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Appendix B
Comparision of Existing Lakes Protocols


Two research programs - the U.S. Geological Survey's North American Water Quality Assessment (NAWQA) and the USEPA Office of Research and Development's Environmental Monitoring and Assessment Program (EMAP) - incorporate biological monitoring components similar to those of USEPA's Biological Monitoring Programs. The following discussion compares these programs, as well as a program implemented by the Tennessee Valley Authority (TVA) and USEPA's Clean Lakes Program.

NAWQA, EMAP, TVA, and Clean Lakes Program

NAWQA and EMAP are scientific research programs with objectives quite different from those of state-level biological assessment programs (USEPA 1990a, Meador et al. 1993). NAWQA and EMAP differ in the waterbodies they address: NAWQA is designed for streams and rivers and EMAP is designed for all environments. including streams and lakes (EMAP-Surface Waters). The two programs are set apart by the statistical and experimental designs used to accomplish their program.

The NAWQA and EMAP programs make assessments of the environment and trends in environmental quality at the national or regional scales. In these programs, USGS or USEPA scientists and technicians are directly responsible for collecting data from the field and analyzing results. NAWQA and EMAP also use different statistical designs to assess national trends. The NAWQA approach is to sample repeatedly at equal time intervals at the same stations (Gurtz 1994) and to apply nonparametric statistical algorithms to the data, adjusted for seasonal variation (Meador et al. 1993). The EMAP approach is to overlay a region or landscape with a grid and then to monitor a randomly selected subsample of the grid (USEPA 1991d). Both methods are useful to evaluate trends in environmental quality.

The TVA program, which monitors ecological condition of reservoirs,also covers a large percentage of the country. The assessment is based on sediment quality, dissolved oxygen content (DO), chlorophyll a concentration, a benthic macroinvertebrate index, and a Reservoir Fish Assemblage Index (RFAI) (TVA 1994).

USEPA's Clean Lakes Program provides support to water quality agencies for lake assessment, protection, and restoration. The program requires assessments of dissolved oxygen (DO), chlorophyll a, Secchi disk transparency, macrophytes, sediment chemical characterization, and tributary streamflow measurements. A complete description of the Clean Lakes Program recommended sampling methodology is found in the Clean Lakes Program Guidance Manual (USEPA 1980a).

State Mandates

USEPA's Biological Monitoring and Biological Criteria Programs are targeted to state and tribal water quality and environmental management agencies. Monitoring data is collected at the state or local watershed level by state agency personnel or by suitably trained organizations to identify problems and report on control effectiveness. The Biological Monitoring Program accomplishes its mission through training and the translation of research techniques to rapid, efficient and defensible protocols these techniques can be used on an operational basis by state personnel and others to develop biological criteria that can be used in management decision making.

The broad water quality goals of the Clean Water Act are translated by each of the states into water quality standards designed to protect beneficial uses (USEPA 1996a). The USEPA biological monitoring program therefore looks to individual states and tribes rather than federal agencies for the assessment of those beneficial uses, as they have been designated in various administrative codes. The protocols presented in this document are designed to assist states and tribes in making their beneficial use assessments in biological terms. The protocols and measurement techniques will also help states fulfill their obligation to report to Congress biennially on the attainment of designated beneficial uses of their surface waters (USEPA 1994f).

Monitoring Biotic Integrity

Although the statistical designs used by EMAP, NAWQA, and USEPA's biological monitoring programs differ, the monitoring components are generally complementary. These programs assess conditions of lakes, rather than producing comprehensive inventories of biological resources. Some but not all major biological assemblages - invertebrates, fish, plants, birds, microorganisms - are sampled, identified, and counted, using a standardized technique, during a well defined season of the year.

In this kind of monitoring, the focus is on the full array of species captured by the sampling methods to provide cost-effective sampling and standardization. The methods described in this document do not target rare species. Issues of seasonal variation and bias in the sampling protocols are standardized or "indexed" to simplify statistical analysis (Sokal and Rolfe 1969). These monitoring programs produce sensitive and robust estimates of the biological integrity of the aquatic system, as well as the impacts that anthropogenic activities might have on the environment in terms of degrading the aquatic life designated use (Fausch et al. 1984, Karr 1991, USEPA 1989b).

It is desirable for all agencies to use similar water quality monitoring protocols so that data can be shared and compared. The national water quality monitoring council,(NWQMC) which succeeded the Intergovernmental Task Force on Monitoring (ITFM) is the forum for that kind of information exchange, and several of the recommendations of the task force address the issue of data comparability (ITFM 1992). However, in the case of biological monitoring, species characteristics differ regionally, and sampling techniques are not expected to be the same across ecoregions. In USEPA's Biological Monitoring Program and Biological Criteria Program, sampling techniques and index period must be identical for the reference condition and the test locations, and the use of common techniques across agencies within a region would significantly improve the efficiency and power of biological monitoring activities. Table B-1 compares lake habitat and biological monitoring among EMAP, TVA, and the USEPA Biological Monitoring Program. NAWQA has not published specific protocols for lakes and reservoirs.

Table B-1.Comparision of lakes protocols with EMAP, TVA Reservoirs, and Clean Lakes.

Table B-1. The information provided in this graphic is too detailed to be described in this tag. Please contact EPA at OW-GENERAL@epa.gov to ask for this information in another manner.

Table B-1.Comparision of lakes protocols with EMAP, TVA Reservoirs, and Clean Lakes. (continued).

Table 
            B-1, continued. The information provided in this graphic is too 
            detailed to be described in this tag. Please contact EPA at 
            OW-GENERAL@epa.gov to ask for this information in another 
manner.


Home ~ Preface ~ Chapter 1 ~ Chapter 2
Chapter 3 ~ Chapter 4 ~ Chapter 5 ~ Chapter 6
Chapter 7 ~ Chapter 8 ~ Chapter 9 ~ Chapter 10
Appendix A ~ Appendix B ~ Appendix C ~ Appendix D
Appendix E ~ Appendix F ~ Appendix G


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