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EL DORADO
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2900 - Site Mitigation Program
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PR0540858
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Entry Properties
Last modified
8/1/2019 10:18:09 AM
Creation date
8/1/2019 10:06:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0540858
PE
2960
FACILITY_ID
FA0023360
FACILITY_NAME
ARCO SERVICE STATION #2130
STREET_NUMBER
7906
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95210
CURRENT_STATUS
01
SITE_LOCATION
7906 N EL DORADO ST
QC Status
Approved
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EHD - Public
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Standard Operating Procedure <br /> Measurement of Potassium Permanganate SOxD <br /> SOxD analysis using potassium permanganate provides an estimate of the soil oxidant demand for <br /> potassium permanganate. The potassium permanganate soil oxidant demand ( SOxD) is measured <br /> using a small representative sample of soil, a standard potassium permanganate solution, and an <br /> Ultra Violet Visible detector (UV-vis) or spectophotometer to measure the permanganate <br /> concentration in the treatment water over time. The method is presented below: <br /> Triplicate blank samples or controls: <br /> Add 30ml KMn04 standard solution ( 0. 500 g/L) to each of 3 amber VOA bottles <br /> Triplicate samples of each soil sample: <br /> Add 1g soil to each amber VOA bottle <br /> Add 30ml KMn04 standard solution ( 0. 500 g/L) <br /> Vortex bottles for 30 seconds <br /> Allow samples to stand for 15 minutes before reading in the UV-vis spectrophotometer <br /> The analysis can be scaled up using equivalent proportions. If a larger sample is required, 1 <br /> kilogram (kg) of soil can be used with 10 liters of KMn04 solution. Mixing will have to be done by <br /> hand or using a sample roller. The efficiency of mixing will depend on the containers available to do <br /> the mixing in. <br /> Analysis of Samples <br /> Dilute samples 1 /10 to 1 /100 for analysis ( ie. 100 ul sample in 10ml distilled water) depending on the <br /> intensity of the color in the reacted solution. Use a 10ml pipette to dispense 10ml distilled water into <br /> a clean VOA bottle. Add the sample, put on the lid, inverted twice and pour the diluted sample into <br /> the HACH UV-vis spectrophotometer tube. If precipitate is observed in the extracted sample and the <br /> standard used for analysis, filter the sample with a 0. 45 pm filter cartridge or centrifuge at high speed <br /> prior to analysis. Set up a standard concentration curve with the standard solution prepared to treat <br /> the samples. Prepare standards that are between 0 and 500 mg/I of KMn04 to quantify the KMn04 <br /> in each sample. Wipe each tube with a Kimwipe if necessary. Both VOA bottle and spectrometer <br /> tube should be rinsed between sample sets, but not between replicates of the same set. <br /> Sampling Intervals <br /> Samples that contain high concentrations of organic matter or clay will have a large soil oxidant <br /> p 9 <br /> demand. Typical soil samples that have low organic matter and low or moderate clay concentrations <br /> consume oxidant at a more moderate rate. The permanganate solution in samples should be <br /> analyzed immediately after addition, within several hours, and after 1 , 2, 4, 7 , and 10 days. After <br /> approximately ten days the consumption rates have stabilized and the total soil oxidant demand can <br /> be estimated from the results. <br /> Samples should be kept in the dark (in the VOA bottle box) <br /> Samples should be shaken/vortexed after each analysis. <br /> DATA MANIPULATION AND CALCULATIONS <br /> The concentration of KMn04 in the sample is determined from the UV-vis analysis. Multiply the <br /> observed concentration by the dilution factor to get the sample concentration. Subtract the solution <br /> concentration from the initial concentration ( 3.95 g/L or 3950 mg/L) and multiply the total volume <br /> used per sample ( 10 mL or 0. 10 L according to the method above) times the difference. Plot the loss <br /> I:\BP-ARC0\04 BP Valley Portfolio\BP Valley Sites\2130\Work Plan\2130 workplan 2-07.doc <br />
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