Original Research ArticleThe sustainable restoration of lakes—towards the challenges of the Water Framework Directive
Introduction
According to the Water Framework Directive (WFD) (European Community, 2000) all water bodies should achieve good ecological and chemical status before 2015. In Poland there are 1036 lakes above 50 ha that are of interest under the WFD and only about half of them meet these requirements (Ciecierska and Dynowska, in press). To achieve improvements in such a large number of lakes in a short time, appropriate tools and effective methods are indispensable. It is possible to use many methods to protect lake ecosystems. The most important are: (i) diversion of municipal and industrial sewage (both raw and treated), (ii) thorough treatment of storm waters before discharge to the receiving water, (iii) limitation of input of diffuse water pollution from agriculture, by creation of buffer zones, use of sustainable or ecological agriculture, reduction of water and wind erosion of soils, (iv) reduction of the nutrient load reaching the lake by building preliminary reservoirs on inflow rivers to intercept nutrients. In some cases, protection measures alone are sufficiently effective in improving the status of degraded lakes. The example of Lake Washington is well known. About ten years after diversion of sewage effluent previously discharged to the lake from Seattle and other towns, the lake improved in terms of water quality (Kajak, 1998). However, Lake Washington is a large and deep lake (88 km2 and 65 m max. depth) and had ancillary mechanisms involving changes in the food webs that contributed to improvements of water quality. Smaller and shallower lakes may or may not spontaneously return to good ecological status after the application of protective measures only. The example of Lake Sławskie, with a surface area of 8.28 km2 and 12.3 m maximum depth, which has been studied for several years, confirms that it is possible. The lake was polluted for many years by sewage from the city of Sława, which resulted in cyanobacterial water blooms and the closing of the bathing areas. The construction of a new sewage treatment plant in 2008, and transfer of treated wastewater to filtration ponds several kilometres distant from the lake, led to a gradual improvement of its water quality (Kozak et al., 2012).
In many cases, however, protection measures are not sufficient and lakes need additional in-lake restoration treatment. These methods, in order to meet the requirements of the WFD, should be inexpensive, easy to use, effective, and sustainable (energy-efficient, not destructive for most of the biota). Many technical and biological methods of lake restoration are known, but only a few of them fulfil the requirements stated above. Some of such innovative methods have been tested and improved in several lakes situated near Poznań (Wielkopolska Region, West Poland) by our team and a brief account of them is given in this paper.
Section snippets
The Maltański Reservoir case study
This reservoir is a shallow and polymictic water body with an area of 64 ha, 5.5 m max. depth and mean depth of 3.1 m, situated near the centre of Poznań. It is used for recreation and water sports, but since its filling with water in 1990, it has been hypertrophic with cyanobacterial water blooms, owing to a high load of nutrients from the main tributary, the River Cybina. Creation in the river course of four small preliminary reservoirs did not result in any apparent reduction of the nutrient
The Lake Uzarzewskie case study
Lake Uzarzewskie is a small lake, with an area of 10.4 ha and a maximum depth of 7.2 m, but is thermally stratified. It is hypertrophic owing to a high external load of nutrients from its agricultural catchment area, treated sewage from the village of Uzarzewo, and outflow from a fish farm. It was treated in 2006–2007 with iron salts. As a result, internal loading was temporarily decreased, but water quality has improved only slightly. This was due to a deoxygenated meta- and hypolimnion with
The Lake Durowskie case study
Lake Durowskie is a post-glacial lake, thermally stratified, with an area of 143.7 ha and a maximum depth of 14.6 m. In one part it is surrounded by a forest, but otherwise it is adjacent to a city. It is important for recreation for the local population, especially for swimming and fishing. By 2008, the lake had large cyanobacterial water blooms, lack of oxygen and presence of hydrogen sulphide in the hypolimnion, and high external and internal loading of phosphorus. Restoration of the lake
Discussion
The use of minimally invasive measures for lake restoration enables a gradual reconstruction of the composition of communities, from phytoplankton and zooplankton to benthic macroinvertebrates and macrophytes. The most important change is the reduction of cyanobacteria, which allows use of the water by people even if other groups of phytoplanktonic organisms are still relatively frequent. Disappearance of harmful toxic metabolites released by many species of cyanobacteria (Mankiewicz-Boczek et
Conclusions
It is possible to use sustainable lake restoration methods which are cheap, easy to use, effective, energy-efficient and not destructive for most of the biota. These include the use of wind aerators, biomanipulation, iron treatment with small doses of iron sulphate or chloride, and supplying the hypolimnetic water with water from tributaries that are rich in nitrates. Simultaneous application of several methods, which prevents feedback mechanisms, increases the efficiency of restoration.
Financial disclosure
This research was partly supported by the Ministry of Science and Higher Education (Poland), grant nos. N 305 10831/3632 and NN305 372838.
Conflict of Interest
None
Acknowledgments
The authors are very grateful to Professor Brian Moss for his kindly review of the manuscript, which led to a substantial improvement of the final version of this paper.
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