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Performance Objective |
Data Requirements |
Success Criteria |
Results |
---|---|---|---|
1. Equivalent analyte detection limitis |
Detection levels for all AGI and low-flow samples. |
Detection levels near or below EPA’s MCL values for all contaminants tested. |
APG site: The MDL for AGI sampler was below the MCLs. However, it was ~20x > low-flow MCL. Pease site: For most analytes, MDLs equivalent to low-flow. MDLs were 10x < MCLs. |
2. Equivalent analyte concentrations to low-flow sampling |
Analyte concentrations for each sampling method for all wells |
Lack of statistically significant differences at p <0.05 |
APG site: Significant differences for several analytes. Pease site: Generally no significant differences; poorest agreement for benzene and xylenes |
3. Comparable concentrations across the entire range of analyte concentrations present |
Analyte concentrations for each sampling method for all wells |
Linear least fit model shows linear relationship with a slope that is not significantly different from 1.0 |
Both sites: Significant linear relationships between the AGI and low-flow data, with a slope = 1.0, for all analytes except TCA and CF at APG and toluene at Pease. |
4. Ability to measure vertical profiles within wells |
AGI results from all depth intervals tested. |
Vertical profile of wells with AGI Sampler |
Vertical profiles revealed. Pronounced concentration gradients in wells near plume epicenters, even in a well with a 5 ft screen. |
5. Cost savings |
Records of the costs for equipment and supplies Field record of field crew’s time |
Cost savings of at least 25% |
APG site: Cost savings of 18% to 35%, depending upon the size of field crew. Pease site: Cost savings of 10% to 25%, depending on size of field crew. Both sites: Cost savings of 30% to 40% using recent price quote for samplers. |