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HomeMy WebLinkAboutFish_to_Guilds_(Godreau) Ecological Flows Science Advisory Board August 28, 2012 Chris Goudreau, N.C. Wildlife Resources Commission Jennifer Phelan, RTI International Kimberly Meitzen, The Nature Conservancy Review RTI and TNC are investigating flow-ecology relationships by comparing flow metrics to fish abundance RTI Compare different locations, times Statewide TNC Compare same location over time Four basins (LTN, CFR, TAR, RKE) Fish Dataset NCDWQ – wadeable streams; not trout Why Use Guilds? Most species can be grouped by the habitats they use based on life history requirements and physiology “Smooths out” data compared to species data Allows comparison among streams, basins, provinces Used in habitat-based models (e.g., PHabSim) Guild Frameworks NCDWR (14) ENTRIX 2003 (9) Aadland 1993 (6) Vadas & Orth 2000 (7) Persinger 2010 (4) shallow fast higher velocity Shallow Fast Coarse Fast Riffle Riffle Riffle shallow fast moderate velocity shallow fast lower velocity Shallow Fast Slow Riffle Riffle Run deep fast, fine substrate deep fast, gravel/cobble substrate Deep Fast Raceway Fast Generalist Fast Generalist deep fast, coarse substrate Deep Fast Cover shallow slow, coarse substrate Shallow Rheophilic shallow slow, young of year Shallow Slow shallow slow, aquatic vegetation cover shallow slow, woody debris cover Shallow Slow Cover shallow slow, fine substrate, no cover Shallow Slow Fine Shallow Pool Pool Run Pool Run deep slow, no cover Deep Slow Medium Pool Open Pool deep slow, cover Deep Slow Cover Deep Pool Pool Cover Pool Cover deep slow, cover (version 2) Guild Frameworks Vadas Persinger Guild Frameworks Decided to use simple framework Reduce problems of assigning to similar adjacent types Easier for public to understand Restrict guilds to habitats indicative of flow (i.e., ignore substrate/cover parameters, which we can't manage) All the DWR PHabSim guilds (14) can be grouped within the flow-based guilds, except for backwater Proposed NC Guild Structure Persinger NC Study Comment Riffle Riffle Fast-generalist Riffle-run Name change only Pool-run Pool-run Pool-cover Pool Name change; with or without cover Margin Added; shallow-slow habitats Backwater Added; mostly coastal Proposed NC Guild Structure De p t h Velocity Pool Pool-Run Riffle-Run Margin Riffle Backwater Assigning Fish to Guilds Used “Fishes of” books Freshwater Fishes of Virginia (Jenkins and Burkhead 1994) The Fishes of Tennessee (Etnier and Starnes 1993) Freshwater Fishes of South Carolina (Rohde et al. 2009) Inland Fishes of Mississippi (Ross 2001) Fishes of Alabama (Boschung and Mayden 2004) These books describe habitat use based on direct observation and summarizing information from other sources Typically habitat was described for both spawning and adult/juvenile lifestages Assigning Fish to Guilds Goudreau made initial review of books and assigned guilds to spreadsheet of fish Rohde and Tracy reviewed/edited the spreadsheet and added assignments to those species not described in the books Some species use multiple habitat types Made notes on species that are exotic, introduced to particular basins, or estuarine Results Adult/Juvenile Spawning Riffle 15 21 Riffle-run 25 47 Pool-run 49 41 Pool 60 33 Margin 6 7 Backwater 16 22 Note: Species using multiple guilds were assigned to predominant guild Use of Guild Data – RTI Focus on Riffle-Run guild Flow sensitive High number of species Use if either lifestage (adult or spawning) is in guild, but must only use Riffle-Run Select five Riffle-Run species High count (>100 records) Wide geographic distribution (multiple basins) Creek Chub, Fantail Darter, Rosyside Dace, Central Stoneroller, Blacknose Dace Use of Guild Data – TNC Focus on all Guilds, example application: What is the percent occupancy by guild type at each survey site and each survey date? Is guild composition and percent distribution at a site consistent over time? If not, how is it changing, and why? Select sites with multiple surveys over time Measure changes in guild occupancy over time at a specific locations Possible controls on variation: Flow alteration, combined flow and habitat changes, seasonality and lifestage characteristics…