Evidence details
10 Mar 2020
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Study
- Citation
- Zoe S. Dewson, Alexander B. W. James, Russell G. Death (2007). Invertebrate community responses to experimentally reduced discharge in small streams of different water quality. J. N. Am. Benthol. Soc..
- Study description
- Water abstraction can alter invertebrate community composition by changing the availability or
suitability of habitat for invertebrates. The consequences of water abstraction for the physical habitat and
invertebrate communities of small permanent streams are not clear. Therefore, we used whole-channel flow
manipulations to imitate real water abstractions. We used weirs and diversions to reduce discharge by
.85% in 3 small New Zealand streams (mean discharges: 11–84 L/s), ranging in water quality from pristine
to moderately polluted. We sampled benthic invertebrates and periphyton at control and impact sites on
each stream before and during 2 mo of artificially reduced discharge during summer 2005, and then we left
the diversions in operation throughout the following year and sampled invertebrates again after 9 and 12
mo of flow reduction. During the experiment, wetted width decreased by 24 to 34% at impact sites. Water
velocity and depth also decreased at impact sites, but only small changes to conductivity, pH, dissolved O2,
and temperature were observed. At the pristine site, density of invertebrates and percentage of
Ephemeroptera, Plecoptera, Trichoptera (EPT) individuals decreased in response to reduced flows. Only
taxonomic richness decreased at the mildly polluted stream, and reduced discharge had no effect on the
invertebrate community at the stream with the poorest water quality. Overall community structure also
changed in response to flow reduction at all but the poorest-water-quality stream. Alterations to community
composition involved changes in the density of common taxa and collection of fewer rare taxa per sample.
Our results indicate that the impacts of water abstraction on invertebrate communities differ between streams that vary in water quality, probably because of the relative sensitivities of invertebrate communities to changes in the physical habitat of these streams. Here I am recording the results for the pristine stream.
Response
- Cause term/trajectory
-
Hydrology - surface flow (volume)
(Decrease)
- Cause description
- They used weirs and diversions to remove water from the natural channels of 3 small streams for 1 mo . After this time, they removed the weirs and restored natural flow
patterns to the streams until the following summer.
- Effect term/trajectory
-
EPT taxa - richness
(Decrease)
- Effect description
- percentage of Ephemeroptera, Plecoptera, Trichoptera (EPT) individuals
- Response measure type
- F statistic/ratio
- Statistical significance
- yes, values significant at p . 0.05
- Documentation
- p 760
- Response measure description
- BACIP design. Analyzed data from each stream separately because invertebrate communities differed substantially between the streams. 3-factor (control–impact [CI], before–after
[BA], and time) analysis of variance. here I am recording the results for the 'pristine' stream only.
Design
- Source data
- Field
- Study type
- Manipulation
- Study design
- BACIP
- Number of independent control or reference sampling units
- 2
- Number of indendent impact or treatment sampling units
- 2
- Sample size used in analysis
- F 1,3
- Design description
- Here I am recording the results for the pristine stream only.
Context
- Climate
- Temperate
- Country
- New Zealand
- Habitat
- Stream/river
- Spatial extent
- Reach/section
- Temporal extent
- Months
- Context description
- Study done on 3 streams in the Wairarapa region of the lower North Island, New Zealand