| Use: | Subjective interpretation made by a bioassessment expert as to the potential impact of
    a chemical or on the health of an ecosystem. See 6.2.24 for use with VOCs, SVOCs, and pesticides, 7.1.10 for use with metals, and 8.2.6 for use with radionuclides. | 
Description:
Field bioassessments provide an indication of the potential for ecological risk (or lack thereof) that can be used to: (1) estimate the likelihood that ecological risk exists; (2) identify the need for site-specific data collection efforts; and (3) focus site-specific ecological risk assessments where warranted. Initial screening-level assessments are not designed or intended to provide definitive estimates of actual risk, generate cleanup goals, and are not based upon site-specific assumptions. Rather, their purpose is to assess the need to conduct a detailed ecological risk assessment for a particular site. To conduct an initial screening-level assessment for ecological risk, the following steps should be followed:
Analytes:
10. Explosives
Media:
| Soil/Sediment | Water | Gas/Air | 
| BETTER | BETTER | BETTER | 
| Selectivity: | Technique measures a part of the compound. | 
| Susceptibility to Interference: | High. | 
| Detection Limits : | Not Applicable. | 
| Turnaround Time per Sample: | More than a day. | 
| Applicable To: | |||
| Screen/Identify | Characterize Concentration/Extent | Cleanup Performance | Long-Term Monitoring | 
| BETTER | BETTER | SERVICEABLE | ADEQUATE | 
| Quantitative Data Capability: | Does not produce quantitative data. | 
| Technology Status: | Commercially available technology with moderate field experience. | 
| Certification/Verification: | Technology has not participated in CalEPA certification and/or CSCT verification program. | 
| Relative Cost per Analysis: | Most expensive. | 
Limitations:
ASTM Standards/EPA Methods:
No applicable ASTM standards or EPA methods are cited for this technology.
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