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Chapter 2: Summary of Findings

2.1 Summary of Current Biological Assessment Programs and Biocriteria Development

Figure 1a. Percent of total stream/river miles assessed in each state using bioassessments. Nearly 440,000 river and stream miles nationwide are assessed using biological data

This report summarizes the national breadth of biological monitoring and assessment in stream and wadeable river management programs based on 2001 program information (Table 1).

Since this summary pertains to more than just "states," the term "entity" is used to refer to the combination of states, tribes, territories, and interstate commissions.

Survey responses were received from 65 entities (50 states, District of Columbia, four territories, six tribes, and four interstate commissions – see Appendix A for a complete list).

 

 

Figure 1b. Use of Bioassessment to Determine aquatic life use.  40 entities use bioassessment to help determine aquatic life use support (ALUS) for their 305(b) reporting (Figure 1b), and six states (AK, CA, HI, MT, NV, OK) are developing processes for using biological data to interpret ALU. Thirteen entities, including seven states (AZ, AR, CO, DE, LA, SD, UT) either don't have comprehensive statewide bioassessment programs in place, or they don't yet use bioassessment data to determine the condition of their waters.

Although ranging across a wide spectrum – from initial pilot studies to comprehensive assessment – 57 of the 65 entities have bioassessment programs for streams and wadeable rivers, and two (Puerto Rico and the Nez Perce Tribe) have programs under development. Nearly 440,000 river and stream miles nationwide are assessed using biological data (see Figure 1a for state-by-state percentages). More importantly, as shown in Table 1, 40 entities use bioassessment to help determine aquatic life use support (ALUS) for their 305(b) reporting (Figure 1b), and six states (AK, CA, HI, MT, NV, OK) are developing processes for using biological data to interpret ALU. Thirteen entities, including seven states (AZ, AR, CO, DE, LA, SD, UT) either don't have comprehensive statewide bioassessment programs in place, or they don't yet use bioassessment data to determine the condition of their waters.

 

Figure 2a. Narrative biocriteria development.  A total of 29 entities have incorporated narrative biocriteria into their WQS (Figure 2a). The 11 entities (AZ, CO, HI, IL, IN, IA, MD, MT, NV, WA, Pyramid Lake Paiute Tribe) in a developmental phase of adopting narrative biocriteria into their WQS are at various stages in this process. While some may have already developed biocriteria and are working on promulgating the statements into their WQS, others are awaiting state or federal approval, or are in the earlier stages of developing narrative biocriteria to be submitted for review. Although 20 entities do not have narrative biocriteria in their WQS, several of these have incorporated general aquatic life statements.
A total of 29 entities have incorporated narrative biocriteria into their WQS (Figure 2a). The 11 entities (AZ, CO, HI, IL, IN, IA, MD, MT, NV, WA, Pyramid Lake Paiute Tribe) in a developmental phase of adopting narrative biocriteria into their WQS are at various stages in this process. While some may have already developed biocriteria and are working on promulgating the statements into their WQS, others are awaiting state or federal approval, or are in the earlier stages of developing narrative biocriteria to be submitted for review. Although 20 entities do not have narrative biocriteria in their WQS, several of these have incorporated general aquatic life statements. The following five entities – ICPRB, SRBC, Nez Perce Tribe, Oneida Nation of Wisconsin and Passamaquoddy Tribe - Pleasant Point Reservation – do not have federally approved WQS and are not currently working toward that end. Therefore, these entities are not included in any biocriteria counts.

Figure 2b. Narrative biocriteria in WQS with quantitative implementation procedures. Of the 29 entities with narrative biocriteria incorporated into their WQS, 22 have also developed quantitative implementation procedures or translators, and eight are working to develop them.Of the 29 entities with narrative biocriteria incorporated into their WQS, 22 have also developed quantitative implementation procedures or translators, and eight are working to develop them (Figure 2b). These procedures can be found in various documents including WQS, SOPs, 305(b) guidelines, and other agency documents. While numeric procedures are not numeric biocriteria per se, they do provide a quantitative basis for assessing attainment of specific designated aquatic life uses and are an important step in biocriteria development.

 

 

 

 

 


 

Next - Summary of Findings (continued)

Biological Indicators | Aquatic Biodiversity | Statistical Primer


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