Abstract
Distributions of biogeochemical constituents in interstitial water and isolated standing water bodies (or pools) were investigated in gravel bars 1 km in length to assess the ability of these waters to serve as a sink or source for nutrients. The temperature and concentration of major ions in interstitial water differed very little from those of river water. DO concentrations in interstitial waters were 5.7 ± 2.2 mg O 2 /l and 3.5 ± 1.8 mg O 2 /l at the side and dried-up channels, respectively. Concentrations of ammonium and nitrite of both interstitial waters at the side (0.50 ± 0.17μM and 0.13 ± 0.09μM, NH 4 + and NO;) and dried-up channels (0.90 ± 2.14μM and 0.27 ± 0.37μM) were lower than those of river water (1.7 ± 0.8 μM and 0.73 ± 0.22 μM), whereas nitrate (85 ± 25 μM at the side channel and 79 ± 36 μM at the dried-up channel) did not differ on average from those of river water (70 ± 12 μM), though they were often very low (< 10 % of those of river water) at shallow depths of the vegetated areas in the dried-up channel. Soluble reactive phosphorus (SRP) concentrations in interstitial waters at the dried-up channel (0.84 ± 0.53 μM) were lower than those at the side channel (1.9 ± 0.5 μM) and those of river water (1.5 ± 0.5 μM), and decreased downstream. These results suggest that this aerobic hyporheic zone can serve as a sink for ammonium, nitrite and SRP and to a lesser extent of nitrate. Concentrations of these nutrients in pool water varied greatly but did not differ on average from those of river water. Dissolved inorganic nitrogen (DIN) and SRP concentrations were negatively related to the algal biomass. Pool waters also had lower DIN concentrations at the vegetated areas and higher SPR concentrations at the bar head. These results suggest that nutrient concentrations in pool waters are controlled in a complex manner by algal assimilation and surface-subsurface water exchange. Therefore some pools may serve as a sink and others as a source for nutrients.
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