Delineation of Groundwater Potential Zone on Brantas Groundwater Basin

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Delineation of Groundwater Potential Zone on Brantas Groundwater Basin Andi Rachman Putra 1, Ali Masduqi 2 1,2 Departement of Environmental Engineering, Sepuluh Nopember Institute of Technology, Indonesia 1 andi.rachmanp@gmail.com 2 masduqi@its.ac.id Abstract Groundwater is an important source of water for domestic, agricultural and industrial uses. Surface water shortages increased reliance on groundwater as an alternative water source. This study uses the combination between remote sensing and geographic information system to create groundwater potential zone map of Brantas Groundwater Basin. Groundwater potential zone define the availability of groundwater in a particular area. Based on the produced potential map, more than half of the study area fall under moderate potential zone. Keywords Groundwater, Remote Sensing, Geographic Information System, Groundwater Basin, Groundwater Potential Zone I. INTRODUCTION Groundwater is an important source of water for domestic, agricultural and industrial uses. High population density, uneven water distribution, high demand, economic development, changing climate and other causes led to an increase of consumption and shortages of surface water. This surface water shortages causes increased reliance on groundwater. Therefore, it is important to thoroughly understand the groundwater resources for its sustainable development [1]. Groundwater assessment, modeling and management are difficult due to the lack of in-situ observation, especially in zones where only sparse surveillance infrastructure exist. In these environments, generally only a limited number of in-situ measurements are available. Whereas groundwater models need temporal and spatial distribution for data input and calibration. If such data are not available, the models cannot play a relevant role in decision support because the inaccuracy of this models [2]. The term groundwater potential indicated the availability of groundwater in a particular area. A variety of techniques can be used to provide information about its potential occurrence, directly or indirectly [3]. Integrated remote sensing and geographic information system (GIS) are widely used in groundwater mapping. Locating potential groundwater targets is becoming more convenient and cost-effective. Remotely sensed based groundwater exploration has made it feasible to explore the areas with limited human access, for the wide visual range, short time cycle and increasing spatial resolution [4]. GIS application have been utilized for purposes related to water resources and hydrology [5]. Creating connection between multiple parameters obtained from satellite imagery and secondary data is an important process in groundwater exploration. GIS is a technology that can be used to compile these data [6]. Based on the above explanation, remote sensing and GIS can be used to produce groundwater potential zone map. Satellite imagery used to obtain multiple parameters related to groundwater. These parameters and secondary data are compiled using GIS. This groundwater potential zone map can be used as information in decision making related to groundwater management. II. MATERIALS AND METHODS The aim of this study was to create groundwater potential zone map of Brantas groundwater basin in Indonesia. Materials used in this study are as follows: Landsat 8 imagery, used to create land cover map and NDVI (normalized difference vegetation index) map. Digital elevation model (DEM), used to create slope map. Daily rainfall data, used to create isohyet map. Drainage system data, used to create drainage density map. Geological map. Soil map. Groundwater potential zone map created using 7 parameters, where each parameter has its own sub-parameter. Scores are assigned to each parameter and sub-parameter based on previous study and literature review. Scores used in this study are presented in table 1 58

TABLE I PARAMETERS AND ASSIGNED SCORES No. Parameter Score Sub-parameter Score 1 Geology 7 Limestone 4 Clay deposit and sand 3 Silt 3 Clay deposit 3 Claystone and sandstone 2 Volcanic rock 1 2 Drainage Density 7 < 1,5 5 1,5 3,0 4 3,0 4,5 3 4,5 6,0 2 >6,0 1 3 Soil 6 Rapid 4 Moderately rapid 3 Moderate 2 Moderately slow 1 4 Annual rainfall 5 >2.75 mm/year 5 2.5 2.75 mm/year 4 2.25 2.5 mm/year 3 2.00 2.25 mm/year 2 <2.00 mm/year 1 5 Slope 5 0 1% 5 1 3% 4 3 5% 3 5 10% 2 >10% 1 6 Land cover 4 Dense vegetation 5 Vegetation 4 Water bodies 3 Barren land 2 Built-up land 1 7 NDVI 2 >0,4 5 0,3 0,4 4 0,2 0,3 3 0,1 0,2 2 <0,1 1 III. RESULT AND DISCUSSION Seven parameters are used for the creation of ground water potential map in form of thematic maps. Details of all the thematic maps and its relevancies to groundwater are discussed in the following sections: A. Geology The rock type of any area has a significant effect on the groundwater availability and its recharge [1]. The ability of water to flow from surface to underground influenced by the rock type of an area [7]. Based on the Geological Map of Indonesia, Brantas Groundwater Basin has a diverse type of rocks. Most of its area, that is 48,50% are dominated by volcanic rocks. The geological thematic map of Brantas Groundwater Basin can be seen in figure 1. B. Drainage Density Drainage density is defined as the closeness of the spacing of stream channels [3]. Drainage basins with high drainage densities indicate that a large proportion of the precipitation goes as runs off. On the other hand, low drainage densities indicate high rainfall infiltration. Low drainage density value is more favourable for high groundwater potential and assigned higher score [8]. 31,84% of study area has low drainage density. The drainage density thematic map of Brantas Groundwater Basin can be seen in figure 2. 59

Fig. 1 Geological thematic map of Brantas Groundwater Basin Fig. 2 Drainage density thematic map of Brantas Groundwater Basin C. Soil Soil plays an important role in groundwater mapping, where each soil type has a different permeability. Soil with high permeability cause rapid rate of infiltration, allowing more rainwater to reach groundwater table at a faster rate [8]. Based on Soil Map of Indonesia, soil type on Brantas Groundwater Basin has 4 permeability class. The most dominant permeability class is moderately slow, which cover 65,96% of the study area. The soil thematic map of Brantas Groundwater Basin can be seen in figure 3. D. Isohyet Rainfall has the major contribution to recharge the ground sources. It determines the amount of water that would be available to infiltrate into the groundwater system [9]. Annual rainfall data was interpolated using kriging method to produce isohyet thematic map. The amount of rainfall on Brantas Groundwater Basin range between 1.955 to 2.400 mm/year, with eastern part of the area receives the largest amount of rainfall. The isohyet thematic map was categorised into five classes, with higher score is given to the area with higher rainfall due to higher recharge possibility. The isohyet thematic map of Brantas Groundwater Basin can be seen in figure 4. 60

Fig. 3 Soil thematic map of Brantas Groundwater Basin Fig. 4 Isohyet thematic map of Brantas Groundwater Basin E. Slope The gradient of slope is one of the factors that directly influence the infiltration of rainfall [1]. Steeper slopes generate less recharge because water runs rapidly off the surface during rainfall, allowing insufficient time to infiltrate the surface and recharge the saturated zone [8]. The slope map of the study area was derived from SRTM DEM and was categorised into five classes. Area with minimum slope range is given highest score while the class having maximum slope is assigned lowest weight due to relatively high run-off which indicates the possibility of poor groundwater availability. The slope thematic map of Brantas Groundwater Basin can be seen in figure 5. F. Land Use Land use/land cover is a significant factor affecting recharge processes. Vegetation retards the surface runoff, thus increases water detention time and enhances infiltration. Built-up area also retards rainfall infiltration but prevent recharged water to reach groundwater reservoirs [8]. Landsat 8 imagery is used for the identification of land cover of the study area. The land cover thematic map of Brantas Groundwater Basin can be seen in figure 6. 61

Fig. 5 Slope thematic map of Brantas Groundwater Basin Fig. 6 Land cover thematic map of Brantas Groundwater Basin G. NDVI NDVI (Normalized Difference Vegetation Index) is used to obtain vegetation index parameter. Vegetation index is an estimation of vegetation health. NDVI is calculated from multispectral information as normalized ratio between the red and near infrared bands [10]. NDVI is regarded as the rough estimation of vegetation amount present and groundwater prospect over the space [8]. Higher NDVI values increase possibility of groundwater prospect, therefore, assigned more weight. The NDVI thematic map of Brantas Groundwater Basin can be seen in figure 7. H. Groundwater Potential Zone Scores for each parameter and sub-parameter as detailed in Table 1 are assigned for all thematic maps. Weighted sum method is used for generating Groundwater Potential Zone Map. The Groundwater Potential Zone Map of the study area was divided into 5 zones representing high, moderately high, moderate, moderately low and low groundwater potential. It is found that most of the study area, which cover 52,24% (5.219,37 km 2 ) of the total area fall under moderate groundwater potential zone. 27,91% (2.788,42 km 2 ) of study area fall under moderately high potential zone and 17,72% (1.770,10 km 2 ) of study area fall under moderately low potential zone. Only 1,49% (149,05 km 2 ) and 0,64% (63,44 km 2 ) of study area fall under high and low potential zone respectively. The Groundwater Potential Zone Map of Brantas Groundwater Basin can be seen in figure 8. 62

Fig. 7 NDVI thematic map of Brantas Groundwater Basin Fig. 8 Groundwater Potential Zone Map of Brantas Groundwater Basin IV. CONCLUSIONS In this study, Groundwater Potential Zone Map of Brantas Groundwater Basin are delineated using remote sensing and geographic information system. Various thematic maps such as geology, drainage density, soil, isohyet, slope, land use and NDVI were prepared and integrated for delineation process. Scores are assigned to each thematic map based on its relation to groundwater prospect. The delineated Groundwater Potential Zone Map was classified into five zones representing high, moderately high, moderate, moderately low and low groundwater potential. It is found that most of Brantas Groundwater Basin, which cover 52,24% of the total area fall under moderate groundwater potential zone. This Groundwater Potential Zone Map can be used as primary information in decision making related to groundwater management. ACKNOWLEDGMENT The authors are thankful to all parties who provided the necessary input data and all friends who gave supports throughout the process of this study. REFERENCES [1] S. Selvam, F. A. Dar, N. S. Magesh, C. Singaraja, S. Venkatramanan, and S. Y. Chung, Application of remote sensing and GIS for delineating groundwater recharge potential zones of Kovilpatti Municipality, Tamil Nadu using IF technique, Earth Science Informatics, vol. 9, pp. 137-150, 2016. 63

[2] H. C. Montecino, G. Staub, V. G. Ferreira, and L. B. Parra, Monitoring Groundwater Storage in Northen Chile Based on Satellite Observations and Data Simulation, Boletim de Ciências Geodésicas, vol. 22, pp. 1-15, 2016. [3] R. Agarwal, and P. K. Garg, Remote Sensing and GIS Based Groundwater Potential & Recharge Zones Mapping Using Multi-Criteria Decision Making Technique, Water Resources Management, vol. 30, pp. 243-260, 2016. [4] H. Duan, Z. Deng, F. Deng, and D. Wang, Assessment of Groundwater Potential Based on Multicriteria Decision Making Model and Decision Tree Algorithms, Mathematical Problems in Engineering, 2016. [5] J. O. Lilly, A GIS Approach to Modeling Groundwater Levels in the Mississippi River Valley Alluvial Aquifer, ProQuest Dissertations Publishing, 2016. [6] H. P. Patra, S. K. Adhikari, and S. Kunar, Groundwater Prospecting and Management, 1st ed., Singapore: Springer Science+Business Media, 2016. [7] O. A. Mekki, and N. E. Laftouhi, Combination of a geographical information system and remote sensing data to map groundwater recharge potential in arid to semi-arid areas: the Haouz Plain, Morocco, Earth Science Informatics, vol. 9, pp. 465-479, 2016. [8] U. Mandal, S. Sahoo, S. B. Munusamy, A. Dhar, S. N. Panda, A. Kar, and P. Mishra, Delineation of Groundwater Potential Zones of Coastal Groundwater Basin Using Multi-Criteria Decision Making Technique, Water Resources Management, vol. 30, pp. 4293-4310, 2016. [9] Y. Razandi, H. R. Pourghasemi, N. S. Neisani, and O. Rahmati, Application of analytical hierarchy process, frequency ratio, and certainty factor models for groundwater potential mapping using GIS, Earth Science Informatics, vol. 8, pp. 867-883, 2015. [10] J. Xue, and B. Su, Significant Remote Sensing Vegetation Indices: A Review of Developments and Applications, Journal of Sensors, 2017. 64