Hywel Griffiths and I recently attended a UK-Jordan workshop on catchment management and water security in Al Kerak, Jordan (23-25th April 2019). The workshop was supported by a grant from the British Council as part of the Newton Fund Researcher Links Programme, and was organised by Jonathan Bridge (Sheffield Hallam University, UK) and Sultan Tarawneh (Mu’tah University). The idea for the workshop originated from a long-standing collaboration between UK partners and Mu’tah University that has addressed catchment modelling and management in central Jordan. Particular focus has been on the Wadi Wala catchment that drains the western Badia Desert and the central highlands south of Amman. The upper 1743 km2 of the catchment was dammed in 2002 to provide irrigation water and function as a managed aquifer recharge (MAR) test site, with the intended benefits of improving drinking water supply to local communities. Since dam closure, however, high sedimentation rates have decreased reservoir capacity by approximately 30%, impacting its MAR performance and prompting substantial new engineering works to raise the dam wall by 15 m.
Water supply issues in the Wadi Wala catchment are emblematic of the wider water challenges in Jordan, which is widely acknowledged to be one of the most water stressed countries in the world. More than 90% of the country has a mean annual rainfall less than 200 mm, resulting in restricted surface freshwater availability and limited aquifer recharge rates, while climate change and rapid population growth – accelerated in recent years by an influx of refugees from neighbouring territories like Palestine, Syria and Iraq – have substantially increased pressures on water quantity and water quality. According to a 2015 joint UNEP and WaterLex report (see http://www.unwater.org/success-stories-regulating-wastewater-management/), available renewable water resources have dropped dramatically from an annual per capita share of 3600 m3 in 1946 to around 130 m3 in recent years. In addition, short-lived flash floods or longer drought episodes periodically blight different regions, leading to soil erosion, ecological disruption, infrastructural damage, and even loss of human life. So what can we do about this? How can we improve catchment management to improve water security in Jordan? Can we integrate existing and new approaches to water harvesting, wastewater re-use, soil conservation, ecological restoration, river management and so on to achieve this objective?
Hywel and myself had been invited to the workshop on the basis of our previous experience with river and wetland processes, human-environment interactions, and catchment management in drylands. Our recent contribution to the British Council workshop in Argentinian Patagonia (see https://stephentooth.wordpress.com/2019/03/24/wet-places-in-a-normally-dry-land/) was also beneficial for identifying parallels and overlap in themes covered by the workshop. A blend of early career and more established researchers from both the UK (7 others, making 9 UK participants in total) and Jordan (11 total) provided complementary expertise in hydrogeology, hydroclimatology, environmental monitoring, water harvesting techniques, irrigation, sustainable water technology, land and soil conservation, among many others.
The workshop was organised in three parts, covering three days. On Day 1, after a welcome from research and administrative staff at the campus of Mu’tah University (located ½ hour’s drive south of Al Kerak), the participants returned to the Falcon Rock Conference Centre for talks from the invited ‘expert mentors’, followed by breakout group discussions to identify areas of mutual interest that might form the basis for project proposals. As one of the mentors, my contribution was a ½ hour talk that provided a global perspective on rivers and wetlands in drylands. The talk highlighted, inter alia, the diversity of dryland river process and form, the role of wetlands in ecosystem service provision, and approaches to management of wetlands in drylands. A booklet from the Wetlands in Drylands Research Network entitled ‘10 Reasons why the Geomorphology of Wetlands is Important’ (see http://wetlandsindrylands.net/downloads-2/) was distributed to participants, along with copies of Tooth and Ralph’s recent ‘awareness-raising’ article in ‘Geography Review’ (2019, v.32). Part of the purpose of the talk was also to contextualise rivers and wetlands in the drylands of Jordan against this wider international backdrop. What are the key characteristics of Jordan’s dryland rivers? Where are the key wetlands in Jordan’s drylands, and is there any legislative protection? What are the ecosystem services provided by these rivers and wetlands and how might the services change in future?
Building on ideas outlined by Grenfell et al. (2014, Geomorphology, v.205) and Larkin et al. (2017, Earth Surface Processes and Landforms, v.42), Tooth and Ralph’s 2019 ‘Geography Review’ article includes a diagram showing how river and wetland processes, forms and associated ecosystem services might be anticipated to undergo change as systems move along an aridity gradient. The diagram hypothesises what might happen to ecosystem services under conditions of reduced flow frequency that results from climate change (e.g. global warming that leads to lower precipitation and/or greater evapotranspiration) but also perhaps from human activities (e.g. abstraction, flow diversion).
But is it a one-way street? Can we envision scenarios whereby rivers and wetlands might move in the other direction towards a condition of greater flow frequency? One of the provocations in my talk was the potential for use of controlled wastewater discharges (i.e. treated used water, or ‘greywater’) to promote more regular flows along sections of normally ephemeral channels, with the aim of enabling within- and near-channel vegetation growth. In both rural and urban settings, this might have a range of benefits, including ecological enhancement, slowing of flow velocities, increased sediment deposition, and promotion of aquifer recharge. This might help provide some level of protection against potentially erosive flash floods and also slow sedimentation rates in downstream dams. But what might be some of the limits to such schemes? Might they just promote riparian monocultures (e.g. reedbeds) with little biodiversity gains and possibly even displacement of native riparian flora and fauna? Might fine sediment deposition under vegetated, slower flow conditions lead to change in bed surface textures, perhaps detrimentally for native fauna (e.g. macroinvertebrates) adapted to living in typically coarse-grained, open framework gravels, as well as having negative implications for rates of aquifer recharge? Might the inevitable decreases in channel cross-sectional area increase local flash hazards? And what might be the consequences of long-term sediment build-up in such vegetated reaches?
As a water scarce country, Jordan is relatively well advanced in the use of wastewater, even being cited as a ‘success story’ of regulating wastewater management in the joint UNEP/WaterLex report (http://www.unwater.org/success-stories-regulating-wastewater-management/). According to the report, over the last 25 years or so, the number of wastewater treatment plants has more than doubled to around 28, with more than 90% of the treated effluent being re-used in agriculture where it is sometimes mixed with rainwater. But could such treated or blended wastewater be used for the alternative purposes outlined above (e.g. ecological enhancement, flow and sediment control, aquifer recharge)? As far as I am aware there have been no studies in Jordan of the potential benefits or disbenefits – in other words, the ecosystem services or disservices – of using wastewater for these alternative purposes, and no rigorous assessments of the trade-offs involved. Farther west, on the other side of the Dead Sea, ongoing focus is on water quality and human rights issues associated with untreated wastewater discharge in Israel and the Palestinian Territories (https://www.btselem.org/download/200906_foul_play_eng.pdf), but one of the only studies of the potential geomorphological impacts of wastewater was published nearly two decades ago by Hassan and Egozi (2001, Earth Surface Processes and Landforms, v.26). These authors showed how nutrient-rich wastewater flow from developing urban areas caused rapid shifts from dry ephemeral channels with intermittent floods to vegetated channels with continuous flow, in some instance inducing marked decreases in cross-sectional areas. Surely, there is an opportunity to revisit some of that work and examine other aspects, including the implications for ecology and surface water-ground water interactions?
On Day 2, workshop participants were treated to a field trip around central Jordan. The trip was led by Esraa Tarawneh, and included visits to the Wadi Mujib and Wadi Wala dams, and the Dead Sea. Technically, the Dead Sea is an inland saline lake, with water that is nearly 10 times as salty as the ocean. Owing to diversion of inflowing water from the Jordan River that enters the Sea from the north, the level of the Sea has been falling steadily (~1 m per year over the last few decades), prompting a suite of environmental and infrastructural concerns (see https://en.wikipedia.org/wiki/Dead_Sea#Recession_and_environmental_concerns).
Having descended the spectacular eastern flank of the Jordan Rift Valley to park by the side of the road that runs alongside the Sea, we all scrambled down the steeply-sloping shore sediments to the lowest land point on Earth (~430 m below global sea level). Along with the bubbling evidence of subterranean springs, and outcrops of the famous Dead Sea mud (touted by many for its supposed healing properties for skin complaints and physical ailments), there was the depressing sight of the near-ubiquitous plastic trash lines. The lowest point on Earth and surely one of humanity’s lowest points?
One of my earliest memories of learning about the place called the Dead Sea did not involve mention of plastics. Instead, it was a photograph in a children’s atlas from the early to mid 1970s that showed someone reading a newspaper while floating in the Dead Sea. This always intrigued me, but even then I think I vaguely understood the concept of salty water having extra buoyancy. Given the limited time available on the field trip, I decided not to investigate these properties personally (although this did mean passing up a golden photo opportunity) but luckily a random tourist was on hand to provide an ample demonstration. And an impromptu investigation of the influence of buoyancy on stone skimming proved irresistible to many on the trip, myself included. It was hardly an example of controlled experimentation, but some of those stones did seem to skim just a few extra times off the mirror smooth surface.
After returning to the vehicle, we crossed over a number of the spectacular ephemeral wadis that periodically disgorge water and sediment into the Dead Sea, sometimes with catastrophic consequences (https://www.reuters.com/article/us-jordan-floods/jordan-flash-floods-kill-21-people-many-of-them-school-children-on-bus-idUSKCN1MZ2GI). In the blazing afternoon sun, we also had good views of the delta sediments exposed by the falling sea level before we ascended the rift flank for the 30 km journey back to Al Kerak and its spectacular stone castle. From the lowest point on Earth and its plasticized cultural low point to what is certainly one of humanity’s cultural high points.
Given time pressures and other priorities for the field trip, there was little opportunity for further examination or discussion of Jordan’s rivers and wetlands. On this trip and more generally throughout the workshop, wetlands in drylands remained largely out of sight and out of mind. And in the evening, one of the regular stumbling blocks to raising the profile of wetlands in drylands surfaced. Jordan has two wetlands on the Ramsar list (Azraq Oasis and Fifa Nature Reserve – see https://www.ramsar.org/wetland/jordan), plus undoubtedly numerous other smaller wetlands. But a Jordanian participant insisted that the Fifa Nature Reserve is not really a wetland because it only floods occasionally and isn’t always wet. No matter if it is on the Ramsar list: in their view, the absence of water year-round means that it is not really a wetland. My protests about the need for a more inclusive definition of wetlands that recognizes and celebrates those wetlands that aren’t always wet – the ephemeral, seasonal or temporary wetlands of the world – seemingly fell largely on deaf ears. Coming on the back of similar confusion at the Argentinian workshop (http://wetlandsindrylands.net/latest-posts/ – scroll down to ‘Wet Places in a Dry Land: Expanding Research into Patagonia’s Desert Rivers and Wetlands’), the growing community of wetlands in drylands researchers clearly has much work still to do.
On Day 3, the workshop again returned to the Falcon Rock Conference Centre, with activities largely revolving around breakout group discussions to identify potential projects to take forward in UK-Jordan collaborations. A range of viable projects was proposed, with most interest crystallising around projects to develop environmental databases, investigate surface water-groundwater interactions, and model climate change impacts on Jordan’s water resources.
At this stage, and amongst this particular group of researchers, it seemed that there was not much enthusiasm for a project to investigate the potential use of controlled wastewater discharges for promoting more regular flows along sections of normally ephemeral channels, and for monitoring the impacts on river and wetland ecosystem services. To be fair, it would be a challenging project to execute, particularly given the need for controlled experimentation and ongoing monitoring over several years (minimum 3-5 years?), most likely using paired catchments. Input from specialists in Jordanian riparian ecology would also be key to the success of any such project. But at least the idea has been sown, and even if it takes some time to grow, may still be worth pursuing in future. In country so water stressed, yet also periodically blighted by disastrous flash floods, it almost seems criminal not to investigate all possible alternative uses and re-uses of the limited water supplies.