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Present Results for Decision-Making

From the EPA Watershed Academy

It is important to present the results of bioassessments in a manner in which the results are clear, compelling, and meaningful. This can only be done by making sure that the monitoring design chosen matches the needs of management and decision makers. This page shows some examples for you to consider and how to get more information. The examples shown do not represent the depth of these state programs, and we encourage you to explore their websites to learn more.

More about using bioindicators

Ohio EPA Example

Figure 1

Scioto River graph (Click for information about alternate access)

Scioto River Graph

This format has long been a very compelling approach for not only showing the influence of pollution sources through a 40-mile stretch of river, but also showing the change that occurred over 12 years. This graphic keeps the reader aware of the water quality standards for this reach and shows the results relative to those standards

Florida DEP Example

Image of EcoSummary for Florida Stream HealthFlorida DEP's Bioassessment ProgramExit EPA Disclaimerhas also explored different ways to present their results. One unique effort are their EcoSummaries, which presents a one-page summary of a site containing a brief description, picture, water quality rating, and a link to get more detailed information. This provides the basic information for readers and keeps them from being overwhelmed with too much information too soon.

 

 

 

 

Maryland DNR Example

Graph showing relationship of brook trout with % impervious surface - in general, brook trout are intolerant to more than 1% impervious surface in the watershed

Maryland DNR's Biological Stream SurveyExit EPA Disclaimerlooks at a wide variety of issues in the state using a random sample site selection design. The graph on the left shows the statewide relationship with native brook trout abundance and impervious surface. This information should be a clear indication that if brook trout, a native species, is desired, urban and suburban development should be more carefully monitored (at a minimum). The second chart illustrates the relationship of habitat with fish community health in the lower Potomac River basin. This has direct implications for assessing whether point and/or non-point source controls are adequate.

Figure 2

Graphic showing the relationship of the fish IBI with instream habitat score - in general, the higher the habitat score, the higher the IBI

Figure 2: The relationship of the fish IBI with instream habitat score - in general, the higher the habitat score, the higher the IBI.

There are many national, regional, state, and local government programs that struggle with how to convey the information to their management, and the interested public. Keep in mind that there are many ways to present the information, but a"picture" is worth a thousand words... as long as you have the detailed information to support it.

For a more detailed look at presenting biological data and information, please visit

Reference

Karr, J.R. and E. W. Chu. 1997. Biological Monitoring and Assessment: Using Multimetric Indexes Effectively (PDF). (EPA-235-R97-001 December 1997) (155 pp, 7.5M, About PDF)

Biological Indicators | Aquatic Biodiversity | Statistical Primer


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