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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 664
GROUND WATER CONTROL METHOD SIMULATION IN SPHINX AREA"
Dr. Walid Al-Sayed Mohamed
ASSOCIATE PROF. OF IRRIGATION AND HYDRAULICS, AL AZHAR UNIVERSITY
---------------------------------------------------------------------***----------------------------------------------------------------------
Abstract - In terms of the importance of preserving the area
of the Sphinx, pyramids, temples and monuments of Egypt,
where population growth will introduce new sources of water
will certainly increase the rise of groundwater levels, began
with the main objective is to protect the Sphinx from the
dangers of rising groundwater levels. Through the
development of the research objectives, the research
methodology was planned. This methodology includes an
introduction to the importance of the research topic, 5 stages
of investigation. The theoretical stage, the data collection
stage, the numerical modeling phase, the analytical stage and
the theoretical stage. The previous research in the field of
groundwater was presented to utilize the previous studies
through simulations, which are collected. The data collection
stage, where a complete picture of the area was filmed.
Numerical Emphasis several alternatives have been proposed
to limit the rise of groundwater in the Sphinx region in order
to keep it from deteriorating. In addition, the Sphinx was
designed before and after the implementation of alternatives
to predict the impact of such countermeasures. For the
analytical phase, numerical modeling results were analyzed
and the impact of the proposed measures analyzed. With
regard to the deductive phase, conclusions were made;
recommendationswereproposedandanappropriatemeasure
was commended in order to preserve the region from the risk
of rising groundwater. By modeling groundwater using mod
flow, calibrating the model to verify its validity inallcasesand
suggesting measures (alternatives) to counter the rise of
groundwater in the Sphinx (sinks, horizontal wells, vertical
barriers), and simulating the Sphinx Before and after the
implementation of the proposed alternatives to predict the
impact of these measures. The results of the numerical
modeling were analyzed and the impact of the five proposed
measures was evaluated.
Key Words: Ground Water Modelling;Mod-flow;conceptual
model; Numerical model; Drain; Horizontal well; Barrier;
vertical wells.
1. PROPOSED ALTERNATIVES
Based on the results of the previous researches that
investigated the study area, several alternatives and their
combinations were proposed. These are, as follows: -Linear
drains in trenches, Combined Linear drains and Barrier,
Horizontal well, Combined horizontal well and Barrier,
Barrier and vertical wells.
2. LINEAR DRAINS IN TRENCHES
Based on the linear drain system simulation, it was
recommended to lower the drain by an additional 0.5 m.
Thus, the trench invert should be lowered by 1.5 m.
Accordingly, the (13.00) m target level is achieved in Sphinx
Area. In addition, the flow to the drainwouldbe11050m3/d,
figure (1).
Finally, one of the most important featuresleasttotalcost
and the most important disadvantages greatest construction
impact.Finally, one of the most important featuresleasttotal
cost and the most important disadvantages greatest
construction impact.
Drain Flow 11050 m3/d
Drain Elevation 11.95 - 12 m
Figure (1) Calculated Groundwater Levels for Linear
Drain
3. COMBINED LINEAR DRAINS AND BARRIER
Based on the simulation of the linear drain system with a
barrier, it was recommended to lower the drain system by
an additional 0.5 m. Thus, the trench invert should be
lowered by 1.5 m. Accordingly, the (12.00) m target level is
achieved in the Sphinx Area. Inaddition,theflowdischarging
into the drain would be 9805m3/d, figure (2).
As for cost, total cost (L.E) 69 million Including capital
cost (45 million), operation andmaintenance(24million) up
to 40 years.
Finally, one of the most important features high
drawdown and the most important disadvantages greatest
construction impact and high total cost.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 665
Drain Flow 9805 m3/d
Drain Elevation 11.95 - 12 m
Figure (2) Calculated Groundwater Levels for Liner Drain-
with barrier
4. HORIZONTAL WELL
Based on the simulation of the horizontal well, it was
recommended to lower the horizontal well by an additional
0.5 m. Thus, the horizontal well invert should be lowered by
1.5 m. Accordingly, the (12.00) m target level is achieved in
the Sphinx Area. In addition, the flow discharging into the
horizontal well would be 11500m3/d, figure (3).
As for cost, total cost (L.E) 54 million Including capital
cost (30 million), operation and maintenance (24 million)up
to 40 years.
Finally, one of the most important features small
Implementation period and the most important
disadvantages requires importation of equipment and
materials and high capital cost.
Hz. well pumping 11500 m3/d
Hz. well Elevation 12 m
Figure (3) Calculated Groundwater Levels for Horizontal
well
5. HORIZONTAL WELL WITH THE BARRIER
Based on the simulation of the horizontal well with the
barrier, it was recommended to lower the horizontal well by
an additional 0.5 m. Thus, the trench invert should be
lowered by 1.5 m. Accordingly, the (12.00) m target level is
achieved in the Sphinx Area. In addition, theflowdischarging
into the horizontal well would be 9000m3/d, figure (4).
As for cost, total cost (L.E) 69 million Including capital
cost (45 million), operation and maintenance (24 million)up
to 40 years.
Finally, one of the most important features high
drawdown and the most important disadvantages requires
importation ofequipmentandmaterialsandhighcapitalcost.
Hz. well pumping 9000 m3/d
Hz. well Elevation 12 m
Figure (4) Calculated Groundwater Levels for Horizontal
well- with barrier
6. BARRIER
Based on the barrier simulations, the calculated
groundwater levels are presented on figure (5). The16.25m
target level was not achieved in Sphinx Area. This indicated
that it is not recommended to use the barrier, as it does not
achieve the desired goal but when used on low permeable
layers achieves the target level and reduce the groundwater
level to (11.08) m.
As for cost, total cost (L.E) 39.6 million Including capital
cost (9.6 million), operation and maintenance (30 million)
up to 40 years.
Finally, one of the most importantfeaturesleastrunning
cost and the most important disadvantages greatest
construction impact and high capital cost.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 666
Barrier with vertical well pumping 400 m3/d
Figure (5) Calculated Groundwater Levels for Barrier
7. CONCLUSIONS
Based on the obtained results and their analysis, the
following conclusions were deduced:
 Alternative I and III (Linear drains andhorizontal wells)
are the economic measures and could reduce the
groundwater table to a target level of (12.00) m.
However, alternative I is the most economic.
 Alternative II and IV (Linear drains and horizontal wells
with barrier) could reduce the groundwater table to a
target level of (12.50) m. However, it is relatively
uneconomic as the barrier could not beimplemented,as
it requires a low-permeable layer to prevent vertical
flow.
 Alternative V(barrier) did not achieve the target level in
Sphinx Area. Therefore, it is not recommended to use it
at places with layers with high hydraulic conductivity,
but when used on low permeable layers achieves the
target level and reduce the ground water level to
(11.08) m.
8. RECOMMENDATIONS
Based on the deduced conclusions, the following
recommendations were suggested:
 Regarding the Engineering practice, the following are
suggested:
 The first and third alternative (Linear drains and
horizontal wells) is suitable to preserve the area of the
Sphinx from the damage of groundwater, where the
security level (12.00) m above the sea level and
preferably the first alternative (linear drain) as it is
economically feasible and recommend to put it on 1.5m
of the security level.
 The second and fourth (Linear drains and horizontal
wells with barrier) alternative is suitable to preserve
the area of the Sphinx from the damage of groundwater,
where it achieves a more secure level is economically
inappropriate in addition to the use of vertical barriers
in this area does not fit the nature of the layers in the
area of lime limestone highly hydraulic conductivity
where does not prevent the vertical flow, Groundwater
security is not achieved at the Sphinx for the above
reasons. It was studied only to illustrate its effect on the
assumption of a low hydraulic conductivity layer and is
only suitable in areas with green or soil injection with a
research that prevents vertical flow.
 Alternative V is notrecommendedtobeimplemented,as
it does not achieve the target level.
 vertical wells are used where there has been security
level, but you must be careful where the highest value
will be recorded for the decline of alternatives, but
easily characterized by implementation and less to
create value.
 The choice should be governed by the economic
condition, the applicability of the measure without
affecting the tourism in the Sphinx Area and Scalable to
increase the expected groundwater level.
9. SUMMARY FOR STUDY ALTERNATIVES.
After completion of the study of all alternatives from the
point of drawdown and subsidence resulting from that
drawdown and the cost of each alternative for the following
is a summary of the study in the following table to facilitate
the process of comparison between alternatives and choose
the best alternative of all interfaces.
NO ALTERNATIVE
HEAD
(ASL-M)
PUMPING
RATE (CMD)
VERTICAL
DISPLACEMENT
(MM)
CAPITAL
COST (LE)
TOTAL
RUNNING
COST (LE)
/40 YEARS
TOTAL
COST(LE)
THE BEST
RANKING
1 LINEAR DRAIN (12.05) 11050 1.4 15000000 24,000,000 39,000,000 1
2
LINEAR DRAIN WITH
BARRIER
(12.08) 9805 2 45,000,000 24,000,000 69,000,000 6
3 HORIZONTAL WELLS (11.90) 11500 2.4 30,000,000 24,000,000 54,000,000 3
4
HORIZONTAL WELLS
WITH BARRIER
(12.00) 9000 2 45000000 24,000,000 69,000,000 5
5
BARRIER WITH BASE
PLUG
(11.08) 400 1.7 30,000,000 9,600,000 39,600,000 4
6 BARRIER (16.25) 0 0 15,000,000 - 15,000,000 7
7 VERTICAL WELLS (12.05) 25000 5 7,200,000 43,200,000 50,400,000 2
Table (1) Summary for Study Alternatives
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 667
10. LIST OF REFERENCES
1. AECOM (2010) “Groundwater Lowering
Alternatives, Pyramids Plateau Groundwater
Lowering Activity”, USAID Contract No. EDH-I-00-
08-00024-00-OrderNo.02,Technical Memorandum,
submitted to USAID, February 20, 2010, AECOM in
Association with ECG and EDG.
2. American British Consultant “AMBRIC” (1989):
“Greater Cairo Wastewater in the Pyramids Area
Project”- Ministry of Reconstruction, New
Communities, Housing and Utilities
3. Arnold, J.G., Allen,P.M.(1999).“Automated methods
for estimating base flow and groundwater recharge
from stream flow records”. J. American Water
Resource. Assoc. 35 (2), 411–424.
4. Arnold, J.G., Allen, P.M., Bernhardt, G. (1993). “A
comprehensivesurface-groundwaterflowmodel”.J.
Hydrol. 142, 47–69.
5. Arnold, J.G., Fohrer, N. (2005). “SWAT2000: current
capabilities and research opportunities in applied
watershed modeling”. Hydrol. Process. 19 (3),563–
572.
6. Arnold, J.G., Srinivasan, R., Muttiah, R.S., Williams,
J.R. (1998). “Large area hydrologic modeling and
assessment:partI.Model development”.J.American
Water Resource. Assoc. 34 (1), 73–89.
7. Atef Al-Kharabsheh (2000).“Ground-water
modelling and long-term management of the Azraq
basin as an example of arid area conditions (
Jordan)”, Journal ofAridEnvironments44:143–153
8. Bunbury, J., Lutley, C., and Graham, A. (2007). “Giza
Geomorphological Report”,InGiza PlateauMapping
Project, Seasons 2006-2007, Preliminary Report.
Giza Occasional Papers 3, Ancient Egypt Research
Associates, Inc.
9. Cairo University (2007). “Factual Geotechnical
Investigation and Geological Report for
Groundwater Control of Elwadi Temple of Khafra’a
Pyramid – Sphinx Zone”, Giza Governorate.
10. Cairo University (2008). “Drilling and Testing of
Three Wells at the Sphinx Area”, Technical Report.
11. Cairo University (2008). “LoweringofGroundwater
at Wadi Temple and Sphinx Area”, Final Technical
Report.
12. Cairo University (2008). “Operation of Production
Wells and Piezometer Readings below the Sphinx
and Wadi Temple”, from July to October 2008.
13. Cairo University (2008).” Technical Report for the
Drilling of Four Boreholes around the Sphinx”,
Video Logging and Water Level Monitoring
14. Cairo University (2009). “Lowering of Ground
Water below the Sphinx and Wadi Temple”, Final
Report.

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IRJET- Ground Water Control Method Simulation in Sphinx Area

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 664 GROUND WATER CONTROL METHOD SIMULATION IN SPHINX AREA" Dr. Walid Al-Sayed Mohamed ASSOCIATE PROF. OF IRRIGATION AND HYDRAULICS, AL AZHAR UNIVERSITY ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - In terms of the importance of preserving the area of the Sphinx, pyramids, temples and monuments of Egypt, where population growth will introduce new sources of water will certainly increase the rise of groundwater levels, began with the main objective is to protect the Sphinx from the dangers of rising groundwater levels. Through the development of the research objectives, the research methodology was planned. This methodology includes an introduction to the importance of the research topic, 5 stages of investigation. The theoretical stage, the data collection stage, the numerical modeling phase, the analytical stage and the theoretical stage. The previous research in the field of groundwater was presented to utilize the previous studies through simulations, which are collected. The data collection stage, where a complete picture of the area was filmed. Numerical Emphasis several alternatives have been proposed to limit the rise of groundwater in the Sphinx region in order to keep it from deteriorating. In addition, the Sphinx was designed before and after the implementation of alternatives to predict the impact of such countermeasures. For the analytical phase, numerical modeling results were analyzed and the impact of the proposed measures analyzed. With regard to the deductive phase, conclusions were made; recommendationswereproposedandanappropriatemeasure was commended in order to preserve the region from the risk of rising groundwater. By modeling groundwater using mod flow, calibrating the model to verify its validity inallcasesand suggesting measures (alternatives) to counter the rise of groundwater in the Sphinx (sinks, horizontal wells, vertical barriers), and simulating the Sphinx Before and after the implementation of the proposed alternatives to predict the impact of these measures. The results of the numerical modeling were analyzed and the impact of the five proposed measures was evaluated. Key Words: Ground Water Modelling;Mod-flow;conceptual model; Numerical model; Drain; Horizontal well; Barrier; vertical wells. 1. PROPOSED ALTERNATIVES Based on the results of the previous researches that investigated the study area, several alternatives and their combinations were proposed. These are, as follows: -Linear drains in trenches, Combined Linear drains and Barrier, Horizontal well, Combined horizontal well and Barrier, Barrier and vertical wells. 2. LINEAR DRAINS IN TRENCHES Based on the linear drain system simulation, it was recommended to lower the drain by an additional 0.5 m. Thus, the trench invert should be lowered by 1.5 m. Accordingly, the (13.00) m target level is achieved in Sphinx Area. In addition, the flow to the drainwouldbe11050m3/d, figure (1). Finally, one of the most important featuresleasttotalcost and the most important disadvantages greatest construction impact.Finally, one of the most important featuresleasttotal cost and the most important disadvantages greatest construction impact. Drain Flow 11050 m3/d Drain Elevation 11.95 - 12 m Figure (1) Calculated Groundwater Levels for Linear Drain 3. COMBINED LINEAR DRAINS AND BARRIER Based on the simulation of the linear drain system with a barrier, it was recommended to lower the drain system by an additional 0.5 m. Thus, the trench invert should be lowered by 1.5 m. Accordingly, the (12.00) m target level is achieved in the Sphinx Area. Inaddition,theflowdischarging into the drain would be 9805m3/d, figure (2). As for cost, total cost (L.E) 69 million Including capital cost (45 million), operation andmaintenance(24million) up to 40 years. Finally, one of the most important features high drawdown and the most important disadvantages greatest construction impact and high total cost.
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 665 Drain Flow 9805 m3/d Drain Elevation 11.95 - 12 m Figure (2) Calculated Groundwater Levels for Liner Drain- with barrier 4. HORIZONTAL WELL Based on the simulation of the horizontal well, it was recommended to lower the horizontal well by an additional 0.5 m. Thus, the horizontal well invert should be lowered by 1.5 m. Accordingly, the (12.00) m target level is achieved in the Sphinx Area. In addition, the flow discharging into the horizontal well would be 11500m3/d, figure (3). As for cost, total cost (L.E) 54 million Including capital cost (30 million), operation and maintenance (24 million)up to 40 years. Finally, one of the most important features small Implementation period and the most important disadvantages requires importation of equipment and materials and high capital cost. Hz. well pumping 11500 m3/d Hz. well Elevation 12 m Figure (3) Calculated Groundwater Levels for Horizontal well 5. HORIZONTAL WELL WITH THE BARRIER Based on the simulation of the horizontal well with the barrier, it was recommended to lower the horizontal well by an additional 0.5 m. Thus, the trench invert should be lowered by 1.5 m. Accordingly, the (12.00) m target level is achieved in the Sphinx Area. In addition, theflowdischarging into the horizontal well would be 9000m3/d, figure (4). As for cost, total cost (L.E) 69 million Including capital cost (45 million), operation and maintenance (24 million)up to 40 years. Finally, one of the most important features high drawdown and the most important disadvantages requires importation ofequipmentandmaterialsandhighcapitalcost. Hz. well pumping 9000 m3/d Hz. well Elevation 12 m Figure (4) Calculated Groundwater Levels for Horizontal well- with barrier 6. BARRIER Based on the barrier simulations, the calculated groundwater levels are presented on figure (5). The16.25m target level was not achieved in Sphinx Area. This indicated that it is not recommended to use the barrier, as it does not achieve the desired goal but when used on low permeable layers achieves the target level and reduce the groundwater level to (11.08) m. As for cost, total cost (L.E) 39.6 million Including capital cost (9.6 million), operation and maintenance (30 million) up to 40 years. Finally, one of the most importantfeaturesleastrunning cost and the most important disadvantages greatest construction impact and high capital cost.
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 666 Barrier with vertical well pumping 400 m3/d Figure (5) Calculated Groundwater Levels for Barrier 7. CONCLUSIONS Based on the obtained results and their analysis, the following conclusions were deduced:  Alternative I and III (Linear drains andhorizontal wells) are the economic measures and could reduce the groundwater table to a target level of (12.00) m. However, alternative I is the most economic.  Alternative II and IV (Linear drains and horizontal wells with barrier) could reduce the groundwater table to a target level of (12.50) m. However, it is relatively uneconomic as the barrier could not beimplemented,as it requires a low-permeable layer to prevent vertical flow.  Alternative V(barrier) did not achieve the target level in Sphinx Area. Therefore, it is not recommended to use it at places with layers with high hydraulic conductivity, but when used on low permeable layers achieves the target level and reduce the ground water level to (11.08) m. 8. RECOMMENDATIONS Based on the deduced conclusions, the following recommendations were suggested:  Regarding the Engineering practice, the following are suggested:  The first and third alternative (Linear drains and horizontal wells) is suitable to preserve the area of the Sphinx from the damage of groundwater, where the security level (12.00) m above the sea level and preferably the first alternative (linear drain) as it is economically feasible and recommend to put it on 1.5m of the security level.  The second and fourth (Linear drains and horizontal wells with barrier) alternative is suitable to preserve the area of the Sphinx from the damage of groundwater, where it achieves a more secure level is economically inappropriate in addition to the use of vertical barriers in this area does not fit the nature of the layers in the area of lime limestone highly hydraulic conductivity where does not prevent the vertical flow, Groundwater security is not achieved at the Sphinx for the above reasons. It was studied only to illustrate its effect on the assumption of a low hydraulic conductivity layer and is only suitable in areas with green or soil injection with a research that prevents vertical flow.  Alternative V is notrecommendedtobeimplemented,as it does not achieve the target level.  vertical wells are used where there has been security level, but you must be careful where the highest value will be recorded for the decline of alternatives, but easily characterized by implementation and less to create value.  The choice should be governed by the economic condition, the applicability of the measure without affecting the tourism in the Sphinx Area and Scalable to increase the expected groundwater level. 9. SUMMARY FOR STUDY ALTERNATIVES. After completion of the study of all alternatives from the point of drawdown and subsidence resulting from that drawdown and the cost of each alternative for the following is a summary of the study in the following table to facilitate the process of comparison between alternatives and choose the best alternative of all interfaces. NO ALTERNATIVE HEAD (ASL-M) PUMPING RATE (CMD) VERTICAL DISPLACEMENT (MM) CAPITAL COST (LE) TOTAL RUNNING COST (LE) /40 YEARS TOTAL COST(LE) THE BEST RANKING 1 LINEAR DRAIN (12.05) 11050 1.4 15000000 24,000,000 39,000,000 1 2 LINEAR DRAIN WITH BARRIER (12.08) 9805 2 45,000,000 24,000,000 69,000,000 6 3 HORIZONTAL WELLS (11.90) 11500 2.4 30,000,000 24,000,000 54,000,000 3 4 HORIZONTAL WELLS WITH BARRIER (12.00) 9000 2 45000000 24,000,000 69,000,000 5 5 BARRIER WITH BASE PLUG (11.08) 400 1.7 30,000,000 9,600,000 39,600,000 4 6 BARRIER (16.25) 0 0 15,000,000 - 15,000,000 7 7 VERTICAL WELLS (12.05) 25000 5 7,200,000 43,200,000 50,400,000 2 Table (1) Summary for Study Alternatives
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 667 10. LIST OF REFERENCES 1. AECOM (2010) “Groundwater Lowering Alternatives, Pyramids Plateau Groundwater Lowering Activity”, USAID Contract No. EDH-I-00- 08-00024-00-OrderNo.02,Technical Memorandum, submitted to USAID, February 20, 2010, AECOM in Association with ECG and EDG. 2. American British Consultant “AMBRIC” (1989): “Greater Cairo Wastewater in the Pyramids Area Project”- Ministry of Reconstruction, New Communities, Housing and Utilities 3. Arnold, J.G., Allen,P.M.(1999).“Automated methods for estimating base flow and groundwater recharge from stream flow records”. J. American Water Resource. Assoc. 35 (2), 411–424. 4. Arnold, J.G., Allen, P.M., Bernhardt, G. (1993). “A comprehensivesurface-groundwaterflowmodel”.J. Hydrol. 142, 47–69. 5. Arnold, J.G., Fohrer, N. (2005). “SWAT2000: current capabilities and research opportunities in applied watershed modeling”. Hydrol. Process. 19 (3),563– 572. 6. Arnold, J.G., Srinivasan, R., Muttiah, R.S., Williams, J.R. (1998). “Large area hydrologic modeling and assessment:partI.Model development”.J.American Water Resource. Assoc. 34 (1), 73–89. 7. Atef Al-Kharabsheh (2000).“Ground-water modelling and long-term management of the Azraq basin as an example of arid area conditions ( Jordan)”, Journal ofAridEnvironments44:143–153 8. Bunbury, J., Lutley, C., and Graham, A. (2007). “Giza Geomorphological Report”,InGiza PlateauMapping Project, Seasons 2006-2007, Preliminary Report. Giza Occasional Papers 3, Ancient Egypt Research Associates, Inc. 9. Cairo University (2007). “Factual Geotechnical Investigation and Geological Report for Groundwater Control of Elwadi Temple of Khafra’a Pyramid – Sphinx Zone”, Giza Governorate. 10. Cairo University (2008). “Drilling and Testing of Three Wells at the Sphinx Area”, Technical Report. 11. Cairo University (2008). “LoweringofGroundwater at Wadi Temple and Sphinx Area”, Final Technical Report. 12. Cairo University (2008). “Operation of Production Wells and Piezometer Readings below the Sphinx and Wadi Temple”, from July to October 2008. 13. Cairo University (2008).” Technical Report for the Drilling of Four Boreholes around the Sphinx”, Video Logging and Water Level Monitoring 14. Cairo University (2009). “Lowering of Ground Water below the Sphinx and Wadi Temple”, Final Report.