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2900 - Site Mitigation Program
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PR0009275
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Last modified
1/7/2020 2:26:39 PM
Creation date
1/6/2020 1:37:41 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009275
PE
2960
FACILITY_ID
FA0004014
FACILITY_NAME
VALERO ENEREGY CORP/NUSTAR ENERGY
STREET_NUMBER
3505
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95203
APN
16203003
CURRENT_STATUS
01
SITE_LOCATION
3505 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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estimates. Some of the statistical limits used to estimate the BTVs for data sets with and without <br /> NDs as incorporated in ProUCL 4.0 are listed as follows. <br /> 1. Upper Percentiles (e.g., 95%, 99%) for data sets without and with NDs (e.g.,based upon <br /> KM estimates) <br /> 2. Upper Prediction Limit(UPL) for a future (site observation) observation(using KM or <br /> other estimates for data sets with NDs) <br /> 3. UPL for future k(e.g., next k or k site observations) observations <br /> 4. Upper Tolerance limits (UTLs) - Upper Confidence Limits for Upper Percentiles <br /> 5. Upper percentiles, UPLs,UTLs based upon data obtained using ROS methods—data <br /> with NDs <br /> 6. IQR Upper Limit(upper end of the upper whisker in a Box Plot) <br /> 7. UPL and UTL based upon resampling bootstrap <br /> 8. UPL based upon Chebyshev inequality <br /> 9. UTL based upon bootstrap methods for data sets with NDs <br /> 10. BTVs using nonparametric methods based upon higher order statistics (Conover, 1999) <br /> Note: The behavior of the exploratory IQR based upper limit as an estimate of a BTV is not well <br /> studied. This limit should be used with caution to estimate the BTVs or not-to-exceed values. <br /> It should be noted that background versus site comparisons based upon the BTVs are performed <br /> when not enough site data(e.g., <4-6 observations) are available to perform traditional two <br /> sample comparisons using hypotheses testing approaches such as t-test, Wilcoxon Rank Sum <br /> test, and Gehan test. When enough site data are available (e.g., at least 8-10, more are <br /> preferable), it is preferable to use hypotheses testing approaches to compare site data with BTVs <br /> or not-to-exceed values. Thus, in the absence of adequate amount of site data, individual point- <br /> by-point site observations are compared with some BTVs to determine the presence or absence <br /> of contamination due to site related activities. This method of comparing site versus background', <br /> level contamination is particularly helpful to use after some sort of remediation activities have <br /> taken place at the site; and the objective is to determine if the remediated site areas have been <br /> remediated enough to the background level contaminant concentrations. <br /> Typically, a site observation(possibly based upon composite samples)in exceedance of a <br /> background threshold value can be considered as coming from a contaminated site area that may <br /> have been impacted by the site-related activities. In other words, such a site observation may be <br /> considered as exhibiting some evidence of contamination at the site due to site related activities. <br /> In case of an exceedance of the BTV by a site location, some practitioners like to verify the <br /> possibility of contaminated site location by re-sampling (collecting 2-3 additional samples) that <br /> location, and comparing the sampled value(s)with the BTV. <br /> Hypothesis Testing Approaches <br /> Both single sample and two sample parametric and nonparametric hypotheses testing approaches <br /> are available in ProUCL 4.0. The hypotheses testing approaches as incorporated in ProUCL 4.0 <br /> can be used on full data sets without any ND observations, and on left-censored with nondetect <br />
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