where f<strong>as</strong>t flow and rocky substrate inhibits the establishment <strong>of</strong> juveniles. Some species <strong>of</strong>mussels are also sensitive to pollution and may therefore be absent from impaired waters, orfrom streams that lack the fish hosts required by larval mussels to develop to the juvenile stage.Special considerations for OregonMultiple studies conducted in Oregon streams indicate that where<strong>as</strong> sharply delineated perennialobligateor temporary-obligate communities do not exist, certain families <strong>of</strong> macroinvertebratesare present in higher abundances in perennial vs. intermittent or ephemeral streams. This may bedue in part to the greater predictability <strong>of</strong> Oregon’s distinct wet and dry se<strong>as</strong>ons, which coulddrive development <strong>of</strong> a more characteristic faunal community in temporary streams (Dieterich,1992). Many studies have been conducted in the e<strong>as</strong>tern foothills <strong>of</strong> the Co<strong>as</strong>t Range aroundCorvallis Oregon, in intermittent forested or meadow streams that maintain flow from aboutNovember through May. During the dry se<strong>as</strong>on, the meadow channels tended to dry downrapidly and completely, while the forest streams usually dried out more gradually and retainedregions with small pools or seeps, even when dry along much <strong>of</strong> their length (Dieterich, 1992;Dieterich & Anderson, 1998).Many findings regarding the macroinvertebrate communities <strong>of</strong> summer-dry streams in Oregonare similar to those reported above in other geographic are<strong>as</strong>. A great deal <strong>of</strong> overlap is seen inthe fauna <strong>of</strong> perennial and temporary streams, but some groups are found more commonly inintermittent or ephemeral sites, and a smaller subset prefer or are restricted to perennial habitats(Dieterich, 1992; Banks, 2005). Some perennial headwater streams in western Oregon had agreater abundance <strong>of</strong> organisms than intermittent, although the species richness (total number <strong>of</strong>taxa) w<strong>as</strong> similar or even greater in intermittent. Ephemeral streams had only about 25-33% <strong>as</strong>many species <strong>as</strong> the other two stream types (Dieterich, 1992). In addition to flow duration, inOregon timber harvest can be a strong driver <strong>of</strong> macroinvertebrate community composition, <strong>as</strong>logging can alter the degree <strong>of</strong> sunlight reaching the stream and contribute to incre<strong>as</strong>edsedimentation. Differences in adult insect emergence rates, taxa richness, and density have beenobserved in perennial and intermittent streams flowing through logged vs. forested sites inwestern Oregon (Banks, 2005; Banks et al., 2007).Caddisflies <strong>of</strong>ten exhibit very high species diversity in Oregon’s summer-dry streams, eventhough they may comprise a small proportion <strong>of</strong> the overall invertebrate abundance (Dieterich,1992; Anderson & Dieterich, 1992; Anderson 1997); this h<strong>as</strong> also been found in other studies indifferent regions (Mackay & Wiggins, 1979; Smith & Wood, 2002). The Limnephilidae(Northern caddisflies) are the largest caddisfly family in North America; its members exploit awide variety <strong>of</strong> habitats, from permanent streams to temporary pools to moist terrestrial habitats(Wiggins, 1993). Several genera in this family are known to have adaptations that allow them tosurvive periods <strong>of</strong> summer dryness, including: synchronizing their growth period to the wetse<strong>as</strong>on; inhabiting moist seeps that persist in intermittent streams; surviving in moist terrestrialhabitats <strong>as</strong> adults that undergo ovarial diapause, living for 5-7 months and ovipositing whenstream flows resume in fall; or laying desiccation-resistant eggs that persist through the dryse<strong>as</strong>on and hatch when wetted (Clifford, 1966; Tew, 1971; Wiggins, 1973; Mackay & Wiggins,1979; Anderson & Dieterich, 1992). Because <strong>of</strong> these adaptations, limnephilid caddisflies are<strong>of</strong>ten an abundant and diverse component <strong>of</strong> intermittent streams. In studies on Trichopteraconducted by Anderson (1997) on intermittent oak savannah streams near Corvallis OR, the v<strong>as</strong>t<strong>Macroinvertebrates</strong> <strong>as</strong> indicators <strong>of</strong> stream flow duration,The Xerces Society for Invertebrate Conservation10
majority <strong>of</strong> all caddisflies collected were limnephilid species (Pseudostenophylax, Psychoglypha,and Limnephilus). Five species <strong>of</strong> caddisflies in three families (Limnephilidae, Rhyacophilidae,and Lepidistomatidae) accounted for over three-quarters <strong>of</strong> the total number <strong>of</strong> species collectedfrom intermittent streams (Anderson & Dieterich, 1992), with overall species <strong>as</strong>semblagesdiffering in a characteristic way between forested and meadow streams. Six species in threegenera <strong>of</strong> Limnephilidae, all <strong>of</strong> which appeared to have life history adaptations for temporarystreams, were collected from a small second order intermittent stream near Corvallis (Tew,1971).Plecoptera (stoneflies) and Ephemeroptera (mayflies) are more commonly found in f<strong>as</strong>t-flowingperennial waters. An analysis <strong>of</strong> macroinvertebrate data from 167 small, forested, perennialheadwater streams in three different ecoregions in western Oregon showed that 9 <strong>of</strong> the 16 mostcommon taxa reported were Ephemeroptera, Trichoptera, or Plecoptera (Herlihy et al., 2005),with an average 55% <strong>of</strong> all individuals collected at each site being EPT. A comparative study <strong>of</strong>small headwater streams in a portion <strong>of</strong> the Central Oregon Co<strong>as</strong>t Range found a heptageniid(flat headed) mayfly (Ironodes) and a hydropsychid (net-spinning) caddisfly (Parapsyche) onlyin the perennial streams (Banks, 2005). However, some EPT taxa in Oregon occur in temporaryhabitats and possess life history characteristics that allow them to survive periods <strong>of</strong> drought.Lemkuhl (1971) collected stonefly nymphs in the genus Nemoura (Nemouridae; forestflies) andCapnia (Capniidae; small winter stoneflies) from a roadside ditch in Corvallis that dried downregularly for 6 months <strong>of</strong> the year, and hypothesized that eggs or young nymphs present in thewet spring undergo diapause when the habitat is dry, completing development when flowresumes in the fall. Two species <strong>of</strong> stonefly from the Nemouridae and Chloroperlidae (greenstonefly) families (Ostrocerca and Sweltsa, respectively) and a philopotamid caddisfly(Wormaldia) were strongly <strong>as</strong>sociated with intermittent flow in small headwater streams in theCentral Oregon Co<strong>as</strong>t Range (Banks et al., 2007), although a different philopotamid species(Dolophilodes) w<strong>as</strong> found more commonly in perennial streams in the same study. Two mayflyspecies (Leptophlebiidae and Siphlonuridae family) and four stonefly species (Nemouridae,Chloroperlidae, and Perlodidae families) that accounted for >95% <strong>of</strong> mayfly and stoneflyemergence from two temporary forested streams in western Oregon were found to exhibit lifehistory strategies that incre<strong>as</strong>ed the likelihood <strong>of</strong> survival in temporary habitats, including<strong>as</strong>ynchronous development, f<strong>as</strong>ter development at longer day lengths, and egg diapause duringsummer-dry periods (Dieterich & Anderson, 1995). Tew (1971) reported two species <strong>of</strong>Baetidae (small minnow mayflies) <strong>as</strong> extremely abundant in an intermittent Oregon stream,although these are normally a component <strong>of</strong> perennial streams, <strong>as</strong> well <strong>as</strong> five species <strong>of</strong>nemourid and capniid stoneflies, although the precise mechanism <strong>of</strong> their survival during the dryse<strong>as</strong>on w<strong>as</strong> not elucidated.The variety <strong>of</strong> ecoregions in Oregon can complicate the designation <strong>of</strong> flow duration indicatortaxa and community composition. The invertebrate communities in streams in the WillametteValley and C<strong>as</strong>cade Mountain ecoregions in western Oregon show substantial differences, withtotal taxa richness, diversity, and %EPT composition much higher overall in C<strong>as</strong>cade streams (Liet al., 2001). Additionally, taxonomic composition <strong>of</strong> stream communities differs depending onstream elevation, gradient, order, and ecoregion. For example, freshwater mussels, Juga snails,and gomphid dragonfly nymphs rely on permanently flowing water, but are unlikely to be foundin high-gradient forested headwater streams in western Oregon, <strong>as</strong> substrate, amount <strong>of</strong> sunlight,<strong>Macroinvertebrates</strong> <strong>as</strong> indicators <strong>of</strong> stream flow duration,The Xerces Society for Invertebrate Conservation11
- Page 1 and 2: Using Aquatic Macroinvertebratesas
- Page 3 and 4: GoalsThe goal of this project is to
- Page 5 and 6: supported different macroinvertebra
- Page 7 and 8: that some studies have found simila
- Page 9: DispersalAdult invertebrates with s
- Page 13 and 14: North CarolinaAquatic macroinverteb
- Page 15 and 16: Amphipoda), water mites (subclass H
- Page 17 and 18: ScoringThe current Oregon Draft Str
- Page 20 and 21: To sample riffle or run/glide habit
- Page 22 and 23: However, the degree of dryness in b
- Page 24 and 25: Boulton A.J. & Lake P.S. 1992b. Ben
- Page 26 and 27: Li, J., Herlihy, A., Gerth, W., Kau
- Page 28 and 29: Williams, D. D., 1996. Environmenta
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- Page 32 and 33: • Dytiscidae (predaceous diving b