Quantifying Disturbance in Streams: Alternative Measures of Disturbance in Relation to Macroinvertebrate Species Traits and Species Richness

Appropriate tests of disturbance theory require that disturbance is defined and measured in an organism-related sense. We quantified 7 measures of disturbance, 3 dealing with the pattern of disturbance of the stream bed (assessed using painted tracer particles), 3 dealing with aspects of discharge variation and 1 being a subjective composite measure of stream channel stability (Pfankuch's index). Hypotheses relating to invertebrate taxon richness (maximal at intermediate levels of disturbance) and the representation of particular insect species traits (assemblages in more disturbed sites contain higher percentages of individuals possessing high adult mobility and streamlined-flattened larval morphology) were both supported when disturbance was measured in terms of bed movement but generally not when measured in terms of discharge variation. When disturbance was estimated by Pfankuch's index, species trait predictions were supported but the taxon richness prediction was not. A co-inertia analysis, searching for a co-structure between our environmental and faunistic data sets, allowed us to distinguish taxa that apparently are resistant to bed movement from taxa that appear to be resistant to flow variations; this more detailed analysis indicates that the most appropriate measure of disturbance may vary even among quite closely related taxa. The construction of a comprehensive theory of disturbance in streams requires that disturbance is quantified in a way that allows both multi-site and multi-study comparisons. The painted-particle approach, described here, has the potential to permit such standarized comparative studies.

[1]  C. Frissell,et al.  A hierarchical framework for stream habitat classification: Viewing streams in a watershed context , 1986 .

[2]  A. Knight,et al.  The Effects of Washout in a Sierra Foothill Stream , 1977 .

[3]  R. L. Hoopes Flooding, as the result of Hurricane Agnes, and its effect on a macrobenthic community in an infertile headwater stream in central Pennsylvania , 1974 .

[4]  Maurice J. Duncan,et al.  Flow variability in New Zealand rivers and its relationship to in‐stream habitat and biota , 1990 .

[5]  N. Poff,et al.  Physical habitat template of lotic systems: Recovery in the context of historical pattern of spatiotemporal heterogeneity , 1990 .

[6]  Mike R. Scarsbrook,et al.  Species traits in relation to temporal and spatial heterogeneity in streams: a test of habitat templet theory , 1997 .

[7]  R. Virtanen,et al.  The stream as a habitat templet for bryophytes: species' distributions along gradients in disturbance and substratum heterogeneity , 1995 .

[8]  Vincent H. Resh,et al.  Year-to-Year Variation in the Aquatic Macroinvertebrate Fauna of a Northern California Stream , 1989, Journal of the North American Benthological Society.

[9]  S. Dolédec,et al.  The intermediate disturbance hypothesis, refugia, and biodiversity in streams , 1997 .

[10]  P. Sagar The effects of floods on the invertebrate fauna of a large, unstable braided river , 1986 .

[11]  Christopher W. Hickey,et al.  Magnitude of effects of substrate particle size, recent flooding, and catchment development on benthic invertebrates in 88 New Zealand rivers , 1990 .

[12]  B. Biggs,et al.  The contribution of flood disturbance, catchment geology and land use to the habitat template of periphyton in stream ecosystems , 1995 .

[13]  Colin R. Townsend,et al.  The Patch Dynamics Concept of Stream Community Ecology , 1989, Journal of the North American Benthological Society.

[14]  M. Huston A General Hypothesis of Species Diversity , 1979, The American Naturalist.

[15]  P. Giller,et al.  Catastrophic flooding and macroinvertebrate community structure , 1991 .

[16]  J. Allan,et al.  Functional Organization of Stream Fish Assemblages in Relation to Hydrological Variability , 1995 .

[17]  N. Poff Why Disturbances Can Be Predictable: A Perspective on the Definition of Disturbance in Streams , 1992, Journal of the North American Benthological Society.

[18]  Robert K. Colwell,et al.  PREDICTABILITY, CONSTANCY, AND CONTINGENCY OF PERIODIC PHENOMENA' , 1974 .

[19]  T. R. E. Southwood,et al.  Tactics, strategies and templets* , 1988 .

[20]  Steward T. A. Pickett,et al.  The ecological concept of disturbance and its expression at various hierarchical levels , 1989 .

[21]  C. Townsend Concepts in river ecology : pattern and process in the catchment hierarchy , 1996 .

[22]  T. R. E. Southwood,et al.  HABITAT, THE TEMPLET FOR ECOLOGICAL STRATEGIES? , 1977 .

[23]  B. Statzner,et al.  The synthesis of long-term ecological research in the context of concurrently developed ecological theory: design of a research strategy for the Upper Rhône River and its floodplain , 1994 .

[24]  E. W. Lane Design of Stable Channels , 1955 .

[25]  N. LeRoy Poff,et al.  Implications of Streamflow Variability and Predictability for Lotic Community Structure: A Regional Analysis of Streamflow Patterns , 1989 .

[26]  R. Death,et al.  Environmental Stability and Community Persistence: A Multivariate Perspective , 1994, Journal of the North American Benthological Society.

[27]  Robert J. Naiman,et al.  Disturbance regimes, resilience, and recovery of animal communities and habitats in lotic ecosystems , 1990 .

[28]  T. Galloway,et al.  Effects of Discharge and Substrate Stability on Density and Species Composition of Stream Insects , 1992 .

[29]  C. Townsend,et al.  Species traits in relation to a habitat templet for river systems , 1994 .

[30]  J. Ward,et al.  The influence of environmental predictability/disturbance characteristics on the structure of a guild of mountain stream insects , 1989 .

[31]  M. Begon,et al.  Ecology: Individuals, Populations and Communities , 1986 .

[32]  J. Devillers,et al.  Comparison of In Vivo and In Vitro Toxicity Tests from Co-inertia Analysis , 1995 .

[33]  C. Townsend,et al.  Stream community structure in relation to spatial and temporal variation: a habitat templet study of two contrasting New Zealand streams , 1993 .

[34]  J. Connell Diversity in tropical rain forests and coral reefs. , 1978, Science.

[35]  J. Ward,et al.  The Four-Dimensional Nature of Lotic Ecosystems , 1989, Journal of the North American Benthological Society.

[36]  Arthur V. Brown,et al.  The Role of Disturbance in Stream Ecology , 1988, Journal of the North American Benthological Society.

[37]  S. Dolédec,et al.  Co‐inertia analysis: an alternative method for studying species–environment relationships , 1994 .

[38]  Jean Thioulouse,et al.  Co-inertia analysis of amino-acid physico-chemical properties and protein composition with the ADE package , 1995, Comput. Appl. Biosci..

[39]  W. Sousa The Role of Disturbance in Natural Communities , 1984 .

[40]  B. Statzner,et al.  Theoretical habitat templets, species traits, and species richness: a synthesis of long‐term ecological research on the Upper Rhône River in the context of concurrently developed ecological theory , 1994 .