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ARCHIVED REPORTS XR0012610
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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PACIFIC
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6425
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0012610
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Entry Properties
Last modified
8/21/2019 3:01:29 PM
Creation date
8/21/2019 2:18:50 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012610
RECORD_ID
PR0519189
PE
2950
FACILITY_ID
FA0014347
FACILITY_NAME
CURRENTLY VACANT
STREET_NUMBER
6425
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
09741031
CURRENT_STATUS
02
SITE_LOCATION
6425 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Nj� 4 uuu <br />�v <br /> 7.1.3 Dry waste samples amenable to grinding; Grind of <br /> otherwise subdivide the waste so that it: either pa::sa!, <br /> through a 1-mm sieve or can be extruded through a 1-mon <br /> hole, Introduce sufficient sample into thcl grindirip, <br /> apparatus to yield at least. 10 g after grinding. <br /> 7,2 Determination of erUnt moisture: In certain eases, sample <br /> results are desired based on a dry-weight basis. Whon such data <br /> is desired, a portion of sample for moisture determination <br /> should be weighed out at the same time as the portion used for <br /> analytical detergtination. <br /> 7.2.1 Immediately after w-I ghing the sample for extraction, <br /> weight 5-10 g of I :z sample into a tared crucible, <br /> Determine the percent moisture by drying overnight at <br /> 105°C. Allow to cool in a desiccator before weighing. <br /> P. of !-.ample= of dr sam le x100, 4 moisture <br /> g of sample <br /> 7.3 Determination Of 12H (if required': Transfer 5o g of sample to <br /> a 100-mL beaker. Add 50 mL of water and stir for 1 hr. <br /> Determine the pli of sample with glass electrode and pH mete• <br /> while stirring. Discard this portion of sample. <br /> 7.4 Extraction method far sam les expected to contain lots <br /> concentrations of organics and pesticides [20 mg/kg): <br /> 7.4.1 The following step should be performed rapidly to avoid <br /> loss of the more volatile exLractables. Weight <br /> approximately 30 g of sample into a 400-mL beaker. <br /> Record the weight to the nearest 0.1 g. Mon-porous or <br /> wet samples (gummy or clay type) that do not have a <br /> free-flowing sandy texture must be mixed with 60 g of <br /> anhydrous sodium sulfate using a spatula The sample <br /> should be free-flowing at this point. (r.id 1 mL of <br /> surrogate standards to all samples, spikes, and blanks <br /> (see Method 3500 for details on the surrogate standard <br /> solution and the matrix spike solution). For ;he sample <br /> in each analytical batch selected for spiking, add 1.0 <br /> mI. of the matrix spiking standard. For base/neutral- <br /> acid analysis, the amount added of the surrogates and <br /> matrix spiking compounds should result in a final <br /> concentration of 100 ng/uL of each acid analyte in the <br /> extract to be analyzed (assuming a 1 uL injection) . If <br /> Method 3640, Gel-permeation cleanup, is to be used, add <br /> twice the volume of surrogates and matrix spiking <br /> compounds since half of the extract is lost due to <br /> loading of the GPC column. Immediately add 100 mL of <br /> 1:1 methylene chloride:acetone. <br /> 7,4,2 place the bottom surface of the tip of the X207 3/4 in. <br /> disruptor horn about 1/2 in. below the surface of the <br /> solvent, but above the sediment layer. <br />
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