RAREFACTION ANALYSIS TO DETERMINE SUB-SAMPLING EFFORT FOR ESTIMATING CHIRONOMID DIVERSITY IN MINNESOTA FARM PONDS. Benjamin D. Campbell1, Roger J. Haro1, Melinda G. Knutson2, and William B. Richardson2. 1Rivers Studies Center, University of Wisconsin-La Crosse, La Crosse, WI 54601. 2U.S. Geological Survey, Upper Midwest Environmental Sciences Center, La Crosse, WI 54601. Farm ponds experience a variety of disturbances from agricultural practices. Sediments, pesticides, herbicides, and fertilizers are transported by run-off from surrounding-agricultural watersheds and deposited into receiving ponds. Non-biting midges (Chironomidae: Diptera) are one of the largest families of aquatic insects, with representatives found in almost every aquatic habitat. The wide geographical range and diverse composition of chironomid assemblages makes this group very useful for assessing ecological change in a variety of aquatic habitats. Chironomid larvae have been used as biological indicators for lakes and rivers, but little work has focused on ponds. The objective of this study is to determine how patterns in chironomid richness, relative abundance, and instantaneous growth vary across farm ponds under different land uses. Larvae were collected from four types of farm ponds, based on wetland type and adjacent land uses: (1) natural wetlands, and constructed agricultural ponds adjacent to (2) row crop agriculture, (3) grazed grassland, and (4) non-grazed grassland. Constructed ponds were classified based on the land-use practices within the first 100 m of their surrounding drainage basin. The epi- and in- faunal chironomid assemblages were sampled in each pond over a three-month period during the summer of 2001. A pilot study was conducted with samples collected from the summer of 2000 in order to determine sub-sampling effort. Rarefaction was used to determine the minimum number of larvae needed to adequately estimate chironomid diversity across pond type. The rarefaction plot showed a horizontal asymptote around 14 genera that corresponded with 70 larvae per sample whereas at 100 larvae per sample, only one additional genus was represented. Thus, it proved more efficient to measure, mount and, identify up to 70 larvae from each sample. Taxonomic richness, relative abundance, and instantaneous growth within the chironomid assemblages will be compared to develop an index for monitoring disturbances in farm ponds. Key words: chironomids, farm ponds, southeastern Minnesota, rarefaction, taxonomic richness