2008
DOI: 10.1016/j.foreco.2008.04.019
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Assessing the relations between aquatic habitat indicators and forest harvesting at watershed scale in the interior of British Columbia

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Cited by 11 publications
(8 citation statements)
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“…Our results show that Q 5% increases with greater CECA, implying that forest harvesting increases high flows in this area. Consequently, if harvest rates are not limited, changes to the peak flow regime could result in undesirable alterations to riparian ecosystems and aquatic habitat [29,71]. Much of the BC interior is managed to a maximum logged CECA threshold of 20% to 30% [24] of the watershed area, which is intended to serve as a coarse filter to identify watersheds that may have impacts from harvesting [27].…”
Section: Management Implicationsmentioning
confidence: 99%
“…Our results show that Q 5% increases with greater CECA, implying that forest harvesting increases high flows in this area. Consequently, if harvest rates are not limited, changes to the peak flow regime could result in undesirable alterations to riparian ecosystems and aquatic habitat [29,71]. Much of the BC interior is managed to a maximum logged CECA threshold of 20% to 30% [24] of the watershed area, which is intended to serve as a coarse filter to identify watersheds that may have impacts from harvesting [27].…”
Section: Management Implicationsmentioning
confidence: 99%
“…Equivalent clear‐cut area (ECA) was used as an indicator to express the forest disturbance level as not only can it represent all types of disturbances and the range of their intensities but it can also include their cumulative forest disturbance histories and subsequent recovery processes that follow disturbances over space and time (Hudson, ; Talbot and Plamondon, ; Winkler et al ., ; Lewis and Huggard, ; Wei and Zhang, ). Although ECA has been successfully used in British Columbia, Canada, to test watershed‐scale forest disturbances and their effects on various watershed processes (Whitaker et al ., ; Chen and Wei, ; Jost et al ., ; Lin and Wei, ), to our knowledge, its utility in representing all types of forest disturbances in a single large watershed for hydrological studies has not been applied. The objectives of this study were (1) to derive a watershed‐scale cumulative forest disturbance indicator accounting for all types of forest disturbances and subsequent regenerations over time; (2) to assess the impact of cumulative forest disturbances on all the components of flow regimes (magnitude, frequency, timing, duration and variability) of high and low flows (see the definitions in the Methods section); and (3) to discuss the potential ecological implications of those flow alterations caused by cumulative forest disturbances.…”
Section: Introductionmentioning
confidence: 99%
“…Research has established the relationships between vegetation growth (ages or tree heights) following disturbance and hydrological recovery rates, so that ECA can be derived spatially and temporally in a watershed (Hudson, 2000;Talbot and Plamondon, 2002;Winkler et al, 2005;Lewis and Huggard, 2010). The ECA has already been successfully used in British Columbia, Canada, to test watershed-scale forest disturbances and their effects on various watershed processes including aquatic habitat (Chen and Wei, 2008), hydrology (Lin and Wei, 2008) and aquatic biology (Whitaker et al, 2002;Jost et al, 2008). In spite of growing recognition of ECA, its utility in representing various types of forest disturbance (including mountain pine beetle infestation, harvesting, and fire) in a single large watershed for hydrological studies has not been applied as far as we know.…”
mentioning
confidence: 99%