Wastewater is tested and managed in accordance with the ZDHC Wastewater and Sludge Guidelines

Version 2 - Last updated 01 Nov 2026

This is the new version of Wastewater & Sludge Guidelines

This version (V2) is published and available to prepare for. It will replace the active version (V1) and take effect from 01 Nov 2026. Until then, continue using Wastewater & Sludge Guidelines V1. View Changelog

View Active Version

Scope for wastewater guidelines

These guidelines harmonise multiple brand-specific testing requirements for wastewater and sludge. While they are not a legal requirement in any country, their application will help suppliers to align with industry-specific and national wastewater requirements. This does not mean that conformance with listed parameters guarantees legal compliance in any country. 

The guidelines apply to discharged industrial wastewater and sludge produced from wastewater treatment operations of textile, apparel, leather and footwear suppliers with wet processing facilities. This includes, but is not limited to:

  • Dyeing and finishing of fibres, yarns, threads, fabrics, garments, textile trims and laces
  • Fabric mills
  • Laundry, washing and finishing facilities
  • Printing facilities
  • Raw wool scouring
  • Vertical finished goods manufacturing facilities where any wet processes occur
  • Synthetic materials (synthetic fibres or textile-polymer composite microfibres) coated with PU, PVC or similar polymers that hold the appearance of leather but are not made from animal skin or hide.
  • Any supplier who discharges to a central effluent treatment plant (CETP) is deemed an indirect supplier and should test against these guidelines.
  • With reference to leather:
    • Raw materials include: Hides from animal origin.
    • Facility type tanning process includes:
      • Beamhouse and tanning: Including soaking, liming, removal of extraneous tissues, unhairing and fleshing, deliming, bating, pickling, pre-tanning, etc.
      • Wet-end, crusting and/or finishing: Such as washing, degreasing, re-tanning, dyeing, fat liquoring, oiling, coating etc.

The ZDHC Wastewater and Sludge Guidelines do not currently apply to wastewater discharge from suppliers including, but not limited to:

  • Accessories or trim manufacturers e.g. zips, buttons (plastic metal, glass, shells, etc.) and galvanising processes
  • Cotton farming
  • Cattle ranching
  • Polymer production
  • Production of chemicals or mixing of chemical formulations for commercial sale

In addition, the ZDHC Wastewater and Sludge Guidelines do not currently apply to: 

  • Discharge of domestic wastewater only. Such as:
    • From a sewing/garmenting (e.g. staking) facility that employs workers but has no in-house wet processing unit.
    • Domestic wastewater that is not blended with industrial wastewater.
  • Wastewater management and treatment systems beyond the property boundaries of the supplier. This includes any third-party, off-site, centralised or common effluent treatment plants (CETP) that are not under the direct control and/or ownership of the supplier.
    • CETPs can choose to monitor their performance against these guidelines.
    • Any supplier who discharges to a CETP is deemed an indirect discharge supplier and should test against these guidelines under that definition.
  • With reference to leather:
    • Slaughter houses
    • Leather facilities with only mechanical processes/phases e.g. only embossing, polishing, staking or dry milling.

Separate wastewater guidelines are available for Man-Made Cellulosic Fibres (MMCF), Dissolved Pulp, Recycled Polyester Fibre.

Fibre guidelines 

How wastewater is sampled and tested depends on the discharge type and industrial wastewater flow rate. 

Discharge types

Suppliers are categorised into five ZDHC discharge types for sampling and testing wastewater:

Flow rate and threshold limits

Facilities that generate equal to or more than 15m3 of wastewater per day are required to meet more requirements than those that generate less than 15m3 per day.

This is because suppliers that generate less than 15m3 of wastewater per day (for example, screen printing facilities that wash moulds, screens and tools) do not impact the environment in the same way as those that generate more than or equal to 15m3 of wastewater per day (such as a typical dye house or tanneries).

The threshold wastewater average discharge applies to suppliers irrespective of the supplier's production type or production processes.

Flow rate calculation

Wastewater quality requirements

The parameters to be monitored for wastewater quality are:

  1. ZDHC MRSL substances: To check for intentional use of ZDHC MRSL substances and/or high levels of respective contamination in chemical inputs. MRSL detections are not failures but an indication of the presence of restricted substances in the manufacturing process. Detections shall trigger a root cause analysis and, where required, a corrective action plan.
  2. Heavy metals: Must be monitored in the direct discharge and indirect discharge categories only. To conform with these guidelines, at least foundational limit values must be met.
  3. Conventional parameters and anions: Must be monitored in the direct discharge category only. To conform with these guidelines, at least foundational limit values must be met.

Direct discharge generates ≥15m3  industrial wastewater per day

  • Sample untreated wastewater and test for MRSL parameters.
  • Sample discharged wastewater and test for heavy metal parameters.
  • Sample discharged wastewater and test for conventional and anions parameters.
Show Parameter Table

Indirect discharge with pretreatment (with sludge) ≥15m3 industrial wastewater per day

  • Sample untreated wastewater and test for MRSL parameters. 
  • Sample discharged wastewater and test for only arsenic, cadmium,
chromium (VI), lead and mercury parameters.
Show Parameter Table

Indirect discharge with pretreatment (without sludge) ≥15m3 industrial wastewater per day

  • Sample untreated wastewater and test for MRSL parameters.
  • Sample discharged wastewater and test for only arsenic, cadmium,
chromium (VI), lead and mercury parameters.
Show Parameter Table

Indirect discharge without pretreatment ≥15m3 industrial wastewater per day

  • Sample untreated wastewater and test for MRSL parameters.
  • Sample discharged wastewater and test for only arsenic, cadmium,
chromium (VI), lead and mercury parameters.
Show Parameter Table

Zero Liquid Discharge (ZLD) ≥15m3 industrial wastewater per day

  • Sample untreated wastewater and test for MRSL parameters.
Show Parameter Table

Direct discharge generates <15m3 industrial wastewater per day

  • Sample discharged wastewater and test for heavy metal parameters.
  • Sample discharged wastewater and test for conventional and anions parameters.
Show Parameter Table

Indirect discharge with pretreatment (with sludge) <15m3 industrial wastewater per day

No requirement


Indirect discharge with pretreatment (without sludge) <15m3 industrial wastewater per day

No requirement


Indirect discharge without pretreatment <15m3 industrial wastewater per day

No requirement


Zero Liquid Discharge (ZLD) <15m3 industrial wastewater per day

No requirement


Sampling procedure of wastewater and sludge at the facility

The ZDHC Approved Wastewater and Sludge Laboratory will request a 10 day (including weekends, but excluding public holidays) production window from the facility. Upon receiving this request, the facility is required to specify the specific days within that window during which production activities will occur at its peak. This timeframe will then be designated as the sampling window.

During the sampling window, the ZDHC Approved Wastewater and Sludge Laboratory reserves the right to perform sampling on any production day without specifying the exact date in advance. This process follows a semi-announced sampling approach, ensuring both operational feasibility and the integrity of the sampling process is maintained. 

The facility will be notified that a sampler from a ZDHC Approved Wastewater and Sludge Laboratory may visit at any point during the declared production days, and should be prepared to accommodate and to extend co-operation to the sampler for sampling purposes. 

Reporting

Once testing is completed by the ZDHC Approved Wastewater and Sludge Laboratory the supplier should generate a ClearStream Report on the ZDHC Gateway for the April cycle and October cycles.  

Implementation 

ZDHC wastewater quality guidelines should be implemented through sampling and testing of the wastewater at a facility twice a year through a ZDHC Approved Wastewater and Sludge Laboratory.

  • Suppliers should find a ZDHC Approved Wastewater and Sludge Laboratory using Find your Expert
  • Initiate sampling and testing.
  • Sampling before 30 April and before 31 October every year to meet the cycle timelines.
  • There should be at least a 3-month gap between the two sampling and testing cycles.
  • The wastewater test reports for the 2 cycles should be uploaded to the supplier’s ZDHC Gateway account by the ZDHC Approved Wastewater and Sludge Laboratory, completing the sampling and testing.

For further training, suppliers should visit the ZDHC Academy 

Candidate List

The ZDHC Wastewater and Sludge Candidate List signals intended changes to future updates of the guidelines. This list aims to give the industry an advanced indication of what to expect in future updates and, therefore, give the industry enough time to prepare for them, thereby facilitating wide-scale industry adoption and implementation. 

There is no mandatory requirement to conduct testing, do a Root Cause Analysis (RCA), or develop a Corrective Action Plan (CAP) for Candidate List entries, but it is strongly advised that a proactive approach be adopted.

Parameter Intention
Effluent toxicity To check the aquatic toxicity effects of substances that may not appear on the ZDHC MRSL, it is intended to evaluate the impact of wastewater discharge to the environment and biodiversity through water toxicity indicators.
Smart, intelligent testing grid ZDHC intends to review the current wastewater testing protocol and transition to a pragmatic approach that incentivises input chemical management through ZDHC MRSL conformance of chemical inputs (InCheck). For this approach, a smart testing grid based on substrate, chemical and process-specific risks would be required.
Water use targets for leather ZDHC intends to set water use targets for the textile and leather processes that take into account the complexities of the operations (in terms of the production processes, substrate of fibres, types of thickness of hides and absorption, material to liquor ratio, type of the machinery used, inefficiencies, reuse of water, etc.) 
These targets will be categorised into Level 0, 1, 2, and 3 to outline a continuous improvements journey for suppliers. 
Load-based calculation for key conventional parameters Currently, the ZDHC Wastewater and Sludge Guidelines allows reporting of conventional parameters only on a concentration basis (mg/ltr). ZDHC plans to introduce load-based limits (g/kg of material produced) for some conventional parameters linked to ZDHC water use targets.
This approach will support facilities on 
- Tracking reduction in total effluent load over time, even if concentration levels vary due to changes in water usage.
- Support in decision-making for improvements in ETP design and operational control.