The following excerpts are from: Sustainable Land Stewardship Institute. 2003. Biological and Physical/Habitat Assessment of Selected Sites Within the Santa Rosa Watershed. Performed for the City of Santa Rosa as part of Storm Water Monitoring Program. 18 p.

BMI Sampling: The technique used to describe the BMI community and the biotic condition of the six sampling sites was the California Stream Bioassessment Procedure (CSBP).  The California Department of Fish and Game (Harrington 1996) developed the CSBP as standardized and cost-effective sampling, laboratory and quality assurance procedures for the State’s bioassessment programs.  The CSBP is a regional adaptation of the U.S. Environmental Protection Agency (EPA) Rapid Bioassessment Protocols (Barbour et al. 1999) and has been used in various parts of the world to measure biological integrity of aquatic systems (Davis et al. 1996).

Sampling was conducted by the City of Santa Rosa staff in May of 2000, 2001 and 2002.  Riffle length was measured for each of three riffles at each monitoring reach.  Using a random number table, a transect was established perpendicular to stream flow along the upstream third of each riffle.  Starting at the downstream riffle, the benthos within a 2 ft2 area was sampled upstream of a 1 ft wide, 0.5 mm mesh D-frame kick-net.  Sampling of the benthos was performed manually by rubbing cobble and boulder substrates in front of the net, followed by “kicking” the upper layers of substrate to dislodge any remaining invertebrates.  The duration of sampling ranged from 60-120 seconds, depending on the amount of boulder and cobble-sized substrate that required rubbing by hand; more and larger substrates required more time to process.  Three locations representing any habitat diversity along each transect were sampled and combined into a composite sample, representing a 6 ft2 area for each transect and 18 ft2 for the entire reach.  Each composite sample was transferred into a 500 ml wide-mouth plastic jar containing approximately 200 ml of 95% ethanol.  This technique was repeated for each of three riffles in each reach.

BMI Laboratory Analysis: The BMI samples collected in 2000 and 2001 were processed at the EcoAnalysists Laboratory in Moscow Idaho and the 2002 samples were processed by SLSI in Chico California .  At both laboratories, each sample was rinsed through a No. 35 standard testing sieve (0.5 mm brass mesh) and transferred into a tray marked with twenty, 25 cm2 grids.  All sample material was removed from one randomly selected grid at a time and placed in a petri dish for inspection under a stereomicroscope.  All invertebrates from the grid were separated from the surrounding detritus and transferred to vials containing 70% ethanol and 5% glycerol.  This process was continued until 300 organisms were removed from each sample.  The material left from the processed grids was transferred into a jar with 70% ethanol and labeled as “remnant” material.  Any remaining unprocessed sample from the tray was transferred back to the original sample container with 70% ethanol and archived.  BMIs were then identified to a standard taxonomic level using appropriate taxonomic keys (Brown 1972, Edmunds et al. 1976, Klemm 1985, Merritt and Cummins 1995, Pennak 1989, Stewart and Stark 1993, Surdick 1985, Thorp and Covich 1991, Usinger 1963, Wiederholm 1983, 1986, Wiggins 1996, Wold 1974).

See SRSI (2003) for literature citations.