9780521861724htl 1..2

(Jacob Rumans) #1
after it has passed. In other words, both multiple stressors and taxon-specific
solutions can conspire to reduce the likelihood of detecting clear patterns.
We believe that our understanding of the structure and functioning of stream
ecosystems has increased because of size-focused studies, but can this understand-
ing be used to develop biomonitoring tools? Robson, Barmuta and Fairweather
(2005 ) note that body size has appeal as a taxon-free and easy-to-measure metric. In
addition, it bears relationships, either directly or indirectly, to a variety of human-
induced stressors. Size alone will certainly not furnish sufficient predictive power,
however, when prioritizing rivers for rehabilitation or measuring river improve-
ment. On the other hand, body size, in combination with other traits related to
trophic role, survival and reproduction, may be used to create river health metrics
of more general utility than those that depend simply on taxonomic composition
or species diversity (e.g. Charvet, Kosmala & Statzner,1998 ;Gayraudet al., 2003 ;
Statzneret al., 2004 ;Dole ́decet al., 2006 ). The potential advantages of trait-based
metrics are two-fold. First, a multiple-trait index is likely to be applicable across
large geographic areas despite taxonomic differences. Second, the representation
of particular traits can be expected to throw light on the mechanisms underlying
stressor impacts, providing focus for management efforts.

Acknowledgements
Thanks to Sylvain Dole ́dec for supplying Fig.5.1. RT was funded by the
Biodiversity Research Centre at the University of British Columbia.

References
Bourassa, N. & Morin, A. (1995). Relationships
between size structure of invertebrate
assemblages and trophy and substrate
composition in streams.Journal of the
North American Benthological Society, 14 ,
393–403.
Buchwalter, D. B. & Luoma, S. N. (2005).
Differences in dissolve cadmium and zinc
uptake among stream insects: mechanistic
explanations.Environmental Science and
Technology, 39 , 498–504.
Buchwalter, D.B., Jenkins, J.J. & Curtis, L.R.
(2002). Respiratory strategy is a major
determinant of [^3 H] water and [^14 C]
chlorpyfiros uptake in aquatic insects.
Canadian Journal of Fisheries and Aquatic
Science, 59 , 1315–1322.
Camargo, J.A., Alonso, A. & Salamanca, A. (2005).
Nitrate toxicity to aquatic animals: a review

with new data for freshwater invertebrates.
Chemosphere, 58 , 1255–1267.
Charvet, S., Kosmala, A. & Statzner, B. (1998).
Biomonitoring through biological traits of
benthic macroinvertebrates: perspectives
for a general tool in stream management.
Archives fu ̈r Hydrobiologie, 142 , 415–432.
Cummins, K. W. (1974). Structure and function
of stream ecosystems.BioScience, 24 ,
631–641.
Dole ́dec, S., Phillips, N., Scarsbrook, M., Riley, R.H.
& Townsend, C.R. (2006). A comparison
of structural and functional approaches to
determining landuse effects on grassland
stream communities.Journal of the North
American Benthological Society, 25 , 44–60.
Downes B.J., Lake P.S., Schreiber E.S. G. &
Glaister A. (1998). Habitat structure and
regulation of local species diversity in a

94 C. R. TOWNSEND AND R. M. THOMPSON

Free download pdf