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Review Comments for Revised Site Investigation Work Plan-lune 2015 <br /> Former Helena Chemical Facility <br /> Page 4 <br /> exceed the MCLS, cleanup levels cannot be set higher than the MCLS. Cleanup levels <br /> can be addressed further in a feasibility study. <br /> This section has been included in the work plan. <br /> 2. Furthermore, if constituents of concern in soil are detected above DTSC-SLs or RSLs, data <br /> should be further evaluated based on site specific conditions to determine if there is a risk to <br /> human health and/or threat to groundwater(i.e. leaching concerns), and whether further action is <br /> required.Threats to groundwater should be addressed through DI-WET testing and/or modeling. <br /> This section has been included in the work plan. <br /> 3. Section 3.0, Fourth Paragraph: The Work Plan states that "The data quality objective arts not <br /> met by the BC Laboratories EPA Method 504.1 detection limit for the analyte 1,2,3- <br /> trichloropropane. If laboratory data indicate non detect for 1,1,3-trichloropropane, then the <br /> results for otherfrnrigant pesticides may be used to evahrate whether that analyte may be present <br /> at a loner concentration and if additional sampling and/or analysis is needed. BSK Laboratories <br /> is capable of meeting the data quality objective for 1,1,3-trichloropropane using a California <br /> Department of Health Services method. However, the CVRYVQCB letter dated February 6, 2015 <br /> directed the ase of EPA Method 504.1 or an equivalent Method. SYVRCB tvebpage guidance <br /> indicates that the notification level is the same as the detection limit using Method 504.1, but <br /> Condor was unable to evaluate whether BSK methods would be equivalent or justified". Please <br /> use the following analytical methods(or equivalent method): <br /> a. Analytical methods developed by the California Department of Health (DHS) that are <br /> capable of quantification of 1,2,3-TCP at the notification level/detection limit for <br /> purposes of reporting (DLR) of 0.005 ug/L are acceptable. The selected laboratory may <br /> perform analysis for 1,2,3-TCP using one of the DHS gas chromatography/mass <br /> spectrometry (GC/MS) methods - Purge and Trap GUMS or Liquid-Liquid Extraction <br /> GUMS. <br /> This section has been included in the work plan. <br /> b. EPA Method 504.1 is also acceptable if the selected laboratory can demonstrate that the <br /> method is capable of achieving the DLR of 0.005 ug/L without method modification. <br /> See discussion above. <br /> 4. Section 6.0,First Sentence:The Work Plan states that fifty soil and groundwater samples will be <br /> analyzed for TKN, ammonia, and nitrate.However,the numeric value shown in parenthesis is 51 <br /> rather than 50.Please revise the Work Plan to correct this typographical error. <br /> The correction was made. <br /> 5. Sections 7.0 and 8.1: Section 7.0 of the Work Plan states that soil samples will be collected at <br /> approximately 15 feet below ground surface from the three proposed groundwater monitoring <br /> wells, and that one of the samples will be tested to determine permeability (hydraulic <br /> conductivity)of the soil.The Work Plan does not however, state what the other two collected soil <br /> samples will be used for or tested for. Additionally, Section 8.1 states that soil samples will be <br /> collected from the monitoring well borings for laboratory analyses based on field observations <br /> and planned collection depth but does not specify which analyses would be performed on these <br /> samples. The Work Plan should be revised to specify the analysis planned/anticipated for all soil <br /> samples collected from the monitoring wells borings. <br /> A <br /> lkkw- <br /> ILA CONDOR <br />