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Table 1.

Water quality factors across river types and flow conditions.

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Fig 1.

Community compositions of macroinvertebrates (a) and fish (b) across river types and flow conditions.

NH, natural high-flow (Yongding River); NL, natural low-flow (Gaojinggou River); AH, artificial high-flow (Yongding River Diversion Channel); AL, artificial low-flow (Renmin Channel), The same below.

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Fig 2.

NMDS analyses of macroinvertebrate (a) and fish (b) community composition across river types and flow conditions (based on Bray-Curtis dissimilarity coefficient).

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Fig 3.

Redundancy analyses (RDAs) of benthic invertebrate (a) and fish (b) community compositions in relation to water quality factors across river types and flow conditions.

T, Temperature; DO, Dissolved Oxygen; COD, Chemical Oxygen Demand; TP, Total Phosphorus; F, Fluoride; S, Sulfide.

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Fig 3 Expand

Table 2.

Contribution of water quality factors to the variation in macroinvertebrate and fish community composition in the RDAs.

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Table 2 Expand

Table 3.

Summary of ANOVAs examining the effects of river type, river flow and their interaction on species richness, Shannon-Wiener index, biomass of macroinvertebrate and fish communities.

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Table 3 Expand

Fig 4.

Species richness, Shannon-Wiener index and biomass of macroinvertebrates (a, b, c) and fish (d, e, f) across river types and flow conditions.

Data are presented as means+SE (n = 3). Within each panel, shared letters indicate means that are not significantly different from each other (Tukey HSD tests, P < 0.05).

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Fig 4 Expand

Fig 5.

Correlations of species richness, Shannon-Wiener index, and biomass of macroinvertebrates and fish versus water quality factors across river types and flow conditions.

Water quality factors: T (Temperature), pH, DO (Dissolved Oxygen), COD (Chemical Oxygen Demand), NH4+, TP (Total Phosphorus), F (Fluoride), S (Sulfide). Pearson’s r values are shown; *, 0.01 < P < 0.05; **, P < 0.01.

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Fig 5 Expand