2005
DOI: 10.1080/13241583.2005.11465260
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Assessing the impact of farm dams on streamflows, Part II: Regional characterisation

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Cited by 25 publications
(19 citation statements)
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“…First, the infiltration from the reservoir water dominates the groundwater discharge to the reservoir, as stated by the positive annual exchange term in the Kamech reservoir calculated using the water balance approach even when the errors in the estimated values ( Figures 6-8) were considered. Previous studies on reservoir hydrology in arid or semi-arid world regions have already shown that reservoir-subsurface exchanges dominated by infiltration can occur (Jayatilaka et al, 2003;Mugabe et al, 2003;Grünberger et al, 2004;Nasri et al, 2004;Li and Gowing, 2005;Lowe et al, 2005;Zammouri and Feki, 2005;Stiefel et al, 2009;Vervoort, 2010, 2011;Oblinger et al, 2010;Malveira et al, 2012). However, most of these studies were performed over short periods of a few weeks to a few months, corresponding to a temporal integrative estimation of the exchange flux.…”
Section: Discussionmentioning
confidence: 99%
“…First, the infiltration from the reservoir water dominates the groundwater discharge to the reservoir, as stated by the positive annual exchange term in the Kamech reservoir calculated using the water balance approach even when the errors in the estimated values ( Figures 6-8) were considered. Previous studies on reservoir hydrology in arid or semi-arid world regions have already shown that reservoir-subsurface exchanges dominated by infiltration can occur (Jayatilaka et al, 2003;Mugabe et al, 2003;Grünberger et al, 2004;Nasri et al, 2004;Li and Gowing, 2005;Lowe et al, 2005;Zammouri and Feki, 2005;Stiefel et al, 2009;Vervoort, 2010, 2011;Oblinger et al, 2010;Malveira et al, 2012). However, most of these studies were performed over short periods of a few weeks to a few months, corresponding to a temporal integrative estimation of the exchange flux.…”
Section: Discussionmentioning
confidence: 99%
“…Though this relationship was not shown in our data, we obtain a highly conservative estimate of state‐wide farm dam emissions using the Holgerson and Raymond () values for emission‐size decline and the following equation:E=false∑inε×ci×tiwhere E is the mean CO 2 ‐e emissions from small agricultural dams per day (<0.01 km 2 ), ε represents the combined CO 2 and CH 4 emissions reported in this study (treated as size class <0.001 km 2 , expressed as CO 2 ‐e m 2 /day), ci represents a correction value calculated from the variation in emissions between small natural freshwater ponds of size classes <0.001 km 2 and 0.001–0.01 km 2 as reported in Holgerson and Raymond (), and ti represents the total state‐wide surface area of farm dams within size classes <0.001 km 2 and 0.001–0.01 km 2 , obtained from geographical information systems (GIS) data (Department of Environment, Land, Water and Planning ). The farm dam GIS data used here are a combination of high‐resolution aerial photography and satellite imagery (pixels <2.5 m) (Lowe et al., ), and at the smallest scales was distributed in abundance as follows: 3,319 dams in 100–75 m 2 , 2,260 dams in 75–50 m 2 , 1,015 dams in 50–25 m 2 and 170 dams <25 m 2 . Non‐adjusted annual state‐wide reservoir flux (ton CO 2 ‐per year) was calculated by applying the temperate reservoir CO 2 and CH 4 literature values in Table , to the total Victorian reservoir area obtained through GIS (482.5 km 2 , Digital Globe and Google Earth, Supporting Information Table S1).…”
Section: Methodsmentioning
confidence: 99%
“…It also relies on the assumption that reservoir connectivity may play a role in the cumulative impacts. The reservoir network is represented by classes of reservoirs determined following reservoir water capacity (Güntner et al, 2004;Nathan et al, 2005;Lowe et al, 2005)) and also reservoir drainage area (Zhang et al, 2012). Each class is represented as a single equivalent reservoir.…”
Section: Statistical Representationmentioning
confidence: 99%