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PRESPA LAKE WATERSHED MANAGEMENT PLAN

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Location of the Prespa Lake watershed 6 Figure 2. Topography and slope of Prespa Lake watershed 6 Figure 3. Geology Map and Soil Map 7 Figure 4. Prespa socio-economic maps: Settlements and road network; Land Use 9 Figure 5. Hydrological network in the watershed 10 Figure 6. Delineated surface waterbodies in the watershed 11 Figure 7. Hydrogeological map of the delineated groundwater bodies in the Prespa Lake Watershed 13 Figure 8. Major cations and heavy metals in core samples of Prespa Lake 15 Figure 9. Heavy and toxic metals in core samples of Prespa Lake 15 Figure 10. Total P content measured in recent sediments at the sampling sites of Prespa Lake. 16 Figure 11. Total P and total N core sediments of Lake Prespa 16 Figure 12. Comparative presentation of diatom assemblages retrieved from 0.5-10 ka BP core samples of Prespa Lake and some of the most dominant and characteristic taxa in the investigated core samples 17 Figure 13. Plankton sample from Lake Dojran (August 2010) dominated by Aulacoseira granulata and at least three Microcystis taxa; circular filaments belong to Lynbya contorta 18 Figure 14. Water bloom caused by Anabaena affinis and Anabaena contorta in Prespa Lake waters 18 Figure 15. Cyanotoxins-microcystins in Prespa Lake waters during the 12-month investigation period 19 Figure 16. Sources of pollution in the Prespa watershed 28 Figure 17. Water level decrease of Prespa Lake over the period 1951-2008 31 Figure 18. Water objects in the Prespa Lake Watershed 32 Figure 19. Soil erosion risk map of the Prespa Lake Watershed 36 Figure 20. Nature reserves (protected areas according to the Law on Nature) 37 Figure 21. Map of wetlands around Lake Prespa 38 Figure 22. Existing and newly proposed protection zones 39 Figure 23. Monitoring sites in delineated waterbodies in the Prespa Lake watershed which were continuously monitored during the course of this project 41 Figure 24. Map of the classification of ecological status of waterbodies in the Prespa Lake Watershed 43 Figure 25. Map of the delineated groundwater bodies and monitoring sites 44 Figure 26. BIS (2-Ethylhexyl)phthalate MPL<6 ng/l 45 Figure 27 MPL level for organoclorine pesticide 45
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... Unfortunately, in recent years, the entire ecosystem has faced serious environmental challenges such as pollution, ineffective planning for land-and water-use as well as poor preservation of rare and threatened species. The unsustainable agricultural, fishery, forestry, water, wastewater and solid waste management practices have had a severe impact on the ecosystem health (Petrovska et al. 2014). Macrozoobenthos communities indicate different biological water quality in the littoral and profundal parts of the lake. ...
... Macrozoobenthos communities indicate different biological water quality in the littoral and profundal parts of the lake. At different sampling sites, littoral benthic fauna is composed of species and di-versity indicating good to moderate ecological status, while the profundal is almost totally inhabited by fauna indicative of poor to bad ecological status (Petrovska et al. 2014). ...
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Results of the monitoring on the diversity and density of macrozoobenthos from the littoral zone of the locality Krani in Lake Prespa are presented. Three depths along three transects in this locality were sampled in spring and autumn of 2015. We recorded 25 taxa of macrozoobenthos belonging to eight classes: Turbellaria, Oligochaeta, Hirudinea, Gastropoda, Bivalvia, Amphipoda, Isopoda and Insecta. Seasonal changes (temperature, light availability, food availability and habitat conditions) as well as anthropogenic impacts affect macrozoobenthos communities. It was established that the density of communities is higher in autumn than in spring. Three species out of the 25 registered taxa were recorded with significantly higher densities: Dreissena carinata (14400 ind./m2), Gammarus triacanthus prespensis (4950 ind./m2) and Pyrgohydrobia prespaensis (4425 ind./m2). The results could contribute in obtaining a better understanding of the vertical and horizontal distribution, seasonal fluctuations in the population densities and the general state of the benthic fauna of this locality of high conservational importance.
... Koontz Lake contains two other invasive plant species: curly-leaf pondweed, which is also submersed, and purple loosestrife, an emergent aquatic plant. In the 2016 study, (Jermalowicz-Jones 2017) curly-leaf pondweed was found in only two locations in the littoral zone at the lake perimeter, where in the 2009 study (JFNew 2010) it covered approximately 42 acres 17 hectares), about 12% of the lake's surface. The 2009 study was conducted in May where the 2017 study was conducted in October, which could explain the difference in density of curly-leaf pondweed. ...
... Historically, Koontz Lake has had several issues with cyanobacteria. The 2008 study (JFNew 2010) showed that cyanobacteria was the most abundant genera found and accounted for over half of total phytoplankton density. Within the cyanobacteria, Anabaena sp. ...
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Koontz Lake is located in northern Indiana. The lake has had problems with eutrophication, harmful algae, invasive plants, and shallowing due to accumulation of sediment and muck. A study was conducted to assist in evaluating between two ecological restorative options under consideration: aeration and dredging. In this report, both approaches are defined, and various options of each are discussed. The impact of each approach is assessed for key water quality/ecological parameters. The specific needs of Koontz Lake are then discussed. In the case of Koontz Lake, the shallow portions of the lake appear to limit the effectiveness of aeration. Dredging would allow increased recreational use of the lake, particularly minimizing limitations on boating speeds. However, aeration could be integrated for long-term management of the lake. This report summarizes recommendations for Koontz Lake that have a greater applicability to other U.S. Army Corps of Engineers lake/reservoir projects. Several other alternatives are also presented, specifically the use of PhosLock, iron, and alum to bind phosphorus in sediments. (The U.S. Army Engineer Research and Development Center does not endorse any specific products or brands).
... The watershed is 5,324 hectares and is dominated by loams and clay loams formed from glacial till. Land use in the watershed includes 74.6% row crops, 6.7% grass/hay, 5.8% wetlands, 1.9% timber, and 11% other [30]. Two municipalities lie in the watershed: Lake View, population 1,142, lies in the northwest region and Breda, population 483, is situated at the southernmost end of the watershed at the headwaters (2010 census). ...
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Antibiotics are administered to livestock in animal feeding operations (AFOs) for the control, prevention, and treatment of disease. Manure from antibiotic treated livestock contains unmetabolized antibiotics that provide selective pressure on bacteria, facilitating the expression of anti-microbial resistance (AMR). Manure application on row crops is an agronomic practice used by growers to meet crop nutrient needs; however, it can be a source of AMR to the soil and water environment. This study in central Iowa aims to directly compare AMR indicators in outlet runoff from two adjacent (221 to 229 ha) manured and non-manured catchments (manure comparison), and among three catchments (600 to 804 ha) with manure influence, no known manure application (control), and urban influences (mixed land use comparison). Monitored AMR indicators included antibiotic resistance genes (ARGs) ermB, ermF (macrolide), tetA, tetM, tetO, tetW (tetracycline), sul1, sul2 (sulfonamide), aadA2 (aminoglycoside), vgaA, and vgaB (pleuromutilin), and tylosin and tetracycline resistant enterococci bacteria. Results of the manure comparison showed significantly higher (p<0.05) tetracycline and tylosin resistant bacteria from the catchment with manure application in 2017, but no differences in 2018, possibly due to changes in antibiotic use resulting from the Veterinary Feed Directive. Moreover, the ARG analysis indicated a larger diversity of ARGs at the manure amended catchment. The mixed land use comparison showed the manure amended catchment had significantly higher (p<0.05) tetracycline resistant bacteria in 2017 and significantly higher tylosin resistant bacteria in 2017 and 2018 than the urban influenced catchment. The urban influenced catchment had significantly higher ermB concentrations in both sampling years, however the manure applied catchment runoff consisted of higher relative abundance of total ARGs. Additionally, both catchments showed higher AMR indicators compared to the control catchment. This study identifies four ARGs that might be specific to AMR as a result of agricultural sources (tetM, tetW, sul1, sul2) and optimal for use in watershed scale monitoring studies for tracking resistance in the environment.
... Intensive agriculture along with tourism and medium-size industrial enterprises contribute to overall environmental pressure. The continuous and intensive anthropogenic pressure led to increased eutrophication of the Prespa Lake (Krstić 2012, Petrovska et al. 2014) and triggered a "chain reaction" of ecosystem deprivation. ...
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Aldrovanda vesiculosa L., widely known as the waterwheel plant, is a rare aquatic plant that holds the status of a globally endangered (EN) species. Extant populations of A. vesiculosa are rare in Europe and there are only few sites left in the Balkans. In Macedonia, the species was last recorded in 1980 and according to many researchers the plant was considered as extinct in the area. In this paper, we present the recent finding of Aldrovanda vesiculosa and new data on its distribution in Macedonia, including an assessment on the specific habitat type and evident threats.
... Consider the various strategies that use a BMP to control P discharge. Per acre of runoff treatment area, the cost of a constructed wetland is estimated to be around $1,500 ($US2004); a storm-water infiltration system costs around $25,000 ($US2004) (Jarvis, Coverly, &Auch, 2004). To estimate long-term costs, a present value approach can be adopted to calculate the net present value (NPV) over time, with given discount and inflation rates. ...
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A system dynamics method to assess carrying capacity of a defined natural environment is presented. The proposed method seeks to relate per capita resource usage to ranges of population and per capita consumption beyond which the system is not viable relative to population dependent resource constraints. It provides a platform to investigate system behavior through system dynamics simulations where populations change, natural resources decay due to stressor impacts, and feedback occurs via implementation of policy. Application of the model to a case study of Total Maximum Daily Load (TMDL) of phosphorous in Bear Lake, a Lake Michigan estuary (USA), shows the major total phosphorous (P) loading contribution is anthropogenic land use development. Three scenarios are quantitatively explored by assuming changes in land use and/or loading rates. Simulation results show tradeoffs between reduction of total P and land use; economic development can be flexibly evaluated against targets of loading reduction trajectories.
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Surface water is one of the most vital Earth resources changing in time and space as a consequence of land use/land cover (LULC) changes, climate change, and other environmental factors. Timely monitoring of the water area and its surroundings is essential for policy and decision-making processes. Monitoring the land cover changes with conventional methods may consume significant time and resources. With the development of remote sensing, land cover monitoring has become practical and effective. The most practical way for monitoring the changes is with the classification of satellite imagery. The main aim of the study is to make a five-year land cover change in a watershed using remote sensing data. For this purpose, two satellite images, from RapidEye-3 and Sentinel-2 have been classified. As a study area, the Prespa Lake watershed has been selected. The Prespa Lake is situated in the Balkan Peninsula and is shared among Albania, North Macedonia, and Greece. For the purpose of the study, a semi-automated object-based classification model has been developed. The results from the classification showed significant accuracy of 93-96%. For future studies, it is recommended further investigation, such as using monthly satellite imagery and modeling precipitation and meteorological data.
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Healthy environment is rapidly becoming very important value in human life and a criterion of the quality of living. To achieve this target, many of us consider the 'returning to nature' and respecting the ancient laws of nature as the possible solution. Accelerated or fast eutrophization is detected destiny in majority of fresh water ecosystems today, mainly due to global climate changes and adverse human impact. However, this process can be tackled by different activities, ecoremedation (ERM) having an especially important place. Ecoremediation is a system of utilizing the natural processes for revival and protection of the environment. ERM methods may reduce and avert the consequences of agricultural pollution, tourism, transport, industry, land fills and (over)population. In its essence, ERM represents the 'returning to nature' approach aiming to preserve or re-establish the natural balance of the ecosystems, but also a human endevour that enables new jobs and by-side activities important for economic and social (sustainable) development of the human society. In this study we propose the model of eutrophication control achieved on four important levels in the functional dynamics of the ecosystems. ERM is placed as key element in prevention, increasing of decomposition processes through different modes of aeration, decreasing of the total capacity of the ecosystem usually via constructed wetlands, planting and removing of the riparian vegetation.