| Issue | Key causes (physical, demographic, economic) | Typical impacts on development |
|---|---|---|
| Quantity shortage | Low rainfall, high evaporation, over‑extraction, strong seasonal variability, climate‑change‑induced droughts | Reduced crop yields (e.g. a 10 % fall in irrigation water ≈ 6 % drop in wheat yields in the Indo‑Gangetic Plain), limited industrial expansion, higher water tariffs, increased rural poverty |
| Poor water quality | Industrial effluents, agricultural runoff (fertilisers & pesticides), inadequate sanitation, salinisation, acidification | Water‑borne disease, loss of labour productivity, higher treatment costs, damage to aquatic ecosystems and loss of biodiversity |
| Unequal spatial distribution | Geographical concentration of rivers/lakes, urban‑rural divide, trans‑boundary basins, weak infrastructure in remote areas | Urban water stress, rural deprivation, internal migration, potential for inter‑regional or international conflict |
| Infrastructure deficits | Insufficient dams, reservoirs, pipelines, ageing treatment plants, high leakage rates (up to 30 % in some cities) | Unreliable supply, water loss, limited access for households and businesses, higher operating costs |
| Management strategy | Key actions | Benefits for sustainability | Potential limitations | Evaluation note (AO3) |
|---|---|---|---|---|
| Integrated Water Resources Management (IWRM) | Develop basin‑wide plans; coordinate sectoral use; involve government, private sector and communities. | Balanced allocation, reduced conflict, protection of ecosystems. | Requires strong institutions, reliable data and inter‑agency cooperation; may be slow to implement. | High importance – addresses quantity, quality and distribution; data gaps can limit planning; long‑term sustainability depends on governance capacity. |
| Demand‑side management | Water pricing, metering, public‑awareness campaigns, promotion of water‑efficient appliances. | Reduces wastage, encourages behavioural change, lowers per‑capita consumption. | Can be socially inequitable unless subsidies or tiered pricing protect low‑income users; effectiveness relies on public acceptance. | Important for reducing pressure; limited data on actual savings; sustainability enhanced if combined with equity measures. |
| Supply‑side augmentation | Construction of dams/reservoirs, rainwater harvesting, desalination, groundwater recharge schemes. | Increases available water, supports economic growth, buffers against drought. | High capital cost, possible environmental impacts (habitat loss, displacement, salinisation), energy‑intensive (especially desalination). | Crucial where quantity is the main problem; data on long‑term ecological impacts may be limited; sustainability hinges on environmental mitigation. |
| Water‑quality protection | Regulate industrial discharge, promote organic/low‑chemical farming, upgrade sewage treatment, enforce catch‑area controls. | Healthier populations, lower treatment costs, improved ecosystem services. | Enforcement may be weak; monitoring equipment can be expensive; compliance costs for businesses. | Key for health and ecosystem sustainability; data gaps in pollutant loads affect policy; effectiveness depends on regulatory capacity. |
| Reuse & recycling | Treat grey‑water for irrigation, recycle wastewater for industrial cooling or process water. | Conserves fresh water, reduces pollution load, creates secondary water resource. | Requires technical standards, public acceptance and reliable maintenance; potential health risks if standards are not met. | Strong sustainability potential; limited data on long‑term reliability; success linked to institutional support and public education. |
For each case study fill in the headings below. This uniform format helps students retrieve facts rapidly.
| Field | Content (example for Israel) |
|---|---|
| Location | Israel (Mediterranean & arid zones) |
| Water‑supply problem | Severe chronic shortage; >70 % of land arid. |
| Key statistics | 30 % of domestic supply from desalination; >80 % of wastewater reused for agriculture (≈ 1 billion m³ yr⁻¹). |
| Management response | Large‑scale reverse‑osmosis plants; national water‑recycling programme; strict water‑pricing & metering. |
| Outcome / evaluation | Improved water security; high per‑capita water use efficiency; criticism for high energy use and cost. |
Use the same structure for the other case studies (South Africa – Orange River Basin IWRM; India – Rajasthan rain‑water harvesting; Australia – Murray‑Darling water‑buy‑back; Chile – Antofagasta desalination).
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