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International Journal of Modern Engineering Research (IJMER)
                 www.ijmer.com            Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645


              Determination of Optimum Site for Artificial Recharge Aided
               Geographical Information System (GIS) & Logical Overlay
                       Function (Case Study: Sarpaniran Plain)
          Ali Liaghat1, Karim Hejazi Jahromi2, Naeem Shahidi3, Seyed Amir Shamsnia4
                   1,4
                     Department of Water Engineering, Shiraz Branch, Islamic Azad University, Shiraz, Iran.
   2,3
         Post Graduate Student of Water Engineering and Member of young researcher’s club, Shiraz Branch, Islamic Azad
                                                   University, Shiraz, Iran.

ABSTRACT: In dry and semi-dry regions which face acking of water, using flood is one of the suitable solutions to prevent
destruction of agricultural and pasture lands and recharge of ground water aquifers. In this study, flood distribution which
is the most common in Iran was examined among various methods of artificial recharge. This study has been performed in
Sarpaniran catchment, located in Pasargad in Fars province, considered as one of the important agricultural, industrial and
residential centers. In order to flood distribution site selection, slope, surface infiltration, thickness of alluvium
(geomorphology), geology (formations) and lands application information layers have been used. Information layers were
combined based on intersect logical overlay function with Boolean logic in geographical information system (GIS) and
regions suitable for flood distribution were determined. The results of this study show that 2.3 percent of the total area of the
district is suitable for flood distribution. In examination of relation between using parameters and suitable places showed
that geological factor (formations) is the limiting factor. The results indicate that due to the existence of several properties
which are effective in site selection and required analysis with evaluated criteria and their continuous changes,
geographical information system is an efficient tool for management and using site data in this field.

KeyWords: Site location, artificial recharge, Flood Distribution, Sarpaniran Catchment, Intersect Logical Overlay
Function, Geographical Information System (GIS)

                                                  I.    INTODUCTION
           Concerning climatic and geographical conditions, a vast area of Iran includes dry and semi-dry regions in a way that
74% of the country has annual rainfall less than 250mm. In fact, due to lack of precipitation, its unbalanced distribution
regarding time and place and also inexistence of permanent rivers to provide water requirement in dry and semi-dry regions,
exploitation From groundwater resources is the most certain resource for water supply in these regions and done in a vast
area (12). Therefore, groundwater resources are considered as economical and social development factors in dry and semi-
dry regions (17). Helping the increment of groundwater supplies is one of the useful ways in providing required water of
various parts, especially in dry and semi-dry regions and confronting drought crisis.
           Recharging ground waters is possible in natural and artificial ways. Physical (natural) recharge of a region is made
by water infiltration resulted from precipitations inside the ground, infiltration through river aquifers or through underground
flows. Whereas water supply is a main factor of the development of a region and physical supply cannot meet needs, thus
artificial recharge has been developed (8,10, 4). Site selection of artificial recharge systems, specially flood distribution, is
the fundamental principles of making these systems. Selecting the location based on scientific and natural facts plays the
most important role in the stability and application of these systems in the way of realizing relevant objectives (3, 19). To
prevent from problems due to the accumulation of sediments and increase of useful life of design and more efficiency of
system regarding to the control of flood and achievement of considered objectives, site selection should be precisely made
considering return period flood and its mass, size, severity, rainfall distribution, flood quality, soil condition, geology
specifications, land slope, depth of groundwater aquifer, … (12).
           In a research for the examination of ground waters potential qualitatively and quantitatively by using GIS and RS,
simple and weighted models were used. In this study information layers of the land’s shape, geology, faults, waterway,
recharge condition map, compaction of materials and soil type were used and finally have determined regions with
groundwater potential and also regions suitable for ground waters artificial recharge. Results of this study show that remote
sensing (RS) and GIS have high capability for the qualitative and quantitative examination of ground waters and
determination of artificial recharge regions (18). In a research the application of Boolean Logic model in geographical
information system with the aim of natural resources management in Eshkanan, Lamerd desert region was done. In this
study, AND and OR operators of Boolean model have been used and after combining layers and different programs model of
natural resources comprehensive management in deserts, suitable areas were recognized and categorized (6).
           In another study capability and advantage of geographical information system and remote sensing emphasized as an
acceptable solution for decreasing expenses in site selection of suitable regions for artificial recharge of aquifers (9). Using
effective information layers in recharge , such as topography, surface infiltration, alluvium thickness, quality of ground water
and lands usage with Boolean and Fuzzy models, ground water artificial recharges selection in Shoor desert, in geographical
information system and far-distance examination were done. The results has been shown that nearly 5 percent of the studied
region is suitable and 19 percent is almost suitable for groundwater artificial recharge (3). In a research using GIS and RS
techniques, uitable site selection for artificial recharge of ground water resources of Semnan desert was examined and the
results showed that using GIS and RS is an efficient tool for finding place for artificial recharge of ground water (9). In a
                                                   www.ijmer.com                                                     4111 | Page
International Journal of Modern Engineering Research (IJMER)
               www.ijmer.com             Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645
study, Geo statistical models for estimation of transferability and site selection of flood distribution maps, using
transferability and special capacity data were compared. Their result indicate that Co Kriging method is a suitable method of
estimation when correlation coefficient is greater than 0.7(7). Using GIS techniques for determining proper regions for
artificial recharge of coastal aquifers in the south of Iran a research was done and the results shown that about 12% of the
analyzed region is suitable and 8% is relatively suitable for aquifers artificial recharge (1). In another research capability of
artificial recharges of ground waters was addressed by using GIS and economical and environmental aspects (11). Therefore,
the aim of this research is studying and determining the most suitable place for artificial recharge designs and places for
flood distribution and artificial recharge bed as well as studying the relation between different parts of the earth and suitable
regions for ground waters artificial recharge.

                                             II.      Materials and Methods
Studying Region: The studying limitation is Sarpaniran plain. This region has been located in the distance of 120km. east-
northwards of Shiraz and 12 km. of east-northwards of Saadatshahr in Pasargad, Fars province. Sarpaniran plain is in the
limitation of 53°09´ to 53°30´ east longitude and 29°52´ to 30°09´ north latitude. The area of this region is 47288 hectors
and around 31663.24 m3 in a year water harvesting, is considered as an important agricultural, industrial and residential
center with about 90% water consumption in agriculture (figure 1).




                                     Figure 1: Geographical situation of Studying Region

For physical (natural) and topographic evaluation in the manner of aquifer hydrologic specially temporary water supply due
to rainfall and its speed to the out of catchment through river system, Physical specifications of Sarpaniran catchment is
observed (table 1).

                    Physical                               Timeof
                                       Circle Ratio                           Form Factor           Gravelius
                  Specifications                         Concentration
                      level                0.34              6.35                 0.29                1.69
                                   Table 1: Physical Specifications of Sarpaniran Catchment

          For site selection of suitable regions for ground water artificial recharge through flood distribution, evaluating
indexes were selected in site selection. In this research 5 parameters (slope, surface infiltration, geomorphology, geology,
and lands application) are analyzed and selected among effective factors in site selection of suitable regions for artificial
recharge through flood distribution. Flood distribution site selection operation performed by using GIS and logical common
method (common logical overlay) in Sarpaniran plain with the area of 47288 hectors and after throwing on four information
layers of slope, surface infiltration, geomorphology and geology and suitable sites were identified. Then, corresponded with
lands application information layer and those regions where had application limitation separated and the best regions for
flood distribution were determined.
Region slope map: To prepare slope map, digital elevation model (dem) was used. In this research elevation contour lines of
digital topography maps have been used as a primary data to make digital elevation model. Using digital elevation model,
the slope map of catchment plain in GIS environment was prepared based on points’ elevation in the earth digital model and
their distance from each other, slope map of the region on percent (figure 2). The area and percent of slope of each class has
been also presented (table 2).

                         Table 2: Area and percentage of area of each slope class in Sarpaniran plain
                                           Classes range
                      Slope class                                 Area (Hectare)          Area (Percent)
                                             (Percent)
                          apt                  0-3                    11163.4                  23.61
                         inapt                  >3                   36117.94                  76.39




                                                   www.ijmer.com                                                     4112 | Page
International Journal of Modern Engineering Research (IJMER)
               www.ijmer.com                Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645




                                             Figure 2: Slope map of Sarpaniran plain

Surface Infiltration Map: To prepare surface infiltration map by field operation, 17 points were selected for measuring the
soil penetration (filtration) and double-ring method was used. The best method for variable interpolation is the one which has
the least RMS. In this research the best interpolation method is Kriging model of circular type with the RMS equal to 7.876
(table 4). Thus, to convert point map to raster map the same interpolation was used. Surface infiltration map has been shown
in figure 3. The extent and percent of area of each infiltration class was presented in table 3.

                                   Table 3: Area and percent of area of each infiltration class
                        Table 4: RMS results, interpolation methods for preparing surface infiltration map
 Interpolation method           RMS          Interpolation method         RMS           Interpolation method        RMS
   Inverse Distance                                 Kriging                                  CoKriging
                                10.14                                      8.19                                     12.67
      Weighting                                    (Gaussian)                              (pent spherical)
  Global Polynomial                                 Kriging                                  CoKriging
                                14.47                                      8.53                                     12.61
     Interpolation                            (rational quadratic)                          (exponential)
  Local Polynomial                                  Kriging                                  CoKriging
                                12.69                                     50.93                                     12.67
     Interpolation                                (hole effect)                              (Gaussian)

                                              Classes range               Area                     Area
                     Infiltration class
                                                 (mm/hr)                (Hectare)                (Percent)
                            apt                   0 - 25                41490.27                   87.74
                           inapt                   > 25                  5797.03                   12.26
                                                    Kriging                                    CoKriging
Radial Basis Functions             9.19                                   30.57                                     12.58
                                                  (k - Bessel)                           (rational quadratic)
         Kriging                                    Kriging                                    CoKriging
                                   7.18                                   51.45                                     11.34
        (circular)                                (j - Bessel)                               (hole effect)
         Kriging                                    Kriging                                    CoKriging
                                   7.98                                    36.3                                     12.67
       (spherical)                                  (stable)                                  (k - Bessel)
         Kriging                                  CoKriging                                    CoKriging
                                   8.04                                   12.68                                     11.65
    (tetra spherical)                              (circular)                                 (j - Bessel)
        Kirging                                   CoKriging                                  CoKriging
                                   8.08                                   12.67                                     12.67
    (pent spherical)                              (spherical)                                 (stable)
        Kriging                                    CoKriging
                                   8.61                                   12.67
     (exponential)                              (tetraspherical)




                                                    www.ijmer.com                                                 4113 | Page
International Journal of Modern Engineering Research (IJMER)
                www.ijmer.com            Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645




                                     Figure 3: Surface Infiltration Map of Sarpaniran plain

  Geomorphology Map: First, in order to provide the alluvium thickness plan concerning the region’s area 35 well visited
  provided by Fars Regional Water Organization in 2010 were used. Next, for preparing raster plan from point plan, Kriging
  method, Gaussian type with RMS equal to 5.105 was chosen (table 6). Alluvium thickness plan has been shown in figure 4.
  Area extent and percentage of each alluvium thickness class was presented in table 5 as well.

                              Table 5- Area and area percentage of each alluvium thickness class
                Alluvium thickness class        Classes range (m)         Area (Hectare)         Area (Percent)
                          apt                          0-8                  29157.79                 61.66
                         inapt                          >8                    18130                  38.34

                       Table 6- RMS results, interpolation methods for preparing alluvium thickness plan
Interpolation method       RMS         Interpolation method            RMS            Interpolation method          RMS
 Inverse Distance                              Kriging                                       CoKriging
                           6.8                                          5.1                                          5.62
     Weighting                               (Gaussian)                                  (pent spherical)
Global Polynomial                              Kriging                                       CoKriging
                           9.1                                         5.98                                          6.02
   Interpolation                        (rational quadratic)                              (exponential)
 Local Polynomial                              Kriging                                       CoKriging
                          5.71                                         6.14                                          5.26
   Interpolation                            (hole effect)                                   (Gaussian)
    Radial Basis                               Kriging                                       CoKriging
                          5.12                                         5.19                                          5.83
      Functions                              (k - Bessel)                              (rational quadratic)
       Kriging                                 Kriging                                       CoKriging
                          5.63                                         6.18                                          6.54
      (circular)                             (j - Bessel)                                  (hole effect)
       Kriging                                 Kriging                                       CoKriging
                          5.59                                         5.22                                          5.24
     (spherical)                               (stable)                                     (k - Bessel)
       Kriging                               CoKriging                                       CoKriging
                          5.61                                         5.56                                          6.56
  (tetraspherical)                            (circular)                                    (j - Bessel)
       Kirging                               CoKriging                                       CoKriging
                          5.63                                         5.59                                          5.34
  (pent spherical)                           (spherical)                                      (stable)
       Kriging                               CoKriging
                           6.1                                          5.6
   (exponential)                          (tetraspherical)




                                                   www.ijmer.com                                                  4114 | Page
International Journal of Modern Engineering Research (IJMER)
              www.ijmer.com             Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645




                                    Figure 4- Sarpaniran desert alluvium thickness class.

Lands Usage Plan: In order to produce this information layer, lands usage plan provided by Agricultural Jihad Department
of Pasargad, provided for the whole town in 2006 was used. For this purpose, results of combining information layers are
used for determining regions suitable for distribution of flood. The resulted plan was overlaid with lands usage plan to
separate the regions with usage limitations from areas suitable for flood distribution; because flood distribution operation
execution in agricultural lands and other regions with limitation is not possible due to social tensions. Lands usage plan has
been shown in Figure 5 and area and percentage of each usage was presented in table 7.

                     Table7- Area and percentage of pasture and non-pasture usage of Sarpaniran desert
                     Land class               User               Area (Hectare)         Area (Percent)
                         apt                 Pasture               23011.22                 48.66
                        inapt              non-pasture             24276.04                 51.34




                                        Figure5- Sarpaniran desert lands usage plan




                                                  www.ijmer.com                                                   4115 | Page
International Journal of Modern Engineering Research (IJMER)
              www.ijmer.com             Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645
Combining Information Layers & Data Analysis:
         Slop basic map, surface infiltration, geological and desert’s sediments thickness plans based on logical overlay
function, intersect type have been combined in GIS and the output plan resulted from this combination was overlaid once
without considering usage layer and once with land usage layer (Fig.6 & 7). Also, Suitable regions for artificial recharge by
flood distribution method have been shown in satellite image of the desert in figure 8




                Figure 6- Plan of regions suitable for flood distribution combined without lands usage layer




                  Figure7- Plan of regions suitable for flood distribution combined with lands usage layer




                      Figure 8- Sites suitable for artificial nourishment with flood distribution method.
                                                   www.ijmer.com                                                 4116 | Page
International Journal of Modern Engineering Research (IJMER)
               www.ijmer.com             Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645
hen results of relation between layers and sites suitable for flood distribution by omission of selected layers, amount of
suitable regions changes and the most important limiting factor in the area was determined. Since slop and usage information
layers made the least limitation in the final combining, started to omit other layers one by one and its results was presented in
figures 9 to 11.




                       Figure 9- Plan of regions suitable for flood distribution without geological layer
                       Figure10- Plan of regions suitable for flood distribution without infiltration layer




                   Figure11- Plan of regions suitable for flood distribution without alluvium thickness layer

                                           III.     Discussion & Conclusion
          Flood distribution site selection studies are of high importance because of being the basis of aquifer and ground
floor waters artificial nourishment studies. Since a group of condition (suitable and non-suitable) was used in this study and
because the goal is site selection, therefore, logical overlay function, intersect type was used. Flood distribution site selection
operation was done by using geographic Information System and logical intersect method in Sarpaniran desert with 47288
hectares area, after lapping 4 information layer of slop, surface infiltration, alluvium thickness and geology and suitable sites
were determined. It was then combined with lands usage layer and the regions with usage limitation were separated and the
best regions for flood distribution were determined. Geological plan of the region showed that Sarpaniran desert has variety
of formation in a way that the most and the least formation area of the desert related to kk formation equal to 33.79 percent
and Bakhtiari formation with 0.09 percent form total area of the region. Quaternary formation is the important formation for
flood distribution which forms 12.05 percent of the district’s area.
          The results of this study showed that despite the fact that slop, lands usage and alluvium thickness layers are
suitable for artificial recharge in flood distribution method, since quaternary areas form a percentage of the total district and
other formations except Bakhtiari Congolmerate formation is not suitable in flood distribution view, it affects infiltration of
the district in a way that 12.26 percent of the district is among regions suitable for infiltration, for executing this operation.
So one could say that, geological factors (formations) and surface infiltration are among limiting factors which face such
plans with limitation. Ghermezcheshmeh (2000), Al-e-Sheikh (2002), Soltani (2002) and Noori (2003) all have determined
suitable sites for flood distribution using geographical information system which correspond with result of this study.


                                                    www.ijmer.com                                                     4117 | Page
International Journal of Modern Engineering Research (IJMER)
              www.ijmer.com             Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118       ISSN: 2249-6645
          In general, after combining 4 information layers of slop, geology, surface infiltration and alluvium thickness
without considering region’s land usage based on figure 6 the amount of suitable regions for flood distribution is 1162.03
hectares that forms around 2.46 percent of total of the district, however after combining plan of sites suitable for flood
distribution with the region’s land usage plan, based on figure 7 amount of suitable regions for flood distribution decreased
about 0.2 percent, it means reached an amount equal to 1088.32 hectares that forms 2.3 percent of the district. Thus from the
above combination it could be concluded that geological factor is the most limiting layer in determining regions suitable for
flood distribution and infiltration and alluvium thickness factors are the next limiting factors. In general, the most important
limiting factor in suitable lands class, related to alluvium thickness factor and in non-suitable lands class is related to
geological factor.

                                                         Resources
1-    Arasteh, P.D. and S.R. Vahhadj. Simulation of groundwater flow in an artificial recharge system. Proc. 8th
      International Conference on Water Resour. Manage., Isfahan, Iran, 1997. pp. 79 – 87.
2-    Asano, Takashi, Artificial recharge of groundwater, California states water resources pp. 69-96.
3-    Berger. D.L. Ground - water recharge through active sand dunes in northwestern Nevada. Water Resour. Bull. 1992.
      28(5) : 959-965
4-    Ghayoumian, J., Mohseni Saravi, M., Feiznia, S., Nouri, B. and Malekian, A., Application of GIS techniques to
      determine areas most suitable for artificial groundwater recharge in a coastal aquifer in southern Iran, Journal of
      Asian Earth Sciences, Volume 30, Issue 2, 2007. PP 364-374.
5-    Ghermezcheshme, B., and etal . Determination of Quaternary deposits of flood-prone areas. Ms C Thesis, (case study :
      Northeast of Esfahan).2000. pp. 128-131
6-    Hatefi Ardekani, A.H., and rezaee Rad, N., 2011. GIS and RS techniques for artificial recharge of groundwater
      resources located in Semnan plain. Seventh National Seminar on Watershed Management Sciences and Engineering.
7-    Hashemi Tangestani, M.,and Raoufat, M.R. Boolean logic models in GIS applications to natural resources management
      in arid region Ashknan of Fars. Conference Application of remote sensing and geographic information systems of
      deserts.2000. Pp 6
8-    Heydarpour, J. Artificial recharge of groundwater aquifers. Iran University Press. 1990. pp 226.
9     Jalalvand, A., Kallantari, N. and Keshavarzi, M.R.. Locate suitable sites for artificial recharge of groundwater using
      remote sensing and GIS. 10th Symposium of Geological Society of Iran. 2006
10-   Kiaheydari, J. The function of the Flood Plain aquifer recharges Moghar in Isfahan. Master thesis Irrigation and
      Drainage, College of Agriculture, Isfahan University of Technology.2003.
11-   Krishnomurthy, J., N. Kumar, V. Jayaraman & M. Manivel. An Approach to Demarcate Ground Water Potential Zones
      Thorough Remote Sensing and a Geographical Information System, INT. J. Remote Sensing, 17(10). 1998. 1867-1884
12-   Kousar, A., Artificial recharge of groundwater aquifers in the watershed extension methods. Olive Magazine. Volume
      46 & 47. 1985. PP 16-19 & 20-23.
13-   Mahdian, M.H,. Flooding problem and the need to exploit. First Workshop on management and utilization of water.
      Soil Conservatoin and Watershed Management Research Institute.1999.
14-   Noori, B., Designated areas for groundwater supply using remote sensing data and Geographic Information System.
      Master's thesis. University of Tehran.2003.
15-   Pedrero, F., Albuquerque, A., Marecos do Monte, A., Cavaleiro, V., Alarcón, A., Application of GIS-based multi-
      criteria analysis for site selection of aquifer recharge with reclaimed water, Resources, Conservation and Recycling,
      Volume 56, Issue 1, 2011. PP 105-116
16-   Ramalingam, M. and Santhakumar, A.R., Case study on artificial recharge using Remote Sensing and GIS. 2004.
17-   Rezaee, M., and Fakhr bahabadi, M.R., Location of the artificial recharge of groundwater using GIS and remote
      sensing in the Shurro Plains. 4th Conference of Applied Geology and the Environment. 2008.
18-   Salajeghe Tazraji, E.A., Dehloran plain hydrological modeling using remote sensing and GIS. Department of
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19-   Samani, N. and S. Behrooz. Optimal distribution of artificial recharge and its stability. Proc. 8th International
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20-   Soltani, M.J., Land evaluation in order to locate areas prone to flooding broadcast operations in a GIS environment.
      Master's thesis. K.N. Toosi University of Technology. 2002. pp 97.




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Determination of Optimum Site for Artificial Recharge Aided Geographical Information System (GIS) & Logical Overlay Function (Case Study: Sarpaniran Plain)

  • 1. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 Determination of Optimum Site for Artificial Recharge Aided Geographical Information System (GIS) & Logical Overlay Function (Case Study: Sarpaniran Plain) Ali Liaghat1, Karim Hejazi Jahromi2, Naeem Shahidi3, Seyed Amir Shamsnia4 1,4 Department of Water Engineering, Shiraz Branch, Islamic Azad University, Shiraz, Iran. 2,3 Post Graduate Student of Water Engineering and Member of young researcher’s club, Shiraz Branch, Islamic Azad University, Shiraz, Iran. ABSTRACT: In dry and semi-dry regions which face acking of water, using flood is one of the suitable solutions to prevent destruction of agricultural and pasture lands and recharge of ground water aquifers. In this study, flood distribution which is the most common in Iran was examined among various methods of artificial recharge. This study has been performed in Sarpaniran catchment, located in Pasargad in Fars province, considered as one of the important agricultural, industrial and residential centers. In order to flood distribution site selection, slope, surface infiltration, thickness of alluvium (geomorphology), geology (formations) and lands application information layers have been used. Information layers were combined based on intersect logical overlay function with Boolean logic in geographical information system (GIS) and regions suitable for flood distribution were determined. The results of this study show that 2.3 percent of the total area of the district is suitable for flood distribution. In examination of relation between using parameters and suitable places showed that geological factor (formations) is the limiting factor. The results indicate that due to the existence of several properties which are effective in site selection and required analysis with evaluated criteria and their continuous changes, geographical information system is an efficient tool for management and using site data in this field. KeyWords: Site location, artificial recharge, Flood Distribution, Sarpaniran Catchment, Intersect Logical Overlay Function, Geographical Information System (GIS) I. INTODUCTION Concerning climatic and geographical conditions, a vast area of Iran includes dry and semi-dry regions in a way that 74% of the country has annual rainfall less than 250mm. In fact, due to lack of precipitation, its unbalanced distribution regarding time and place and also inexistence of permanent rivers to provide water requirement in dry and semi-dry regions, exploitation From groundwater resources is the most certain resource for water supply in these regions and done in a vast area (12). Therefore, groundwater resources are considered as economical and social development factors in dry and semi- dry regions (17). Helping the increment of groundwater supplies is one of the useful ways in providing required water of various parts, especially in dry and semi-dry regions and confronting drought crisis. Recharging ground waters is possible in natural and artificial ways. Physical (natural) recharge of a region is made by water infiltration resulted from precipitations inside the ground, infiltration through river aquifers or through underground flows. Whereas water supply is a main factor of the development of a region and physical supply cannot meet needs, thus artificial recharge has been developed (8,10, 4). Site selection of artificial recharge systems, specially flood distribution, is the fundamental principles of making these systems. Selecting the location based on scientific and natural facts plays the most important role in the stability and application of these systems in the way of realizing relevant objectives (3, 19). To prevent from problems due to the accumulation of sediments and increase of useful life of design and more efficiency of system regarding to the control of flood and achievement of considered objectives, site selection should be precisely made considering return period flood and its mass, size, severity, rainfall distribution, flood quality, soil condition, geology specifications, land slope, depth of groundwater aquifer, … (12). In a research for the examination of ground waters potential qualitatively and quantitatively by using GIS and RS, simple and weighted models were used. In this study information layers of the land’s shape, geology, faults, waterway, recharge condition map, compaction of materials and soil type were used and finally have determined regions with groundwater potential and also regions suitable for ground waters artificial recharge. Results of this study show that remote sensing (RS) and GIS have high capability for the qualitative and quantitative examination of ground waters and determination of artificial recharge regions (18). In a research the application of Boolean Logic model in geographical information system with the aim of natural resources management in Eshkanan, Lamerd desert region was done. In this study, AND and OR operators of Boolean model have been used and after combining layers and different programs model of natural resources comprehensive management in deserts, suitable areas were recognized and categorized (6). In another study capability and advantage of geographical information system and remote sensing emphasized as an acceptable solution for decreasing expenses in site selection of suitable regions for artificial recharge of aquifers (9). Using effective information layers in recharge , such as topography, surface infiltration, alluvium thickness, quality of ground water and lands usage with Boolean and Fuzzy models, ground water artificial recharges selection in Shoor desert, in geographical information system and far-distance examination were done. The results has been shown that nearly 5 percent of the studied region is suitable and 19 percent is almost suitable for groundwater artificial recharge (3). In a research using GIS and RS techniques, uitable site selection for artificial recharge of ground water resources of Semnan desert was examined and the results showed that using GIS and RS is an efficient tool for finding place for artificial recharge of ground water (9). In a www.ijmer.com 4111 | Page
  • 2. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 study, Geo statistical models for estimation of transferability and site selection of flood distribution maps, using transferability and special capacity data were compared. Their result indicate that Co Kriging method is a suitable method of estimation when correlation coefficient is greater than 0.7(7). Using GIS techniques for determining proper regions for artificial recharge of coastal aquifers in the south of Iran a research was done and the results shown that about 12% of the analyzed region is suitable and 8% is relatively suitable for aquifers artificial recharge (1). In another research capability of artificial recharges of ground waters was addressed by using GIS and economical and environmental aspects (11). Therefore, the aim of this research is studying and determining the most suitable place for artificial recharge designs and places for flood distribution and artificial recharge bed as well as studying the relation between different parts of the earth and suitable regions for ground waters artificial recharge. II. Materials and Methods Studying Region: The studying limitation is Sarpaniran plain. This region has been located in the distance of 120km. east- northwards of Shiraz and 12 km. of east-northwards of Saadatshahr in Pasargad, Fars province. Sarpaniran plain is in the limitation of 53°09´ to 53°30´ east longitude and 29°52´ to 30°09´ north latitude. The area of this region is 47288 hectors and around 31663.24 m3 in a year water harvesting, is considered as an important agricultural, industrial and residential center with about 90% water consumption in agriculture (figure 1). Figure 1: Geographical situation of Studying Region For physical (natural) and topographic evaluation in the manner of aquifer hydrologic specially temporary water supply due to rainfall and its speed to the out of catchment through river system, Physical specifications of Sarpaniran catchment is observed (table 1). Physical Timeof Circle Ratio Form Factor Gravelius Specifications Concentration level 0.34 6.35 0.29 1.69 Table 1: Physical Specifications of Sarpaniran Catchment For site selection of suitable regions for ground water artificial recharge through flood distribution, evaluating indexes were selected in site selection. In this research 5 parameters (slope, surface infiltration, geomorphology, geology, and lands application) are analyzed and selected among effective factors in site selection of suitable regions for artificial recharge through flood distribution. Flood distribution site selection operation performed by using GIS and logical common method (common logical overlay) in Sarpaniran plain with the area of 47288 hectors and after throwing on four information layers of slope, surface infiltration, geomorphology and geology and suitable sites were identified. Then, corresponded with lands application information layer and those regions where had application limitation separated and the best regions for flood distribution were determined. Region slope map: To prepare slope map, digital elevation model (dem) was used. In this research elevation contour lines of digital topography maps have been used as a primary data to make digital elevation model. Using digital elevation model, the slope map of catchment plain in GIS environment was prepared based on points’ elevation in the earth digital model and their distance from each other, slope map of the region on percent (figure 2). The area and percent of slope of each class has been also presented (table 2). Table 2: Area and percentage of area of each slope class in Sarpaniran plain Classes range Slope class Area (Hectare) Area (Percent) (Percent) apt 0-3 11163.4 23.61 inapt >3 36117.94 76.39 www.ijmer.com 4112 | Page
  • 3. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 Figure 2: Slope map of Sarpaniran plain Surface Infiltration Map: To prepare surface infiltration map by field operation, 17 points were selected for measuring the soil penetration (filtration) and double-ring method was used. The best method for variable interpolation is the one which has the least RMS. In this research the best interpolation method is Kriging model of circular type with the RMS equal to 7.876 (table 4). Thus, to convert point map to raster map the same interpolation was used. Surface infiltration map has been shown in figure 3. The extent and percent of area of each infiltration class was presented in table 3. Table 3: Area and percent of area of each infiltration class Table 4: RMS results, interpolation methods for preparing surface infiltration map Interpolation method RMS Interpolation method RMS Interpolation method RMS Inverse Distance Kriging CoKriging 10.14 8.19 12.67 Weighting (Gaussian) (pent spherical) Global Polynomial Kriging CoKriging 14.47 8.53 12.61 Interpolation (rational quadratic) (exponential) Local Polynomial Kriging CoKriging 12.69 50.93 12.67 Interpolation (hole effect) (Gaussian) Classes range Area Area Infiltration class (mm/hr) (Hectare) (Percent) apt 0 - 25 41490.27 87.74 inapt > 25 5797.03 12.26 Kriging CoKriging Radial Basis Functions 9.19 30.57 12.58 (k - Bessel) (rational quadratic) Kriging Kriging CoKriging 7.18 51.45 11.34 (circular) (j - Bessel) (hole effect) Kriging Kriging CoKriging 7.98 36.3 12.67 (spherical) (stable) (k - Bessel) Kriging CoKriging CoKriging 8.04 12.68 11.65 (tetra spherical) (circular) (j - Bessel) Kirging CoKriging CoKriging 8.08 12.67 12.67 (pent spherical) (spherical) (stable) Kriging CoKriging 8.61 12.67 (exponential) (tetraspherical) www.ijmer.com 4113 | Page
  • 4. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 Figure 3: Surface Infiltration Map of Sarpaniran plain Geomorphology Map: First, in order to provide the alluvium thickness plan concerning the region’s area 35 well visited provided by Fars Regional Water Organization in 2010 were used. Next, for preparing raster plan from point plan, Kriging method, Gaussian type with RMS equal to 5.105 was chosen (table 6). Alluvium thickness plan has been shown in figure 4. Area extent and percentage of each alluvium thickness class was presented in table 5 as well. Table 5- Area and area percentage of each alluvium thickness class Alluvium thickness class Classes range (m) Area (Hectare) Area (Percent) apt 0-8 29157.79 61.66 inapt >8 18130 38.34 Table 6- RMS results, interpolation methods for preparing alluvium thickness plan Interpolation method RMS Interpolation method RMS Interpolation method RMS Inverse Distance Kriging CoKriging 6.8 5.1 5.62 Weighting (Gaussian) (pent spherical) Global Polynomial Kriging CoKriging 9.1 5.98 6.02 Interpolation (rational quadratic) (exponential) Local Polynomial Kriging CoKriging 5.71 6.14 5.26 Interpolation (hole effect) (Gaussian) Radial Basis Kriging CoKriging 5.12 5.19 5.83 Functions (k - Bessel) (rational quadratic) Kriging Kriging CoKriging 5.63 6.18 6.54 (circular) (j - Bessel) (hole effect) Kriging Kriging CoKriging 5.59 5.22 5.24 (spherical) (stable) (k - Bessel) Kriging CoKriging CoKriging 5.61 5.56 6.56 (tetraspherical) (circular) (j - Bessel) Kirging CoKriging CoKriging 5.63 5.59 5.34 (pent spherical) (spherical) (stable) Kriging CoKriging 6.1 5.6 (exponential) (tetraspherical) www.ijmer.com 4114 | Page
  • 5. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 Figure 4- Sarpaniran desert alluvium thickness class. Lands Usage Plan: In order to produce this information layer, lands usage plan provided by Agricultural Jihad Department of Pasargad, provided for the whole town in 2006 was used. For this purpose, results of combining information layers are used for determining regions suitable for distribution of flood. The resulted plan was overlaid with lands usage plan to separate the regions with usage limitations from areas suitable for flood distribution; because flood distribution operation execution in agricultural lands and other regions with limitation is not possible due to social tensions. Lands usage plan has been shown in Figure 5 and area and percentage of each usage was presented in table 7. Table7- Area and percentage of pasture and non-pasture usage of Sarpaniran desert Land class User Area (Hectare) Area (Percent) apt Pasture 23011.22 48.66 inapt non-pasture 24276.04 51.34 Figure5- Sarpaniran desert lands usage plan www.ijmer.com 4115 | Page
  • 6. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 Combining Information Layers & Data Analysis: Slop basic map, surface infiltration, geological and desert’s sediments thickness plans based on logical overlay function, intersect type have been combined in GIS and the output plan resulted from this combination was overlaid once without considering usage layer and once with land usage layer (Fig.6 & 7). Also, Suitable regions for artificial recharge by flood distribution method have been shown in satellite image of the desert in figure 8 Figure 6- Plan of regions suitable for flood distribution combined without lands usage layer Figure7- Plan of regions suitable for flood distribution combined with lands usage layer Figure 8- Sites suitable for artificial nourishment with flood distribution method. www.ijmer.com 4116 | Page
  • 7. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 hen results of relation between layers and sites suitable for flood distribution by omission of selected layers, amount of suitable regions changes and the most important limiting factor in the area was determined. Since slop and usage information layers made the least limitation in the final combining, started to omit other layers one by one and its results was presented in figures 9 to 11. Figure 9- Plan of regions suitable for flood distribution without geological layer Figure10- Plan of regions suitable for flood distribution without infiltration layer Figure11- Plan of regions suitable for flood distribution without alluvium thickness layer III. Discussion & Conclusion Flood distribution site selection studies are of high importance because of being the basis of aquifer and ground floor waters artificial nourishment studies. Since a group of condition (suitable and non-suitable) was used in this study and because the goal is site selection, therefore, logical overlay function, intersect type was used. Flood distribution site selection operation was done by using geographic Information System and logical intersect method in Sarpaniran desert with 47288 hectares area, after lapping 4 information layer of slop, surface infiltration, alluvium thickness and geology and suitable sites were determined. It was then combined with lands usage layer and the regions with usage limitation were separated and the best regions for flood distribution were determined. Geological plan of the region showed that Sarpaniran desert has variety of formation in a way that the most and the least formation area of the desert related to kk formation equal to 33.79 percent and Bakhtiari formation with 0.09 percent form total area of the region. Quaternary formation is the important formation for flood distribution which forms 12.05 percent of the district’s area. The results of this study showed that despite the fact that slop, lands usage and alluvium thickness layers are suitable for artificial recharge in flood distribution method, since quaternary areas form a percentage of the total district and other formations except Bakhtiari Congolmerate formation is not suitable in flood distribution view, it affects infiltration of the district in a way that 12.26 percent of the district is among regions suitable for infiltration, for executing this operation. So one could say that, geological factors (formations) and surface infiltration are among limiting factors which face such plans with limitation. Ghermezcheshmeh (2000), Al-e-Sheikh (2002), Soltani (2002) and Noori (2003) all have determined suitable sites for flood distribution using geographical information system which correspond with result of this study. www.ijmer.com 4117 | Page
  • 8. International Journal of Modern Engineering Research (IJMER) www.ijmer.com Vol.2, Issue.6, Nov-Dec. 2012 pp-4111-4118 ISSN: 2249-6645 In general, after combining 4 information layers of slop, geology, surface infiltration and alluvium thickness without considering region’s land usage based on figure 6 the amount of suitable regions for flood distribution is 1162.03 hectares that forms around 2.46 percent of total of the district, however after combining plan of sites suitable for flood distribution with the region’s land usage plan, based on figure 7 amount of suitable regions for flood distribution decreased about 0.2 percent, it means reached an amount equal to 1088.32 hectares that forms 2.3 percent of the district. Thus from the above combination it could be concluded that geological factor is the most limiting layer in determining regions suitable for flood distribution and infiltration and alluvium thickness factors are the next limiting factors. In general, the most important limiting factor in suitable lands class, related to alluvium thickness factor and in non-suitable lands class is related to geological factor. Resources 1- Arasteh, P.D. and S.R. Vahhadj. Simulation of groundwater flow in an artificial recharge system. Proc. 8th International Conference on Water Resour. Manage., Isfahan, Iran, 1997. pp. 79 – 87. 2- Asano, Takashi, Artificial recharge of groundwater, California states water resources pp. 69-96. 3- Berger. D.L. Ground - water recharge through active sand dunes in northwestern Nevada. Water Resour. Bull. 1992. 28(5) : 959-965 4- Ghayoumian, J., Mohseni Saravi, M., Feiznia, S., Nouri, B. and Malekian, A., Application of GIS techniques to determine areas most suitable for artificial groundwater recharge in a coastal aquifer in southern Iran, Journal of Asian Earth Sciences, Volume 30, Issue 2, 2007. PP 364-374. 5- Ghermezcheshme, B., and etal . Determination of Quaternary deposits of flood-prone areas. Ms C Thesis, (case study : Northeast of Esfahan).2000. pp. 128-131 6- Hatefi Ardekani, A.H., and rezaee Rad, N., 2011. GIS and RS techniques for artificial recharge of groundwater resources located in Semnan plain. Seventh National Seminar on Watershed Management Sciences and Engineering. 7- Hashemi Tangestani, M.,and Raoufat, M.R. Boolean logic models in GIS applications to natural resources management in arid region Ashknan of Fars. Conference Application of remote sensing and geographic information systems of deserts.2000. Pp 6 8- Heydarpour, J. Artificial recharge of groundwater aquifers. Iran University Press. 1990. pp 226. 9 Jalalvand, A., Kallantari, N. and Keshavarzi, M.R.. Locate suitable sites for artificial recharge of groundwater using remote sensing and GIS. 10th Symposium of Geological Society of Iran. 2006 10- Kiaheydari, J. The function of the Flood Plain aquifer recharges Moghar in Isfahan. Master thesis Irrigation and Drainage, College of Agriculture, Isfahan University of Technology.2003. 11- Krishnomurthy, J., N. Kumar, V. Jayaraman & M. Manivel. An Approach to Demarcate Ground Water Potential Zones Thorough Remote Sensing and a Geographical Information System, INT. J. Remote Sensing, 17(10). 1998. 1867-1884 12- Kousar, A., Artificial recharge of groundwater aquifers in the watershed extension methods. Olive Magazine. Volume 46 & 47. 1985. PP 16-19 & 20-23. 13- Mahdian, M.H,. Flooding problem and the need to exploit. First Workshop on management and utilization of water. Soil Conservatoin and Watershed Management Research Institute.1999. 14- Noori, B., Designated areas for groundwater supply using remote sensing data and Geographic Information System. Master's thesis. University of Tehran.2003. 15- Pedrero, F., Albuquerque, A., Marecos do Monte, A., Cavaleiro, V., Alarcón, A., Application of GIS-based multi- criteria analysis for site selection of aquifer recharge with reclaimed water, Resources, Conservation and Recycling, Volume 56, Issue 1, 2011. PP 105-116 16- Ramalingam, M. and Santhakumar, A.R., Case study on artificial recharge using Remote Sensing and GIS. 2004. 17- Rezaee, M., and Fakhr bahabadi, M.R., Location of the artificial recharge of groundwater using GIS and remote sensing in the Shurro Plains. 4th Conference of Applied Geology and the Environment. 2008. 18- Salajeghe Tazraji, E.A., Dehloran plain hydrological modeling using remote sensing and GIS. Department of Geography, Tarbiat Modares University. 1998. 19- Samani, N. and S. Behrooz. Optimal distribution of artificial recharge and its stability. Proc. 8th International Conference on Rainwater Catchment Systems, Tehran, Iran, 1997. pp. 182 - 189 . 20- Soltani, M.J., Land evaluation in order to locate areas prone to flooding broadcast operations in a GIS environment. Master's thesis. K.N. Toosi University of Technology. 2002. pp 97. www.ijmer.com 4118 | Page