Laserfiche WebLink
BACKGROUND <br /> Aerially Deposited Lead <br /> Ongoing testing by Caltrans throughout the State has indicated that ADL exists along transportation <br /> corridors due to emissions from vehicles powered by leaded gasoline. The ADL is generally limited to <br /> the upper 2 feet of soil material within the unpaved shoulder and median areas. <br /> For a solid waste containing lead, the waste is classified as California hazardous when: 1) the total <br /> lead content equals or exceeds the respective Total Threshold Limit Concentration (TTLC) of <br /> 1,000 milligrams per kilogram(mg/kg); or 2)the soluble lead content equals or exceeds the respective <br /> Soluble Threshold Limit Concentration(STLC) of 5 milligrams per liter (mg/1) based on the standard <br /> Waste Extraction Test (WET). A waste has the potential for exceeding the lead STLC when the <br /> waste's total lead content is greater than or equal to ten times the respective STLC value since the <br /> WET uses a 1:10 dilution ratio. Hence, when total lead is detected at a concentration greater than or <br /> equal to 50 mg/kg, and assuming that 100 percent of the total lead is soluble, soluble lead analysis is <br /> required. Lead-containing waste is classified as"Resource, Conservation, and Recovery Act"(RCRA) <br /> hazardous, or Federal hazardous, when the soluble lead content equals or exceeds the Federal <br /> regulatory level of 5 mg/1 based on the Toxicity Characteristic Leaching Procedure(TCLP). <br /> The regulatory criteria for suspected hazards on the Site are based on toxicity. Wastes may also be <br /> classified as hazardous based on other criteria such as flammability, reactivity, corrosivity, and <br /> ignitability. However, for the purposes of this investigation, toxicity (i.e., lead concentrations) and <br /> corrosivity (i.e., pH analysis) are the primary factors considered for waste classification. Based on <br /> current and past site usage, onsite soil is not expected to exhibit other hazardous waste characteristics. <br /> The Department of Toxic Substances Control(DTSC)regulates and interprets hazardous waste laws in <br /> California. The DTSC generally considers excavated or transported materials that exhibit "hazardous <br /> waste" characteristics to be a "waste" requiring proper management, treatment and disposal. Soil that <br /> contains lead above hazardous waste thresholds and is left in-place would not be necessarily classified <br /> by DTSC as a"waste."The DTSC has provided site-specific determinations that"movement of wastes <br /> within an area of contamination does not constitute "land disposal" and, thus, does not trigger <br /> hazardous waste disposal requirements." Therefore, lead-impacted soil that is scarified in-place, <br /> moisture-conditioned, and recompacted during landscaping improvement activities might not be <br /> considered a "waste;" DTSC should be consulted to confirm waste classification. It is noted that in <br /> addition to DTSC regulations, health and safety requirements and other local agency requirements may <br /> also apply to the handling and disposal of lead-impacted soil. Waste that is classified as either <br /> "California hazardous" or "RCRA hazardous," requires management as a hazardous waste and <br /> disposal at an appropriately permitted disposal facility. <br /> DTSC Variance <br /> The DTSC issued a statewide Variance effective July 1, 2009, regarding the reuse of ADL-impacted <br /> soils within Caltrans right-of-way. Under the Variance, soil that is classified as a non-RCRA <br /> hazardous waste, based primarily on ADL content, may be suitable for reuse within Caltrans right of <br /> way. ADL soil that is classified as a RCRA hazardous waste is not eligible for reuse under the <br /> Variance and must be disposed as a RCRA hazardous waste(Caltrans Type Z3). <br /> Project No.E8504-06-01 -3- July 13,2011 <br />