EPA-OW: EPA RBP (Inverts MHAB):  Benthic Macroinvertebrate RBP, multiple habitat, D-frame dip net

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Benthic Macroinvertebrate Protocols: 7.2, Multiple Habitat Approach: D-frame Dip Net
Current Revision
Second Edition, 1999
Media
WATER  (Waterbody type - Wadeable stream)
Instrumentation
Invertebrate Net (w/ handle)
Method Subcategory
Population/Community
Method Source
  EPA-OW
Citation
  EPA Rapid Bioassessment Protocols for Use in Streams and Wadeable Rivers: Periphyton, Benthic Macroinvertebrates and Fish
Protocol
EPA RBP Protocol - Rapid Bioassessment Protocols for Use in Streams and Wadeable Rivers: Periphyton, Benthic Macroinvertebrates, and Fish - Second Edition
Brief Method Summary
A 100m reach representative of the characteristics of the stream should be selected that is at least 100m from any road, bridge crossing, or major tributary. Prior to sampling, the physical/chemical field sheet should be completed and a map should be drawn showing in-stream attributes and structures. Sampling begins at the downstream portion of the reach and proceeds upstream. Different types of habitat are to be sampled in approximate proportion to their representation of surface area of the total macroinvertebrate habitat in the reach. For example, if snags comprise 50% of the habitat in a reach and riffles comprise 20%, then 10 jabs should be taken in snag material and 4 jabs should be take in riffle areas. The remainder of the jabs (6) would be taken in any remaining habitat type. Habitat types contributing less than 5% of the stable habitat in the stream reach should not be sampled. The jabs or kicks collected from the multiple habitats will be composited to obtain a single homogeneous sample.
Scope and Application
This protocol is appropriate for the sampling of wadeable streams and rivers. Programmatic applications of the biological data generated using these methods include, CWA Section 305(b) water quality assesments, CWA Section 319 nonpoint source assessments, watershed protection, CWA Section 303(d) TMDL development, CWA Section 402 NPDES permits and individual control strategies, ecological risk assessment, and development of USEPA water quality criteria and standards
Applicable Concentration Range
Interferences
Every 3 jabs, more often if necessary, wash the collected material by running clean stream water through the net two to three times.
Quality Control Requirements
Proper sample labeling; Net, pan, etc. rinsed thoroughly between samples; Replicate (1 duplicate sample) collected at 10% of sites
Sample Handling
Rinse large debris and place any organisms found into sample container; place all small debris directly into sample container. Preserve in 95% ethanol sufficient to cover the sample. Place a label indicating the sample identification code or lot number, date, stream name, sampling location, and collector name into the sample container. The outside of the container should include the same information and the words "preservative, 95% ethanol". If more than one container is needed for a sample, each container label should contain all of the information for the sample and should be numbered (e.g., 1 of 2, 2 of 2, etc)
Maximum Holding Time
Indefinite with proper preservation.
Relative Cost
Greater than 6 hrs. per site/sample
Sample Preparation Methods
95% ethanol