in the VCP and is referenced as “VCP Site #127”. This plan discusses materials management, identification, handling, segregation, and disposal requirements for unidentified containers and chemicals such as fuels, used oil, solvents, metals, or other waste chemicals that may be discovered at the Site. This MMP describes safe work practices which will be used to address potential waste materials and/or containers that may be found at the site during assessment and remediation activities, including chemical contaminants, and storage tanks. The Utah Division of Environmental Quality (UDEQ)/Division of Environmental Response and Remediation (DERR) Voluntary Cleanup Program (VCP) is the lead regulatory agency responsible for oversight of this Materials Management Plan (MMP) which will be implemented by Lonestar. 2.0 Site Information and Background The site is comprised of approximately 3.9 acres of land currently owned by Lonestar Properties LLC. The site comprises two parcels consisting of the addresses, Utah County Assessor Parcel Numbers (APNs), and land uses listed below: Address Parcel Number Acres Use 2890 South State Street 27:010:0140 1.875 Vacant 1215 North SR 51 27:010:0139 2.024 Residence/Vacant The site was formerly occupied by the Anderson Auto Wrecking facility, which historically operated as an automotive salvage yard from approximately 1977 to the mid-2010s. The Anderson Auto Wrecking facility formerly stored large numbers of old vehicles, trailers, tires, engines, scrap-metal, and other vehicle parts. Storage sheds at the wrecking yard stored car batteries, gasoline cans, engine wastes, scrap metal, asphaltic tar, paint, as well as miscellaneous debris. A crushing station, used to crush cars and other metallic debris, was located on the southern portion of the yard behind a single-family home. The site currently consists primarily of vacant land. Proposed development of the site includes residential apartments. Heavy metals and petroleum hydrocarbons have been documented at the site above applicable regulatory screening levels. Materials Management Plan Former Anderson Auto Wrecking Site | Spanish Fork, Utah March 28, 2024 | Terracon Project No. 61237032 Facilities | Environmental | Geotechnical | Materials 2 3.0 Materials Management Procedures 3.1 General Materials Management Procedures An area will be designated for short-term stockpiling of containers that may be discovered at the site. The stockpile area will be lined with 10-mil (0.01 inches) plastic sheeting. The stockpile will be covered with 10-mil plastic sheeting at the end of each workday that has been weighted to limit or prevent wastes from being blown away from the stockpile. Stockpiles will be segregated based on general waste types, media, and waste disposal requirements. If labeled chemical containers or unlabeled suspect chemical containers are identified a multiple step assessment will be performed: 1.Containers will be assessed in-situ, the likely chemical content based on labeling, container type/shape, etc. Potentially contaminated soils will be assessed based on nearby chemical containers, if present, or based on field screening observations. 2.The container will be observed for crystallization or other evidence of reactively unstable materials. Reactively unstable materials are considered unlikely, but if present, they will not be moved until they can be chemically or physically stabilized. 3.If the condition of a container can be assessed in place, the environmental field team lead will note the condition of the container, evidence of releases, etc. If a container appears to be actively leaking, it will not be removed until a suitable overpack container is available for containment. 4.The environmental field team lead will observe and document whether releases, if any, appear likely to have impacted soils around or below the container. If a suspected release has occurred, the extent of the release will not be assessed at this time but will be documented for further investigation and potential removal. Where contaminated soils are observed, it will be assumed that the soils have been impacted by containers located physically above or adjacent to the location of the observed contamination, regardless of the presence of visible leakage from each container. 5.The location will be logged via GPS and/or measured from a fixed reference point and plotted on a scaled drawing; if it is practical, the location will be marked in the field with flagging or stakes. 6.The environmental field team lead will take photograph(s) documenting the container location and general condition. 3.2 Waste Characterization Chemical containers and other wastes found at the site will be characterized based on labeling, if present, observations of contents, sampling, and laboratory analysis. Field-based characterization and laboratory analyses will be performed by the environmental consultant Materials Management Plan Former Anderson Auto Wrecking Site | Spanish Fork, Utah March 28, 2024 | Terracon Project No. 61237032 Facilities | Environmental | Geotechnical | Materials 3 and Utah certified laboratory. For labeled containers, the contents will be visually examined to verify that the content appears to match the labeling. If uncertain, the contents will be sampled with a drum thief or equivalent sampling device. Container samples will be submitted to a Utah-certified laboratory to be analyzed for hazardous waste characteristics such as toxicity characteristic leaching procedure (TCLP) analyses. The specific types of analyses will be selected based on the requirements of the specific disposal facility, the materials released, if known, or will include the full range of hazardous waste characteristics for unknown wastes. Additionally, analytical methods will meet the requirement of the disposal facility chosen to receive the waste and may include additional analysis not listed here. In general, likely analyses may include: Paint Filter Ignitability Corrosivity Reactivity TCLP Metals (RCRA 8) TCLP VOCs TCLP SVOCs TCLP Pesticides TCLP Herbicides PCBs Total Petroleum Hydrocarbons (TPH) – extended (gasoline and diesel) range; and/or Oil & Grease 3.3 Waste Disposal The following sections discuss waste disposal for unidentified containers and chemicals that may be encountered at the site.Disposal manifests will be included in the final report submitted to the DERR. Hazardous Wastes It is not anticipated that hazardous waste is present at the site, but if hazardous wastes are identified each identified material will be profiled based on field observations and laboratory analyses. Upon approval of each waste profile, the remediation contractor will load each waste into an appropriate container and transport vehicle and haul to the approved off-site hazardous waste disposal facility. The remediation contractor will comply with all applicable state and Federal regulations applying to transport and disposal. Final disposal facilities for hazardous wastes include Clean Harbors’ Grassy Mountain Landfill in Clive, Utah. If Materials Management Plan Former Anderson Auto Wrecking Site | Spanish Fork, Utah March 28, 2024 | Terracon Project No. 61237032 Facilities | Environmental | Geotechnical | Materials 4 necessary, Clean Harbors will be contracted for transport of hazardous wastes to their disposal facility. Universal Wastes The following hazardous wastes materials will be handled as universal wastes on-site: Batteries Electronic wastes Lighting wastes The universal waste will be profiled and transported to an approved recycler for the waste or to a permitted hazardous waste disposal facility. Disposal facilities that may receive universal waste include South Utah Valley Solid Waste District. Non-Hazardous Solid Wastes Based on field observations and/or laboratory analyses, waste materials that are not regulated as hazardous waste, such as tires, empty drums and containers, petroleum- contaminated soils, general construction debris, or other municipal, or industrial wastes, will be managed as solid waste. The identified solid wastes will be profiled, appropriately containerized, or packaged and labeled if required, and transported to an appropriate offsite permitted solid waste landfill for disposal. The remediation contractor will follow all applicable state and Federal regulations during transport. Disposal facilities that may be used for non-hazardous waste disposal include ET Technologies and South Utah Valley Solid Waste District. Asbestos Contaminated Wastes Asbestos containing material (ACM), if identified, will be managed in conjunction with the UDEQ Division of Air Quality. ACM waste will be handled and disposed of in accordance with local, state, and Federal requirements. 4.0 Quality Assurance Sampling will proceed according to the methods described in the approved QAPP and this MMP. The quality assurance/quality control reporting package requested from the analytical laboratory for waste characterization will meet the requirements of the DERR and the disposal facility. This will include case narratives, laboratory control sample/laboratory control sample duplicate, laboratory matrix spike/matrix spike duplicate, and method blanks. Field quality control samples such as equipment blanks, trip blanks, and field duplicate samples will not be collected on waste characterization samples. Laboratory analytical samples will be collected using disposable equipment when possible. Materials Management Plan Former Anderson Auto Wrecking Site | Spanish Fork, Utah March 28, 2024 | Terracon Project No. 61237032 Facilities | Environmental | Geotechnical | Materials 5 5.0 Contingency Plan In cases where unexpected containers, contaminants, or conditions are encountered at the site, such as unidentified chemicals, significantly greater lateral and/or vertical extent of contamination, unexpected release points (both at and below the surface), obstacles to sampling or remediation work, or other unforeseen conditions that prevent or significantly alter materials management from that proposed in this plan, a contingency strategy will be developed in consultation with the DERR.