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Collaborative research project:

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Presentation on theme: "Collaborative research project:"— Presentation transcript:

1 Collaborative research project:
Explaining variation in functional composition of benthic communities across multi-scaled environmental gradients in the western United States Collaborative research project: N. LeRoy Poff & Brian P. Bledsoe R

2 197 Study Sites in 9 Ecoregions:
pre-2000 (R)EMAP (snapshot data) Colorado 59 sites 101 Genera Oregon 69 sites 119 Genera R Washington 69 sites 96 Genera

3 Approach for testing: 1) Identify “mechanistic” species traits that respond to environmental conditions. 2) Quantify meaningful environmental filters at different scales. 3) Use hierarchical modeling approach to evaluate predictions of HFM. (Eco)regional Pool of Species Multi-scale Habitat Template Watershed Controls Valley / Process Domain Controls Reach / Channel Unit Controls Microhabitat Biotic Composition Hierarchical Filtering Model (HFM) (Poff 1997) Species TRAITS

4 Macroinvertebrate traits?

5 20 traits; 57 states, or ‘modalities’
Traits for North American lotic insects 20 traits; 57 states, or ‘modalities’ Life History: Voltinism (3) Development (3) Emergence Synchronization (2) Adult life span (3) Adult exiting ability (2) Desiccation tolerance (2) Mobility: Adult female dispersal (2) Adult flying strength (2) Occurrence in drift (3) Maximum crawling rate (3) Swimming ability (3) Morphology: Attachment (2) Armoring (3) Rheophily (3) Shape (2) Respiration mode (3) Size at maturity (3) Ecology: Habit (5) Feeding mode (5) Thermal preference (3) Given available traits, which ones can we choose? Pick ones that have “mechanistic” link to environmental variables we have!

6 20 traits; 57 states, or ‘modalities’
Traits for North American lotic insects 20 traits; 57 states, or ‘modalities’ Life History: Voltinism (3) Development (3) Emergence Synchronization (2) Adult life span (3) Adult exiting ability (2) Desiccation tolerance (2) Mobility: Adult female dispersal (2) Adult flying strength (2) Occurrence in drift (3) Maximum crawling rate (3) Swimming ability (3) Morphology: Attachment (2) Armoring (3) Rheophily (3) Shape (2) Respiration mode (3) Size at maturity (3) Ecology: Habit (5) Feeding mode (5) Thermal preference (3) Disturbance Tolerance: which traits indicative??

7 Disturbance Tolerance
(Eco)regional Pool of Species Multi-scale Habitat Template Watershed Controls Valley / Process Domain Controls Reach / Channel Unit Controls Microhabitat Trait Composition Hierarchical Filtering Model (HFM) (Poff 1997) bi/multivoltine OR abundant drifter OR strong swimmer OR strong flyer Disturbance Tolerance bi/multivoltine OR high drift OR strong swimmer OR strong flyer mean = 0.23 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 10 20 30 40 50 60 70 80 90 100 Weedy Species Number of Sites Proportion of Assemblage What environmental factors and at what scales represent “disturbance”? -> WS flow regime -> Local bed stability

8 WATERSHED SCALE (15) Geomorphic (2) Geology (3) Climate (3)
Hydrology (4) Land Use (3) [GIS] (Eco)regional Pool of Species Multi-scale Habitat Template Watershed Controls Valley / Process Domain Controls Reach / Channel Unit Controls Microhabitat Trait Composition Hierarchical Filtering Model (HFM) (Poff 1997) VALLEY (link) SCALE (7) Geomorphic (4) Land Use (3) [GIS, field] REACH SCALE (11) Geomorphic (4) Riparian (3) Substrate (4) [EMAP, Field]

9 Disturbance Tolerance (Model R2 = 0.68)
Reach Scale Watershed Scale Valley Scale Filters 0.23 = 197 n 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 10 20 30 40 50 60 70 80 90 100 Weedy Species Number of Sites Proportion of Assemblage X = 0.23 0.22 = 152 n Yes No 0.27 = 45 W_G - Specific Stream Power (D84) < 2.44 high power low power Yes No 0.20 = 110 n 0.26 =42 W_L - % Agri < 13.4% Yes 0.34 = 14 n 0.24 = 31 No R_R - Riparian Canopy < 52.3% low agri low canopy 0.14 = 15 n 0.21 = 95 Yes No R_G - Width/Depth < 5.1 15 sites with fewest weedy 0.43 = 5 n 0.30 = 9 Yes No V_G - Hlsp Connectivity < 8.4 5 sites with most weedy deep channels entrenched

10 Disturbance Tolerance (Model R2 = 0.68)
Reach Scale Watershed Scale Valley Scale Filters 0.23 = 197 n 0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0 10 20 30 40 50 60 70 80 90 100 Weedy Species Number of Sites Proportion of Assemblage X = 0.23 0.22 = 152 n Yes No 0.27 = 45 W_G - Specific Stream Power (D84) < 2.44 high power low power Yes No 0.20 = 110 n 0.26 =42 W_L - % Agri < 13.4% Yes 0.34 = 14 n 0.24 = 31 No R_R - Riparian Canopy < 52.3% low agri high agri low canopy 0.14 = 15 n 0.21 = 95 Yes No R_G - Width/Depth < 5.1 15 sites with fewest weedy 0.24 = 36 n 0.37 = 6 Yes No V_L - % Agri < 1.0% 0.43 = 5 n 0.30 = 9 Yes No V_G - Hlsp Connectivity < 8.4 5 sites with most weedy deep channels high agri entrenched Context matters!

11 Filters High Weediness Low Weediness High Weediness Reach Scale
Watershed Scale Valley Scale Filters Yes No [1W, 1V, 3R] 0.22 = 152 n 0.20 = 110 0.26 =42 0.14 = 15 0.21 = 95 0.24 = 36 0.37 = 6 [5W] [1W, 2V, 2R] 0.23 = 197 [4W, 1V] 0.27 = 45 0.34 = 14 0.43 = 5 0.30 = 9 [4W, 1R] = 31 R_R - Riparian Canopy < 52.3% V_L - % Agri < 1.0% W_L - % Agri < 13.4% R_G - Width/Depth < 5.1 V_G - Hlsp Connectivity < 8.4 W_G - Specific Stream Power (D84) < 2.44 Relatively deep channel Low Disturbance Low Weediness Low % Agriculture Low Disturbance High Weediness High % Agriculture Low Riparian Canopy High Disturbance Low Floodplain connectivity High Weediness

12 Models of Community Structure in Streams
Intermediate Disturbance Hypothesis disturbance diversity Habitat Template Model Patch Dynamics Model

13 Patch Dynamics Model [Townsend, CR. 1989. J.No.Amer.Benthol.Soc.]
Patchwork of habitat with different disturbance histories Stream organisms are very mobile and colonize quickly  adjacent patches may have very different fauna  over many patches, there’s a kind of mosaic equilibrium with a “predictable” assemblage (at the scale of say, a riffle) Community structure reflects an interplay of biotic and abiotic factors, depending on the degree of spatial and temporal heterogeneity of the system. Temporal heterogeneity (disturbance) sets population sizes and regulates competition Spatial heterogeneity (habitat structure) provides refugia, and sets habitat diversity for niche segregation higher diversity possible when disturbance intermediate habitat heterogeneous

14 Habitat comprised of two axes - spatial and temporal heterogeneity
Niche control Competition dominates (community response to removal of Glossosoma by parasite Cougourdella ? (Kohler & Wiley 1997) Dominance control Competitive replacement sequence following disturbance “reset” (Hydropsyche and Simulium - Hemphill & Cooper 1983) Founder control Priority effect (Cladophora and Leucotrichia - Hart 1992) Mobility control Weedy species (habitat template studies, e.g., Scarsbrook & Townsend 1993; Richards et al. 1997) Phased succession All patches undergo similar successional sequence due to synchronized disturbance in homogeneous environment


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