Conjunctive use of groundwater and surface water resources with aquifer recharge by treated wastewater: evaluation of management scenarios in the Zarqa River Basin, Jordan
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Abstract
We study the effects of treated wastewater (TWW) discharge into the Zarqa River in Jordan and the underlying unconfined limestone Hummar Aquifer. The main objectives were to develop a conceptual model of the aquifer, to gain better understanding of water dynamics in the basin and to investigate different management scenarios of conjunctive use of groundwater and surface water. The model using MODFLOW 2005 code was developed over a selected part of the Zarqa River Valley of area 387 km2, including the As Samra wastewater treatment plant (WWTP). The annual TWW discharge of 110 million m3 significantly augments the groundwater storage and allows for expansion of agricultural practices in the area, providing large reserve during dry spells. On average, the water table rises by 29 m following the inception of the WWTP. The results indicate that the aquifer will be able to accommodate extra discharge of TWW when the plant will operate at full capacity as planned and upon increase in the abstraction rate for irrigation by 30 %, based on farming land availability. This abstraction will result in an average water table drawdown of 0.3 m. Because around 20 % of the discharged TWW only reach the aquifer, we recommend direct use of river water, especially during drought periods to reduce the stress on the aquifer storage and its associated depletion. The simulated conjunctive use and MAR utilizing both TWW and the groundwater present a salient case study of intricate management of water resources in arid zone. Augmentation of groundwater resources by both banking of the TWW and management of water use will allow more agricultural activities that would result in a better income for farming communities and social stability in the MENA region, where water is a precious commodity.
Keywords
Groundwater–surface water interactions Zarqa River As Samra wastewater treatment plant Jordan Conjunctive water use MODFLOW 2005Abbreviations
- BC
Base case scenario (current situation)
- BG
Background scenario
- C
River conductance (m2/day)
- D
Recharge rate (m3/day)
- Depth
Soil depth (m)
- Depth_min
Depth of the horizon above the horizon with the lowest hydraulic conductivity (m)
- ET
Evapotranspiration (mm/year)
- GIS
Geographical information system
- H
Stream depth at the gauging station (m)
- HBC
Average river water depth for base scenario (m)
- HS
Average river water depth for a given scenario (m)
- IDW
Inverse distance weighing method
- J2000
Hydrological and physical processes-based model of the water balance of large catchment areas
- kf_max
Maximum coefficient of hydraulic conductivity (m/day)
- kf_min
Minimum coefficient of hydraulic conductivity (m/day)
- ks
Hydraulic conductivity of streambed sediments (m/day)
- l
Length of the river reach (m)
- MAR
Managed aquifer recharge
- MENA
Middle East and North Africa
- ModelMuse
A graphical user interface for MODFLOW-2005
- MODFLOW
Finite-difference groundwater flow model
- ms
Thickness of the streambed sediments (m)
- MWI
Ministry of Water and Irrigation of Jordan
- NE
North East
- NRA
Natural Resources Authority, Amman, Jordan
- P
Precipitation (mm/year)
- Q
River discharge
- QTWW
River discharge changes among various scenarios
- RIV
River MODFLOW package
- Roff
Runoff (mm/year)
- SCS
Soil Conservation Service, the United States Department of Agriculture
- SID
Soil type ID
- STP
Sewage treatment plant
- SW
South West
- TWW
Treated wastewater
- USA
United States of America
- USAID
United States Agency for International Development
- USGS
US Geological Survey
- w
Width of the river reach (m)
- WAJ
Jordan Water Authority, Amman, Jordan
- WWTP
Wastewater treatment plant
- ΔS
Change in soil water storage in the soil column (mm/year)
Notes
Acknowledgments
This study was conducted as part of a collaborative project between Sultan Qaboos University, Oman, University of Jordan, and University of Nebraska-Lincoln, USA. This project and publication were funded by USAID-FABRI, task order number: AID-OAA-TO-11-00049 (Subcontracts: 1001626-104, 1001624-12S-19745). The authors acknowledge support from the Water Centers in their universities. First author (M. El-Rawy) acknowledges Sultan Qaboos University, Oman, for the postdoctoral fellowship. Second author (V. Zlotnik) acknowledges support and encouragement from the Daugherty Water for Food Institute, University of Nebraska. The authors are grateful to the Ministry of Water and Irrigation, Jordan, for providing access to the data and field assistance. The authors also would like to thank Dr. Jihad Al Mahamid and Geol. Mamoun Ismail from Ministry of Water and Irrigation and Water Authority of Jordan for help and support.
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