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Response to EPA Comments: RCRA Facility Investigation Phase I ...

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Table II - Overall Evaluation of Data - Data Validation Memorandum<br />

Semivolatil e Organic s<br />

DQO Samplin g and/or Measuremen t Error Samplin g<br />

(List all Analytical Method Analytica l Erro r Samplin g Error* Variability**<br />

DQOs) Appropriate<br />

Yes or No<br />

Determine level of Analytical Method: Refer <strong>to</strong> qualifications in Refer <strong>to</strong> Qualifications in<br />

soil contamination in SW-846 ­ <strong>EPA</strong> Method 8270 Table 1: Table 1:<br />

order lo decide Yes J<br />

whether or not <strong>to</strong><br />

dispose of soil SW-846-<strong>EPA</strong>Method8080 R, J<br />

off-site. Yes<br />

SW-&46-<strong>EPA</strong> Method 8150 J<br />

Yes<br />

* The evaluation of "sampling error" cannot be completely assessed in data validation.<br />

** Sampling Variability is not assessed in data validation.<br />

Valida<strong>to</strong>r: M A<br />

Date:<br />

<strong>EPA</strong>-NE - Data Validation Worksheet<br />

Page 12<br />

Potential Usability<br />

Issues<br />

'^ Estimate non detect result<br />

for n-nitrosodimethylamine<br />

due <strong>to</strong> neg. bias of %D<br />

exceedance.<br />

^ Estimate detection limits for<br />

DDD and Dieldrin due <strong>to</strong><br />

neg. bias of %D<br />

exceedance.<br />

> Endrin result of non-detect<br />

is unusable due <strong>to</strong> negative<br />

bias caused by elevated<br />

%breakdoviffi. Detection limit<br />

unusable due <strong>to</strong> possibility<br />

of false negatives.<br />

V Estimate non-detect results<br />

limits for MCPA,<br />

Dichloroprop, 2,4-D, and<br />

2,4-DB due <strong>to</strong> neg. bias of<br />

%D exceedance.<br />

^l^ln

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