<?xml version="1.0" encoding="utf-8" standalone="no"?>
<!DOCTYPE article SYSTEM "http://www.hydrol-earth-syst-sci.net/inc/hess/copernicus.dtd">
<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-12-509-2008</doi>
	<article_url>http://www.hydrol-earth-syst-sci.net/12/509/2008/</article_url>
	<abstract_html>http://www.hydrol-earth-syst-sci.net/12/509/2008/hess-12-509-2008.html</abstract_html>
	<fulltext_pdf>http://www.hydrol-earth-syst-sci.net/12/509/2008/hess-12-509-2008.pdf</fulltext_pdf>
	<start_page>509</start_page>
	<end_page>522</end_page>
	<publication_date>2008-03-05</publication_date>
	<article_title content_type="html">Ecosystem effects of thermal manipulation of a whole lake, Lake Breisjøen, southern Norway (THERMOS project)</article_title>
	<authors>
		<author numeration="1" affiliations="1,3">
			<name>E. Lydersen</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>K. J. Aanes</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>S. Andersen</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>T. Andersen</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>P. Brettum</name>
		</author>
		<author numeration="6" affiliations="1">
			<name>T. Baekken</name>
		</author>
		<author numeration="7" affiliations="1">
			<name>L. Lien</name>
		</author>
		<author numeration="8" affiliations="1">
			<name>E. A. Lindstrøm</name>
		</author>
		<author numeration="9" affiliations="2">
			<name>J. E. Løvik</name>
		</author>
		<author numeration="10" affiliations="1">
			<name>M. Mjelde</name>
		</author>
		<author numeration="11" affiliations="1">
			<name>T. J. Oredalen</name>
		</author>
		<author numeration="12" affiliations="1">
			<name>A. L. Solheim</name>
		</author>
		<author numeration="13" affiliations="1">
			<name>R. Romstad</name>
		</author>
		<author numeration="14" affiliations="1">
			<name>R. F. Wright</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Norwegian Institute for Water Research, Gaustadallèen 21, 0349, Oslo, Norway</affiliation>
		<affiliation numeration="2" content_type="html">Norwegian Institute for Water Research, Sandvikaveien 41, 2312 Ottestad, Norway</affiliation>
		<affiliation numeration="3" content_type="html">now at: Telemark University College, 3800 Bø i Telemark, Norway</affiliation>
	</affiliations>
	<abstract content_type="html">We conducted a 3-year artificial deepening of the thermocline in the
dimictic Lake Breisjøen, southern Norway, by means of a large submerged
propeller. An adjacent lake served as untreated reference. The manipulation
increased thermocline depth from 6 to 20 m, caused a significant increase in
the heat content, and delayed ice-on by about 20 days.
&lt;br&gt;&lt;br&gt;
There were only minor changes in water chemistry. Concentrations of sulphate
declined, perhaps due to greater reduction of sulphate at the sediment-water
interface. Concentrations of particulate carbon and nitrogen decreased,
perhaps due to increased sedimentation velocity. Water transparency
increased. There was no significant change in concentration of phosphorus,
the growth-limiting nutrient.
&lt;br&gt;&lt;br&gt;
There were few significant changes in principal biological components.
Phytoplankton biomass and productivity did not change, although the
chlorophyll-&lt;i&gt;a&lt;/i&gt; concentration showed a small decrease. Phytoplankton species
richness increased, and the species composition shifted. Growth of
periphyton increased. There was no change in the macrophyte community. The
manipulation did not affect the zooplankton biodiversity, but caused a
significant shift in the relative abundance (measured as biomass) in the two
major copepod species. The manipulation did not affect the individual
density, but appeared to have changed the vertical distribution of
zoobenthos. Fish populations were not affected.
&lt;br&gt;&lt;br&gt;
The lake is oligotrophic and clearwater and the manipulation did not change
the supply of phosphorus, and thus there were only minor changes in lake
chemistry and biology. Effects might be larger in eutrophic and dystrophic
lakes in which internal processes are stronger.</abstract>
	<references>
		<reference numeration="1" content_type="text"> Carpenter, S. R., Frost, T. M., Heisley, D., and Kratz, T. K.: Random intervention analysis and the interpretation of whole-ecosystem experiments, Ecology, 70, 1142&amp;ndash;1152, 1989. </reference>
		<reference numeration="2" content_type="text"> Danis, P. A., von Grafenstein, U., Masson-Delmotte, V., Planton, S., Gerdeaux, D., and Moisselin, J.-M.: Vulnerability of two European lakes in response to future climatic changes, Geophys. Res. Lett., 31, L21507, doi:10.1029/2004GL020833, 2004. </reference>
		<reference numeration="3" content_type="text"> Diehl, S., Berger, S., and Wohrl, R.: Flexible nutrient stoichiometry mediates environmental influences, on phytoplankton and its resources, Ecology, 86, 2931&amp;ndash;2945, 2005. </reference>
		<reference numeration="4" content_type="text"> DN: Nasjonal rødliste for truede arter i Norge 1998, Norwegian Red List 1998, DN-rapport 3, Directorate for Nature Management, Trondheim, Norway, 1999. </reference>
		<reference numeration="5" content_type="text"> Faafeng, B., Berge, D., and Tjomsland, T.: Planteplanktonets primǽrproduksjon. III Beregning av primǽrproduksjon ved in-situ metoden, NIVA-rapport FR-458, Norwegian Institute for Water Research, Oslo, Norway, 1982. </reference>
		<reference numeration="6" content_type="text"> Lindstrøm, E.-A.: The Humic Lake Acidification Experiment (Humex): Impacts of acid treatment on periphyton growth and nutrient availability in Lake Skjervatjern, Norway, Environ. Int., 22, 629&amp;ndash;642, 1996. </reference>
		<reference numeration="7" content_type="text"> Murtaugh, P. A.: On rejection rates of paired intervention analysis, Ecology, 83, 1752&amp;ndash;1761, 2002. </reference>
		<reference numeration="8" content_type="text"> RegClim: Norges klima om 100 &amp;aring;r. Usikkerhet og risiko, Norwegian Meteorological Institute, Oslo, 2005. </reference>
		<reference numeration="9" content_type="text"> Saksgard, R. and Hesthagen, T.: A 14-year study of habitat use and diet of brown trout (Salmo trutta) and Arctic charr (Salvelinus alpinus) in Lake Atnsjoen, a subalpine Norwegian lake, Hydrobiologia, 521, 187&amp;ndash;199, 2004. </reference>
		<reference numeration="10" content_type="text"> Schindler, D. W.: Whole-lake experiments at the Experimental Lakes Area, in: Ecosystem Experiments, edited by: Mooney, H. A., Medina, E., Schindler, D. W., Schulze, E. D., and Walker, B. H., 121&amp;ndash;139, SCOPE 45, Wiley and Sons, Chichester, UK, 268 pp., 1991. </reference>
		<reference numeration="11" content_type="text"> Schindler, D. W., Bayley, S. E., Parker, B. R., Beaty, K. G., Cruikshank, D. R., Fee, E. J., Schindler, E. U., and Stainton, M. P.: The effects of climatic warming on the properties of boreal lakes and streams at the Experimental Lakes Area, northwestern Ontario, Limnol. Oceanogr., 41, 1004&amp;ndash;1017, 1996. </reference>
		<reference numeration="12" content_type="text"> Skjelkv&amp;aring;le, B. L., Mannio, J., Wilander, A., and Andersen, T.: Recovery from acidification of lakes in Finland, Norway and Sweden 1990&amp;ndash;1999, Hydrol. Earth Syst. Sci., 5, 327&amp;ndash;338, 2001. </reference>
		<reference numeration="13" content_type="text"> Walseng, B. and Karlsen, L. R.: Planktonic and littoral microcrustaceans as indices of recovery in limed lakes in SE Norway, Water Air Soil Poll., 130, 1313&amp;ndash;1318, 2001. </reference>
	</references>
</article>

