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Hammamet, Tunisia, 25-26 September 2014
National Workshop on Water Resources and Livelihoods in the Dry Areas Considering Climate Uncertainty Hammamet, Tunisia, September 2014 INTEGRATED TECHNICAL AND ECONOMIC ASSESSMENT OF WATER HARVESTING INTERVENTIONS IN PERSPECTIVE FOR CC MITIGATION (Case of Oum Zessar Watershed)
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OUTLINE
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Introduction & general approach
Review of conducted works WLI and CRP-DS findings Conclusions & prospects
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INTRODUCTION
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Socio-economic mutations
Climate Soil Rainfed dominated Socio-economic mutations CC
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WH Biophysical Environmental Economic Social CC
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OVERVIEW OF CONDUCTED WORKS
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Catchment Cropping Area 400 100 Jessour Dike
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Mean annual temperature (°C) 20
Oum Zessar Area (km2) 350 Annual rainfall (mm) 180 Mean annual temperature (°C) 20 Altitude (m) 0-715 Population (inhabitants) 24000
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Water balance Hyd. Year ETrel (2/1) ETrel (3/1) ETrel (3/2) Wet 1.1 -
Water balance on the terrace Hyd. Year ETrel (2/1) ETrel (3/1) ETrel (3/2) Wet 1.1 - Dry 2.3 2.5 Very dry 12.0 15.6 1.3 Hyd. Year: type of the hydrological year ETrel: relative ETa 1: ETa with only rainfall on the terrace 2: ETa with rainfall and runoff on the terrace 3: ETa with rainfall, runoff and supplemental irrigation
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Recharge structures Capacity loss of the gabion structures Wadi
Location Sediment (cm) Loss (%) Oum Zessar Down 5 Koutine 50 14 Mid 20 18 21 Nkim 56 Hallouf Up 150 88
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Recharge well filter transmission capacity
Runs K (cm/h) Loss (%) 1 193.5 0.0 5 52.7 72.8 6 40.2 79.2 7 33.0 82.9 13 7.0 96.4
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Effets des aménagements
Piézométrie et exploitation de la nappe de ZK Effets des aménagements Exploitation accrue !!! Chute de la de la PZ quelque soit la pluviométrie
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SC0 SC1 SC2 SC3 mm % Rainfall 183.9 - - ET 107.0a 58.2 147.2b 80.1 150.9 b 82.0 Outflow 34.3 a 18.7 4.0 b 2.2 0.1 c 0.0 Perco 14.5 a 7.9 24.3 b 13.2 28.2 b 15.4 28.3 b TLOSS 28.0 a 15.2 8.2 b 4.4 3.1 c 1.7 3.2 c Seepage 0 a 1.1 b 0.6 0.9 b 0.5
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SC0 SC2 VD D N W VW VD
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WLI CRP-DS FINDINGS
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Chabeat Anez Site
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Loudayette site
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Oued Moussa Site
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Integrated impact assessment of livelihood & water management practices in oum zessar watershed
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Methodology Extended cost-benefit analysis (ECBA) to environmental externalities : It was carried out in order to assess the costs and benefits of WHT works implemented by the WLI project in the selected farms. External economic and environmental phenomena, tangible as well as intangible effects have been integrated in the analysis. Evaluation criteria used were the Net Present Value (NPV) and the Internal Rate of Return (IRR). Data for CBA come from a survey conducted during An appropriate time horizon was set at 30 years Sustainable Livelihoods Approach (SLA): this approach is carried out in order to assess patterns and drivers impacts on livelihood condition. SLA is an analytical framework that helps to understand the factors that influence the ability of people to achieve sustainable development in a particular circumstance. The livelihood framework is based on five capital assets; social, human, physical and financial capital. To evaluate the five livelihood assets in the up-stream, mid-stream and down-stream of Oum Zessar watershed, data has been gathered using socio economic survey (139 surveys) conducted in LADA approach was adapted in order to select indicators and carry out the scoring for each asset.
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List of indicators by type of livelihood capital
Sustainable Livelihoods Approach (SLA) List of indicators by type of livelihood capital Natural capital Financial capital Physical capital Human capital Social capital Livestock Farm size Land quality Water quality Olive trees Agriculture income Livestock income Off-farm income Jessour Ownership of plowing means Education, Household size Age Households expenditure Member of association, Distance to nearest hospital , Certificate of Ownership, SONEDE network
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Social capital is the most dominating capital in the three locations followed by physical capital mainly in Beni khdeche and Sidi Makhlouf. Financial capital seems to be not representative in the different location due to the low agriculture and livestock incomes. Projections indicate that the livelihood assets will be changed during period. Physical, human and social capital will be improved with very little increment in financial capital. Natural capital will slowly decrease. Factors that contributed to the decline of natural capital were agricultural intensification and poor land management.
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Trends of different livelihood capitals over time
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IRR and sensitivity analysis (WHT investment at farm level)
IRR % Observed Costs + 10 % Benefits - 20 % Financial CBA 24% 27% 21% Economic CBA 29% 23% Extended CBA 20% Net Present Value , WHT investment NPV (DT) Discount rate 12% 10% 8% Costs + 10 % Benefits - 20 % Finacial CBA 2491 3615 5231 2340 1691 Economic CBA 3023 4283 6092 2884 2140 Extended CBA 2073 3027 4402 1910 1333
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The CBA shows that the WHT works are profitable at the private level with an IRR of 24 % and an NPV (at 12 % discount rate) of 2491 DT. The inclusion in the analysis of the off-site benefits improves the economic profitability considerably, with an NPV (at 12% discount rate) of 3023 DT DT and an IRR of 27 %. The incorporation of other external and indirect effects with no market prices (failure of jessour) resulted in a decrease NPV (at 12 % discount rate) of 2073 DT and IRR of 23 %. The sensitivity analysis confirm the basic analysis. The WHT works are apparently beneficial at private and social levels for local population within the watershed. Conclusion Integrated impact assessment can be a useful tool for community inclusion and livelihood strategy assessment. Sustainable land and water management practices and livelihood strategies improve rural livelihoods of farmers in dry area. The presented results are under finalization, the next steps consist of hypothesis verification and scenario building.
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CONCLUSIONS & PROSPECTS
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Water harvesting techniques have been developed since antiquity to cope with climate variability in the dry areas. They played major role in the development of rainfed agriculture and others (recharge, flood control, etc.) With the prospect of CC, those systems/techniques would be more useful.
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Technical adaptation and adoption (SI, etc.)
However: Economic profitability is becoming increasingly low and variable Migration (due to cities attractions) and competition of other sectors would favor abandonment Need for new paradigm (water productivity, local products value chain, etc.) Technical adaptation and adoption (SI, etc.) Other functions (ecosystem services, etc.)
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Thank you
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