• Ground Water

  • Irrigation Water

  • Waste Water  

  • Water Strategy 

  • Water Utility

  •  

    GROUND WATER MANAGEMENT POLICY

     
    Background

    Groundwater in the Hashemite Kingdom of Jordan occurs in a renewable and nonrenewable form in 12 distinct basins. The exploitation of groundwater in ancient times was done through the exploitation of springs where groundwater emerges to the ground surface, and through the artificial means of tapping the aquifers by drilling shafts. Archaeological remains in the Jordan Rift Valley indicate the sinking of such shafts at different angles. They date back to the Nabatean era (300 B.C - 106 A.C) and the Roman era thereafter. Jordanians continued to harness the benefits of the use of spring water for different purposes. In the Ottoman era (1516-1916), the use of water was regulated and water rights were kept by the district administration in an official register. Legislation for water acquisition and use in the Hashemite Kingdom started in 1938, and due consideration was taken of the prior water rights recognized by the previous Ottoman administration.
    Modern technology to access groundwater aquifers was introduced to the Kingdom in the late fifties; legislation to regulate the exploitation of groundwater resources and to have it supervised by government was soon introduced. The country had its population doubled as it hosted the first wave of Palestinian refugees in 1948. It united with the West Bank in 1951 in one Hashemite Kingdom. Free movement of people, goods, and services was normal and added more to the population. The increase in population occurred in and around urban areas, which intensified the demand for urban water. Springs that had been the source of urban water could no more cope with the increased demand. Streams that emerged from them dried up with adverse environmental consequences. Tube wells were drilled to pump more water from the aquifers for urban supply purposes.
    Demand also increased for food. Permits were also issued to interested developers to drill wells for agricultural development. The drilling and abstraction of groundwater were monitored and controlled until the outbreak of the 1967 war and its aftermath. Government control weakened, and many wells were drilled without permits. The relaxation of Government controls thereafter continued primarily because of the institutional instability and the shifting of institutional responsibilities.
    Today, each of the 12 water basins has wells sunk in it and pumps installed in them capable of abstracting more water than the safe yield of each. The average annual abstraction from all basins exceeds the renewable average of recharge and currently stands at 159% of that average. The over pumping ratio ranges between 146% in minor aquifers to 235% in major ones. This situation could not be tolerated, and decisions were taken to treat the situation.
    and WAJ assumed the responsibility of groundwater administration, management and development. The concerned directorate of NRA and that of the JVA were transferred to WAJ in 1984. Both WAJ and JVA came under the umbrella of a newly founded Ministry, the Ministry of Water and Irrigation, MWI in 1988.
    Currently, MWI/WAJ is in charge of groundwater administration and management in addition to its responsibilities in providing municipal water supplies to all population centers in Jordan, and the collection and treatment of their wastewater. MWI/WAJ receives application for drilling licenses and abstraction permits, and issues such licenses and permits in accordance with the effective groundwater legislation. MWI/WAJ also supervises the drilling, the abstraction, and makes arrangements for the lease of land and use of groundwater for agricultural purposes in remote arid areas. Recently, MWI has stepped up the activities of groundwater resources studies on a national scale.
    Conditions of Groundwater Aquifers
    There are eleven renewable groundwater reservoirs in the country. Their sustainable yields vary from one reservoir to another, and their combined sustainable yield is 275 million cubic meters per year.
    The majority of the reservoirs are being utilized at rates exceeding their sustainable yields. The important ones are of particular concern because they are the most over utilized aquifers. The combined abstraction rate of all renewable reservoirs approaches 437 MCM per year, a rate equal to 159% of their sustainable yield. The over pumping ratio varies from 146% in minor aquifers to 235% in major ones.
    The over pumping from one aquifer in the 1960's and 1970!s caused its loss due to high salinity ratios. It is feared that this unpleasant experience will be repeated in some other aquifers if they are not rescued through proper management.
    There are extensive non-renewable reservoirs in the sandstone formation underlying almost the entire area of the country. The water quality of these reservoirs varies and is known to be fresh in the Disi-Mudawwara area.
    Qualities elsewhere have been sparsely investigated and preliminary findings indicate brackish water qualities. More work is needed to investigate these reservoirs.
    The use of fresh fossil waters from the non-renewable reservoir in Disi-Mudawwara started in the early eighties for municipal and industrial purposes in the city of Aqaba. This was followed by the use of the same aquifer (Disi) for agricultural purposes. Future use of this aquifer is earmarked for municipal purposes for the city of Amman, and pumping for agricultural purposes is being reduced.

     
    The Policy
     

    Objective

    The objective of this policy is to outline in more detail the statements contained in the document entitled: "Jordan's Water Strategy". The policy statements set out the Government's policy and intentions concerning groundwater management aiming at development of the resource, its protection, management and measures needed to bring the annual abstractions from the various renewable aquifers to the sustain-able rate of each.

    On Resource Exploration
    o       1. Plans and implementation measures for the exploration of ground-water resources shall be prepared and updated. Theoretical investigation and field operations in the form of drilling, sampling and logging shall be conducted continually.
    o       2.Assessment and re-assessment of the sustainable yields of ground-water reservoirs shall be made in light of the accumulation of data and information
    o       3. Monitoring of each reservoir shall be conducted through a network of observation wells. Such crucial data as the groundwater table, the draw down as a result of development, the physical, chemical and biological characteristics and their changes will be collected.
    o       4. Implementation of groundwater exploration will be conducted by MWI/WAJ personnel as a priority. The service can be out-sourced when deemed necessary or required by any partnership with others in this activity.
    o       5. Equipment, hardware and computer software needed for groundwater investigation and exploration shall be maintained by MWI/WAJ. Drilling services can be out-sourced when needed and so will be the maintenance of software packages.
    o       6. Advanced methods and tools for investigation including landsat imagery shall be employed, and co-operation with other countries in this field will be promoted.
    o       7. A comprehensive program to assess the potential of brackish groundwaters shall be conducted. Brackish groundwaters will be used to augment water supply for domestic uses through desalination in due time and specified localities. They also may be used for agricultural purposes where appropriate.
    o       8. Compilation of oil and gas drilling data as well as geophysical data shall be made to gain better understanding of the potential of the deep aquifers.


    On Monitoring
    o       9. A network of observation wells shall be installed in each of the groundwater reservoirs or parts thereof for the purpose of monitoring the conditions and performance of the reservoirs in response to development and abstraction.
    o       10. A groundwater reservoir can be divided into sub-units for the purposes of monitoring and control of abstraction
    o       11. Advanced technology shall be employed in the monitoring processes including the installation of water meters, remote control devices, telemetry, automation and field central controls.
    o       12. Data collected in the monitoring process shall be formatted for storage in and retrieval from computer files. Hard copies and computer back up copies shall be maintained at all times.
    o       13. Analysis and interpretation of data shall be made by a specialized group of professionals and their aides, and results published in special reports by MWI/WAJ.
    o       14. Logistics for the field teams shall be secured, and their working conditions improved to the best affordable levels.
    o       15. MWI/WAJ shall evaluate, update and redesign the groundwater-monitoring plan to cover all aquifers with emphasis on the overex-ploited and polluted aquifers.
     
    o       16. A special monitoring network of industries and olive presses will be adopted and installed for those with potential pollution to groundwater.

    On Resource Protection, Sustainability, and Quality Control
    o       17. Recharge areas of aquifers shall be protected to the maximum extent possible. Conflicts arising out of urbanization shall be addressed, and mitigation measures specified for the urban planners to have them included in the urban planning process.
    o       18. Recharge areas shall be protected against pollution caused by whatever means including solid and liquid waste disposal, mining, land fills, brine disposal, agricultural inputs and the like.
    o       19. Drilling of wells and abstraction of groundwater from them shall be prohibited without a drilling license and an abstraction permit issued by WAJ.
    o       20. Withdrawal from wells shall not exceed the abstraction permit rate under penalty of substantial fines and / or revoking the abstraction permit and the closure of the well. Over-abstraction from aquifers shall be reduced to sustainable levels in accordance with a time-phased plan.
    o       21. The laboratories of the Water Authority of Jordan shall be equipped with the latest technologies and equipment to match the requirements of good quality controls and assurance. Monitoring of groundwater qualities shall be made, hazards identified and mitigation measures specified and implemented.
    o       22. Withdrawal from non-renewable fossil aquifers shall be made carefully and after elaborate studies and investigations. A lifetime will be assigned for each of these aquifers and an abstraction rate specified accordingly.
    o       23. The MWI will co-operate with planning and environmental authorities to have polluting industries and solid waste dumps located outside the protection zones of aquifers.
    o       24. The MWI shall co-operate with the Ministry of Agriculture and its arm of extension service to regulate the type and application rate of fertilizers, pesticides, and sludge used within the area of aquifer recharge.
    o       25. MWI/WAJ in liaison with other authorities will seek to restrict storage of chemicals, waste materials and sewage treatment works within the inner circle protection zone.


    On Resource Development
    o       26. Development of groundwater reservoirs shall be commenced only after careful studies are made of the potential of each, and observation wells installed in carefully chosen locations to monitor the reservoir during exploitation. Wellfields shall be distributed with a proper distance between wells to minimize sudden drawdown of water levels.
    o       27.Development of deep groundwater aquifers shall be carefully made. Abstraction from them shall be gradual with periodic assessment of quality and quantity.
    o       28. Potentials of reservoirs shall be based on the natural rate of recharge. These can be augmented through means of artificial recharge induced through proper designs.
    o       29. Natural rainwater and treated effluent of wastewater are considered primary sources for artificial recharge. Monitoring of recharge facilities and their maintenance shall be made periodically.
    o       30 Development of groundwater reservoirs shall not be allowed without a license issued by MWI/WAJ. Private developers and public entities shall all be required to apply for any development they intend to undertake.%25
    o       31. Inflow into and outflow from each groundwater reservoir shall be determined as accurately as possible before any permit is issued for the development of that reservoir.
    o       32. Artificial underground storage, especially in the alluvial fans of the Jordan Valley shall be investigated.
    o       33. Groundwater mathematical models shall be developed or updated for all regional aquifers of the basins to predict their yield under various pumping scenarios.
    o       34. New nonrenewable groundwater sources shall be allocated to municipal and industrial uses as a first priority.
    o       35. MWI/WAJ shall encourage the use of groundwater conjunctively with surface water in places where such joint management has the potential for increasing the benefits of water use.
    o       36. MWI/WAJ shall encourage the use of marginal groundwater quality for agricultural uses especially when such use may relieve pumping from fresh groundwater aquifers.


    On Priority of Allocation
    o       37. Priority of allocation of groundwater shall be given to municipal and industrial uses, to educational institutes and to tourism. These purposes are deemed to have the higher returns in economic and social terms .
    o       38. Priority shall also be given to the sustainablility of existing irrigated agriculture where high capital investment had been made. In particular, trees irrigated from groundwater shall continue to receive an amount sufficient for their sustainability with the use of advanced irrigation methods.
    o       39. Expropriation of use rights arising from legal use of groundwater, or of water rights established on springs rising from groundwater reservoirs shall not be made without clear higher priority need, and against fair compensation.
    o       40. Priority shall be given to the use in irrigated agriculture of the reservoirs whose water quality does not qualify them for use in municipal and industrial purposes.
    o       41. Priority for use in agriculture shall also be given to the cases where supplementary irrigation from the groundwater reservoir is possible.
    o       42. A contingency plan shall be made and updated for the purpose of allocating the water from privately operated wells for use in the municipal networks.

    On Regulation and Control
    o       43. Campaigns shall be waged against illegal drilling of tube wells, and wells thus drilled shall be stopped, rigs confiscated and legal action taken against violators.
    o       44. Comprehensive groundwater basin management plan for each aquifer shall be developed as part of the National Water Master Plan.
    o       45. Water meters installed on groundwater wells shall be read on quarterly basis to make sure that abstraction from the wells do not exceed their allocations, specified in the permits.
    o       46. Prohibition of well licensing for agricultural purposes will be sustained. Only high priority purposes shall be entertained for licensing.
    o       47. Fees and charges will be used as an instrument to control ground-water over-pumping.

     

    On Legislation and Institutional Arrangements
    o       48. Legislation and institutional arrangements for the development and management of groundwater resources shall be reviewed from time to time. Shortcomings shall be addressed and institutional arrangements shall be updated, adjusted or restructured..
    o       49 Effective laws shall be reviewed from time to time with the intention of updating their provisions to match the requirements of changing times. By-laws issued under the applicable laws shall also be updated to serve the purpose of performance efficiency. Institutional set-up shall be reviewed in parallel, updated, adjusted or restructured to improve performance.
    o       50. Close co-operation will be maintained with the other organizations whose activities may directly impact the performance in the water sector.

    On Research, Development and Technology Transfer
    o       51. A study and research activity shall be entrusted with a specialized unit within MWI. The unit will be entrusted with technology transfer responsibilities.
    o       52. Due emphasis will be made on the efforts targeting human resources development.
    o       53. Training centers will be reinforced and upgraded. Cooperation with outside centers and agencies will be promoted.
    o       54. International and regional cooperation shall be pursued in the fields of research, development and technology transfer in ground-water exploration, management, quality control, and economics shall be promoted. Exchange of information and experience shall be maintained with regional and international parties.

    On Shared Groundwater Resources
    o       55. Legal research shall be made on the sharing of groundwater aquifers and their protection.
    o       56. Efforts shall be made and sustained to establish Jordan's rights in shared groundwater resources through international agreements.
    o       57. Regional data exchange on shared groundwater resources shall be encouraged.
    o       58. Cooperation with neighboring countries for the optimal and sus-tainable use and management of the shared groundwater resources, shall be sought.
    o       59. Special attention will be paid to the monitoring, assessment and development of shared groundwater resources.

    On Public Awareness
    o       60. Workshops and seminars for well owners will be organized to promote groundwater conservation and raise efficiency of groundwater use.
    o       61. Training programs for Ministry staff shall be conducted to build capacity for public awareness campaigns related to groundwater use and protection.
    o       62. MWI/WAJ in cooperation with other concerned agencies shall maintain a program to educate farmers on the importance of groundwater protection and shall promote technology transfer related to groundwater use in irrigation.
    o       63. Cooperation with other concerned agencies shall be maintained to encourage the reuse of groundwater in beneficial purposes.

    On Private Sector Participation
    o       64. The role of the private sector in the development of fresh ground-water resources shall be reduced where reduction of abstraction is sought. The private sector shall be encouraged to co-operate in the rehabilitation of aquifers where needed.
    o       65. The Private sector shall be encouraged to develop aquifers of marginal water quality for use in irrigation. It shall also be encouraged to develop fossil and renewable aquifers in remote areas for agricultural uses with the intention of promoting technology transfer and the creation of job opportunities.
    o       66. Desalination of brackish groundwater by the private sector shall be promoted. Care shall be given to the environmental impacts of such activities, particularly the safe disposal of brines.

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    IRRIGATION WATER POLICY

    Background 

    The Hashemite Kingdom of Jordan has been facing a chronic imbalance in the population - water resources equation, which imbalance is manifested by a substantial  in deficit in the foreign trade in food commodities ($110 per capita in 1997), and by rationing of municipal water that is serviced to the population twice a week. The total renewable freshwater resources of the country amount to an average of 750 MCM per year/ . The population in 1997 was around 4.4 million people, growing at an annual rate of 3.6%. The per capita share was 160 cubic meter per annum in 1997 and declines at a rate equal to that of the population increase .

    The production of food in semi-arid countries like Jordan is hardly possible without irrigation. The irrigated areas are located in the Jordan Valley (some 33,000 hectares), and in the Plateau (some 44,100 hectares). Some 400,000 hectares are fit for dry land farming, but it is practiced on half of this potential because of the insecurity associated with erratic rainfall and other reasons. Irrigated agriculture, however, provides most of the agricultural production in the Kingdom and offers the higher percentage of agricultural jobs and other jobs in support services.

    Because of the huge imbalance in the population - water resources equation, the treated wastewater effluent is added to the water stock for use in irrigated agriculture. It will constitute a substantial percentage of the irrigation water in future years.

    Development of Irrigated Agriculture

    Irrigated agriculture has been practiced in the Jordan Valley since the dawn of  civilization.  there Archaeological remains tell of the construction of water storage facilities and irrigation networks by the Nabateans before the Christian era in the Jordan Rift Valley and elsewhere. Irrigation was developed in the Rift Valley by channeling the uncontrolled perennial flow of side wades and rivers through well-developed water conveyance systems and irrigation techniques.

    Formal development and a rebirth of irrigated agriculture in Jordan started in the early 1950s in the Zarqa Triangle with irrigation from the uncontrolled flow of the Zarqa River. The Deir Alia agricultural experimental station was established at that time. The more serious effort was planned in 1954 - 1955, and implementation commenced with grant assistance from the United States towards the East Ghor Canal Project, renamed in 1986 as the King Abdallah Canal Project. The Project was implemented between 1959 and 1966 with USAID grant funds, and between 1968 - 1970 with support from the Kuwait Fund, between 1975 and 1980 with loan funds from USAID, IDA and KFW, and between 1983 and 1988 with loan funds from KFW, and, south of the Dead Sea with loan funds from the Kuwait Fund, the Saudi Fund and the Government of Italy. The older parts of the project were upgraded by conversion of surface canal networks to pressure pipe distribution networks between 1986 and 1996 with loan funds from the Arab Fund and the Government of Japan.

    Five storage dams have been built in the process; they serve as important feeders to the King Abdallah Canal. The Canal itself was rehabilitated between 1994 and 1998 with funds from the EIB.

    The total area thus developed in the Jordan Valley, under the responsibility and supervision of successive Government agencies, is about 33,000 hectares. About 8,000 more hectares of arable lands remain to be irrigated north of the Dead Sea, and some 2,000 hectares south of the Dead Sea. A potential exists for irrigated agriculture in Wadi Araba with groundwater sources and surface water sources.

    More development has taken place on the plateau using groundwater sources. The private sector was behind all that development, with the exception of small and scattered irrigation projects supervised by Government agencies in the 1960s. The total area thus irrigated amounts to about 44,100 hectares.

    The Policy

     Objective

    The following policy statements detail the long-term objectives outlined in the Water Strategy. It is to be noted that this policy addresses the irrigation water and does not extend to the issues of irrigated agriculture. It addresses in more detail water-related issues of resource development: agricultural use, resource management, the imperative of technology transfer, water quality, efficiency, cost recovery, management and other issues. Linkages with energy and the environment are accorded a separate chapter. This policy is compatible with the Water Strategy and is in conformity with its long-term objectives. Most of the provisions of this policy are being exercised, and some others are needed to maximize the benefit from irrigation water, and improve the social returns from its uses.

    While the policy is national, its implementation is vested in the respective Government agencies as stipulated by applicable laws. Of particular importance is the role of the Ministry of Water and Irrigation and the Ministry of Agriculture.

    On the Role of Irrigated Agriculture:

    1. Irrigated agriculture is a trade of Jordanian ancestry practiced in the Jordan Rift Valley and on its escarpment. Archaeological irrigation networks and facilities are standing evidence. Irrigated agriculture contributes to the production of food, and provides job opportunities in direct and indirect agricultural employment and supporting services. It also enhances the environment and helps arrest desertification.

    On Sustainability of Irrigated Agriculture :

    2. Existing areas of irrigated agriculture shall be accorded the chances for sustainability. No diversion of its waters to other uses shall be allowed without providing a replacement source fit for agricultural use unrestricted by health and public health considerations, and unduly hampered by chemical constraints.

    3. Sustainability of agriculture shall be compromised only if it threatens the sustainability of use of ground water resources. Potential pollution of underlying aquifers or the depletion thereof are among the reasons that can prompt such compromise.

    4. Irrigation water sources shall be protected against pollution which degrades water quality, is hazardous to the environmental integrity of soils, or can endanger animal health, particularly livestock. In this regard the adoption of biological control methods shall be promoted in lieu of the use of pesticides. Where desalination of brackish water is practiced, particular attention will be paid to the disposal of brine especially when such practice is done within the catchments area of dams.

    5. Close coordination shall be maintained with the Ministry of Agriculture and its research and development arm and with other related institutions with the aim of enhancing on-farm irrigation efficiencies and maximizing the agricultural output of a unit of land area per unit flow of irrigation water.

    6. Surplus surface water during the wet season shall be provided to farmers through the irrigation networks free of charge to leach soils especially those farms that are irrigated with treated wastewater in the dry season.

    7. Drainage networks shall be installed in irrigated areas where natural drainage is not sufficient to serve the purpose. Disposal of drainage water shall be made in an environmentally friendly manner. Maintenance of such networks shall be accorded attention similar to that paid to the maintenance of irrigation networks.

    On Resource Development and Use

    8. For irrigation purposes, and in light of the tight water situation, wastewater is considered a resource and can not be treated as "waste." It shall be collected and treated to standards that allow its reuse in irrigation unrestricted by health and public health considerations or unduly constrained by high salinity contents.

    9. In remote sparsely populated areas, and after satisfying the local municipal and industrial needs from unallocated water resources, water resources shall be allocated to agricultural production including livestock. Such development shall be planned and implemented in an integrated social and economic fashion in order that communities can be formed, settled and developed.

    10. Maximum use shall be made of rainfall for crop production, and supplementary irrigation shall be employed to maximize production including increasing cropping intensities.

    11. The use of brackish water in irrigation shall be pursued with care. Soil salinity resulting there from shall be monitored and its buildup managed and mitigated. Land shall be managed with the attention it deserves as a non-renewable resource.

    12. A revolving development plan for water resources, including irrigation resources, shall be adopted. The use of modern techniques made available by software development will be employed for the purpose.

    On Technology Transfer and Adaptation

    13. Despite the high percentage of agricultural water uses, the quantities used fall short of the needs. Higher agricultural yields shall be targeted and the transfer of advanced technology shall be endorsed and encouraged. The transformation of traditional irrigation and farming practices into modern methods shall be endorsed and promoted.

    14. Such advanced methods as drip irrigation, spray irrigation, micro-sprinkler irrigation are favored over less efficient methods. Local manufacturing of these equipment will be encouraged.

    15. Irrigation water conveyance and distribution shall be made through the installation of pressure pipe networks. Maximum use shall be made of gravity  generated pressures to operate these systems.

    16. Operation of the irrigation network will be improved to have the water filling the network for 24 hours. Such operation will enhance the benefits that accrue from drip irrigation. While in a rotation system the drip irrigation pipes act as on-farm conveyor,  24-hour operation has the advantage of operating the drippers as designed.

    17. Plant varieties developed as a result of genetic engineering research shall be favored for introduction into Jordan's markets. Maximizing resistance to pests, salinity and adverse conditions are features that are needed. Additionally, the maximization of crop yields is another beneficial feature of such varieties.

    18. Leasing of Government lands with permits to use water resources not earmarked for higher priority uses, especially in remote areas, shall be encouraged with the view of introducing advanced agricultural practices. Cooperation with advanced countries through technical co-operation shall be sought and promoted to advance technology transfer and adaptation.

    On-Farm Water Management

    19. Crop water requirements in the various micro-climatic zones of the country shall be experimentally determined, taking into consideration the prevailing different water qualities.

    20. Farmers shall be encouraged to monitor soil moisture on their farms to determine the timing for irrigation water application. The rate and duration of the application shall be adjusted to match the crop water requirements.

    21. In as much as is practical, investments on the farm to provide overnight water storage facilities shall be discouraged through providing a continuous supply of irrigation water in the distribution networks.

    22. Along with water management, farmers should be able to manage such other agricultural inputs as chemical fertilizers with the irrigation water.

    23. Night application of irrigation water, especially in the dry season, shall be encouraged to reduce evaporation losses.

    24. Automation of on-farm irrigation networks and their operation will be encouraged and training of farmers on advanced water management techniques shall be sought by cooperating with the research and extension service of the Ministry of Agriculture. Cooperation with other countries in this regard and in technology transfer in general shall be pursued.

    25. Programs shall be prepared to raise the public and farmers awareness of the availability of reused water, its rational and economic use and on the impacts of its quality.

    On Irrigation Water Quality

    26. Irrigation water quality shall be monitored through sampling at the sources and from the conveyance and distribution network. Farmers shall be alerted to any degradation of water quality. This is important so that they can plan the use of such water for the suitable farming purposes.

    27. Where marginal quality water, such as treated wastewater effluent, is a source of irrigation water, care should be taken, to the maximum extent possible, to have the quality improved to standards that allow its use for unrestricted irrigation. This can be achieved through blending with fresher water sources.

    28. The same applies to the potential use of drainage water or brackish water sources. However, farmers should be appraised of the potential quality of irrigation water so that their choice of crops is made with the necessary background information and knowledge.

    29. Soil salinity and water chemical contents are also constraining factors. Where its salinity is combined with water salinity, the environment of the root zone can cause high stress. Care shall be taken in providing testing services to farmers, and in promoting extension service in such zones where soil salinity and irrigation water salinity produce hostile roots environments.

    On Management and Administration

    30. Government agencies have been responsible for the development of water resources in the Jordan Valley and for the construction of the irrigation network. The Jordan Valley Authority (JVA) is the legal successor of these agencies and has been in operation since May 1977. It is the agency amongst them that has lived longest. The JVA is, as the predecessor agencies had been, responsible for the operation and maintenance of irrigation facilities, from the source (dams, rivers, springs) to the destination (farm gate).

    31. Piped irrigation networks shall be the standard method of irrigation conveyance and distribution. Where possible, gravity pressure shall provide the heads in the distribution networks. Supplementary pumping shall be used where needed.

    32. Irrigation water shall be metered at the farm turn-out. Digital meters shall be installed at each farm unit for volumetric measurement of in-flowing water.

    33. Government shall gradually phase-out of the business of irrigation water distribution, as is feasible, as soon as possible.

    34. Pilot irrigation areas shall be designated to test the workability of Participatory Irrigation Management (PIM), where farmers will assume the responsibility of water delivery to their farms. When found successful, PIM will be extended to the Jordan Valley irrigation systems.

    35. Development of water resources, including groundwater, outside the Jordan Valley has been the responsibility of the Water Authority, WAJ which since 1983 has been the successor, among others, of the Natural Resources Authority. Private farmers are allowed, by license and abstraction permit from WAJ, to exploit groundwater for all purposes, including irrigated agriculture. These private farmers operate their irrigation systems, and have introduced advanced irrigation techniques to their operations.

    36. Abstraction from all groundwater wells shall be metered, and monitoring of abstraction shall be made periodically to assure conformity with the provisions of the abstraction permits.

    On Public Awareness

    37. Public awareness campaigns shall be waged to urge the public to protect water resources against pollution, and to bring home the economic and social value of a unit flow of water.

    38. The cost of irrigation water development shall be emphasized, and the importance of protection of structures and utilities against vandalism shall be advocated.

    On Water Pricing

    39. Irrigation water shall be managed as an economic commodity that has an immense social value. Like other water resources, irrigation water is a national commodity owned by society at large without prejudice to existing water rights.

    40. Agriculture provides service to society in the form of employment, population distribution, provision of food that would otherwise have to be imported, and enhancing the environment. It is for this reason that agriculture enjoys support from society in the form of tax exemptions and subsidies.

    41. The water price shall at least cover the cost of operation and maintenance, and, subject to some other economic constraints, it should also recover part of the capital cost of the irrigation water project. The ultimate objective shall be full cost recovery subject to economic, social and political constraints. Due consideration shall be made of any water rights as established by law.

    42. Part of the capital cost shall be recovered through the application of a one-time charge against irrigation rights. This is applied as a rate per unit area of the irrigated farm. The size of the portion thus recovered shall not be less that half the irrigation network development cost.

    43. Differential prices can be applied to irrigation water to account for its quality.

    On Regulation and Controls

    44. Planting of crops with high water requirements shall be discouraged. Market forces shall be applied to discourage such plantations.

    45. Planting of perennial crops shall be allowed only with permits until such time as the water balance and the operation system show no signs of water stress in any of the dry months.

    46. Cooperation with other countries, regional and world wide, shall be promoted to enhance the marketing potential of Jordanian agricultural commodities and the products of its agro-industries.

    On Irrigation Efficiency

    47. Maximum overall irrigation efficiency shall be a standing target. Government agencies in charge of operation and maintenance shall endeavor to approach this target and maintain it.

    48. Automation of irrigation networks shall be pursued, and electronic surveillance and monitoring of irrigation networks shall be employed to reduce losses through leakage and breaks.

    49. Preventive maintenance of pumps, motors and valves shall be programmed and conducted periodically. Human resources for proper management of maintenance shall be secured to the maximum extent possible.

    50. On-farm automation, although the responsibility of farmers, shall be promoted through extension service and demonstration farms.

    51. Programs for manpower training to perform duties of irrigation operations, forecasts and scheduling of irrigation service shall be a standing objective.

    On Linkages with Energy and the Environment

    52. The use of herbicides that are environmentally friendly shall be encouraged. The savings in evapo-transpiration by unwanted plants is a positive outcome. Similar advantage is gained through the savings in plant nutrition that otherwise will be absorbed by unwanted vegetation.

    53. Serious care shall be taken in choosing the technology of wastewater treatment. The treated effluent, considered part of the irrigation water stock, shall be maintained as an environmentally accepted resource that can be safely handled by agricultural labor. It shall not be harmful to wild life or to domesticated animals on the farms.

    54. A trade-off shall be made between capital investment, energy requirements for operation, and the losses that will otherwise be incurred in the irrigation water resource. Choice of the optimal configuration shall be based on a thorough analysis of these factors.

    55. Maximum use shall be made of the gravity head inherent in the irrigation water sources of the Jordan Rift Valley. Supplementary head shall be generated through pumping interventions to maintain a suitable pressure head at the farm gate.

    On Legislation and Institutional Arrangements

    56. Legislation and institutional arrangements for the development and management of irrigation water resources shall be periodically reviewed. Gaps shall be filled, and updating of institutional arrangements with parallel legislation shall be made periodically.

    57. The role of government shall be fine-tuned and its involvement reduced over time to regulation and supervision. Involvement of stakeholders and the private sector in irrigation management and support will be introduced and expanded.

    58. The role of the private sector in the development of irrigated agriculture shall be promoted. Care will be taken to monitor and supervise the use of water resources in that regard.

    On Shared Water Resources

    59. Shared water resources occur in the Jordan River basin and in ground water resources to the south, east and north, and that are either used for irrigation or are mixed with irrigation water of the Jordan Valley. Priority shall be given to the development and management of shared water resources.

    60. The quality and flow rates of water obtained by Jordan shall always be monitored and proper records kept of such data.

    61. The establishment of Joint Water committees to co-operate with neighboring countries over issues affecting other riparians shall be promoted.

    62. Regional cooperation will be proposed, promoted and sustained with the neighboring countries with whom Jordan shares international waters.

    On Research and Development

    63. Applied research on water topics will be adopted and promoted. Such topics as water economics, resource management, crop water requirement, use of brackish water, irrigation technologies, farming practices, crop yields, moisture storage and the like are among favored topics.

    64. Cooperation with specialized centers in the country and outside will be promoted, and raising of funds for this purpose will be supported.

    65. Technology transfer and adaptation to local conditions will be a primary target for development activities and for adaptive research.

     

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    WASTEWATER MANAGEMENT POLICY

    Background

     The Hashemite Kingdom of Jordan is an arid to semi-arid country, with a land area of approximately 90,000 km2. Its topographic features are variable. A mountain range runs from the north to the south of the country. Land slopes gently to the east of this range to form the eastern deserts, but to the west the ground slopes steeply towards the Rift Valley, which extends from Lake Tiberias in the north, at an elevation of -220 m below see level, to the Red Sea at Aqaba.

    The growth of its population has not been natural over the past few decades. The more recent average population growth rate stands today at about 3.5% due to natural and non-voluntary migration. Although population growth rates are declining, the expanding population will continue to place enormous pressures on water resources. About 78 percent of the population is located in urban areas concentrated in four Govemorates: Amman, Balqa, Zarqa, and Irbid. The influx of waves of refugees and displaced persons has resulted largely in fast and almost uncontrolled urbanization.

     Jordan has been experiencing an imbalance in the population - water resources equation. Its per capita share of renewable water resources is among the lowest in the world, and is declining with time. It is projected to fall from 180 m3/capita/year at present to 90 m3/capita/year by 2025.

    Water resources consist primarily of surface and ground-water resources, with treated wastewater being used on an increasing scale for irrigation, mostly in the Jordan Valley. Renewable fresh water resources are estimated at about 850 million cubic meters  (MCM) per year, including water added by the Peace Treaty. About 125 MCM/ year is expected to be available from fossil aquifers and through desalination by the year 2005, making the annual freshwater stock about 975 MCM per year.

    Treated wastewater generated at sixteen existing wastewater treatment plants is an important component of Jordan's water resources. Due to the terrain and the concentration of the urban population above the Jordan Valley escarpment, the majority of treated wastewater is discharged into various watercourses and flows to the Jordan Valley where it is used for irrigation. About 60 MCM per year of treated wastewater are effectively discharged today into the watercourses or are used directly in irrigation.

    Wastewater quantity is increasing with the increase of population, increase in water use and the development of sewerage systems. Thus, by the year 2020 when the population is projected to be about 9.9 million and when the percentage of the population with sewerage service will have increased from the current 50 percent today to percentages that will cover most of the townships and cities of the country, about 240 MCM per year of wastewater are expected to be generated.

    Development and Status of Wastewater Sector

    Wastewater collection has been practiced in Jordan in a limited way since 1930 in the town of Salt. Some treatment was achieved by utilizing primitive physical processes. Mostly, however, septic tanks and cesspits were used with gray water often discharged to gardens. This practice resulted in major environmental problems, especially groundwater pollution. The pollution problems were complicated by the rapid urban growth. The population in the capital city of Amman, for example, increased from 50,000 in 1940 to 800,000 in 1985.

    Modern technology to collect and treat wastewater was introduced in the late 1960s when the first collection system and treatment plant was built at Ain Ghazal utilizing the conventional activated sludge process. The system consisted of a sewage network that runs by gravity to the lowest point in Amman, where the treatment plant was located and built. The treatment plant was designed to handle an average flow of 60,000 m3/d with a BOD5 loading of 18,000 kg/d, for a population of 300,000. The design effluent standard was BOD5 20 mg/1. The treated effluent was discharged to Sell Zarqa.

    However, due to the high strength of the raw sewage (i.e. the BOD5 of the incoming sewage was greater than 600 mg/1) the effectiveness of the activated sludge process was drastically reduced. Nevertheless, AGTP continued to operate under high organic overloading conditions, which resulted in major operational and environmental problems. As a result, AGTP produced odors that were a source of public nuisance to the surrounding areas. The quality of the effluent of AGTP deteriorated the quality of surface, ground and irrigation water in the region.

    Since the year 1980 and during the International Drinking Water and Sanitation Decade (1980-1990), the Government of Jordan carried out significant and comprehensive plans with regard to the different issues of wastewater management primarily related to the improvement of sanitation. About 75% of the urban population and 52% of the total population (at that time) gained access to wastewater collection and treatment systems. This has raised the sanitation level, improved public health, and strengthened pollution control of surface and groundwater in the areas served by wastewater facilities. Presently, there are 16 treatment plants serving most of the major cities and towns in the country. Ten facilities are conventional mechanical treatment plants and six employ waste stabilization ponds. Another two treatment plants are under construction. About 2 million people (nearly 50% of the population) are served by sewerage systems and the effluent quantity is estimated at about 60 million cubic meters per year.

    The characteristics of wastewater in Jordan are somewhat different from other countries. The average salinity of municipal water supply is 580 ppm of TDS, and the average domestic water consumption is low (around 70 1/c/d country wide). This results in very high organic loads and in a higher than normal salinity in wastewater. This is particularly applicable to wastewater treated in waste stabilization ponds (85% of the total generated wastewater), where part of the water is lost through evaporation, thus increasing salinity levels in the effluents. In addition, high organic loads impose operational problems where the plants become biologically overloaded with only a portion of their hydraulic loads.

    Given the low level of industrial discharges to sewage treatment plants, wastewater in Jordan is comparatively low in toxic pollutants such as heavy metals and toxic organic compounds. It is estimated that 10% of the biological load comes from industrial discharges.

    The major receiving streams for wastewater have very low flow with wastewater comprising a significant portion of stream flow. These streams are not used for bathing or fishing. Much of Amman's wastewater treated effluent is discharged in the Zarqa River and is impounded by the King Talal Dam where it gets blended with fresh flood water and is subsequently released for irrigation use in the Jordan Valley.

    It is worth mentioning that the increased supply of water to Jordan's cities came about at the expense of spring flows discharging into such streams as the Zarqa River, Wadi Shueib, Wadi Karak, Wadi Kufrinja and Wadi Arab. The flow of freshwater in these streams dried up as a result of increased pumping from the aquifers, and the flow was replaced with the effluent of treatment plants, a process that transformed the ecological balance over time.

    Varieties of crops are grown using irrigated wastewater including citrus, vegetables, field crops and bananas. Soil characteristics vary widely from sand to clay. Principal concerns in the use of wastewater for irrigation include its salinity, chloride concentrations, and the presence of fecal coliforms and nematode eggs. Concern about heavy metal, has not been substantiated but is an area of public concern warranting monitoring.

    The Jordanian standards and regulations which specify the quality of the treated effluents allowed to be discharged into wadis or destined for reuse in agriculture, require a secondary level of treatment. Quality specifications follow the WHO guidelines for the safe use of treated effluent in irrigation.

    In order to develop a Wastewater Management Policy, the following represent the key issues under consideration:

    1. Provision of adequate wastewater collection and treatment facilities for all the major cities and towns in Jordan.

    2. Protection of the environment and public health in the areas affected by the proposed systems, especially, surface waters and ground waters.

    3. Consideration of treated effluents as a source for irrigation reuse.

    4. Improvement of the socioeconomic conditions in the areas to be served by the proposed systems.

    The Policy

    On Resource Development

    1. Wastewater is a perennial water source and shall form an integral part of renewable water resources and the national water budget.

    2. Collection and treatment of wastewater is a necessity to circumvent hazards to the public health and the environment. It becomes imperative when contamination of freshwater resources with wastewater is immineat.

    3. Collection and treatment of wastewater becomes mandatory to protect public health against water borne diseases, and where epidemics become a threat otherwise.

    4. Existing levels of wastewater services shall be maintained and upgraded where necessary to enhance public health and the environment.

    5. Treatment of wastewater shall be targeted towards producing an effluent fit for reuse in irrigation in accordance with WHO and FAO guidelines as a minimum. Reuse of treated wastewater in other purposes shall be subject to appropriate specifications.

    6. Coordination shall be maintained with the official bodies in charge of urban development to account for the treatment and disposal of their liquid wastes. Central treatment plants shall be built to serve semi-urban and rural comunities, and collection of wastewater can be made initially through trucking until collection systems are justified.

    7. Specifications and minimum standards shall be issued by the competent authorities for the use of septic tanks in rural areas. Particular attention shall be paid to the protection of underlying aquifers.

    On Resource Management

    8. It is highly imperative that a section in the Water Authority be responsible for the development and management of wastewater systems as well as the treatment and reuse of the effluent.

    9. A basin management approach shall be adopted where possible. 'Ihe use of treated wastewater in irrigation shall be given the highest priority and shall be pursued with care.

    10. Effluent quality standards shall be defined based on the best attainable treatment technologies, and calibrated to support or improve ambient receiving conditions, and to meet public health standards for end users. Key factors will include the location of the discharge, its proximity to wells, the type of receiving water, and the nature and extent of end uses. Wastewater intended for irrigated agriculture will be regulated based on the soil characteristics of the irrigated land, the type of crops grown, the irrigation schedule and methods