4.4 Article

Assessing the long-term efficacy of internal loading management to control eutrophication in Lake Rauwbraken

期刊

INLAND WATERS
卷 12, 期 1, 页码 61-77

出版社

TAYLOR & FRANCIS LTD
DOI: 10.1080/20442041.2021.1969189

关键词

cyanobacteria; eutrophication control; in-lake; lake restoration; sediment P release

资金

  1. Regional Water Authority De Dommel
  2. Province of North-Brabant
  3. municipality of Tilburg
  4. Dutch Underwater Park Foundation
  5. Conselho Nacional de Desenvolvimento Cientifico e Tecnologico (CNPq), Brazil [304284/2017-3]

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The study investigated the chemical and ecological responses to the internal loading treatment at Lake Rauwbraken, showing that the treatment effectively controlled internal loading and improved water quality. However, over time, the coverage of submerged macrophytes decreased, and the lake is returning to a eutrophic state due to ongoing external phosphorus loads.
Lake Rauwbraken was impacted by eutrophication caused by diffuse external phosphorus (P) loads (total 1.21 mg m(-2) d(-1), estimated in 2008). Over 40 years, this load built up a legacy pool in the sediments, resulting in 6.82 mg m(-2) d(-1) PO4-P internal load (estimated in 2008), causing cyanobacterial blooms and swimming bans. To address the internal load in this lake, a low dose treatment of flocculant (polyaluminium chloride) combined with a solid phase phosphate fixative (lanthanum-modified bentonite) was applied in 2008. We examined the chemical and ecological responses to this treatment to demonstrate the efficacy of controlling internal loading without reducing external loading. Based on 2 years pre- and 10 years post-treatment monitoring, the mean Secchi disk depth (3.5-4.0 m) and the hypolimnetic oxygen concentration (0.86-4.55 mg L-1) increased while decreases occurred in turbidity (5.4 to 2.2 NTU), chlorophyll a (16.5 to 5.5 mu g L-1), contribution of cyanobacteria (64% to 17% of chlorophyll a), total phosphorus (134 to 14 mu g L-1), and total nitrogen (0.96 to 0.50 mg L-1). The treatment reduced the PO4-P release from sediment under anoxic conditions from 15.1 to 1.7 mg m(-2) d(-1) post-treatment in 2008, 2.3 mg m(-2) d(-1) in 2011, and 4.7 mg m(-2) d(-1) in 2013. Post-treatment, submerged macrophytes reached high coverage in 2008 and 2009. Longer term, post-treatment macrophyte cover was reduced. The lake is returning to a eutrophic state as a result of ongoing external P loads 10 years following the control of internal loading.

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