European and national authorities should align farming, land restoration, urban planning, flood management, and water funding around measurable physical outcomes. A common scorecard should track soil water-holding capacity, infiltration, groundwater recharge, wetland and floodplain connectivity, urban permeability, ecological and chemical status, and the share of rainfall retained locally; spending and project counts should be reported separately rather than treated as proof of resilience. The assessment should cover the full water cycle—blue, green and atmospheric water—and test proposals against efficiency, sufficiency and resilience together, as recommended in Climate KIC’s work on systemic water management. Existing river basin plans should identify the largest opportunities to save water, including less water-intensive protein production and crops, industrial reuse, efficient buildings, and leakage reduction, then assign delivery responsibility, funding, and deadlines. The Water Framework Directive provides common standards and a basin-planning framework. Its function here is to coordinate objectives, monitoring, and review across sectors and borders, while implementation should strengthen existing plans rather than create another planning cycle.

Major water, drainage and flood-protection projects receiving public support should assess natural, hybrid, and engineered options before funding is approved. Promoters should state the service required, the options assessed, performance under present and future climate conditions, ecological and social effects, whole-life cost, maintenance, and skills needs, and why the selected option provides the strongest overall result. The comparison should cover flood-peak reduction, drought buffering, soil-moisture retention, groundwater recharge, water quality, river continuity, carbon, biodiversity, cooling, public-health benefits, land requirements, distributional effects, and avoided damage. A grey-only design should require a documented justification, while treatment plants, barriers and engineered drainage should remain available where natural measures cannot meet safety or reliability requirements. The Room for the River programme shows how flood safety can be combined with restored river space and spatial improvements.

Article 9 of the Water Framework Directive requires member states to consider cost recovery for water services and the polluter-pays principle. National authorities could assess how compliant funding arrangements might recognise verified retention, recharge, filtration, and risk reduction. Utilities and flood authorities should be able to invest in upstream soils, wetlands, forests and floodplains when these measures are cost-effective and linked to measured changes in water quality, flow, retention or risk rather than hectares treated. Funding can combine regulated investment, catchment water funds, payments for ecosystem services, outcome-based contracts, guarantees, resilience bonds, insurance participation, and aggregation facilities for small land-management projects. South West Water’s Upstream Thinking programme shows how utility investment can support farmers and reduce pollution upstream of drinking-water sources. Land-manager support should distinguish payment for ongoing services, compensation for temporary flood storage, transition support for investment and learning, and rapid compensation after extreme events. Essential household consumption should remain affordable through targeted support, while stronger conservation incentives and progressive charges can apply above normal use; every arrangement should disclose who pays, who benefits and which outcomes are purchased.

River basin plans should assemble connected rural, river, urban, and groundwater portfolios rather than fund isolated assets. Farm measures can include soil cover, reduced compaction, agroforestry, hedgerows, field margins, small wetlands, and temporary flood-storage agreements. River measures can include reconnected floodplains, rewetted peatlands, restored wetlands and riparian corridors, removal of obsolete barriers, and space for safe flooding. Urban measures can include de-paving, restored soils, rain gardens, bioswales, permeable streets, tree canopy, rainwater capture and reuse, green roofs, constructed wetlands, floodable public space, and safe overflow routes. In the Amsterdamse Waterleidingduinen, about 70 million cubic metres of Rhine water pass through the dunes each year, with sand providing natural filtration over roughly three months. Copenhagen’s Cloudburst Management Plan connects streets, parks, storage, and engineered drainage as one city-wide system. Each portfolio should specify ownership, maintenance, land agreements, monitoring, and how risks could shift elsewhere.

Basin water budgets should combine renewable supply, ecological needs, abstraction, consumption, leakage, return flows, reuse, water retained in landscapes, and expected climate pressures. They should distinguish essential from non-essential uses, make distributional effects explicit and test short-term measures against long-term hydrological limits so emergency responses do not lock in greater scarcity, following the European Parliament’s foresight study on water availability and use. They should inform river basin plans, agricultural decisions, land-use plans, infrastructure investment, permits, and drought preparation, while water allocation remains with national, basin and local authorities. WISE, Copernicus, the European Flood Awareness System, the European Drought Observatory, and national services provide much of the required information. Each warning level should specify the responsible authority, legal power, budget, review date, and action, including public communication, drinking-water protection, temporary conservation measures, reservoir and flood-storage operations, protection of hospitals and infrastructure, deployment of specialist teams, evacuation or shelter, and European civil-protection support. Annual exercises and post-event reviews should test the full chain from observation to public action. Compound stress tests should cover prolonged drought, intense rainfall, pollution, infrastructure failure, heat, and wildfire together, and assess continuity of drinking water, wastewater, electricity, food, navigation, health, communications, and industrial cooling.

A Catchment Compact should turn a river basin plan into a shared programme of investment, maintenance, and preparedness. It should include a basin water budget; agreed outcomes for ecological status, retention, recharge and preparedness; a map of priority landscapes, infrastructure and vulnerable communities; an investment and maintenance portfolio; assigned responsibilities; contributions from public and private beneficiaries; a standing participation forum; annual reporting; emergency exercises; and reviews after major droughts, floods or pollution events. Parties could include national, regional and local authorities, water and wastewater utilities, flood and civil-protection bodies, farmers, foresters, businesses, infrastructure operators, insurers, community organisations, and scientific bodies. A compact could begin as a voluntary agreement attached to a river basin plan and gain contractual or statutory force if experience shows value. The Rhine Action Programme and the Danube Flood Risk Management Plan provide precedents for sustained cross-border coordination, shared planning, and emergency cooperation. Compacts should make upstream costs and downstream benefits explicit and prevent one territory from transferring flood, scarcity or pollution risk to another.

Regional and local authorities should be able to request tailored teams for hydrological and ecological assessment, portfolio design, technical specifications, permits, procurement templates, land agreements, cost-benefit analysis, outcome measurement, and public participation. Climate KIC’s place-based adaptation work and WRI’s water-security programmes reinforce the same implementation lesson: data and pilots need institutions, skills, finance and collaborative catchment governance to change decisions at scale. A library of proven-solution profiles should state the problem addressed, the conditions in which a measure works, expected water and social outcomes, indicative cost and delivery time, responsible institutions, permitting and procurement requirements, required skills, maintenance, financing routes, and limits to transferability. A finance navigator should connect projects to cohesion, agricultural, adaptation, national, and European Investment Bank funding and aggregate small interventions into portfolios large enough to finance efficiently. Multi-year basin programmes should cover project preparation, construction, monitoring and long-term maintenance, while shared expertise should allow smaller municipalities to participate without maintaining every specialist role themselves. MIP4Adapt supports regional adaptation planning and capacity. Its delivery role should extend further into procurement, contracting, and project finance.