NCC 2022 Volume Three - Plumbing Code of Australia
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C4
TAS Part C4 On-site liquid trade waste systemsTAS Part C4 On-site liquid trade waste systems
This Part sets out the requirements for the on-site treatment and disposal of liquid trade waste.
An on-site liquid trade waste system must ensure—
C4P3(2)(e) does not apply in cases where a contaminated stormwater discharge of limited volume is accepted by the Network Utility Operator.
Low risk liquid trade wastes can be described as those water-borne discharges, other than sewerage, that are classified by the Permit Authority as presenting a low risk to cause harm to the environment and on-site wastewater management systems. These discharges must be trapped and partially treated before being permitted to enter the on-site wastewater management system.
Trade waste products or installations may be used if they are considered low risk.
Performance Requirements C4P1 to C4P3 are satisfied by complying with C4D2 to C4D19.
Part B1 of NCC Volume One sets out requirements relevant to the excavation of pipework adjacent to a building and footings for the purpose of installing liquid trade waste systems in Class 2 to Class 9 buildings.
Examples of low-risk trade wastes are discharges from—
It is the role of the Permit Authority to determine whether trade waste discharge is high-risk or low-risk when installed in areas outside the jurisdiction of the Network Utility Operator.
Trade waste appliances must be fitted with covers which can withstand vehicular or pedestrian traffic or other loads likely to be imposed on them and be easily removable by one person.
Trade waste appliances must be constructed from materials suitable for the characteristics of the liquid wastes likely to be discharged.
Sizing of trade waste ventilation should take into consideration the expected discharge volumes and cooling requirements of the specific installation.
Installations outside C4D7(1) may be permitted by the Permit Authority.
See TAS Figure C4D8 for a typical silt pit.
See TAS Figure C4D9 for a typical silt trap.
See TAS Figure C4D10 for a typical straining pit.
See TAS Figure C4D11 for a typical straining trap.
Where the Permit Authority has not specified the capacity of a grease interceptor in accordance with C4D12(5), it must be—
Where the Permit Authority has not specified the capacity of a grease interceptor in accordance with C4D13(1), it must be—
See TAS Figure C4D13 for a typical portable grease interceptor appliance.
See TAS Figure C4D14a and TAS Figure C4D14b for typical venting arrangement for grease trap chambers.
Grease traps in multi-storey buildings must have a reflux valve installed between the outlet and connection to the sanitary plumbing system.
See TAS Figure C4D15 for a typical installation of a grease trap in a multi-storey building.
Where the Permit Authority has not specified the capacity of an oil and petrol interceptor in accordance with C4D16(1), it must be no less than 11400 litres, below the outlet.
See TAS Figure C4D16 for a typical oil and petrol interceptor appliance.
The requirements of C4D17(4) does not apply to existing systems.
The capacity of an acid neutralising tank as shown in Tas figure C4D17 is the minimum requirement of 27 litres between the marble chip level and the outlet level.
See TAS Figure C4D17 for an acid neutralising tank.
The minimum capacity requirement of a typical mixing tank in accordance with C4D18(1) is 100 litres.
See TAS Figure C4D18 for a typical mixing tank.
Consideration should be given to a mixing tank being provided with adequate structural support.
Where the Permit Authority has not specified the capacity of a settling tank in accordance with C4D19(1), it must be—
See TAS Figure C4D19 for a typical settling tank.