| Industry Definition | Core activity | Water recycling treats municipal, industrial, agricultural, or stormwater flows so that the resulting water can be used again for beneficial purposes. | The industry includes collection, treatment, advanced purification, storage, monitoring, distribution, and operation of reuse systems. | U.S. Environmental Protection Agency, Guidelines for Water Reuse |
| Global Water Pressure | Freshwater withdrawals by agriculture | Approximately 70% of global freshwater withdrawals are used by agriculture. | Reclaimed water can supplement irrigation supplies and reduce pressure on rivers, reservoirs, and groundwater sources. | FAO AQUASTAT and UN-Water global water-use assessments |
| Environmental Condition | Domestic wastewater safely treated | About 56% of domestic wastewater was safely treated globally in 2022. | The remaining treatment gap represents both an environmental risk and a potential source of recoverable water, nutrients, and energy. | UN-Water, SDG 6.3.1 progress reporting |
| Environmental Benefit | Reduction of freshwater abstraction | Reusing treated water can replace part of the demand for potable or natural freshwater, although the actual reduction depends on treatment quality, local demand, and system losses. | Benefits are usually greatest in water-stressed regions and for non-potable uses such as irrigation, industrial cooling, and urban landscaping. | UNESCO World Water Development Reports; U.S. EPA water-reuse guidance |
| Environmental Risk | Residual contaminants | Recycled water may contain trace pharmaceuticals, personal-care chemicals, nutrients, salts, pathogens, or industrial contaminants if treatment and source control are insufficient. | Risk management requires treatment barriers, source control, monitoring, operational controls, and a use-specific water-quality plan. | World Health Organization, Guidelines for the Safe Use of Wastewater, Excreta and Greywater |
| Energy Consideration | Treatment-energy relationship | Conventional biological treatment generally requires less energy than advanced membrane treatment and potable reuse, while energy demand increases with salinity, contaminant load, and required water quality. | Energy efficiency, renewable electricity, process optimization, and recovery of biogas can materially affect operating costs and emissions. | International Water Association and U.S. EPA water-reuse technical guidance |
| Economic Model | Main cost categories | Typical cost categories include source-water collection, treatment equipment, energy, chemicals, laboratory testing, permits, storage, pumping, distribution, maintenance, and replacement of assets. | Reuse projects must be evaluated as complete systems; advanced treatment alone does not represent total project cost. | U.S. EPA, Guidelines for Water Reuse |
| Economic Driver | Value of a reliable alternative supply | The economic value of recycled water increases when freshwater is scarce, drought restrictions are frequent, or the cost of developing new supplies is high. | Financial feasibility depends on avoided water-supply costs, avoided wastewater-discharge costs, user demand, infrastructure distance, and regulatory requirements. | World Bank and OECD water-economics assessments |
| Potential Revenue | Water and resource recovery | Potential revenue or avoided costs can come from reclaimed-water sales, wastewater-service fees, nutrient recovery, biogas production, reduced discharge fees, and avoided freshwater purchases. | Projects with several revenue streams are generally less dependent on a single water tariff or end-use market. | International Water Association resource-recovery frameworks |
| EU Regulation | Agricultural irrigation | Regulation (EU) 2020/741 establishes minimum requirements for the safe reuse of urban wastewater for agricultural irrigation and has applied since 26 June 2023. | The regulation uses water-quality classes, monitoring requirements, risk management, and permits to control public-health and environmental risks. | European Union, Regulation (EU) 2020/741 |
| EU Reuse Quality | E. coli limits for agricultural irrigation classes | For the EU agricultural-reuse framework, the maximum E. coli values are generally 10, 100, 1,000, or 10,000 colony-forming units per 100 mL, depending on the assigned quality class and crop exposure. | Required quality becomes stricter when workers, consumers, or edible crop portions have greater exposure to reclaimed water. | European Union, Regulation (EU) 2020/741, Annex I |
| United States Regulation | Regulatory structure | Water-reuse requirements are primarily established by states, territories, tribes, and local authorities; the federal government provides guidance rather than one nationwide reuse standard. | Project developers must verify requirements for the intended end use, including treatment performance, monitoring, permits, reporting, and cross-connection control. | U.S. Environmental Protection Agency, Water Reuse Action Plan and Guidelines for Water Reuse |
| Potable Reuse | Public-health safeguards | Potable reuse requires multiple treatment barriers, validated monitoring, strict operational controls, and compliance with drinking-water standards; no single treatment step is considered sufficient by itself. | Public acceptance and regulator confidence depend on transparent risk assessment, independent oversight, reliable operation, and clear communication. | World Health Organization and U.S. EPA potable-reuse frameworks |
| Infrastructure | Centralized versus decentralized systems | Centralized systems treat large flows at regional facilities, while decentralized systems serve individual buildings, districts, or smaller communities. | Decentralized systems can reduce distribution distances, but they require strong local management, maintenance, monitoring, and safeguards against cross-connections. | U.S. EPA and UN-Habitat wastewater-management guidance |
| Circular Economy | Recovered resources | Wastewater can provide three resource streams: water, recoverable nutrients such as nitrogen and phosphorus, and energy through organic-matter conversion. | Resource recovery can reduce disposal needs and improve the environmental and economic performance of treatment facilities. | UN-Water and International Water Association resource-recovery guidance |
| Social Acceptance | Trust and adoption | Acceptance is influenced by perceived health risk, the intended use, trust in institutions, transparency of monitoring data, and public participation. | Communication and community engagement are operational requirements for many reuse projects, not merely marketing activities. | World Health Organization water-safety and risk-communication guidance |
| Key Performance Measures | Recommended project metrics | Useful indicators include reclaimed-water volume, percentage of demand served, energy intensity, treatment reliability, compliance rate, greenhouse-gas emissions, freshwater displacement, and cost per cubic meter. | A balanced scorecard prevents projects from being judged only by production volume or treatment cost. | International Water Association and U.S. EPA performance-management guidance |