NCC 2019 Volume Three
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Tas Section H On-site waste water systems
This Part sets out the requirements for the design, construction, installation, replacement repair, alteration and maintenance of any part of an on-site wastewater management system.
Objective
Tas HO1
The Objective of this Part is to—
Functional statements
Tas HF1.1
On-site wastewater management systems must collect, contain, treat and assimilate and process domestic-wastewater, human excreta, or both so that public health and environmental standards required by the authority having jurisdiction are achieved.
An on-site wastewater management system must ensure the following:
Risks associated with the discharge of treated wastewater to the environment are minimised.
Risks associated with the discharge of the end product of a composting toilet to the environment are minimised.
Surface and ground water are not polluted.
Soil productivity is maintained or enhanced.
Wastewater must be transferred to an on-site wastewater management system in a way that avoids the following:
Entry of foul air and gases into buildings.
Wastewater must be transferred to an on-site wastewater management system in a way that ensures the following:
Safe and hygienic transferal of waste.
Safe access for maintenance.
An on-site wastewater management system must avoid the following:
Contamination of drinking water, soils, ground water and waterways.
Foul air and gases accumulating within or entering buildings.
Unauthorised access by people.
Entry of stormwater to the system.
An on-site wastewater management system must ensure the following:
Cleaning, maintenance, measurement and performance sampling can be conducted as appropriate.
The manufacturer, model, serial number and designed capacity is easily identifiable after installation.
Materials which are resistance to the water and waste that will be disposed.
Appropriate treatment and storage capacity for the volume of waste and frequency of disposal.
Appropriate size, strength and rigidity for the nature, flow rates, volume of wastes and/or waste products which must be processed.
Vehicle access for the collection of waste water.
The installation throughout its serviceable life will continue to satisfy the requirements of items Tas HP1.3(2)(a) to Tas HP1.3(2)(f).
An on-site wastewater management system and associated land application system must avoid the following:
Damage from root penetration, superimposed loads or ground movement.
Entry of water, foul air or gases from the system into buildings.
Entry of stormwater to the system.
Blockage and unintended or uncontrolled discharge.
An on-site wastewater management system, and any associated land application system must provide the following:
Protection against internal contamination.
Access for maintenance and cleaning.
Ventilation to avoid foul air and gases accumulation in the system.
A facility must continue to satisfy the requirement of items Tas HP1.4(1) – Tas HP1.4(2).
There are no Verification Methods in this Part.
Performance RequirementsTas HP1.1 to Tas HP1.4 are satisfied by complying with Tas H1.2.
The manufacture of septic tanks and their associated fittings for the treatment of domestic wastewater up to 14,000 litres per week must be in accordance with AS/NZS 1546.1.
Waterless composting toilets must meet the requirements of AS/NZS 1546.2.
The design, means of compliance and specification for testing of aerated wastewater treatment systems and associated fitting must be in accordance with AS/NZS 1546.3.
The design and installation of sanitary plumbing and drainage systems must be in accordance with AS/NZS 3500.2 and the requirements of this Part.
The design and sustainable management of domestic land application systems must be in accordance with AS/NZS 1547.
An on-site wastewater management system must be designed and constructed in accordance with a Certificate of Accreditation issued under Tas I102.
The installation of an on-site wastewater management system must comply with the additional installation requirements set out in Tas H101.
This Part is an addition to Tas Part H1 and sets out the requirements for the connection of water flushed sanitary fixtures and sanitary appliances to an on-site wastewater management system other than a sewerage system. It also sets out the installation requirements for on-site wastewater management systems.
Installation must be in accordance with Tas Figure H102.2 and in accordance with Parts C1 and C2 for pipework and venting arrangements.
An overflow relief gully must be installed and positioned so as to provide protection against surcharge of waste into a building.
An alternative to the ground vent may be used by extending a vent to terminate as an upstream vent, with the vent connection between the last sanitary fixture or sanitary appliance and the on-site wastewater management system.
Inspection openings must be located at the inlet to an on-site wastewater management system treatment unit and the point of connection to the land application system and must terminate as close as practicable to the underside of an approved inspection opening cover installed at the finished surface level.
Access openings for desludging or maintenance of on-site wastewater management system treatment units must terminate at or above finished surface level.
This Part sets out the requirements for how greywater is managed for domestic premises in Tasmania. It also sets out classification levels and methods of disposal for each of the three options.
A greywater re-use system may be achieved through any one of the following options:
Treatments systems.
Diversion.
Manual Bucketing (exempt from Tas H102.2).
The type of option selected will depend on what the water is to be used for and how much land is available.
Option (a), treatment systems, must be designed, installed and maintained in accordance with AS/NZS 1546.4, the system must be accredited in Tasmania and maintained in accordance with the schedule of maintenance determined under the Tasmanian Building Act provisions.
Option (b), Diversion systems, must be designed, installed and maintained in accordance with AS/NZS 3500.2, the Tasmanian Consumer Building and Occupational Services — Guide to Domestic Greywater Re-use and the schedule of maintenance (as applicable) and as determined under the Tasmanian Building Act provisions and Tas A5.3(1)(c).
Option (c) there are no installation requirements.
This Part sets out the requirements for the design, construction, installation, replacement, repair, alteration and maintenance of any part of a system of a property used for the on-site treatment, conveyance and/or disposal of liquid trade waste.
An on-site liquid trade waste system must ensure the following:
Risks associated with the discharge of treated liquid trade waste to the environment are minimised.
Surface and ground water are not polluted.
Soil productivity is maintained or enhanced.
Liquid trade waste must be conveyed within the disposal system and treatment devices in a way that avoids the following:
Entry of foul air and gases into buildings.
Liquid trade waste must be conveyed within the disposal system and treatment devices a way that ensures the following:
Safe and hygienic transferal.
Safe access, as appropriate, for clearing blockages.
A trade waste treatment device must:
Have appropriate treatment and storage capacity for the volume of waste and frequency of disposal.
Be of the appropriate size, strength and rigidity for the nature, flowrates, volume of wastes, by-products and residues which must be processed.
Have vehicle access, for collection.
Be of an appropriate structural strength for where pedestrian or vehicular traffic is likely.
Be constructed of materials which are resistant to water and the expected waste that will be disposed.
A trade waste treatment device must avoid the likelihood of the following:
Contamination of drinking water, soils, ground water and waterways.
Foul air and gases accumulating within or entering buildings.
Unauthorised access by people.
Entry of stormwater to the sewerage system.
Tas HP2.3(2)(e) does not apply in cases where a contaminated stormwater discharge of limited volume is accepted by the Network Utility Operator as a trade waste.
A trade waste treatment device must be designed, constructed and installed to allow the following:
Cleaning, maintenance, measurement and performance sampling provisions to the requirements of the Authority having Jurisdiction.
Identification of the manufacturer, model, serial number and capacity after installation.
A trade waste treatment device must continue to satisfy the requirements of items Tas HP2.3(1) – Tas HP2.3(3) throughout its expected lifetime.
be a trade waste treatment device approved by the receiving Network Utility Operator or for on-site disposal the Authority having jurisdiction.
There are no Verification Methods in this Part.
Performance RequirementsTas HP2.1 to Tas HP2.3 are satisfied by complying with Tas H2.2.
Where pre-treatment facilities are required, they must comply with the requirements of the authority having jurisdiction, including receiving Network Utility Operator (where relevant) and those responsible for occupational health and safety, dangerous goods management and environmental protection.
Where the written agreement of the authority having jurisdiction and the receiving Network Utility Operator is required, the liquid trade waste systems and pre-treatment facilities are to comply with the requirement of the authority having jurisdiction and the receiving Network Utility Operator.
Where pre-treatment facilities are not required by the Network Utility Operator or the permit authority, Tas HP2.2 or Tas HP2.3 must comply with AS/NZS 3500.2 and Tas Part H201 and Tas Part H202 as appropriate.
If a Network Utility Operator accepts the discharge of a liquid trade waste to their sewerage system after pre-treatment—
the pre-treatment equipment or system is deemed to satisfy the Performance Requirements of Tas HP2.1 – Tas HP2.3, if the equipment or system is capable of discharging liquid trade waste at a quality set under a Consent to Discharge issued for that equipment or system by the Network Utility Operator; and
that part of the installation used to convey the liquid trade waste after treatment must comply with AS/NZS 3500.2, Tas H201, Tas H202, and the Network Utility Operator's Guidelines, insofar as the provisions relate to the system.
The use of a product or system must comply with the details described in Tas H201 and Tas H202 insofar as they relate to the product or system installed in systems not connected to the Network Utility Operator's infrastructure.
The use of a product or system must comply with the details described in Tas H201, Tas H202 and the Network Utility Operator's Guidelines, insofar as they relate to the product or system installed in systems connected to the Network Utility Operator's infrastructure.
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 9 buildings
This Part is an addition to Tas Part H2 and sets out the requirements for the roofing of liquid trade waste generation areas to prevent entry of stormwater to an approved disposal system other than a sewerage system.
Roofing requirements for systems connected to the Network Utility Operator's sewerage system must as a minimum comply with Tas Figure H201.2.
When a liquid trade waste generating process does not fully occur within a building, suitable roofing must be installed to prevent the entry of stormwater to the disposal system. For a structure where one or more sides are open to the weather, at least 10 degrees from the vertical overhang of the roofing must be provided.
To ensure that surface water cannot flow onto the liquid trade waste generating process area a bund or other feature (speed hump) at least 150 mm high around the area must be installed. On the upper side of the area, stormwater drains alone are not adequate as stormwater flows will often bridge over the grate and enter the process area. The overall surface water flow across the site is to be considered and the height of the bund or other feature must be increased where the calculated stormwater flow will enter the process area.
This design is likely to allow wind driven rainwater to enter under the roof in extreme storm conditions. The roof must overhang by an amount not less than that shown in Tas Figure H201.2.
This Part is an addition to Tas Part H2 and depicts low risk trade waste products and installations connected to an approved disposal system other than a sewerage system.
This Part applies to trade waste installations not connected to a Network Utility Operator's system.
Trade waste products or installations depicted in Tas Section H are considered low risk and may be used if they are installed in accordance with the details shown therein and the following.
Low risk liquid trade wastes can be described as those water-borne discharges — other than sewage —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.
Examples of low risk liquid trade wastes are discharges from—
It is the role of the permit authority to determine whether the trade waste discharge is high risk or low risk when installed in areas outside the jurisdiction of the Network Utility Operator.
Location
Low-risk trade waste appliances must be located as close as practicable to the fixtures and floor waste gullies served whether installed internally or externally and may be above or below ground. Portable appliances may only be installed above ground.
Covers
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.
Materials
Trade waste appliances must be constructed of materials suitable for the nature of the liquid wastes likely to be discharged through the appliance.
Ventilation
Where airtight covers are fitted, trade waste appliances must be vented with either a DN 50 or DN 80 vent (refer to relevant figure). Outlet ventilation is to be provided by either a—
DN 100 riser from a disconnector gully outside a building (refer clause 4.6.2 AS/NZS 3500.2); or
DN 50 vent from a disconnector gully at the outlet of a non-portable appliance inside a building (refer clause 4.6.5 AS/NZS 3500.2); or
DN 50 vent from a DN 80 trap riser at the outlet of a portable appliance, inside a building (refer clause 4.6.5 AS/NZS 3500.2).
Trade waste appliance vents and outlet vents may be combined inside a building (refer clause 6.8.3 AS/NZS 3500.2).
Connections
Unless otherwise permitted by the permit authority, the plumbing and drainage installation upstream of a low-risk trade waste appliance must comply with AS/NZS 3500.2 and be compatible to the nature of the waste.
A trap must be fitted to the outlet pipe of every appliance and sized as follows—
DN 50 minimum for a portable appliance with hydraulic loading up to 5 fixture units.
DN 80 minimum for a portable appliance with hydraulic loading greater than 5 fixture units
DN 100 minimum for all other appliances.
The low risk trade waste products and installations depicted below may be used if they are installed in accordance with the diagrams and notes shown.
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