Nepal’s freshwater availability and timing are under thread by extreme temperature and precipitation variations, changing monsoon patterns, melting of ice caps and glaciers, and reduced snow cover. Some initial estimated economic cost of climate change in agriculture, hydropower and water induced disasters show a number of up to 2-3% of GDP per year by 2050.

The proposed project aims to improve landscape-scale adaptation and disaster risk management through a set of outputs:

  1. Climate-smart landscape management practices adopted and enhanced
  2. Climate-resilient rural livelihoods developed
  3. Integrated disaster risk reduction and climate change adaptation approaches
  4. Capacities of local communities, regional and national decision-makers, and institutions on climate change adaptation and disaster risk reduction strengthened

FutureWater developed a so-called “Problem Tree” analysis for the proposed project. A Problem Tree is a helpful tool to understand the relationships between a problem, its causes, and its effects. The trunk of the tree represents the main problem, the roots the causes of the problem, and the branches the direct and indirect effects of the problem.

The project will be further developed as a so-called Climate Change Adaptation Project. More traditional development projects include also climate proofing, but focus is on development investments and adaptation is a secondary objective. Although those development projects contribute to adaptation (by helping the proposed asset or activity being financed to adapt to identified physical climate risks to the asset/activity), the primary objective of such a project is not adaptation. Climate Change Adaptation Projects are intentionally designed to enable climate adaptation of a high-risk topics. This is achieved by supporting outputs and activities that reduce the impacts of current and future expected climate risks and/or address barriers to adaptation, thereby advancing resilience. So this Climate Change Adaptation Project is meant to advance Nepal’s goal on adaptation.

FutureWater has undertaken a country wide climate risk screening as starting point for further project specific assessments. Main conclusions in the context of the program objectives were that by increased temperatures water supply will be challenged by the risk that water demand will increase and that at the same that supply will reduce by higher evaporation from catchments. Also waste water treatment will face the risk of reduced efficiencies.

India’s number of warm days and nights are expected to increase up to 70%. Water supply, wastewater treatment and urban water bodies will face same challenges as by increased temperature but more intense during those days. Similarly, heat waves are projected to be 3 to 4 times higher by the end of the twenty-first century. The result will be that water supply, waste water treatments and urban water bodies will face same challenges as under increased temperature but even more pronounced during those heat wave periods.

An increase in mean precipitation is uncertain according to various climate projection. If this increase will happen the impact on the three program components (water supply, waste water, urban water bodies) will be manageable. However, a decrease in mean precipitation is projected as well according to some climate scenarios. If this will happen then water supply will be at high risk of water shortages by a higher demand from users and a reduction in supply from rivers, streams and in the longer run from groundwater. An increase in daily precipitation extremes is quite likely to happen according to most climate scenario. Risk of additional flooding will increase.

The analysis concluded that since the location where projects will be implemented in the context of this program has to be defined yet, only generic conclusions relevant for the entire country could be provided. It was highly advised that for each specific project that will be implemented a detailed Climate Risk Assessment has to be undertaken.

The study will focus on selection of key traded crops between the EU and Africa and their key producing regions. The tasks will include overall analysis of current practices and the background in the regions, determination of key sensitive parameters in order to select key crops and food products and map hotspot regions. In addition, project team will assess climate risks for these hotspots on key crops and food products and link these risks with the importing countries. Climate risks will be assessed by identifying the multiple climate sensitivities on the food systems in each region, assessing changes predicted by a CMIP6 (latest) climate model ensemble on key agriculture-related climate indices, and analysing impacts on production-related indices, distinguishing between rainfed and irrigated production systems. It will be focused on country specific case studies in each partner country. The impacts of climate change on trade patterns will be evaluated to assess the carbon- and water footprints and virtual water profiles of key traded commodities of these countries. At the end, the project team will focus on policy relevance and assessment of adaptation strategies and identify interventions that will be needed, at which point in the system, and from which sector (or actor) is of interest.

The outcomes of CREATE will be used to increase awareness of the risks that climate change poses to the agro-food trade and the broader economy at large. They can contribute to efforts by the governments (macro-scale), the communities (meso-scale), as well as relevant agricultural producers (micro scale) in the case study countries, by providing essential information for promoting actions towards mitigating the negative consequences of climate change on agro-food trade.

The objectives of this climate risk assessment for the Li River in China is to assess current flood risk and future flood risk in the Li river basin in China. With an average of 1800 mm annual total rainfall, floods are severe and frequent in the region. Additionally to rainfall, severe floods in are often related to discharges from upstream reservoirs

Given the fact that this area is data scarce, global datasets with climatic data (ERA5-Land), soil parameters (HiHydroSoil) and land cover (Copernicus) were used to feed a hydrological HEC-HMS model to calculate the discharge for the extreme event of June 2020. Based on measured water levels and discharge, it was possible to develop rating curves and with these rating curves, it was possible to estimate water levels in the river for current (validation) and future conditions. This analysis served as input for the full climate risk assessment,  in which possible interventions were proposed to reduce flood risk in the future.

The goal of the Asian Development Bank project ‘Renewable Energy for Climate Resilience’ in Bhutan is to diversify Bhutan’s energy portfolio. Bhutan’s power sector almost exclusively relies on hydropower generation. Hydropower, however, is vulnerable to climate change and natural disasters caused by climate change. The first deployment of non-hydro renewables at utility scale in Bhutan will be the first step to diversify the power generation portfolio, increase the resilience against severe weather events such as droughts, and complement the hydropower generation profile during the dry season. Other renewable energy resources such as solar photovoltaic (PV) and wind can complement hydropower in forming a more diversified electricity generation portfolio, which is, in healthy mix, resilient to changes in seasonal weather patterns and weather extremes that can adversely affect power supply.

Within this project ADB develops two solar and one wind plant. FutureWater has undertaken a Climate Risk and Adaptation assessment (CRA) for these power plants, with a two-fold objective:

  1. Validate the underlying rationale for diversification of Bhutan’s energy generation portfolio. The rationale is that more unreliable flows under climate change adversely affect the hydropower generation, in particular in the low flow season outside the monsoon season. This are the seasons with high potential for solar and wind energy, under the current climate conditions. The diversification of Bhutan’s energy generation portfolio is considered as type 2 adaptation, related to system change and resilience building in the climate change context.
  2. Assess the vulnerability of the project components to future climate change and recommend adaptation options for climate-proofing of the design. This is considered as type 1 adaptation, related to climate proofing.

The rationale for diversification is related to the expectation that climate change impacts on the cryosphere and hydrology in Bhutan will lead to less reliable flows, in particular outside the monsoon season. This will make hydropower a less reliable source of energy, which may not be sufficient during the dry season. During these periods outside the monsoon season, the climate in Bhutan is characterized by clear skies and daily patterns of wind. This intuitively makes solar and wind suitable energy sources to complement hydropower.

The CRA concludes that this rationale holds when validated with future scenarios of climate change and hydrological changes. These project more erratic flows, meaning on one hand more extremes on the high end (floods), in itself posing risks for hydropower infrastructure, but also through increasing sediment loads and risks of exposure to landslides and glacier lake outburst floods. On the other hand, a small increase in frequency and length of hydrological droughts is projected. Furthermore, projections of wind speed and incoming solar radiation indicate more or less stable conditions compared to the present day climate, further substantiating the rationale for portfolio diversification.

For adaptation and climate proofing the main recommendation is to verify that the proposed drainage systems at the sites are sized for extreme flows that are 20-30% larger in magnitude than current extremes. This is valid across return periods. The second high priority recommendation is to design foundations of solar, wind, and transmission infrastructure to withstand increased erosion rates and substantially increased risk of landslides in landslide prone areas. A third recommendation is to take into account lower production for solar panels at increased frequency of heat stress, as well as in the sizing of capacity of transmission infrastructure, which may have reduced capacity during periods of high heat stress.

Het doel van deze berekeningen was om uitsluitsel te kunnen geven over de nut en noodzaak van de geplande bergingsgebieden ter invulling van de wateropgave uit 2009. Met behulp van een Sobek-model zijn verschillende scenarioberekeningen uitgevoerd waarbij waterstanden, afvoeren en NBW-knelpunten zijn vergeleken onder het huidige en toekomstig klimaat en met en zonder integratie van bergingsgebieden.

De werkzaamheden bestonden onder meer uit:

  1. Toetsing van afvoer en waterstanden op kritieke locaties voor het klimaatscenario bij verschillende herhalingstijden (NBW-toetsing voor toekomstig klimaat),
  2. Vergelijking van NBW-knelpunten onder het huidige en toekomstige klimaat,
  3. Integratie van bergingsgebieden in het Sobek model en analyse van de impact op waterstanden, afvoer en toekomstige NBW-knelpunten (resultaat nut en noodzaak bergingsgebieden: antwoord op het LBW-vraagstuk),
  4. Een eerste inschatting van kritieke locaties langs de overige keringen voor de verschillende scenarios (hoge resolutie vergelijking van waterstanden en keringenhoogtes) en
  5. Een vergelijking van de resultaten met een aantal eerder uitgevoerde studies.

Tijdens het project is de NBW-toetingsmethode, die in 2020 was ontwikkeld door Arcadis, (verder) geautomatiseerd, zodat de methode sneller en voor andere vergelijkbare projecten binnen Vechtstromen kan worden toegepast. Op basis van de uitkomsten uit de berekeningen kon een duidelijk advies worden gegeven over de nut en noodzaak van de voorgestelde bergingsgebieden uit 2009.

Meer informatie over de methode rondom de normering van regionale wateroverlast (NBW / LBW) die wordt gehanteerd door waterschap Vechtstromen is te vinden op de volgende website: https://www.vechtstromen.nl/over/klimaat/wateroverlast/normering/werkt-normering/

 

Geodata tools have been developing rapidly in the past years and are vastly adopted by researchers and increasingly by policy-makers. However, the is still great potential to increase the practical application of these tools in the agricultural sector, which is currently applied by a limited number of ‘pioneering’ farmers. The information that can be gained from geodata tools on irrigation management, pest and nutrient management, and crop selection, is a valuable asset for farmers. Key players for providing such information to the farmers are the extensions officers. This project aims at training extension officers in the use of these geodata tools. The beneficiaries in Egypt are: Tamkeen for Advanced Agriculture, FAODA, IDAM, Bio-Oasis, and LEPECHA. The selected participants will receive a training programme which consists firstly of several session on the background and theory of the geodata tools, provided through our online teaching platform (futurewater.moodle.school). Starting from May (2021) field schools will be set up to use the geodata tools for decision-making in these demonstration plots. In addition, modules are taught on the quality of the data, and profitability of such tools. Altogether, a group of carefully selected participants will receive training on these innovative tools and create a bridge to providing this information to farmers specifically the smallholder farmers.

Asian Development Bank (ADB) is supporting the Government of Kazakhstan in it’s “Wastewater Treatment Plants Reconstruction and Construction Program”. The overall aim is to improve the wastewater treatment facilities in the 53 cities across Kazakhstan. The Program will be implemented through a phased approach. During the first phase five Wastewater Treatment Plants in Stepnogorsk, Zhezkazgan, Satpayev, Balkhash and Zhanatas are to be financed by ADB.

FutureWater has undertaken a climate risk and adaptation analysis for those facilities. FutureWater has extended and updated a previous climate risk assessment (CRA). The original CRA was based on the CMIP3 projections and only some selected climate models were used. FutureWater has updated the original CRA by using downscaled CMIP5 projections (NASA-NEX) for RCP4.5 and RCP8.5 and the full range of climate models. Also adaptation strategies were refined.

Results show that the key climate risks includes a projected increase in mean annual temperature for all five waste water treatment plants and hottest day temperature are in the same range. Those higher temperatures might negatively affect operations and efficiencies of the plants. Mean annual precipitation is projected to increase for all five treatment plants. Potential risk of flooding of the infrastructure or large influx of storm water is determined by wettest day precipitation. An increase in wettest day precipitation is projected to be between 6% to 14%. Zhanatas and Stepnogorsk waste water treatment plants are most vulnerable regarding the risk of increased severity and frequency of floods.

Adaptation interventions to those projected climate changes are explored in the initial environmental examination (IEE) and will be further developed during the detailed design phase. The following broad adaptation options are foreseen:

  • selection of sites less prone to flooding for the two new WWTP,
  • flood protection of the three WWTP to be rehabilitated,
  • selection of sewerage technology that will function under higher temperatures,
  • awareness raising of staff, and
  • monitoring to avoid sewer overflows during storm events.

The Asian Development Bank is supporting the Government of Indonesia in developing its water infrastructure. Impact of climate change and potential adaptation to those changes are evaluated. One component of the project is to assess water availability for all Indonesian catchments currently and under changing climate. FutureWater has supported the program by developing a climate risk screening approach to rapidly assess current water resource availability and the impact of climate change on this.

Various rapid assessment assessments have been tested and the Turc implementation of the Budyko framework has been proven to be effective for basins in Indonesia. ERA5 past climate and NASA-NEX GDDP climate projections have been applied for all basins in Indonesia. Results show that all Indonesian basins are likely to see an increase in runoff over the coming century. However, variability in runoff will increase, with more extreme dry and wet periods. This will have implications for water management planning and climate related hazards such as more prolonged droughts and higher risks of flooding.

Recently, the Central Asia Regional Economic Cooperation (CAREC) Program introduced agriculture and water as a new cluster in its strategic framework. Recognizing the complexities of the water sector and the existing landscape of cooperation activities, the strategic framework proposes a complementary approach that uses the strengths of CAREC to further promote dialogue on water issues. A scoping study was commissioned, supported by the Asian Development Bank (ADB), to develop a framework for the Water Pillar for further consideration by the governing bodies of CAREC. It was agreed that the initial focus of the Water Pillar should be on the five Central Asian states with consideration given to expanding to other CAREC member countries over time.

The objective of the study is to develop the scope of a Water Pillar Framework that includes a roadmap of national development interventions for each of the five Central Asian Republics that responds to the prevailing challenges and opportunities in water resources management.

The framework will be derived from three specific outputs:

  • Output 1: Projection of future availability and demand for water resources for the Central Asia region up to 2050 including implications of climate change.
  • Output 2: Identification of future water resources development and management opportunities in the form of a sector specific framework for water resources infrastructure taking into consideration sustainability issues through a comparative assessment of cost recovery mechanisms and operation and maintenance (O&M) practices.
  • Output 3: Preparation of a framework for policy and institutional strengthening that addresses common themes and issues related to national water resources legislation and the capacity and knowledge development needs of water resources agencies with an emphasis on economic aspects and sustainable financing.

For this work, several consultants were recruited. FutureWater provides key inputs on the climate change and water resources aspects, including desk review, stakeholder consultations across the five regions and across all sectors, and analysis of climate change risks and identification of adaptation options that have a regional dimension and can be taken up through regional or bilateral cooperation.