Stoichiometric Constraints on Food-Web Dynamics: A Whole-Lake Experiment on the Canadian Shield
A whole-lake manipulation of food-web structure (introduction of a top predator, northern pike, to a minnow-dominated lake) was performed in a Canadian Shield lake (L110) to examine the stoichiometric consequences of changes in planktonic community structure generated by altered food-web structure....
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Veröffentlicht in: | Ecosystems (New York) 1998-01, Vol.1 (1), p.120-136 |
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description | A whole-lake manipulation of food-web structure (introduction of a top predator, northern pike, to a minnow-dominated lake) was performed in a Canadian Shield lake (L110) to examine the stoichiometric consequences of changes in planktonic community structure generated by altered food-web structure. Minnow abundance, zooplankton biomass and community composition, microconsumer abundance, and concentration and carbon-phosphorus (C:P) ratio of suspended particulate matter were monitored in L110 and unmanipulated L240 before (1992) and after (1993-95) pike introduction. Algal biomass in L110 determined from microscopic examination for postmanipulation and premanipulation periods was also compared with dynamics in a suite of unmanipulated reference lakes from longterm monitoring records. Pike were added in spring in 1993 and 1994 in sufficient quantity to raise pike biomass to levels of around$22\ {\rm kg}\ {\rm ha}^{-1}$by 1994. Minnow populations in L110 responded dramatically, decreasing to levels 30% (1993), 10% (1994), and less than 1% (1995) of premanipulation values. However, most components lower in the food web did not respond in a manner consistent with predictions of existing food-web theory, such as the idea of cascading trophic interactions (CTI). While Daphnia biomass increased in L110 in the first year following manipulation, consistent with CTI, this effect was temporary and Daphnia collapsed in 1995, the year of lowest minnow abundance. Total zooplankton biomass in both lakes declined during the study period and, contrary to CTI, this decline appeared somewhat stronger in L110 than in L240. Dominant microconsumers (heterotrophic microflagellates) did not differ among years in either lake and did not appear to respond to food-web manipulation. At the bottom of the food web, no changes in bacterial biomass occurred in either lake. However, total concentrations of particulate matter appeared to increase in L110 after manipulation (contrary to expectations based on the theory of CTI) while algal biomass did not change in the manipulated lake relative to reference systems. Finally, particulate C:P increased in both L110 and L240 during the study period. The lack of strong response of Daphnia, the lack of response of the microbial food web, decreases in zooplankton biomass and increases in particulate biomass following reduction of minnow populations after piscivore introduction are at odds with expectations from existing food-web theory, such as the |
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Minnow abundance, zooplankton biomass and community composition, microconsumer abundance, and concentration and carbon-phosphorus (C:P) ratio of suspended particulate matter were monitored in L110 and unmanipulated L240 before (1992) and after (1993-95) pike introduction. Algal biomass in L110 determined from microscopic examination for postmanipulation and premanipulation periods was also compared with dynamics in a suite of unmanipulated reference lakes from longterm monitoring records. Pike were added in spring in 1993 and 1994 in sufficient quantity to raise pike biomass to levels of around$22\ {\rm kg}\ {\rm ha}^{-1}$by 1994. Minnow populations in L110 responded dramatically, decreasing to levels 30% (1993), 10% (1994), and less than 1% (1995) of premanipulation values. However, most components lower in the food web did not respond in a manner consistent with predictions of existing food-web theory, such as the idea of cascading trophic interactions (CTI). While Daphnia biomass increased in L110 in the first year following manipulation, consistent with CTI, this effect was temporary and Daphnia collapsed in 1995, the year of lowest minnow abundance. Total zooplankton biomass in both lakes declined during the study period and, contrary to CTI, this decline appeared somewhat stronger in L110 than in L240. Dominant microconsumers (heterotrophic microflagellates) did not differ among years in either lake and did not appear to respond to food-web manipulation. At the bottom of the food web, no changes in bacterial biomass occurred in either lake. However, total concentrations of particulate matter appeared to increase in L110 after manipulation (contrary to expectations based on the theory of CTI) while algal biomass did not change in the manipulated lake relative to reference systems. Finally, particulate C:P increased in both L110 and L240 during the study period. The lack of strong response of Daphnia, the lack of response of the microbial food web, decreases in zooplankton biomass and increases in particulate biomass following reduction of minnow populations after piscivore introduction are at odds with expectations from existing food-web theory, such as the idea of CTI as currently formulated. However, the extremely high C:P ratios in particulate matter at the base of the food webs in these lakes, the coincidence of zooplankton declines and increases in particulate C:P ratios, and the results of small-scale mesocosm food-quality experiments are consistent with a hypothesis of a stoichiometric constraint operating on food-web dynamics in this and similar ecosystems.</description><identifier>ISSN: 1432-9840</identifier><identifier>EISSN: 1435-0629</identifier><identifier>DOI: 10.1007/s100219900009</identifier><language>eng</language><publisher>New York: Springer-Verlag</publisher><subject>Aquatic ecosystems ; Biomass ; Community composition ; Community structure ; Daphnia ; Esox lucius ; Food chains ; Food webs ; Freshwater ecosystems ; Freshwater fishes ; Lakes ; Lentic systems ; Minnows ; Particulate matter ; Plankton ; Predation ; Seston ; Trophic cascades ; Trophic relationships ; Zooplankton</subject><ispartof>Ecosystems (New York), 1998-01, Vol.1 (1), p.120-136</ispartof><rights>Copyright 1998 Springer-Verlag New York Inc.</rights><rights>Springer-Verlag New York Inc. 1998</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c380t-fbbc530974752a0aae904d83a3dc0a850a2b0f34814676e92e8a03101605f6cb3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/3658708$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/3658708$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,776,780,799,27903,27904,57995,58228</link.rule.ids></links><search><creatorcontrib>Elser, James J.</creatorcontrib><creatorcontrib>Chrzanowski, Thomas H.</creatorcontrib><creatorcontrib>Sterner, Robert W.</creatorcontrib><creatorcontrib>Mills, Kenneth H.</creatorcontrib><title>Stoichiometric Constraints on Food-Web Dynamics: A Whole-Lake Experiment on the Canadian Shield</title><title>Ecosystems (New York)</title><description>A whole-lake manipulation of food-web structure (introduction of a top predator, northern pike, to a minnow-dominated lake) was performed in a Canadian Shield lake (L110) to examine the stoichiometric consequences of changes in planktonic community structure generated by altered food-web structure. Minnow abundance, zooplankton biomass and community composition, microconsumer abundance, and concentration and carbon-phosphorus (C:P) ratio of suspended particulate matter were monitored in L110 and unmanipulated L240 before (1992) and after (1993-95) pike introduction. Algal biomass in L110 determined from microscopic examination for postmanipulation and premanipulation periods was also compared with dynamics in a suite of unmanipulated reference lakes from longterm monitoring records. Pike were added in spring in 1993 and 1994 in sufficient quantity to raise pike biomass to levels of around$22\ {\rm kg}\ {\rm ha}^{-1}$by 1994. Minnow populations in L110 responded dramatically, decreasing to levels 30% (1993), 10% (1994), and less than 1% (1995) of premanipulation values. However, most components lower in the food web did not respond in a manner consistent with predictions of existing food-web theory, such as the idea of cascading trophic interactions (CTI). While Daphnia biomass increased in L110 in the first year following manipulation, consistent with CTI, this effect was temporary and Daphnia collapsed in 1995, the year of lowest minnow abundance. Total zooplankton biomass in both lakes declined during the study period and, contrary to CTI, this decline appeared somewhat stronger in L110 than in L240. Dominant microconsumers (heterotrophic microflagellates) did not differ among years in either lake and did not appear to respond to food-web manipulation. At the bottom of the food web, no changes in bacterial biomass occurred in either lake. However, total concentrations of particulate matter appeared to increase in L110 after manipulation (contrary to expectations based on the theory of CTI) while algal biomass did not change in the manipulated lake relative to reference systems. Finally, particulate C:P increased in both L110 and L240 during the study period. The lack of strong response of Daphnia, the lack of response of the microbial food web, decreases in zooplankton biomass and increases in particulate biomass following reduction of minnow populations after piscivore introduction are at odds with expectations from existing food-web theory, such as the idea of CTI as currently formulated. However, the extremely high C:P ratios in particulate matter at the base of the food webs in these lakes, the coincidence of zooplankton declines and increases in particulate C:P ratios, and the results of small-scale mesocosm food-quality experiments are consistent with a hypothesis of a stoichiometric constraint operating on food-web dynamics in this and similar ecosystems.</description><subject>Aquatic ecosystems</subject><subject>Biomass</subject><subject>Community composition</subject><subject>Community structure</subject><subject>Daphnia</subject><subject>Esox lucius</subject><subject>Food chains</subject><subject>Food webs</subject><subject>Freshwater ecosystems</subject><subject>Freshwater fishes</subject><subject>Lakes</subject><subject>Lentic systems</subject><subject>Minnows</subject><subject>Particulate matter</subject><subject>Plankton</subject><subject>Predation</subject><subject>Seston</subject><subject>Trophic cascades</subject><subject>Trophic relationships</subject><subject>Zooplankton</subject><issn>1432-9840</issn><issn>1435-0629</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1998</creationdate><recordtype>article</recordtype><sourceid>8G5</sourceid><sourceid>BENPR</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNpd0LFOwzAQAFALgUQpjGwMFgNb4Bw7ic1WlRaQKjEU1DFyHEdxSexiuxL9e1KKkOCGuxueTneH0CWBWwJQ3IUhp0QIGEIcoRFhNEsgT8Xxd58mgjM4RWchrAFIxhkboXIZnVGtcb2O3ig8dTZEL42NATuL587VyUpX-GFnZW9UuMcTvGpdp5OFfNd49rnR3vTaxr2OrcZTaWVtpMXL1uiuPkcnjeyCvvipY_Q2n71On5LFy-PzdLJIFOUQk6aqVEZBFKzIUglSagGs5lTSWoHkGci0goYyTlhe5FqkmkugBEgOWZOrio7RzWHuxruPrQ6x7E1Quuuk1W4bSlIQlgKHAV7_g2u39XbYreSccWAF2aPkgJR3IXjdlJvhSul3JYFy_-vyz68Hf3Xw6xCd_8U0z3gBnH4BLpp48A</recordid><startdate>19980101</startdate><enddate>19980101</enddate><creator>Elser, James J.</creator><creator>Chrzanowski, Thomas H.</creator><creator>Sterner, Robert W.</creator><creator>Mills, Kenneth H.</creator><general>Springer-Verlag</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7SN</scope><scope>7ST</scope><scope>7XB</scope><scope>88I</scope><scope>8FK</scope><scope>8G5</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>M2O</scope><scope>M2P</scope><scope>MBDVC</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>SOI</scope><scope>7UA</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>19980101</creationdate><title>Stoichiometric Constraints on Food-Web Dynamics: A Whole-Lake Experiment on the Canadian Shield</title><author>Elser, James J. ; 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Minnow abundance, zooplankton biomass and community composition, microconsumer abundance, and concentration and carbon-phosphorus (C:P) ratio of suspended particulate matter were monitored in L110 and unmanipulated L240 before (1992) and after (1993-95) pike introduction. Algal biomass in L110 determined from microscopic examination for postmanipulation and premanipulation periods was also compared with dynamics in a suite of unmanipulated reference lakes from longterm monitoring records. Pike were added in spring in 1993 and 1994 in sufficient quantity to raise pike biomass to levels of around$22\ {\rm kg}\ {\rm ha}^{-1}$by 1994. Minnow populations in L110 responded dramatically, decreasing to levels 30% (1993), 10% (1994), and less than 1% (1995) of premanipulation values. However, most components lower in the food web did not respond in a manner consistent with predictions of existing food-web theory, such as the idea of cascading trophic interactions (CTI). While Daphnia biomass increased in L110 in the first year following manipulation, consistent with CTI, this effect was temporary and Daphnia collapsed in 1995, the year of lowest minnow abundance. Total zooplankton biomass in both lakes declined during the study period and, contrary to CTI, this decline appeared somewhat stronger in L110 than in L240. Dominant microconsumers (heterotrophic microflagellates) did not differ among years in either lake and did not appear to respond to food-web manipulation. At the bottom of the food web, no changes in bacterial biomass occurred in either lake. However, total concentrations of particulate matter appeared to increase in L110 after manipulation (contrary to expectations based on the theory of CTI) while algal biomass did not change in the manipulated lake relative to reference systems. Finally, particulate C:P increased in both L110 and L240 during the study period. The lack of strong response of Daphnia, the lack of response of the microbial food web, decreases in zooplankton biomass and increases in particulate biomass following reduction of minnow populations after piscivore introduction are at odds with expectations from existing food-web theory, such as the idea of CTI as currently formulated. However, the extremely high C:P ratios in particulate matter at the base of the food webs in these lakes, the coincidence of zooplankton declines and increases in particulate C:P ratios, and the results of small-scale mesocosm food-quality experiments are consistent with a hypothesis of a stoichiometric constraint operating on food-web dynamics in this and similar ecosystems.</abstract><cop>New York</cop><pub>Springer-Verlag</pub><doi>10.1007/s100219900009</doi><tpages>17</tpages></addata></record> |
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subjects | Aquatic ecosystems Biomass Community composition Community structure Daphnia Esox lucius Food chains Food webs Freshwater ecosystems Freshwater fishes Lakes Lentic systems Minnows Particulate matter Plankton Predation Seston Trophic cascades Trophic relationships Zooplankton |
title | Stoichiometric Constraints on Food-Web Dynamics: A Whole-Lake Experiment on the Canadian Shield |
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