1993
DOI: 10.1016/s0380-1330(93)71218-6
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Lake Erie Offshore in 1990: Restoration and Resilience in the Central Basin

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Cited by 58 publications
(33 citation statements)
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“…This finding is consistent with observed reduction in total P, chlorophyll a, and phytoplankton biomass in the water column during the 1970s and 1980s (Makarewicz and Bartram 199 1). Other expected ecosystem responses to reduced P loading, such as reduced rates of hypolimnetic oxygen depletion in the central basin, have not been found (see Charlton et al 1993). The use of 613C,,,, to infer trends in paleoproductivity is strengthened by our results from Lake Erie in which the inferences about productivity are similar for two cores with distinctly different stratigraphies.…”
Section: Discussionmentioning
confidence: 58%
“…This finding is consistent with observed reduction in total P, chlorophyll a, and phytoplankton biomass in the water column during the 1970s and 1980s (Makarewicz and Bartram 199 1). Other expected ecosystem responses to reduced P loading, such as reduced rates of hypolimnetic oxygen depletion in the central basin, have not been found (see Charlton et al 1993). The use of 613C,,,, to infer trends in paleoproductivity is strengthened by our results from Lake Erie in which the inferences about productivity are similar for two cores with distinctly different stratigraphies.…”
Section: Discussionmentioning
confidence: 58%
“…Eadie et al (1995) suggested that most of the historic increase in 61SN may be due to denitrification in the seasonally anoxic central basin of Lake Erie, with subsequent transport of this signal downstream to Lake Ontario. During denitrification in suboxic environments, NO,-is converted to N,, with a strong fractionation leaving the dissolved NO, enriched in "N. The area of central basin anoxia in Lake Erie increased substantially from the 1930s to the early 1970s (Herdendorf 1980), and has not decreased significantly since the 1970s despite large decreases in P loading (Bertram 1993;Charlton et al 1993). The fact that the iY5N increased in both cores until 1960 and then remained relatively constant thereafter is broadly consistent with the history of anoxia in the central basin of Lake Erie.…”
Section: Discussionmentioning
confidence: 99%
“…Although this target load was met by the mid-1980s (Dolan 1993) and remains near the target load with weather-induced annual variation (Dolan and McGunagle 2005), total phytoplankton biomass has increased after a mid-1990s minimum (Conroy et al 2005b), cyanobacterial blooms have increased (Conroy and Culver 2005), hypolimnetic hypoxia occurs annually to varying extents in the central basin (Charlton and Milne 2004;Burns et al 2005;Conroy 2007; Rao et al 2008), and indicators of overall system ''health'' continue to show impairment (Conroy et al 2008). Charlton et al (1993) proposed that the actual range of external P load change from an estimated \5 Gg P year -1 prior to European settlement (Harris and Vollenweider 1982), to a maximum of about 30 Gg P year -1 at the height of cultural eutrophication (Sly 1976) and back to about 11 Gg P year -1 post GLWQA implementation (Dolan 1993;Dolan and McGunagle 2005) was insufficient to affect HOD rates or Lake Erie in general, due to system resilience or the continued oxidation of reduced substances present in historically loaded sediments (Matzinger et al 2010). That is, processes and features such as P sorption to suspended sediments with concomitant sedimentation and burial, the large distance between the site of most P loading in the western basin and the hypoxic area of the central basin, and re-aeration of the hypolimnion due to physical entrainment and mixing events (Ivey and Boyce 1982), were sufficient to buffer Lake Erie from observable changes in HOD rates as external P loading increased and subsequently was reduced.…”
Section: Introductionmentioning
confidence: 99%