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. 2011 Aug;8(8):3416-36.
doi: 10.3390/ijerph8083416. Epub 2011 Aug 19.

Estimation of the effect of soil texture on nitrate-nitrogen content in groundwater using optical remote sensing

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Estimation of the effect of soil texture on nitrate-nitrogen content in groundwater using optical remote sensing

Yongyoot Witheetrirong et al. Int J Environ Res Public Health. 2011 Aug.

Abstract

The use of chemical fertilizers in Thailand increased exponentially by more than 100-fold from 1961 to 2004. Intensification of agricultural production causes several potential risks to water supplies, especially nitrate-nitrogen (NO(3) (-)-N) pollution. Nitrate is considered a potential pollutant because its excess application can move into streams by runoff and into groundwater by leaching. The nitrate concentration in groundwater increases more than 3-fold times after fertilization and it contaminates groundwater as a result of the application of excess fertilizers for a long time. Soil texture refers to the relative proportion of particles of various sizes in a given soil and it affects the water permeability or percolation rate of a soil. Coarser soils have less retention than finer soils, which in the case of NO(3) (-)-N allows it to leach into groundwater faster, so there is positive relationship between the percentage of sands and NO(3) (-)-N concentration in groundwater wells. This study aimed to estimate the effect of soil texture on NO(3) (-)-N content in groundwater. Optical reflectance data obtained by remote sensing was used in this study. Our hypothesis was that the quantity of nitrogen leached into groundwater through loam was higher than through clay. Nakhon Pathom province, Thailand, was selected as a study area where the terrain is mostly represented by a flat topography. It was found that classified LANDSAT images delineated paddy fields as covering 29.4% of the study area, while sugarcane covered 10.4%, and 60.2% was represented by "others". The reason for this classified landuse was to determine additional factors, such as vegetation, which might directly affect the quantity of NO(3) (-)-N in soil. Ideally, bare soil would be used as a test site, but in fact, no such places were available in Thailand. This led to an indirect method to estimate NO(3) (-)-N on various soil textures. Through experimentation, it was found that NO(3) (-)-N measured through the loam in sugarcane (I = 0.0054, p < 0.05) was lower than clay represented by paddies (I = 0.0305, p < 0.05). This had a significant negative impact on the assumption. According to the research and local statistical data, farmers have always applied an excess quantity of fertilizer on paddy fields. This is the main reason for the higher quantity of NO(3) (-)-N found in clay than loam in this study. This case might be an exceptional study in terms of quantity of fertilizers applied to agricultural fields.

Keywords: Geographic Informationc Systems (GIS); groundwater; nitrates; remote sensing; soil texture; spatial autocorrelation.

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Figures

Figure 1.
Figure 1.
Study area in Nakhon Pathom province, Thailand.
Figure 2.
Figure 2.
The false color composite of LANDSAT imagery data (432) of Nakhon Pathom, Thailand.
Figure 3.
Figure 3.
Main landuses of the study area in Nakhon Pathom in 2010.
Figure 4.
Figure 4.
Map of soil texture classes in the study site.
Figure 5.
Figure 5.
Map of soil pH classes in the study site.
Figure 6.
Figure 6.
Location of groundwater wells.
Figure 7.
Figure 7.
Surface results from several interpolation methods, darker colors mean higher NO3-N content in groundwater.
Figure 8.
Figure 8.
Nitrate interpolated by Kriging employing Gaussian.
Figure 9.
Figure 9.
Spatial autocorrelation analysis of NO3-N.
Figure 10.
Figure 10.
The spectral reflectance value and layer classes.
Figure 11.
Figure 11.
Location of groundwater monitoring stations showing nitrate concentration (mg/L).
Figure 12.
Figure 12.
Effects of nitrate concentration in groundwater on the accuracy of the spatial interpolation methods (Kriging-Gaussian) compared in the average soil pH from soil unit.
Figure 13.
Figure 13.
Combination of landuse crops and NO3-N concentration from Kiginging-Gaussian interpolation.
Figure 14.
Figure 14.
Pixel distribution from spectral extraction analysis.

References

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