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<article language="en">
	<journal>
		<journal_title>Hydrology and Earth System Sciences</journal_title>
		<journal_url>www.hydrol-earth-syst-sci.net</journal_url>
		<issn>1027-5606</issn>
		<eissn>1607-7938</eissn>
		<volume_number>12</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2008</publication_year>
	</journal>
	<doi>10.5194/hess-12-383-2008</doi>
	<article_url>http://www.hydrol-earth-syst-sci.net/12/383/2008/</article_url>
	<abstract_html>http://www.hydrol-earth-syst-sci.net/12/383/2008/hess-12-383-2008.html</abstract_html>
	<fulltext_pdf>http://www.hydrol-earth-syst-sci.net/12/383/2008/hess-12-383-2008.pdf</fulltext_pdf>
	<start_page>383</start_page>
	<end_page>392</end_page>
	<publication_date>2008-03-05</publication_date>
	<article_title content_type="html">The impacts of future climate change and sulphur emission reductions on acidification recovery at Plastic Lake, Ontario</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>J. Aherne</name>
			<email>julian.aherne@ucd.ie</email>
		</author>
		<author numeration="2" affiliations="2">
			<name>M. N. Futter</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>P. J. Dillon</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Environmental and Resource Studies, Trent University, Peterborough, Canada</affiliation>
		<affiliation numeration="2" content_type="html">Watershed Ecosystems Graduate Program, Trent University, Peterborough, Canada</affiliation>
	</affiliations>
	<abstract content_type="html">Climate-induced drought events have a significant influence on sulphate
export from forested catchments in central Ontario, subsequently delaying
the recovery of surface waters from acidification. In the current study, a
model chain that employed a statistical downscaling model, a hydrological
model and two hydrochemical models was used to forecast the chemical
recovery of Plastic Lake sub-catchment 1 (PC1) from acidification under
proposed deposition reductions and the A2 emission scenario of the
Intergovernmental Panel on Climate Change. Any predicted recovery in stream
acid neutralising capacity and pH owing to deposition reductions were
clearly offset by large acid effluxes from climate-induced drought events.
By 2100, ANC is predicted to show large variations ranging between 10 and
&amp;minus;30 μmol&lt;sub&gt;&lt;i&gt;c&lt;/i&gt;&lt;/sub&gt; L&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. Similarly, predicted pH in 2100 is lower (&amp;gt;0.05
of a pH unit) than the value simulated for 2000 (pH 4.35). Despite
emission reductions, the future scenario paints a bleak picture of
reacidification at PC1 to levels commensurate with those of the late 1970s.
The principal process behind this reacidification is the oxidation of
previously stored (reduced) sulphur compounds in wetlands during periods of
low-flow (or drought), with subsequent efflux of sulphate upon re-wetting.
Simulated catchment runoff under the A2 emissions scenario predictes
increased intensity and frequency of low-flow events from approximately 2030
onwards. The Integrated Catchments model for Carbon indicated that stream
DOC concentrations at PC1 will also increase under the future climate
scenario, with temperature being the principal driver. Despite the predicted
(significant) increase in DOC, pH is not predicted to further decline
(beyond the climate-induced oxidation scenario), instead pH shows greater
variability throughout the simulation. As echoed by many recent studies,
hydrochemical models and model frameworks need to incorporate the drivers
and mechanisms (at appropriate time-scales) that affect the key
biogeochemical processes to reliably predict the impacts of climate change.</abstract>
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</article>

