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International Refereed Journal of Engineering and Science (IRJES)
ISSN (Online) 2319-183X, (Print) 2319-1821
Volume 6, Issue 2 (February 2017), PP.01-06
www.irjes.com 1 | Page
Determination of Tigris Bismil Agricultural Plain’s Groundwater
Static Water Level (SWL) Changes Caused by Irrigation
Using GIS Technic.
Recep Çelik*
*
Department Of Civil Engineering, Dicle University, 21280, Diyarbakir, Turkey;
ABSTRACT: The unconscious use of groundwater in agricultural irrigation threatens the potential
and level of groundwater. So it is imperative to follow the groundwater Static Water Level (SWL)
change in places where watering with the groundwater is made. The reason for the study area Bismil
is that Bismil district of Diyarbakir entirely on agriculture and animal husbandry in the Upper Tigris
Basin. Tigris River goes through the middle of the Bismil plain. There are two kinds of agricultural
irrigation takes place in this region. The first, on the edge of the river Tigris fields during irrigation
pumping from River. In the latter the field which far areas from river are provided from groundwater
by wells more than last 15 years. However, consumption of more than feeding to bring this situation
poses a threat for the groundwater. For this reason, the region's groundwater changes are studied with
the data of water well the years between 1996 and 2011. Arc Info 10.2.1 programme Spatial Analysed
Extension used as GIS technic.
Keyword: Groundwater, GIS, Agricultural area, Upper Tigris Basin
I. INTRODUCTION
The importance of groundwater increases gradually as an alternative water source at the world. Due to
the increasing in the population and demand for drinking water, and the increased use of water for agriculture, in
addition, different threats of pollution for water resources, reduces the amount of water per capita.In addition to
the climatic changes caused by irregular rainfall regimes and some years of drought, especially in semi-arid
regions indicates serious problemsarising in the future.
According toUNESCO'S REPORT (2006), it is foreseen that in 2025, 1.8 billionpeople in the worldwill
experience water scarcity. It is reported that, in the last decade40% ofthe populationin approximately 80
countries it seemsthat the water demand will be insufficient to meet the needs (Bennett, 2000). Annual mean
precipitation in Turkey is 643 mm, which corresponds to 501 bm3
(billion m3
) of annual water volume in the
country. A volume of 274 bm3
water evaporates from water bodies and soils to atmosphere. 69 bm3
of volume of
water leaks into groundwater, whereas 28 bm3
is retrieved by springs from groundwater contributing to surface
water. Also, there are 7 billion m3
volume of water coming from neighbouring countries. Thus, total annual
surface runoffamounts to a volume of 193 bm3
of water. Including 41 (69-28) bm3
net discharging into
groundwater (covering safe yield extraction, unregistered extraction, emptying into the seas, and
transboundary), the gross (surface and groundwater) renewable water potential of Turkey is estimated as 234
bm3
. However, under current technical and economic constraints, annual exploitable potential has been
calculated as 112 bm3
of thenet water volume, as 95 bm3
from surface water resources, 3 bm3
from neighbouring
countriesand14 bm3
from groundwater safe yield (Nalbantoglu,U.,2006).
The River Tigris, which is the second-largest river in the western Asia, originates near Lake Hazar
(elevation 1150 m) in eastern Turkey. The Tigris is fed by several tributaries in Turkey. It forms the Turkish–
Syrian boundary for 32 km, and crosses into Iraq. From the Iraqi border up to Mosul, the river is bordered by
rolling hills on either side but is still confined to a deep valley in the Mosul area. Within Iraq, the Tigris has
several tributaries which contribute significantly to the water potential of the river (Altinbilek 2004).The total
length of the river isapproximately 1900 km, from which 523 km is within Turkey. It drainsa catchment area of
about 57,614 km2
(Akbulut 2009).
The irrigated agriculture is mostly performed by water wells in Bismil. According to TUIK (2011) data,
60,000 decares of cotton, 2,500 decares of tobacco are cultivated in Bismil. Besides, production of other field
crops also carried out using groundwater. Bismil District is in the domain of Batman Dam, Dicle Dam,
Pamukçay dam and inBaşlar dam’s irrigation project area (DVCSIM 2011). As these irrigation projects
completed then start activity the need to use groundwater will reduce.
The GIS technique, with field ground surveys, is well known as apowerful technique for groundwater
mapping in the world. Over the last few decades, the international scientific community has shown great interest
Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)...
www.irjes.com 2 | Page
in this topic and thus, many authors have used remote sensing and GIS techniques for groundwater prospecting
Sander, 1997; Procter et al.,2006; Sikdaret al., 2004;VanderPost, 2007; Dineshkumaret al., 2007; Celik,
R.,2015; Ozturk,M. and Celik,R.,2008;Chowdhury et al., 2010; Chawlaet al.; Jha et al., 2010. The reason for
choosing the study area as Bismil is that approximately all of the economic activities at Bismil, a district of the
Diyarbakir province, depend mainly on agriculture and animal husbandry in the Upper Tigris Basin. There are
two kinds of agricultural irrigation taking place in this region. The first is irrigation of the fields just on the
coasts of the Tigris River by pumping the water directly from the river during the irrigation session. In the latter
the fields which are far from the river are irrigated providing the water from the groundwater resources by wells
for more than the last 15 years. However, as the consumption is more than feeding of the groundwater resources
poses a serious threat for the groundwater resources. For this reason, the changes in the groundwater levels
studied using the data relevant to the water wells during the last 15 years. Bismil plain obviously good sample
that may show using groundwater for irrigation how affect groundwater level changes by year.
II. MATERIAL AND METHODS
2.1 Study Area’s Features
2.1.1 Geographic Structure:
The geographical location coordinates of Bismil district centre is 37°50'45'' N, 40°40'33'' E, and Bismil
is the second largest county in the province of Diyarbakir (Figure1). It is located in the South eastern Anatolia
region of Turkey. Settled on aflat land, it has fertile land of the Tigris plain. The Tigris River passes through
Bismil. There are slight hills to its north and south. The South-eastern Toros Mountains are located on the south
side of Bismil. Its distance from Diyarbakır is 55 kilometres; it has both the railway and highway of Diyarbakir-
Batman passing through it. Total area of Bismil district is 1748 km2
.
Figure 1. Bismil Urban Location map
2.1.2 Rivers and Lakes:
The Tigris River runs through Bismil, and many small and large streams and creeks flow into it. The
most important ones among these streams are Pamuk, Göksu, Kurmuşlu, Kuru, Ambar, Caferi andSalatstreams.
Not exactly blessed with many lakes, Bismil has only one, which is near the Çöltepe village.
2.1.3 Climate:
Bismil has a terrestrial climate. Its summers are dry and hot, and winters are cold and rainy. The dams
constructed around the sub-province in the recent years have altered its climate. The snow was remaining on the
ground for months before construction of the dams, but in the recent years there is not any snowfall at all.
Despite not experiencing frost, temperature goes below zero degrees Celsius during the months December and
January, and above 45 degrees in the summer. Especially during July and August the heat tends to get
unbearable (Bismil gov.tr, 2013). Average long term precipitation of Bismil is 447,9 mm(Table 1).
Table 1. Long term average Bismil precipitation (mm)(DVCSIM), 2011)
Dist./Month Jan Feb March Apr May June July Aug Sep Oc Nov Dec Total
Bismil 57,9 68,6 62,1 50 37,8 9,6 3,5 0,3 0,6 32,4 56,7 68,4 447,9
Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)...
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2.1.4 Bismil Population
The population of Bismil has shown a noticeable increase due to regional migration in the 1990s as it
isseen in Figure2. The population of Bismil shows a similar distribution as for those live in the rural areas and
those in the city centre, with a proportion above the average rate of Turkey. Thereasonfor this is the heavy
agricultural employment in the rural regions.
Figure 2. Bismil District Population Changes by years(TUIK 2013)
2.2 Methods
In the study, 316 wells drilled by public institutions such as DSİ, District Governorships, Special
Provincial Administration, as well as private persons for watering purposes between the years 1996-2011 have
been examined. The drilling data was ranked with the aid of Microsoft Excel software, and the coordinates have
been arrangedaccordingly. These data was run on the ARC Map software. The data that havebeen converted to
Shape (shp) format havebeen modelled through Spatial analyse. In the followingmaps, a basemap has been
prepared through “Open Street Maps and Contributes” found under the Arc Info software. UTM Datum 1950 37
has been used as projection. Static water level maps relevantto the years 1996-2000 (Figure 2), 2001-2004
(Figure 3), 2005-2008 (Figure 4), and 2009-2011 (Figure 5) have been obtained through all these processes.
Changes in the groundwater levelsrelevantto the nominatedyears have been detected usingthese maps. The
settlement examples and groundwater graphic changes of the Bismil districtand its villages have been drawn
(figures 7, 8 and 9) with these maps. In the light of this data, results have been obtained. Otherwise all term of
groundwater changes raster data had been analysed with spatial analyst Local cell statistics menu. Results figure
shows in figure 13.
III. RESULTS
Figure 3. 1996-2000 years Tigris Bismil Figure 4. 2001-2004 years Tigris Bismil Basin Basinstatic water
level map static water level map
0
20,000
40,000
60,000
80,000
100,000
120,000
140,000
1970 1975 1980 1985 1990 2000 2007 2008 2009 2010 2011
total
population
Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)...
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Figure 5. 2005-2008 years Tigris Bismil Figure 6. 2009-2011 years Tigris Bismil Basinstatic water
level map static water level map
Figure 7. Bismil Centre SWL changes Figure 8. North-West Region SWL changes
Figure 9. Bismil North Region SWL changes Figure 10.Bismil West Region SWL(changes)
0.0
10.0
20.0
30.0
40.0
50.0
60.0
70.0
80.0
1996-2000 2001-2004 2005-2008 2009-2011
staticwaterdepthfromground(m)
Bismil
Centre
0
10
20
30
40
50
60
70
80
1996-2000 2001-2004 2005-2008 2009-2011
staticwaterdepthfromground(m)
Işıklar
Serçeler
0
10
20
30
40
50
60
70
80
1996-2000 2001-2004 2005-2008 2009-2011
staticwaterdepthfromground(m)
Uğrak
0
10
20
30
40
50
60
70
80
1996-2000 2001-2004 2005-2008 2009-2011
staticwaterdepthfromground(m)
Ambar
Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)...
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Figure 11. Bismil South-East Region SWL changes Figure 12. Bismil South-East Region SWL changes
Figure 13. Bismil 1996-2001 terms mean SWL value changes
Following conclusions have been obtained from thematic maps groundwater changes are classified
relevant to urban centre (Figure 7), North-West(Figure 8), North (Figure 9), West(Figure 10), South, South-
East, East and South West region.
1. The groundwater levels in all other regions show a significant dropped. Even though it is known that
groundwater levels havesome small seasonal changes.
2. In the Bismil settlement area the static water levels have dropped by over 55-60 meters. Especially after the
year 2005, the groundwater levels have started todecrease increasingly. For example, in the
Türkmenhacivillage it has dropped from 4.8 meters in 1996-2000 to 15.1 meters the years between 2001-
2004.It has further dropped from 47 meters between 2005-2008 down to 103 meters between 2009-2011.
Such changes are alsofound in other areas of thesettlement as well. The main reasons for thiswere
theinsufficient precipitation during the years 2009-2011, and the use of thegroundwaterresourcesmore
thantheir feeding. It can also be claimed that the unauthorized water wells drilled in the area have an
importanteffect on these dramaticchanges in groundwater levels.The groundwater level in Central
Bismilthat was at 12 meters between the years1996-2000 decreased up to 73 meters betweenthe years 2009-
2011.The groundwater level in Işıklarvillage was 17 meters between the years1996-2000 has gone down to
73 meters between the years2009-2011.
3. From the 2000 years, rural and urban population of Bismil is steadily. Whereas as seen Figure 7-12
groundwater level change is decreased after 2005-2008 period sharply. So effect of population growth on
groundwater is little.
4. In Bismil region, 60,000 decares of cotton, 2,500 decares of tobacco are cultivated (TUIK 2011). These
crops needs more water. Besides, production of other field crops also carried out using groundwater. That
would be main effect of groundwater level decrease.According to DVCSIM 2013 report, In Bismil
groundwater used 0,92 hm3
/years water for drinking, 85.47 hm3
/year water for irrigation. While it seeding
Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)...
www.irjes.com 6 | Page
groundwater average is 31,25 hm3
/year. There is huge negative budge about groundwater consumption and
seeding. That would be main reason groundwater decrease.
IV. CONCLUSIONS
Groundwater level dropped average 50-60 meters in Bismil central, Northern and Western Region.
South, southwest and south-eastern regions of the groundwater static level dropped average 82 m (figure 13).
This change occurred especially after 2005 years. There would be main 3 factor effect the groundwater change;
population growth, climate effect on precipitation and groundwater use for irrigation unconscious. Population
and climate effect is very lowrather thangroundwater using for irrigation effect. So that the main reason of
groundwater level decrease is using water for irrigation unconscious in the semi arid region. Suggestions:In the
agricultural area groundwater use is must be under control. The using groundwater must be reducing at least
%70 for irrigation in the Bismil plain. Additionally special wateringprojects (GAP Projects) should be executed
as soon as possible. The need to use groundwater resources should be eliminated. In this manner the
groundwater resources can reach at abalanced acceptable levelby thetimepasses.
REFERENCES
[1]. Akbulut, E.N., Bayarı, S., Akbulut, A.Sahin, Y. S Rivers Of Turkey, In: K. Tockner,C., T., Robinson,
U.,Uehlinger (Eds.), Rivers Of Europa, Academic Press, New York,2009, Pp. 643–672
[2]. Altinbilek, D. (2004) Development And Management Of The Euphrates–Tigris Basin,Water Resources
Development,Vol. 20, No. 1, 15–33, March 2004
[3]. Bennett, 2000.A.J., Environmental Consequences Of Increasing Production: Some Current
Perspectives. Agric. Ecosys. Environ.82 (2000), Pp. 89–95.
[4]. Chawla, J. K., Khepar, S. D., Sondhi ,S. K. , Yadav, A. K.2010.Assessment Of Long-Term
Groundwater Behaviour In Punjab, India, Water International Vol. 35, No. 1, January, 63–77
[5]. Chowdhury, A., Jha, Metersk.,Chowdary, V.Meters, 2010.Delineation Of Groundwater Recharge
Zones And Identification Of Artificial Recharge Sites In West Medinipur District, West Bengal Using
Rs, Gis And Mcdm Techniques. Environmental Earth Sciences 59 (6), 1209–1222.
[6]. Çelik, R. 2015. “Temporal Changes In The Groundwater Level In The Upper Tigris Basin, Turkey,
Determined By A Gis Technique.” Journal Of African Earth Sciences 107: 134-143.
[7]. Dineshkumar, P.K., Gopinath, G., Seralathan, P., 2007.Application Of Remote Sensing And Gis For
The Demarcation Of Groundwater Potential Zones Of A River Basin In Kerala, Southwest Coast Of
India. International Journal Of Remote Sensing 28, 5583–5601.
[8]. Diyarbakır Valiliğiçevreveşehircilikilmüdürlüğü (Dvcsim), 2011.İl Çevre Durum Raporu-2011,
Diyarbakir.Available
Inttp://Www.Csb.Gov.Tr/Db/Ced/Editordosya/Diyarbakir_Icdr2011.Pdf[Accessed 17. 02.2014]
[9]. Diyarbakır Valiliğiçevreveşehircilikilmüdürlüğü (Dvcsim), 2013.İl Çevre Durum Raporu-2012,Pp
83.Diyarbakir (Turkish Report).Available In:
Http://Www.Csb.Gov.Tr/Db/Ced/Editordosya/Diyarbakir_Icdr2012.Pdf[Accessed 14. 03.2014]
[10]. Http://Www.Diyarbakir.Bel.Tr/Images/Diyarbakir2011.Jpg [Accessed 14.11.2013]
[11]. Http://Www.Bismil.Gov.Tr/Default_B0.Aspx?Content=193 [Accessed: 10/11/2013]
[12]. Nalbantoğlu,U., 2006.Dsi - State Hydraulıc Works And Water Database At Dsi. Available
From:Http://Www.Minenv.Gr/Medeuwi/Meetings/Conference.Of.The.Water.Directors.Athens.6&7-
11- 06_En/00/Dsi-Turkey.Pdf]
[13]. Procter,C., Comber, L., Betson, Meters, Buckley,D., Frost,A., Lyons,H., Riding,A., Voyce,K.,2006
Identifying Crop Vulnerability To Groundwater Abstraction: Modelling And Expert Knowledge In A
Gis, Journal Of Environmental Management 81, 296–306.
[14]. Öztürk, M., Çelik R., 2008, Diyarbakır Ovasıyeraltı Su Seviyeharitalarınıncoğrafikbilgisistemiiletesbiti
(Turkish Article), Tmmob 2.Su Politikalarıkongresi Cilt1 Sayı: 1shf: 125-133 Ankara
[15]. Sander, P., 1997. Water Well Sitting In Hard Rock Areas: Identifying Promising Targets Using A
Probabilistic Approach. Journal Of Hydrogeology 5, 32–43.
[16]. Sikdar, P.K.,Chakraborty, S., Enakshi, A., Paul, P.K., 2004. Land Use/Land Cover Changes And
Groundwater Potential Zoning In And Around Raniganj Coal Miningarea, Bardhamandistrict, West
Bengal – A Gis And Remote Sensing Approach. Journal Of Spatial Hydrology 4, 1–24
[17]. Vanderpost,C., Mcfarlane,M., 2007. Groundwater Investigation In Semi-Arid Developing
Countries,Using Simple Gis Tools To Facilitate Interdisciplinary Decision Making Under
Poorlymapped Conditions: The Boteti Area Of The Kalahari Region In Botswana, International Journal
Of Applied Earth Observation And Geoinformation 9 343–359
[18]. Unesco. 2006 Coping With Water Scarcity Astrategic Issue Andpriorityforsystem-
Wideactionftp://Ftp.Fao.Org/Agl/Aglw/Docs/Waterscarcity.Pdf

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Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL) Changes Caused by Irrigation Using GIS Technic.

  • 1. International Refereed Journal of Engineering and Science (IRJES) ISSN (Online) 2319-183X, (Print) 2319-1821 Volume 6, Issue 2 (February 2017), PP.01-06 www.irjes.com 1 | Page Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL) Changes Caused by Irrigation Using GIS Technic. Recep Çelik* * Department Of Civil Engineering, Dicle University, 21280, Diyarbakir, Turkey; ABSTRACT: The unconscious use of groundwater in agricultural irrigation threatens the potential and level of groundwater. So it is imperative to follow the groundwater Static Water Level (SWL) change in places where watering with the groundwater is made. The reason for the study area Bismil is that Bismil district of Diyarbakir entirely on agriculture and animal husbandry in the Upper Tigris Basin. Tigris River goes through the middle of the Bismil plain. There are two kinds of agricultural irrigation takes place in this region. The first, on the edge of the river Tigris fields during irrigation pumping from River. In the latter the field which far areas from river are provided from groundwater by wells more than last 15 years. However, consumption of more than feeding to bring this situation poses a threat for the groundwater. For this reason, the region's groundwater changes are studied with the data of water well the years between 1996 and 2011. Arc Info 10.2.1 programme Spatial Analysed Extension used as GIS technic. Keyword: Groundwater, GIS, Agricultural area, Upper Tigris Basin I. INTRODUCTION The importance of groundwater increases gradually as an alternative water source at the world. Due to the increasing in the population and demand for drinking water, and the increased use of water for agriculture, in addition, different threats of pollution for water resources, reduces the amount of water per capita.In addition to the climatic changes caused by irregular rainfall regimes and some years of drought, especially in semi-arid regions indicates serious problemsarising in the future. According toUNESCO'S REPORT (2006), it is foreseen that in 2025, 1.8 billionpeople in the worldwill experience water scarcity. It is reported that, in the last decade40% ofthe populationin approximately 80 countries it seemsthat the water demand will be insufficient to meet the needs (Bennett, 2000). Annual mean precipitation in Turkey is 643 mm, which corresponds to 501 bm3 (billion m3 ) of annual water volume in the country. A volume of 274 bm3 water evaporates from water bodies and soils to atmosphere. 69 bm3 of volume of water leaks into groundwater, whereas 28 bm3 is retrieved by springs from groundwater contributing to surface water. Also, there are 7 billion m3 volume of water coming from neighbouring countries. Thus, total annual surface runoffamounts to a volume of 193 bm3 of water. Including 41 (69-28) bm3 net discharging into groundwater (covering safe yield extraction, unregistered extraction, emptying into the seas, and transboundary), the gross (surface and groundwater) renewable water potential of Turkey is estimated as 234 bm3 . However, under current technical and economic constraints, annual exploitable potential has been calculated as 112 bm3 of thenet water volume, as 95 bm3 from surface water resources, 3 bm3 from neighbouring countriesand14 bm3 from groundwater safe yield (Nalbantoglu,U.,2006). The River Tigris, which is the second-largest river in the western Asia, originates near Lake Hazar (elevation 1150 m) in eastern Turkey. The Tigris is fed by several tributaries in Turkey. It forms the Turkish– Syrian boundary for 32 km, and crosses into Iraq. From the Iraqi border up to Mosul, the river is bordered by rolling hills on either side but is still confined to a deep valley in the Mosul area. Within Iraq, the Tigris has several tributaries which contribute significantly to the water potential of the river (Altinbilek 2004).The total length of the river isapproximately 1900 km, from which 523 km is within Turkey. It drainsa catchment area of about 57,614 km2 (Akbulut 2009). The irrigated agriculture is mostly performed by water wells in Bismil. According to TUIK (2011) data, 60,000 decares of cotton, 2,500 decares of tobacco are cultivated in Bismil. Besides, production of other field crops also carried out using groundwater. Bismil District is in the domain of Batman Dam, Dicle Dam, Pamukçay dam and inBaşlar dam’s irrigation project area (DVCSIM 2011). As these irrigation projects completed then start activity the need to use groundwater will reduce. The GIS technique, with field ground surveys, is well known as apowerful technique for groundwater mapping in the world. Over the last few decades, the international scientific community has shown great interest
  • 2. Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)... www.irjes.com 2 | Page in this topic and thus, many authors have used remote sensing and GIS techniques for groundwater prospecting Sander, 1997; Procter et al.,2006; Sikdaret al., 2004;VanderPost, 2007; Dineshkumaret al., 2007; Celik, R.,2015; Ozturk,M. and Celik,R.,2008;Chowdhury et al., 2010; Chawlaet al.; Jha et al., 2010. The reason for choosing the study area as Bismil is that approximately all of the economic activities at Bismil, a district of the Diyarbakir province, depend mainly on agriculture and animal husbandry in the Upper Tigris Basin. There are two kinds of agricultural irrigation taking place in this region. The first is irrigation of the fields just on the coasts of the Tigris River by pumping the water directly from the river during the irrigation session. In the latter the fields which are far from the river are irrigated providing the water from the groundwater resources by wells for more than the last 15 years. However, as the consumption is more than feeding of the groundwater resources poses a serious threat for the groundwater resources. For this reason, the changes in the groundwater levels studied using the data relevant to the water wells during the last 15 years. Bismil plain obviously good sample that may show using groundwater for irrigation how affect groundwater level changes by year. II. MATERIAL AND METHODS 2.1 Study Area’s Features 2.1.1 Geographic Structure: The geographical location coordinates of Bismil district centre is 37°50'45'' N, 40°40'33'' E, and Bismil is the second largest county in the province of Diyarbakir (Figure1). It is located in the South eastern Anatolia region of Turkey. Settled on aflat land, it has fertile land of the Tigris plain. The Tigris River passes through Bismil. There are slight hills to its north and south. The South-eastern Toros Mountains are located on the south side of Bismil. Its distance from Diyarbakır is 55 kilometres; it has both the railway and highway of Diyarbakir- Batman passing through it. Total area of Bismil district is 1748 km2 . Figure 1. Bismil Urban Location map 2.1.2 Rivers and Lakes: The Tigris River runs through Bismil, and many small and large streams and creeks flow into it. The most important ones among these streams are Pamuk, Göksu, Kurmuşlu, Kuru, Ambar, Caferi andSalatstreams. Not exactly blessed with many lakes, Bismil has only one, which is near the Çöltepe village. 2.1.3 Climate: Bismil has a terrestrial climate. Its summers are dry and hot, and winters are cold and rainy. The dams constructed around the sub-province in the recent years have altered its climate. The snow was remaining on the ground for months before construction of the dams, but in the recent years there is not any snowfall at all. Despite not experiencing frost, temperature goes below zero degrees Celsius during the months December and January, and above 45 degrees in the summer. Especially during July and August the heat tends to get unbearable (Bismil gov.tr, 2013). Average long term precipitation of Bismil is 447,9 mm(Table 1). Table 1. Long term average Bismil precipitation (mm)(DVCSIM), 2011) Dist./Month Jan Feb March Apr May June July Aug Sep Oc Nov Dec Total Bismil 57,9 68,6 62,1 50 37,8 9,6 3,5 0,3 0,6 32,4 56,7 68,4 447,9
  • 3. Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)... www.irjes.com 3 | Page 2.1.4 Bismil Population The population of Bismil has shown a noticeable increase due to regional migration in the 1990s as it isseen in Figure2. The population of Bismil shows a similar distribution as for those live in the rural areas and those in the city centre, with a proportion above the average rate of Turkey. Thereasonfor this is the heavy agricultural employment in the rural regions. Figure 2. Bismil District Population Changes by years(TUIK 2013) 2.2 Methods In the study, 316 wells drilled by public institutions such as DSİ, District Governorships, Special Provincial Administration, as well as private persons for watering purposes between the years 1996-2011 have been examined. The drilling data was ranked with the aid of Microsoft Excel software, and the coordinates have been arrangedaccordingly. These data was run on the ARC Map software. The data that havebeen converted to Shape (shp) format havebeen modelled through Spatial analyse. In the followingmaps, a basemap has been prepared through “Open Street Maps and Contributes” found under the Arc Info software. UTM Datum 1950 37 has been used as projection. Static water level maps relevantto the years 1996-2000 (Figure 2), 2001-2004 (Figure 3), 2005-2008 (Figure 4), and 2009-2011 (Figure 5) have been obtained through all these processes. Changes in the groundwater levelsrelevantto the nominatedyears have been detected usingthese maps. The settlement examples and groundwater graphic changes of the Bismil districtand its villages have been drawn (figures 7, 8 and 9) with these maps. In the light of this data, results have been obtained. Otherwise all term of groundwater changes raster data had been analysed with spatial analyst Local cell statistics menu. Results figure shows in figure 13. III. RESULTS Figure 3. 1996-2000 years Tigris Bismil Figure 4. 2001-2004 years Tigris Bismil Basin Basinstatic water level map static water level map 0 20,000 40,000 60,000 80,000 100,000 120,000 140,000 1970 1975 1980 1985 1990 2000 2007 2008 2009 2010 2011 total population
  • 4. Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)... www.irjes.com 4 | Page Figure 5. 2005-2008 years Tigris Bismil Figure 6. 2009-2011 years Tigris Bismil Basinstatic water level map static water level map Figure 7. Bismil Centre SWL changes Figure 8. North-West Region SWL changes Figure 9. Bismil North Region SWL changes Figure 10.Bismil West Region SWL(changes) 0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 1996-2000 2001-2004 2005-2008 2009-2011 staticwaterdepthfromground(m) Bismil Centre 0 10 20 30 40 50 60 70 80 1996-2000 2001-2004 2005-2008 2009-2011 staticwaterdepthfromground(m) Işıklar Serçeler 0 10 20 30 40 50 60 70 80 1996-2000 2001-2004 2005-2008 2009-2011 staticwaterdepthfromground(m) Uğrak 0 10 20 30 40 50 60 70 80 1996-2000 2001-2004 2005-2008 2009-2011 staticwaterdepthfromground(m) Ambar
  • 5. Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)... www.irjes.com 5 | Page Figure 11. Bismil South-East Region SWL changes Figure 12. Bismil South-East Region SWL changes Figure 13. Bismil 1996-2001 terms mean SWL value changes Following conclusions have been obtained from thematic maps groundwater changes are classified relevant to urban centre (Figure 7), North-West(Figure 8), North (Figure 9), West(Figure 10), South, South- East, East and South West region. 1. The groundwater levels in all other regions show a significant dropped. Even though it is known that groundwater levels havesome small seasonal changes. 2. In the Bismil settlement area the static water levels have dropped by over 55-60 meters. Especially after the year 2005, the groundwater levels have started todecrease increasingly. For example, in the Türkmenhacivillage it has dropped from 4.8 meters in 1996-2000 to 15.1 meters the years between 2001- 2004.It has further dropped from 47 meters between 2005-2008 down to 103 meters between 2009-2011. Such changes are alsofound in other areas of thesettlement as well. The main reasons for thiswere theinsufficient precipitation during the years 2009-2011, and the use of thegroundwaterresourcesmore thantheir feeding. It can also be claimed that the unauthorized water wells drilled in the area have an importanteffect on these dramaticchanges in groundwater levels.The groundwater level in Central Bismilthat was at 12 meters between the years1996-2000 decreased up to 73 meters betweenthe years 2009- 2011.The groundwater level in Işıklarvillage was 17 meters between the years1996-2000 has gone down to 73 meters between the years2009-2011. 3. From the 2000 years, rural and urban population of Bismil is steadily. Whereas as seen Figure 7-12 groundwater level change is decreased after 2005-2008 period sharply. So effect of population growth on groundwater is little. 4. In Bismil region, 60,000 decares of cotton, 2,500 decares of tobacco are cultivated (TUIK 2011). These crops needs more water. Besides, production of other field crops also carried out using groundwater. That would be main effect of groundwater level decrease.According to DVCSIM 2013 report, In Bismil groundwater used 0,92 hm3 /years water for drinking, 85.47 hm3 /year water for irrigation. While it seeding
  • 6. Determination of Tigris Bismil Agricultural Plain’s Groundwater Static Water Level (SWL)... www.irjes.com 6 | Page groundwater average is 31,25 hm3 /year. There is huge negative budge about groundwater consumption and seeding. That would be main reason groundwater decrease. IV. CONCLUSIONS Groundwater level dropped average 50-60 meters in Bismil central, Northern and Western Region. South, southwest and south-eastern regions of the groundwater static level dropped average 82 m (figure 13). This change occurred especially after 2005 years. There would be main 3 factor effect the groundwater change; population growth, climate effect on precipitation and groundwater use for irrigation unconscious. Population and climate effect is very lowrather thangroundwater using for irrigation effect. So that the main reason of groundwater level decrease is using water for irrigation unconscious in the semi arid region. Suggestions:In the agricultural area groundwater use is must be under control. The using groundwater must be reducing at least %70 for irrigation in the Bismil plain. Additionally special wateringprojects (GAP Projects) should be executed as soon as possible. The need to use groundwater resources should be eliminated. In this manner the groundwater resources can reach at abalanced acceptable levelby thetimepasses. REFERENCES [1]. Akbulut, E.N., Bayarı, S., Akbulut, A.Sahin, Y. S Rivers Of Turkey, In: K. Tockner,C., T., Robinson, U.,Uehlinger (Eds.), Rivers Of Europa, Academic Press, New York,2009, Pp. 643–672 [2]. Altinbilek, D. (2004) Development And Management Of The Euphrates–Tigris Basin,Water Resources Development,Vol. 20, No. 1, 15–33, March 2004 [3]. Bennett, 2000.A.J., Environmental Consequences Of Increasing Production: Some Current Perspectives. Agric. Ecosys. Environ.82 (2000), Pp. 89–95. [4]. Chawla, J. K., Khepar, S. D., Sondhi ,S. K. , Yadav, A. K.2010.Assessment Of Long-Term Groundwater Behaviour In Punjab, India, Water International Vol. 35, No. 1, January, 63–77 [5]. Chowdhury, A., Jha, Metersk.,Chowdary, V.Meters, 2010.Delineation Of Groundwater Recharge Zones And Identification Of Artificial Recharge Sites In West Medinipur District, West Bengal Using Rs, Gis And Mcdm Techniques. Environmental Earth Sciences 59 (6), 1209–1222. [6]. Çelik, R. 2015. “Temporal Changes In The Groundwater Level In The Upper Tigris Basin, Turkey, Determined By A Gis Technique.” Journal Of African Earth Sciences 107: 134-143. [7]. Dineshkumar, P.K., Gopinath, G., Seralathan, P., 2007.Application Of Remote Sensing And Gis For The Demarcation Of Groundwater Potential Zones Of A River Basin In Kerala, Southwest Coast Of India. International Journal Of Remote Sensing 28, 5583–5601. [8]. Diyarbakır Valiliğiçevreveşehircilikilmüdürlüğü (Dvcsim), 2011.İl Çevre Durum Raporu-2011, Diyarbakir.Available Inttp://Www.Csb.Gov.Tr/Db/Ced/Editordosya/Diyarbakir_Icdr2011.Pdf[Accessed 17. 02.2014] [9]. Diyarbakır Valiliğiçevreveşehircilikilmüdürlüğü (Dvcsim), 2013.İl Çevre Durum Raporu-2012,Pp 83.Diyarbakir (Turkish Report).Available In: Http://Www.Csb.Gov.Tr/Db/Ced/Editordosya/Diyarbakir_Icdr2012.Pdf[Accessed 14. 03.2014] [10]. Http://Www.Diyarbakir.Bel.Tr/Images/Diyarbakir2011.Jpg [Accessed 14.11.2013] [11]. Http://Www.Bismil.Gov.Tr/Default_B0.Aspx?Content=193 [Accessed: 10/11/2013] [12]. Nalbantoğlu,U., 2006.Dsi - State Hydraulıc Works And Water Database At Dsi. Available From:Http://Www.Minenv.Gr/Medeuwi/Meetings/Conference.Of.The.Water.Directors.Athens.6&7- 11- 06_En/00/Dsi-Turkey.Pdf] [13]. Procter,C., Comber, L., Betson, Meters, Buckley,D., Frost,A., Lyons,H., Riding,A., Voyce,K.,2006 Identifying Crop Vulnerability To Groundwater Abstraction: Modelling And Expert Knowledge In A Gis, Journal Of Environmental Management 81, 296–306. [14]. Öztürk, M., Çelik R., 2008, Diyarbakır Ovasıyeraltı Su Seviyeharitalarınıncoğrafikbilgisistemiiletesbiti (Turkish Article), Tmmob 2.Su Politikalarıkongresi Cilt1 Sayı: 1shf: 125-133 Ankara [15]. Sander, P., 1997. Water Well Sitting In Hard Rock Areas: Identifying Promising Targets Using A Probabilistic Approach. Journal Of Hydrogeology 5, 32–43. [16]. Sikdar, P.K.,Chakraborty, S., Enakshi, A., Paul, P.K., 2004. Land Use/Land Cover Changes And Groundwater Potential Zoning In And Around Raniganj Coal Miningarea, Bardhamandistrict, West Bengal – A Gis And Remote Sensing Approach. Journal Of Spatial Hydrology 4, 1–24 [17]. Vanderpost,C., Mcfarlane,M., 2007. Groundwater Investigation In Semi-Arid Developing Countries,Using Simple Gis Tools To Facilitate Interdisciplinary Decision Making Under Poorlymapped Conditions: The Boteti Area Of The Kalahari Region In Botswana, International Journal Of Applied Earth Observation And Geoinformation 9 343–359 [18]. Unesco. 2006 Coping With Water Scarcity Astrategic Issue Andpriorityforsystem- Wideactionftp://Ftp.Fao.Org/Agl/Aglw/Docs/Waterscarcity.Pdf