2012
DOI: 10.1038/nclimate1724
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Water-quality impacts from climate-induced forest die-off

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Cited by 80 publications
(85 citation statements)
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“…16 For example, drinking water quality was affected by changes in dissolved organic carbon (DOC) and DBP formation attributed to bark-beetle-caused tree mortality in the forest watershed. 17 Compared to such chronic change by forest die-off, wildfire causes a more intensive, acute, and long-term forest mortality that is recognized as one of the strongest natural disturbances. 18 The combustion losses of organic-rich soil horizons and vegetation biomass may reduce the amount of DOC exported from detritus materials.…”
Section: ■ Introductionmentioning
confidence: 99%
“…16 For example, drinking water quality was affected by changes in dissolved organic carbon (DOC) and DBP formation attributed to bark-beetle-caused tree mortality in the forest watershed. 17 Compared to such chronic change by forest die-off, wildfire causes a more intensive, acute, and long-term forest mortality that is recognized as one of the strongest natural disturbances. 18 The combustion losses of organic-rich soil horizons and vegetation biomass may reduce the amount of DOC exported from detritus materials.…”
Section: ■ Introductionmentioning
confidence: 99%
“…10,11 Safe drinking water is an important demand for public health, 12,13 but drinking water quality (e.g., DOM and disinfection byproducts (DBPs)) is very sensitive to landscape/ecosystem changes as affected by changing climate and natural/anthropogenic disturbances. 14, 15 Recent case studies revealed that forest fires alter DOM chemistry and thus DBP formation in drinking water, such as the possibly carcinogenic trihalomethanes (THMs), haloacetic acids (HAAs), and haloacetonitriles (HANs). 16−18 With greater wildfire severity, wildfires can potentially decrease the reactivity of terrestrial DOM in forming carbonaceous DBPs such as USEPA-regulated THMs and HAAs but increase the reactivity for forming more carcinogenic nitrogenous DBPs such as HANs and Nnitrosodimethylamine and brominated DBPs such as dichlorobromomethane.…”
Section: ■ Introductionmentioning
confidence: 99%
“…Forests in the Western U.S. are experiencing larger wildfire disturbances attributed to warmer temperatures and earlier spring snowmelts [5], with a 60% increase in large fires from the mid-1980s in the Northern Rocky Mountains and significantly greater extents of severe fires in the Southern Rocky Mountains [6]. Furthermore, unprecedented mountain pine beetle (MPB; Dendroctonous ponderosae) outbreaks in Western North America killed >10 Mha of trees over the last 2-3 decades [7,8], with major impacts on water resources [9,10], nutrient cycling [11], and forest carbon storage [12]. These disturbance-caused changes require consideration when assessing global change risks to the stability of forest carbon [13,14].…”
Section: Introductionmentioning
confidence: 99%
“…The extent of post-fire changes in soil geochemistry reflects ecosystem type, burn severity, and fire frequency [27][28][29], all of which are influenced by topography [30]. Forest diebacks driven by MPB outbreaks alter C and N cycling pathways to varying degrees, depending on percent tree mortality [8] and phase of infestation [9,10,31,32], among other factors. The changes in soil biogeochemistry following MPB infestation include greater soil moisture availability likely due to reduced evapotranspiration associated with high tree mortality [33]; a reduction in phosphate (PO 4 3 ) concentrations [34]; lower C/N ratios in the leaf litter compared to little to no change in soil C/N ratios [34]; greater aromaticity of dissolved organic carbon (DOC) [8] and elevated concentrations of NH 4 + in the soil environment given the cessation of nitrogen uptake and more litter available following tree mortality [11,35,36].…”
Section: Introductionmentioning
confidence: 99%
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