North American Benthological Society [NB]

NB24A   CC:R02   Tuesday  1530h

Bioassessment II: Douglas Nieman Memorial

Presiding:  M B Griffith, National Center for Environmental Assessment, Office of Research and Development, U.S. Environmental Protection Agency; J Orr, Pennsylvania State

NB24A-01   15:30h

A RIVPACS Type Model for Wadeable Streams of Wyoming

* Hargett, E G (eharge@state.wy.us) , Wyoming Department of Environmental Quality - Water Quality Division, Herschler Bldg. 4W, 122 W. 25th St., Cheyenne, WY 82002 United States
Zumberge, J R (jzumbe@state.wy.us) , Wyoming Department of Environmental Quality - Water Quality Division, 1866 S. Sheridan Ave., Sheridan, WY 82801 United States
Hawkins, C P (chuck.hawkins@usu.edu) , Department of Aquatic, Watershed and Earth Resources, Utah State University , 5210 Old Main Hill, Logan, UT 84322 United States

RIVPACS models produce a community-level measure of biological condition known as O/E, which is derived from a comparison of the observed (O) biota with those expected (E) to occur in the absence of anthropogenic stress. Benthic macroinvertebrate and environmental data collected at 739 stream monitoring stations, from 1993 to 1999, were used to develop, validate, and apply a RIVPACS model to assess the biological condition of wadeable streams in Wyoming. We used multivariate analyses to group 157 reference sites based on similarities in macroinvertebrate community structure as well as examine which environmental variables best discriminated among reference groups. A suite of fifteen categorical and continuous environmental variables best discriminated among fifteen reference groups and explained >75% of the natural variability in biota within the reference dataset. Mean reference site O/E values were near unity. Mean test site values ranged from 0 to 1.60 (mean =0.79). Our model was accurate and reasonably precise (SD of O/E values for validation data = 0.17). O/E responded to anthropogenic stressors and was robust both temporally and spatially. These results show that RIVPACS models can produce effective assessments of biological condition over broad, ecologically diverse, geographic regions of the intermountain west such as Wyoming.

NB24A-02   15:45h

A Comparison of Trichoptera (Caddisfly) Species Diversity From Several Peninsular Florida Waterbodies Using Benthic and Terrestrial Sampling Methods

* Rasmussen, A K (rasandy@freenet.tlh.fl.us) , Florida A&M University, Entomology, Center for Water Quality, Tallahassee, FL 32307-4100 United States
Denson, D R (dana.denson@dep.state.fl.us) , Florida Department of Environmental Protection, 3319 Maguire Blvd., Orlando, FL 32803-3767 United States

Typically, environmental agencies tasked with water quality bioassessment solely use benthic sampling methods to collect aquatic insects. Because most aquatic insects live in water only as immatures, benthic samples consist largely of larvae. In Trichoptera, and most insect groups, alpha taxonomy is chiefly based on adult reproductive structures, thus specimens from benthic samples in many cases cannot be assigned species names. Therefore, benthic sampling gives a limited picture of species diversity within aquatic insect communities and may result in monitoring programs not detecting biological impairment involving population losses or declines. In this study of several waterbodies on the Florida peninsula we compare caddisfly species diversity in samples collected using benthic protocols used by the Florida Department of Environmental Protection with that of samples of adult caddisflies collected using UV-blacklight. Light-trap samples yielded significantly higher numbers of both caddisfly individuals and taxa. Benthic samples because of smaller sample sizes and genus-level determinations gave relatively incomplete characterizations of caddisfly community structure. So that aquatic communities can be better understood and protected, we recommend that environmental agencies begin to incorporate additional sampling methods such as light trapping into their assessment and monitoring programs.

NB24A-03   16:00h

Macroinvertebrate Community Response to the Elimination of Concentrated Feedlot Runoff to a Headwater Stream

* Snitgen, J L (jsnitgen@oneidanation.org) , Oneida Environmental, Health and Safety, 3759 W. Mason Street, P.O. Box 365 , Oneida, WI 54155
Moren, M M (mmoren@oneidanation.org) , Oneida Environmental, Health and Safety, 3759 W. Mason Street, P.O. Box 365 , Oneida, WI 54155

During rainfall and snow melt events, a first order, cold-water stream was receiving varying amounts of liquefied manure from a concentrated feed lot. Stream restoration efforts included the implementation of best management practices to prevent further discharge of the water/manure mixture to the stream. Physical, chemical and biological data were collected pre-construction and two years post-construction of the containment system at a fixed location downstream of the feedlot. Hilsenhoff Biotic Index scores improved significantly, from 6.79 or "Fairly Poor" before the installation of the manure containment system, to 5.28 or "Good" after the installation of the manure containment system. Taxa richness improved from 25 to 34 and the EPT score improved from 0 to 4. Key words: macroinvertebrate, community response, manure, feedlot runoff, stream restoration

NB24A-04   16:15h

Correlation of Fish and Benthic Macroinvertebrate Communities With Multi-scale Environmental Descriptors in Wadeable Streams of the Yukon River Basin

* Bailey, J L (jbaile3@uwo.ca) , Department of Biology, The Univeristy of Western Ontario , LONDON, ON N6A 5B7 Canada
Bailey, R C (drbob@uwo.ca) , Department of Biology, The Univeristy of Western Ontario , LONDON, ON N6A 5B7 Canada

We sampled fish and benthic macroinvertebrates at thirty wadeable stream sites in the Yukon River basin in Yukon Territory, Canada during July, 2004, to establish reference conditions in Yukon River basin stream communities. We also measured water quality (eg. temperature, dissolved oxygen, conductivity, pH), stream flow, substrate characteristics and riparian vegetation at each site. Water samples from each site were subsequently analyzed for nutrients and metals. In addition, catchment area, catchment perimeter, catchment land cover, distance of each site to major water bodies and stream barriers were determined through Geographic Information System and satellite photography analysis. Fish and benthic macroinvertebrate community structures and their relationships with the multi-scale description of the stream environment were quantified with non-metric multidimensional scaling, principal component analysis, and correlation analysis.

NB24A-05   16:30h

Ecological Relevance of Abiotic Factors on Macroinvertebrate Communities and its Importance to Validate Portuguese River Typology

* Pinto, P (ppinto@uevora.pt) , Centro De Ecologia e Ambiente, Universidade de Evora, Largo dos Colegiais, Evora, 7001 Portugal
Morais, M , Centro De Ecologia e Ambiente, Universidade de Evora, Largo dos Colegiais, Evora, 7001 Portugal
Cortes, R , Dep. Florestal, Universidade de Tras-os-Montes e Alto Douro, Quinta dos Prados Aptd 1013, Vila Real, 5000-911 Portugal
Feio, M J , Dep. Zoologia, Faculdade de Ciencias e Tecnologia, Universidade de Coimbra, Largo Marques Pombal, Coimbra, 3004-517 Portugal
Formigo, N , Dep. Zoologia e Antropologia, Faculdade de Ciencias, Universidade do Porto, Praca Gomes Teixeira, Porto, 4099-002 Portugal
Duarte, E , Dep. Zoologia e Antropologia, Faculdade de Ciencias, Universidade do Porto, Praca Gomes Teixeira, Porto, 4099-002 Portugal
Marques, A , Dep. Zoologia e Antropologia, Faculdade de Ciencias, Universidade do Porto, Praca Gomes Teixeira, Porto, 4099-002 Portugal
Mourinha, E , Centro De Ecologia e Ambiente, Universidade de Evora, Largo dos Colegiais, Evora, 7001 Portugal
Ramalhinho, R , Centro De Ecologia e Ambiente, Universidade de Evora, Largo dos Colegiais, Evora, 7001 Portugal

The objective of this study is to validate an abiotic river typology in Portugal in order to fulfil the requirements of the Water Framework Directive. Macroinvertebrate samples were taken at 155 potential reference sites covering a set of pre-established river types. At each collecting site 6 hand net kick samples (500 mm mesh size, multi-habitat approach) were taken.. In a PCA ordination of the sites the factors altitude, runoff, mean annual precipitation, annual precipitation variability and mean annual temperature (climatic and morphological features) were correlated with the first axis (p<0.01), while distance to source and drainage area (longitudinal dimension) were correlated with the second axis (p<0.01). Geology, expressed as mineralization classes, is correlated with the three first axis (p<0.01). ANOSIM was used to merge river types when none significant differences were detected (p>0.05). Nemouridae and Leptophlebidae tend to be associated to river types with less runoff, while Leuctridae and Heptagenidae usually are more abundant at river types with higher runoff. Sites with drainage area higher than 100 km2 tend to have lower diversities in EPT taxa. From the initial 27 abiotic river types only 17 proved to be ecological relevant.

NB24A-06   16:45h

Evaluation of the Representative Reach Sampling Methodology for Biomonitoring Using Benthic Macroinvertebrates

* Orr, J C (jorr@srbc.net) , Susquehanna River Basin Commission, 1721 N. Front Street, Harrisburg, PA 17102 United States
* Orr, J C (jorr@srbc.net) , The Pennsylvania State University, School of Forest Resources, 113 Ferguson Building, University Park, PA 16802 United States
Ferreri, C P (cpf3@psu.edu) , The Pennsylvania State University, School of Forest Resources, 113 Ferguson Building, University Park, PA 16802 United States
Nieman, D (dnieman@normandeau.com) , Normandeau Associates, 400 Old Reading Pike, Building A, Suite 101, Stowe, PA 19464 United States
Martin, T H (tmartin@wcu.edu) , Western Carolina University, Department of Biology, 132 Natural Science Building , Cullowhee, NC 28723 United States

Bioassessments by resource management agencies to determine the condition of streams often rely on sampling benthic macroinvertebrate assemblages in "representative reaches". That information is used to represent assemblages in other reaches with similar characteristics. The goal of our study was to evaluate the effectiveness of using "representative reach" sampling to characterize assemblages at different scales (local-regional). During summer 1999, we sampled assemblages in a relatively undisturbed area in northwestern Pennsylvania using a nested design (n=81) to describe variation in assemblages at different scales. We found that assemblages changed gradually along the stream continuum rather than forming discrete groups based a priori on knowledge of environmental variables. Taxa richness in any sample averaged 12.5% of total taxa richness summed across all scales, requiring 4-30 1-m2 samples to be taken in any reach to capture the majority (>70%) of taxa. Due to the continuous nature of assemblages, and the inability to collect the majority of taxa in any sample, caution should be used in relying solely on representative sampling to characterize other assemblages. An iterative process of refinement using a posteriori knowledge to test validity of methods should be used in establishing biomonitoring programs to assure accuracy and precision in management decisions.