dc.contributor.author |
Stamatis, G |
en |
dc.contributor.author |
Parpodis, K |
en |
dc.contributor.author |
Filintas, A |
en |
dc.contributor.author |
Zagana, E |
en |
dc.date.accessioned |
2014-06-06T06:51:20Z |
|
dc.date.available |
2014-06-06T06:51:20Z |
|
dc.date.issued |
2011 |
en |
dc.identifier.issn |
18666280 |
en |
dc.identifier.uri |
http://dx.doi.org/10.1007/s12665-011-0926-y |
en |
dc.identifier.uri |
http://62.217.125.90/xmlui/handle/123456789/5461 |
|
dc.subject |
Central Thessaly (Greece) |
en |
dc.subject |
Evapotranspiration and irrigation analysis |
en |
dc.subject |
Groundwater and irrigation water quality |
en |
dc.subject |
Hydrochemical and factor analysis |
en |
dc.subject |
Neogene sediments |
en |
dc.subject |
Nitrate pollution and GIS geostatistical analysis |
en |
dc.subject.other |
Agricultural use |
en |
dc.subject.other |
Central Thessaly (Greece) |
en |
dc.subject.other |
Chemical fertilizers |
en |
dc.subject.other |
Degradation degree |
en |
dc.subject.other |
Factor analysis |
en |
dc.subject.other |
GIS application |
en |
dc.subject.other |
Groundwater quality |
en |
dc.subject.other |
Groundwater quality degradation |
en |
dc.subject.other |
High salinity |
en |
dc.subject.other |
Human activities |
en |
dc.subject.other |
Human consumption |
en |
dc.subject.other |
Human use |
en |
dc.subject.other |
Hydrochemicals |
en |
dc.subject.other |
Hydrogeological |
en |
dc.subject.other |
Inhabited areas |
en |
dc.subject.other |
Irrigation management |
en |
dc.subject.other |
Irrigation waters |
en |
dc.subject.other |
Low sodium |
en |
dc.subject.other |
Neo genes |
en |
dc.subject.other |
Nitrate pollution |
en |
dc.subject.other |
Nitrate pollution and GIS geostatistical analysis |
en |
dc.subject.other |
Shallow aquifers |
en |
dc.subject.other |
Statistical data analysis |
en |
dc.subject.other |
Study areas |
en |
dc.subject.other |
Anoxic sediments |
en |
dc.subject.other |
Aquifers |
en |
dc.subject.other |
Chemical analysis |
en |
dc.subject.other |
Chemical compounds |
en |
dc.subject.other |
Chlorine |
en |
dc.subject.other |
Data reduction |
en |
dc.subject.other |
Degradation |
en |
dc.subject.other |
Environmental management |
en |
dc.subject.other |
Fertilizers |
en |
dc.subject.other |
Geographic information systems |
en |
dc.subject.other |
Groundwater pollution |
en |
dc.subject.other |
Groundwater resources |
en |
dc.subject.other |
Hydrogeology |
en |
dc.subject.other |
Irrigation |
en |
dc.subject.other |
Pollution |
en |
dc.subject.other |
Quality control |
en |
dc.subject.other |
Salinity measurement |
en |
dc.subject.other |
Sedimentology |
en |
dc.subject.other |
Sodium |
en |
dc.subject.other |
Soils |
en |
dc.subject.other |
Solvent extraction |
en |
dc.subject.other |
Water quality |
en |
dc.subject.other |
Water supply |
en |
dc.subject.other |
Water treatment |
en |
dc.subject.other |
Hydrochemistry |
en |
dc.subject.other |
agricultural intensification |
en |
dc.subject.other |
agricultural land |
en |
dc.subject.other |
aquifer pollution |
en |
dc.subject.other |
borehole |
en |
dc.subject.other |
chemical composition |
en |
dc.subject.other |
data interpretation |
en |
dc.subject.other |
environmental degradation |
en |
dc.subject.other |
environmental impact assessment |
en |
dc.subject.other |
environmental management |
en |
dc.subject.other |
evapotranspiration |
en |
dc.subject.other |
factor analysis |
en |
dc.subject.other |
fertilizer application |
en |
dc.subject.other |
geostatistics |
en |
dc.subject.other |
GIS |
en |
dc.subject.other |
groundwater abstraction |
en |
dc.subject.other |
groundwater pollution |
en |
dc.subject.other |
hill |
en |
dc.subject.other |
human activity |
en |
dc.subject.other |
hydrochemistry |
en |
dc.subject.other |
hydrogeology |
en |
dc.subject.other |
irrigation system |
en |
dc.subject.other |
nature-society relations |
en |
dc.subject.other |
Neogene |
en |
dc.subject.other |
nitrate |
en |
dc.subject.other |
salinity |
en |
dc.subject.other |
sodium |
en |
dc.subject.other |
spatial distribution |
en |
dc.subject.other |
spring water |
en |
dc.subject.other |
vulnerability |
en |
dc.subject.other |
water quality |
en |
dc.subject.other |
water use |
en |
dc.subject.other |
water yield |
en |
dc.subject.other |
Greece |
en |
dc.subject.other |
Thessaly |
en |
dc.title |
Groundwater quality, nitrate pollution and irrigation environmental management in the Neogene sediments of an agricultural region in central Thessaly (Greece) |
en |
heal.type |
journalArticle |
en |
heal.identifier.primary |
10.1007/s12665-011-0926-y |
en |
heal.publicationDate |
2011 |
en |
heal.abstract |
The degradation of groundwater quality, which has been noted in the recent years, is closely connected to the intensification of agriculture, the unreasonable use of chemical fertilizers and the excess consumption of large volumes of irrigation water. In the hilly region of central Thessaly in Greece, which suffers the consequences of intense agricultural use, a hydrogeological study is carried out, taking groundwater samples from springs and boreholes in the Neogene aquifers. The aim of this study is the investigation of irrigation management, water quality and suitability for various uses (water supply, irrigation), the degradation degree and the spatial distribution of pollutants using GIS. The following hydrochemical types prevail in the groundwater of the study area: Ca-Mg-HCO3, Mg-Ca-Na-HCO3 and Na-HCO3. In the above shallow aquifers, especially high values of NO3- (31. 7-299. 0), NH4+ (0. 12-1. 11), NO2- (0. 018-0. 109), PO43- (0. 07-0. 55), SO42- (47. 5-146. 5) and Cl- (24. 8-146. 5) are found, particularly near inhabited areas (values are in mg L-1). The water of shallow aquifers is considered unsuitable for human use due to their high polluting load, while the water of the deeper aquifers is suitable for human consumption. Regarding water suitability for irrigation, the evaluation of SAR (0. 153-7. 397) and EC (481-1,680 μS cm-1) resulted in classification category 'C3S1', indicating high salinity and low sodium water which can be used for irrigation in most soils and crops with little to medium danger of development of exchangeable sodium and salinity. The statistical data analysis, the factor analysis and the GIS application have brought out the vulnerable-problematic zones in chemical compounds of nitrogen and phosphates. The groundwater quality degradation is localized and related exclusively to human activities. Based on 2005 and 2008 estimates, the annual safe yield of the region's aquifers were nearly 41. 95 MCM. However, the existing situation is that 6. 37 MCM of water is over extracted from these aquifers. © 2011 Springer-Verlag. |
en |
heal.journalName |
Environmental Earth Sciences |
en |
dc.identifier.issue |
4 |
en |
dc.identifier.volume |
64 |
en |
dc.identifier.doi |
10.1007/s12665-011-0926-y |
en |
dc.identifier.spage |
1081 |
en |
dc.identifier.epage |
1105 |
en |