Author:
Johnson M. G.,George S. E.,Kelso J. R. M.
Abstract
The Wright–Henriksen model was used to estimate chemical changes in 255 central Ontario lakes attributable to strong acid loading. Background SO42− in precipitation, 14.5 μeq∙L−1, was estimated by analysis of "clean" events in contemporary data and used to determine background SO42− in lakes, which averaged 26 μeq∙L−1. Net (excess) SO42− averaged approximately 100 μeq∙L−1. An empirical function was used to calculate ANC0 (at historical t0) and ANC loss from net SO42−. Then, pH0 was estimated from ANC0, obtained with empirical and theoretical relationships of contemporary pHc and ANCc. Almost all of ANC0 of 125 μeq∙L−1 on average was lost in one group of lakes near Sudbury. Associated mean pH decrease was 0.8–1.4 depending on the model used. Approximately 60–70% of ANC0 of 110 μeq∙L−1 was lost, with a pH decrease of 0.3–0.8, in lakes of two groups near Parry Sound. Only 20–30% of ANC0 of 160 μeq∙L−1 had been lost, with little pH change, in a group of lakes closer to Sault Ste. Marie. Such estimates are required for a rational interpretation of data on the distribution of fish species in Ontario lakes and estimation of losses of fish.
Publisher
Canadian Science Publishing
Subject
Aquatic Science,Ecology, Evolution, Behavior and Systematics
Cited by
5 articles.
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