top of page

Build a water balance that exposes gaps in the records

Writer: Divya Khatwani
Divya Khatwani
Oct 10
4 min read

Start with one facility and one period. Map water entering the boundary, water leaving it, changes in storage and the records supporting each quantity. Keep internal transfers separate. The first useful result may be an unexplained difference with an owner, rather than a perfectly balanced diagram.

This guide is for facilities, operations and sustainability teams reconciling available water records before preparing disclosures or commissioning further technical work. It is a data-review workflow, not a design for a treatment plant or an instruction to change operating conditions.

 

Fictional facility diagram: 1,000 m³ enters the boundary, 650 m³ is discharged, 100 m³ goes to products and assessed evaporation, and storage rises by 150 m³. The 300 m³ internal circulation remains inside the boundary. The unexplained difference is 100 m³, with its cause unassigned.

Fictional physical reconciliation for one facility and period. The diagram separates external input and outputs, the increase in storage and internal circulation. The 100 m³ unexplained difference remains a review item, not an identified loss route. Arrows are schematic, not to scale.

Choose the boundary before adding volumes

Draw a simple list of the buildings, production areas, tanks and treatment systems included. Record the period start and end, the reporting unit and the person who knows the pipe and meter arrangement. A factory, an industrial estate and a corporate group have different boundaries.

List every supply route, including municipal connections, borewells, tanker deliveries, captured rainwater and externally supplied reclaimed water where present. Then list discharge routes and storage points. Check actual coverage with the site team; a finance ledger may describe a water supplier without showing which part of the site it serves.

The US EPA's WaterSense water-management guidance, printed pages 12–13, uses facility balances to compare source water with measured or estimated uses and identify unaccounted quantities. It is a practical reference for commercial and institutional facilities, not an Indian regulatory requirement or a universal acceptance threshold.

Give each quantity a role

Build a record with the source or meter ID, physical location, direction of flow, dates, original volume and unit, evidence reference, estimation basis and reviewer. Classify its role before entering a total:

  • Boundary input: water crossing into the selected system.

  • Boundary output: water leaving through a discharge route, or a separately assessed route such as water incorporated into products.

  • Internal transfer: water moving between processes or being recirculated within the same boundary.

  • Storage: opening and closing inventories measured on compatible dates and bases.

A treatment-plant outlet returned to production is an internal flow when both are inside the boundary. Do not add it to external supply. Likewise, a main meter and its downstream sub-meters are overlapping observations; use the sub-meters to explain the main total, not increase it.

Preserve original units. One cubic metre equals one kilolitre; 1,000 cubic metres equals one megalitre. A charge in rupees is not a measured volume. Where the records show only cost, retain the gap until a defensible quantity basis is available.

Reconcile the same period

Align meter readings, delivery dates, discharge records and tank readings. Investigate meter resets, estimated invoices, shared connections and records covering different dates. Mark every estimate with its assumption; do not copy a supplier's tanker capacity into every delivery unless the delivered quantity is supported.

For a whole-facility physical check, a useful starting relationship is: inputs = external discharge + other identified water leaving or being used up + increase in stored water + unexplained difference. This is an accounting check for the defined system. Its categories must be adapted to the actual process; it is not the definition of a reporting metric.

A fictional balance with an open difference

Assume a site's records cover the same month and have already been checked for overlapping meters. All quantities below are invented and expressed in cubic metres.

  • External inputs: 800 from the municipal connection and 200 from documented tanker deliveries, totalling 1,000.

  • External discharge: 650.

  • Water in products and assessed evaporation: 100 combined, with the underlying assumptions retained.

  • Stored water: 50 at opening and 200 at closing, an increase of 150.

The unexplained difference is 1,000 − 650 − 100 − 150 = 100 cubic metres. The check also works as opening stock plus inputs: 50 + 1,000 = 650 + 100 + 200 + 100.

A separate record shows 300 cubic metres recirculated internally. Adding that to the external 1,000 would count internal movement as new supply. It stays in the process map, outside the external-input total.

The 100-cubic-metre difference needs investigation. It might reflect an omitted route, inconsistent readings, an unsuitable estimate, leakage or another issue. The balance alone cannot identify the cause. Do not relabel it as “leakage” or quietly increase an estimate to force the result to zero.

Turn the difference into a review task

For each unresolved item, record the suspected mismatch, evidence needed, responsible person and decision date. Prioritise records that could change the conclusion, such as an unrecorded discharge connection or an opening tank volume measured on the wrong date. Any physical inspection or operational change belongs with the site's authorised technical team.

Keep the physical reconciliation separate from disclosure calculations. For example, GRI 303 has its own consumption calculation and storage disclosure guidance in Disclosure 303-5. Do not transfer a balance label into a report without checking its definition.

A reviewable handover contains the boundary map, source register, period-aligned quantities, assumptions, reconciliation and open actions. Nitium's sustainability and GRI reporting support can help organise evidence and disclosure gaps within an agreed scope. Discuss your reporting preparation or email contact@nitium.in.

Reviewed 5 October 2026. A balanced spreadsheet does not demonstrate water quality, legal compliance, safe operations or engineering adequacy. Those questions require their own evidence and qualified review.

 
 
 

Comments


bottom of page