Abstract
Background: Lake Datong has undergone several stages of aquaculture from 1980 to 2017, with a rapid increase in fish production and inorganic fertilizer supplementation at every stage. Its water quality has been deteriorating since the introduction of aquaculture. The major pollutants are total phosphorus and total nitrogen, and the lake displays moderate eutrophication. In the present study, we used historical hydrobiont data, diatom inferred-total phosphorous (DI-TP) data, and an Ecopath model to explore the effects of aquaculture on the shallow lake aquatic ecological environment.Results: According to the DI-TP data, before 1930, Lake Datong was in a mesotrophic state (50–60 μg/L DI-TP). Between 1930 and 1980, the number of nutrient-tolerant species increased slightly, which indicates an increase in nutrient enrichment in the lake (66–83 μg/L DI-TP). From the 1980s to 2010 and especially since 2000, eutrophication increased rapidly, with eutrophic species dominating the diatom assemblage. The annual average DI-TP concentration was 202 μg/L. After 2010, the nutritional level dropped to 127–152 μg/L DI-TP. In 2019, consumer biomass in Lake Datong was relatively low, and biomass of submerged hydrophytes was relatively high, indicating that a high amount of primary produce could not be exploited by consumers and therefore, could not enter the food web. This led to reduction in the energy transfer efficiency (TE) of the ecosystem. Therefore, aquatic ecology management plans ought to be formulated in future, with focus on removing macrophytes, stocking herbivorous and omnivorous fish.Conclusions: Lake Datong has experienced four stages of nutritional succession following the introduction of aquaculture activities. Its aquatic ecological environment has experienced dramatic changes in the composition and biomass of its aquatic life. The Ecopath model illustrated the instability of the lake’s ecological environment. Owing to low consumer biomass and high submerged macrophyte biomass, a substantial quantity of primary produce remained unused by consumers. It was therefore, unable to enter the food web and led to reduction in the energy TE of the ecosystem. Our results provide important reference values and theoretical support for decision-makers and stakeholders in the subsequent management of similar shallow lake water ecosystems.