The wastewater network
From blockages and damage to the network infrastructure.
Trade waste is the commercial and industrial liquid waste that is disposed of through the Christchurch City Council wastewater network.
Currently, about 10% (15,000 m3) of the wastewater treated at the Christchurch Wastewater Treatment Plant comes from industry. This includes discharges from restaurants, takeaway outlets, food processors, metal finishers, service stations, and chemical manufacturers. A trade waste consent is required for these types of discharges. Trade waste does not include wastewater from toilets or bathrooms.
From blockages and damage to the network infrastructure.
From chemicals and pollutants that could cause harm to our health.
From chemicals and pollutants being released and causing adverse effects to our environment.
The Trade Waste Bylaw sets the rules for the trade waste consent system. We have a legal requirement to review this bylaw before 26 November 2025. Seeking feedback now will ensure the review is completed before this deadline and that it remains fit for purpose and up to date.
Although national changes have been signalled in the Local Water Done Well (LWDW) Programme, the full extent of the proposals is not yet known. There are some uncertainties regarding the impact this reform will have on the bylaw. To meet our legal requirements, we are reviewing the bylaw now and will manage any potential impacts of LWDW if they arise.
Inorganic mineral solids (e.g. sand, silt, clay) don’t break down and can cause wastewater network issues, such as blocked or damaged pipes. These solids need to be removed from the network, which is expensive.
The current maximum permitted concentration of total suspended solids (which includes inorganic mineral solids) is 600g/m3.
The current total suspended solids limit of 600g/m3 will remain, however for discharges containing only inorganic mineral solids, we propose reducing the total suspended solids limit to 100g/m3. This will affect activities such as dewatering, hydro-excavation, stone cutting, and concrete production.
A lower limit will better protect our wastewater infrastructure and treatment processes and will be beneficial for network maintenance. Adding the limit to the bylaw will set the expectation from the outset of the consent process that inorganic mineral solids should be managed by the discharger.
View draft bylaw clause: Schedule 1A.2.4, 5(1) and 37(5).
Environmental and health concerns are emerging about persistent organic pollutants (POPs), especially polyfluoroalkyl substances (PFAS) . The wastewater treatment plant can’t remove these substances, which are highly resistant to degradation and remain in the environment for many years.
Prohibit POPs (including PFAS, perfluorooctane sulfonate (PFOS) and perfluorooctanic acid (PFOA)) from any trade waste discharge.
Prohibiting the intentional discharge of these chemicals in trade waste is one way we can help prevent further discharges of POPS, PFAS, PFOS and PFOA into the natural environment.
View draft bylaw clause: Schedule 1B.2.2.
Currently, permitted consents are granted indefinitely, with no expiry date. Although this category of consent is typically low risk, the perpetual nature of the consent is not beneficial for ensuring that the consent holder keeps their pretreatment devices or processes in good condition and working order, and that the consent remains appropriate over time.
Examples include restaurants and takeaway businesses, which are required (as a consent condition) to install and regularly empty grease traps to remove fats and solids from their trade waste discharges and prevent blockages in the wastewater network .
Introduce a maximum duration of up to 10 years for all permitted consents.
Providing a maximum term on permitted trade waste consents will ensure they are periodically reviewed to confirm they remain appropriate and fit for purpose.
Confirming the appropriate conditions are in place for the type of discharge, and that conditions are being met, it will also help to reduce the risk of damage or blockages to the consent holder’s private drains.
View draft bylaw clause: 15 and 37(4)
There are some gaps in the decision-making provisions of the bylaw, or improvements that could be made to provide more clarity and certainty. Issues identified include:
To ensure the bylaw is regulating the right things, and to provide clarity and certainty on the consent decision making requirements.
View draft bylaw clauses:
In limited circumstances, some discharges from dewatering can’t be accepted to the stormwater network and instead are considered for discharge to the wastewater network as trade waste. The bylaw is not clear on the requirement for trade waste consent in these instances.
Clarification that a trade waste consent is required under the Trade Waste Bylaw for dewatering activities, where applicable.
To reflect the change in practice, to align with the Water Supply and Wastewater Bylaw 2022, and to provide clarity on the requirement for consent and when it applies.
View draft bylaw clause: 10(1)(c) (including explanatory note); and definitions in clause 5(1).
Tankered waste is wastewater or trade waste that is transported away from the originating site by vehicle for disposal at an approved point, rather than being discharged directly from a premises through wastewater pipes.
The Trade Waste Reception Facility (TWRF) at the Christchurch Wastewater Treatment Plan (CWTP) became operational in 2016, after the bylaw was last reviewed. As a result, the tankered waste provisions of the bylaw could be improved to reflect operational changes.
Improve the regulation of tankered waste discharges to include the following:
These changes are proposed to help ensure that:
View draft bylaw clauses: 5(1); 6(1)(d); 8(1)(c); 10(1)(b); 13(1)(c); 14(1)(t); and 17.
In addition to the key changes we’ve summarised, we also propose some minor amendments including to:
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