Water is deceptively easy to count and notoriously hard to measure. At the operational level, companies can increasingly meter withdrawals, consumption, discharge, and leakage with reasonable confidence. Reporting frameworks such as GRI 303, site-based stewardship standards such as AWS, and the spread of smart metering and leak-detection technologies have pushed facility-level water accounting into a more mature phase, especially for asset-heavy sectors like real estate and infrastructure (Global Reporting Initiative, 2021; Alliance for Water Stewardship, n.d.; Yussof et al., 2022; Zapata-Sierra et al., 2023).
The real difficulty begins when measurement moves from operations to basin reality. A cubic meter saved in a water-abundant catchment does not carry the same value as a cubic meter saved in a stressed basin. Nor can water quantity be separated from water quality, seasonal variability, environmental flow requirements, or competing social uses. Reviews of water security and water footprint methodologies show a crowded landscape of indicators, inconsistent boundaries, and persistent problems of spatial and temporal comparability (Octavianti & Staddon, 2021; Chapagain & Tickner, 2012).
This is why operation-level measurement is comparatively mature, while basin or landscape-level measurement remains low maturity and often bespoke. In real estate sector, for example, owners can install submeters, benchmark buildings, detect leaks, and connect water data to asset-management routines. The management question is largely operational: where is water used, lost, or discharged, and what intervention lowers cost and risk fastest? In basin terms, however, the question changes: does this portfolio operate in places where scarcity, pollution, or ecosystem degradation make each unit of water materially different? That requires contextual data beyond the asset itself (Yussof et al., 2022; World Resources Institute, 2021).
The challenge becomes sharper for sectors with complex supply chains such as cosmetics. A brand may know the water intensity of its factories, yet struggle to measure basin-level impacts across a fragmented sourcing network spanning surfactants, plant oils, fragrance ingredients, specialty chemicals, and agricultural feedstocks. At that point, water use is no longer a single metric but a mosaic of local hydrology, irrigation pressure, wastewater treatment performance, and chemical risk. Recent reviews of cosmetics sustainability and water related supply chain assessment underline that impacts are distributed across the full life cycle and that indirect water dependencies can outweigh what is visible in direct operations (Martins et al., 2023; Aivazidou et al., 2016; Wirtu et al., 2024).
The limitation of water impact measurement is also its opportunity. The field does not merely need more disclosure; it needs interoperability. Water accounting becomes useful only when facility data can speak to basin data, and when corporate metrics can be interpreted against catchment conditions and shared water challenges. This is the logic behind contextual water targets, basin-informed risk tools such as WRI Aqueduct, and the Water4All push for a FAIR, interoperable water data ecosystem (World Resources Institute, 2021; Water4All Partnership, 2022, 2025, 2026). The next frontier is a shared, basin-linked intelligence. Companies that learn to connect site data with watershed context will not just report water better; they will understand where their business model is hydrologically exposed, and where their interventions can actually matter.
References
Aivazidou, E., Tsolakis, N., Vlachos, D., & Iakovou, E. (2016). The emerging role of water footprint in supply chain management: A systematic literature review and a critical discussion. International Journal of Production Economics, 172, 107–124.
Alliance for Water Stewardship. (n.d.). AWS Standard.
Chapagain, A. K., & Tickner, D. (2012). Water footprint: Help or hindrance? Water Alternatives, 5(3), 563–581.
Global Reporting Initiative. (2021). GRI 303: Water and Effluents 2018.
Martins, A. M., Marto, J., Gonçalves, L. M., et al. (2023). A sustainable life cycle for cosmetics: From design and development to post-use phase. Molecules, 28(5), 2084.
Octavianti, T., & Staddon, C. (2021). A review of 80 assessment tools measuring water security. WIREs Water, 8(3), e1516.
Water4All Partnership. (2022). Data Management Plan.
Water4All Partnership. (2025). White paper: Towards a European Water Data Ecosystem (Version 1.5).
Water4All Partnership. (2026). Data Sharing.
Wirtu, Y. D., et al. (2024). A review of environmental and health effects of synthetic cosmetics. Frontiers in Environmental Science, 12, 1402893.
World Resources Institute. (2021). Aqueduct Water Risk Atlas.
Yussof, N. A. M., et al. (2022). Review of water leak detection methods in smart building applications. Buildings, 12(10), 1535.
Zapata-Sierra, A. J., et al. (2023). The scientific landscape of smart water meters: A comprehensive review. Water, 16(1), 113.
