GIS-based pollution hazard mapping and assessment framework of shallow lakes: Southeastern Pampean lakes (Argentina) as a case study

The assessment of water vulnerability and pollution hazard traditionally places particular emphasis on the study on groundwaters more than on surface waters. Consequently, a GIS-based Lake Pollution Hazard Index (LPHI) was proposed for assessing and mapping the potential pollution hazard for shallow...

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Autor principal: Romanelli, A.
Otros Autores: Esquius, K.S, Massone, H.E, Escalante, A.H
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Publicado: 2013
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024 7 |2 pubmed  |a 23355019 
024 7 |2 cas  |a Water Pollutants 
040 |a Scopus  |b spa  |c AR-BaUEN  |d AR-BaUEN 
030 |a EMASD 
100 1 |a Romanelli, A. 
245 1 0 |a GIS-based pollution hazard mapping and assessment framework of shallow lakes: Southeastern Pampean lakes (Argentina) as a case study 
260 |c 2013 
270 1 0 |m Romanelli, A.; Instituto de Geología de Costas y Del Cuaternario, FCEyN, Universidad Nacional de Mar Del Plata, Funes 3350, Nivel 1, 7600 Mar del Plata, Argentina; email: aromanel@mdp.edu.ar 
506 |2 openaire  |e Política editorial 
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520 3 |a The assessment of water vulnerability and pollution hazard traditionally places particular emphasis on the study on groundwaters more than on surface waters. Consequently, a GIS-based Lake Pollution Hazard Index (LPHI) was proposed for assessing and mapping the potential pollution hazard for shallow lakes due to the interaction between the Potential Pollutant Load and the Lake Vulnerability. It includes easily measurable and commonly used parameters: land cover, terrain slope and direction, and soil media. Three shallow lake ecosystems of the southeastern Pampa Plain (Argentina) were chosen to test the usefulness and applicability of this suggested index. Moreover, anthropogenic and natural medium influence on biophysical parameters in these three ecosystems was examined. The evaluation of the LPHI map shows for La Brava and Los Padres lakes the highest pollution hazard (≈30 % with high to very high category) while Nahuel Rucá Lake seems to be the less hazardous water body (just 9.33 % with high LPHI). The increase in LPHI value is attributed to a different loading of pollutants governed by land cover category and/or the exposure to high slopes and influence of slope direction. Dissolved oxygen and biochemical oxygen demand values indicate a moderately polluted and eutrophized condition of shallow lake waters, mainly related to moderate agricultural activities and/or cattle production. Obtained information by means of LPHI calculation result useful to perform a local diagnosis of the potential pollution hazard to a freshwater ecosystem in order to implement basic guidelines to improve lake sustainability. © 2013 Springer Science+Business Media Dordrecht.  |l eng 
593 |a Instituto de Investigaciones Marinas y Costeras (IIMyC), Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), 7600 Mar del Plata Buenos Aires, Argentina 
593 |a Instituto de Geología de Costas y Del Cuaternario, FCEyN, Universidad Nacional de Mar Del Plata, Funes 3350, Nivel 1, 7600 Mar del Plata, Argentina 
593 |a Laboratorio de Limnología, FCEyN, Universidad Nacional de Mar Del Plata, Funes 3250, Nivel 2, 7600 Mar del Plata, Argentina 
690 1 0 |a BIOPHYSICAL ATTRIBUTES 
690 1 0 |a GIS-BASED LAKE POLLUTION HAZARD INDEX 
690 1 0 |a LAND COVER 
690 1 0 |a SHALLOW LAKES 
690 1 0 |a BIOPHYSICAL ATTRIBUTES 
690 1 0 |a LAND COVER 
690 1 0 |a POLLUTION HAZARDS 
690 1 0 |a SHALLOW LAKES 
690 1 0 |a BIOCHEMICAL OXYGEN DEMAND 
690 1 0 |a ECOSYSTEMS 
690 1 0 |a GEOGRAPHIC INFORMATION SYSTEMS 
690 1 0 |a GROUNDWATER 
690 1 0 |a LAKE POLLUTION 
690 1 0 |a LAKES 
690 1 0 |a POLLUTION 
690 1 0 |a RIVER POLLUTION 
690 1 0 |a BIOHAZARDS 
690 1 0 |a DISSOLVED OXYGEN 
690 1 0 |a GROUND WATER 
690 1 0 |a SURFACE WATER 
690 1 0 |a BIOCHEMICAL OXYGEN DEMAND 
690 1 0 |a DISSOLVED OXYGEN 
690 1 0 |a EUTROPHICATION 
690 1 0 |a FRESHWATER ECOSYSTEM 
690 1 0 |a GIS 
690 1 0 |a GUIDELINE 
690 1 0 |a HAZARD MANAGEMENT 
690 1 0 |a LAKE POLLUTION 
690 1 0 |a LAND COVER 
690 1 0 |a PARAMETERIZATION 
690 1 0 |a POLLUTION MONITORING 
690 1 0 |a SHALLOW WATER 
690 1 0 |a TERRAIN 
690 1 0 |a ARTICLE 
690 1 0 |a BIOCHEMISTRY 
690 1 0 |a ENVIRONMENTAL MONITORING 
690 1 0 |a EUTROPHICATION 
690 1 0 |a GEOGRAPHIC INFORMATION SYSTEM 
690 1 0 |a GEOGRAPHIC MAPPING 
690 1 0 |a GEOGRAPHY 
690 1 0 |a HAZARD ASSESSMENT 
690 1 0 |a LAKE 
690 1 0 |a LAND USE 
690 1 0 |a SOIL ANALYSIS 
690 1 0 |a WATER ANALYSIS 
690 1 0 |a WATER POLLUTION 
690 1 0 |a AGRICULTURE 
690 1 0 |a ANIMALS 
690 1 0 |a CATTLE 
690 1 0 |a ENVIRONMENTAL MONITORING 
690 1 0 |a GEOGRAPHIC INFORMATION SYSTEMS 
690 1 0 |a LAKES 
690 1 0 |a RISK ASSESSMENT 
690 1 0 |a WATER POLLUTANTS 
690 1 0 |a PAMPAS 
690 1 0 |a BOS 
651 4 |a PAMPA PLAIN (ARGENTINA) 
651 4 |a ARGENTINA 
651 4 |a ARGENTINA 
651 4 |a ARGENTINA 
651 4 |a ARGENTINA 
700 1 |a Esquius, K.S. 
700 1 |a Massone, H.E. 
700 1 |a Escalante, A.H. 
773 0 |d 2013  |g v. 185  |h pp. 6943-6961  |k n. 8  |p Environ. Monit. Assess.  |x 01676369  |w (AR-BaUEN)CENRE-4627  |t Environmental Monitoring and Assessment 
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856 4 0 |u https://doi.org/10.1007/s10661-013-3077-7  |y DOI 
856 4 0 |u https://hdl.handle.net/20.500.12110/paper_01676369_v185_n8_p6943_Romanelli  |y Handle 
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