| Possible criteria | Fully centralised system | Combination of on-site and centralised system |
Cluster system | Fully on-site systems |
|---|---|---|---|---|
| Physical characteristics of site | ||||
| Limitation of site or area, (eg, soils climate, groundwater aspect proximity) | Not applicable | The on-site component acts as pretreatment to the central system. This is likely to be a septic tank and/or pump and sump. Suitable area of land required on site. Some limitations of site. Septic tank to be accessible for pumpout servicing | Suitable local site location and area required. Specific site conditions and area required, especially for return of treated wastewater and sludge to the ecosystem | Site area, soils, topography and ground water conditions may limit on-site options. Septic tank to be accessible for pumpout servicing |
| Resilience to natural hazards | Vulnerable to natural hazards such as earthquakes and floods | Vulnerable to natural hazards
such as earthquakes and floods |
Impact of natural hazard
event less than a fully centralised system. Flood risk |
More resilient to natural hazard events. Flood risk |
| Ecological | ||||
| Impact on surface and ground water, aquatic and other habitats, ecosystem services, soils | Large conventional sewer network resulting in urban impacts. Older networks can result in stormwater infiltration overflows from sewers and pumping stations. Site and technology specific. Must meet RMA consent requirements. Ecological impact of emissions (treated wastewater, sludges and any odorous gases) will depend on standard of treatment, plant management and sensitivity of receiving ecosystem and proximity of human neighbours | Modified or alternative sewer network required. Site and technology specific. Overflows from infiltration substantially reduced or eliminated. Must meet RMA consent requirements. Ecological impact of emissions (treated wastewater, sludges and any odorous gases) will depend on standard of treatment, plant management and sensitivty of receiving ecosystem and proximity of human neighbours. | Small scale modified or alternative sewer network required. Overflows can be substantially reduced by good design and construction. Site and technology specific. Must meet RMA consent requirements. Each cluster handles a smaller volume than a centralised system, so the ecological impact is likely to be less. Impact will depend on standard of treatment, plant management, sensitivity of receiving ecosystem and proximity of human neighbours. | No sewer networks required. Ecological impact all on-site. Very dependent on system technology and ongoing management. Will also be depend on sensitivity of receiving ecosystem. |
| Ecological restoration opportunities | Highly treated wastewater
could be used for wetland resortoration |
Highly treated wastewater
could be used for wetland restoration |
Highly treated wastewater
could be used for wetland restoration |
On-site wetlands could be
fed with secondary treated wastewater |
| Resource efficiency – closing of ecological cycles | Often not considered by central authority. Very dependent on design and management of the system | Often not considered by central
authority. Very dependent on design and management of the system |
Local sewer network
may save pumping and consequent energy demand. More recent systems are designed for efficient resource use and closing of ecological cycles |
No sewer networks required.
Greater opportunity for closing of nutrient cycles |
| Water recycling | Possible to achieve but would require high-quality treatment as well as provision of separate and readily identifiable reticulation to users | Possible to achieve but would require high-quality treatment as well as provision of separate and readily identifiable reticulation to users | Possible, but would require high-quality treatment and separate reticulation to user. | Very possible, but would require high-quality treatment. Greywater recycling for toilet flushing and garden watering is a viable technology already in use in NZ |
| Compatibility with Māori perspectives | ||||
| Issue of passage through land | May be an issue but needs to site specific analysis. RMA process will address these issues | Maybe an issue - site specific.
RMA process will address these issues |
Cluster schemes provide opportunity for local land application and ecosystem re-entry | |
| Protection of mauri | Dependent on siting and ecosystem re-enty type | Dependent on siting and ecosystem re-entry type | Dependent on siting and ecosystem re-entry type | All effluent applied to land,
hence likely compatible. Unlikely to be a problem |
| Other cultural concerns | ||||
| Local stewardship/ responsibility | Central system disconnects waste producers from relevant ecosystem's realities | Central system disconnects waste
producers from relevant ecosystem's realities |
More opportunities to
'tailor fit' local cultural requirements. Community has closer link to receiving ecosystem |
Possible to fit to individual's
cultural requirements. Very close links with receiving ecosystem "Neighbourly" conflicts possible |
| Re-use of reclaimed water | Likely to be a general cultural difficulty | Likely to be a general cultural difficulty | Likely to be a general cultural difficulty | Because of individual choice,
expect wider acceptance |
| Public health | ||||
| Operational safety |
Generally a very high standard
of public health safety |
Generally a very high standard
of public health safety. |
Generally a very high
standard of public health safety. |
Dependent on technology and management.
Approved systems that are well designed and subject to an inspection
and management programme will be safe |
| Impacts on community health |
Central systems generally remove
and treat wastewater well away from public contact, thus minimising
health risks. Treated effluent discharge to receiving waters must meet
health standards for recreation and shellfish harvesting. Stormwater
overflows from sewer networks can pose short term health risks. Strict
controls apply to land application by spray irrigation |
Central systems generally remove
and treat wastewater well away from public contact, thus minimising
health risks. Treated effluent discharge to receiving waters must meet
health standards for recreation and shellfish harvesting. Stormwater
overflows from sewer networks can pose short term health risks. Strict
controls apply to land application by spray irrigation |
Local cluster schemes
mean public closer to treatment and re-entry areas. Health risk low
if management of treatment and re-entry system maintained at a high
standard |
Risk low provided well designed
and managed. Neglected systems can give rise to failure conditions,
effluent surfacing, and high health risk to property dwellers and immediate
neighbours |
| Residual management |
All residual products are managed
centrally |
All residual products are managed
centrally |
All residual products
are managed by the cluster management agency |
Treated wastewater is managed on-site. Sludge must be managed off-site at an approved location. Composting toilets not favoured in urban areas by MoH |
| The technical system | ||||
| Reliability |
Usually reliable. Older sewer networks
can present a significant infiltration problem. New networks are also
subject to infiltration |
Reliable. Infiltration can be minimised |
Most modern systems will
be reliable. More dependent on management structure, knowledge and skill |
Dependent on technology quality,
knowledge and skill, and a regular inspection and management programme |
| Serviceability | Usually easily serviced, although
dependent on system design and management structure |
More geographically dispersed, therefore serviceability more difficult. Dependent on system design and magagement structure | Usually easily serviced, although dependent on system design and management structure | Dependent on type of system installed and servicing protocol |
| Operational requirements |
Operated by trained technicians |
Operated by trained technicians |
Should be operated and maintained
by trained technicians |
Operation and maintenance requirements
must be diligent to avoid failure. Council organised management programme
or independent operation and management contracts will reduce such risk
of failure |
| Engineering life of the system |
Long life |
On-site components possess a medium
to long life, whilst central components possess a long life |
Medium to long life. |
Medium to long life when subject
to a management programme |
| Resilience to acts of vandalism. | Depends on system design and management. Because of centralised location, easier to reduce acts of vandalism | Depends on system design and management.
Because of mostly centralised location, easier to reduce acts of vandalism |
Generally located away from public eye, creating higher risk of vandalism | Systems are not normally secure, but vandalism not normally a significant problem |
| Linkages with other opportunities and services (eg water supply) | There are opportunities to recycle water and nutrients, recover energy, restore/create wetlands and provide an ecological education facility. Short-term economics usually constrains implementation | There are opportunities to recycle
water and nutrients, recover energy, restore/create wetlands and provide an ecological education facility. Short-term economics usually constrains implementation |
There are opportunities to recycle water and nutrients, recover energy, restore/create wetlands and provide an ecological education facility. Short-term economics usually constrain implementation | There are opportunities to recycle water and nutrients, recover energy, restore/create wetlands and other on-site landscaping. Implementation is dependent on individual motivation, funding and regulatory constraints |
| Ability to be changed | ||||
| Extendability | Depending on design, most of the older, centralised systems are not so extendable or adaptable to changing requirements. Sewer infrastructure (and required flow velocities) can restrict future changes to other parts of the system. Land can be limiting. Infrastructure locks in system capacity, limiting adaptability. Normally adaptable to trade waste inflows | Depending on design, these system tend to be more recent and therefore extendibility may have been included in the design | Depends on design, but more likely to be adaptable due to being a smaller system. Funding may limit extendibility and adaptability | It is the individual property owner's responsibility to build in extendability and adaptibility. Most likely funding but also land area will limit the ability to respond to changes. On-site secondary treatment systems have limited opportunity to be extended for increased loading |
| Adaptability/flexibility | These systems tend to be a little more adaptable due to the lower cost of reticulation. However, adaptability will be rather limited. Normally adaptable to trade waste inflows | |||
| Management | ||||
| Ownership |
Normally owned and managed
by city/district council |
Normally owned and managed
by city/district council |
Can be owned and managed
by city/district council or by corporate body |
Owned by property owner.
Normally managed by property owner, although owners can form a body
corporate to oversee O&M |
| Convenience |
Having all the operation at
a central location simpifies management requirements |
With some components on-site
and most central, management will be less convenient |
Management of cluster
systems may be perceived as less convenient than a larger centralised system and more convenient than on-site systems. Centralised management of a group of cluster systems is recommended |
Management requirements will
depend on type of system installed. Traditionally, management responsibility lies with the property owner. Management may be by contract, or by a management agency, thus providing maximum convenience to the owner |
| Operation and maintenance
implications |
The centralised nature of
this system makes operation and management uncomplicated |
The operation and maintenace
programme will need to be designed for a combination of on-site and
centralised requirements |
Operation and maintenance
requirements will depend on the type of system installed. Servicing
contracts are often employed, and inspection and management programmes
are recommended to ensure long life of the system |
|
| Economic factors | ||||
| Capital and operating costs | City/district council responsibility. Capital and annual operating costs are normally evenly spread across the community served. User-pays possible with water metering | City/district council responsible
for off-site costs, and maybe on-site costs. In some situations on-site costs may lie with property owner. Capital and annual operating costs are normally evenly spread across the community served. User-pays possible with water metering. |
Capital costs may
be the responsibility of the developer or city/district council. Operating
costs may be the responsibility of city/district council or a specially
constituted corporate body |
Capital and operating costs are the responsibility of the property owner. Where a council or body corportate management programme is in place, annual charges will be levied for O&M |
| Funding | Rates | Rates | Rates, or built into
purchase price |
Individual capital funding,
and individual or body corporate or managment agency fees for O&M
|
| Local community impacts |
||||
| Level of local control |
Community generally has minimal
input into the design, operation and management of these systems |
Community generally has minimal
input into the design, operation and management of these systems |
More opportunity for
community input into the design, operation and management of these systems |
Greater degree of control lies
with individual property owners. |
| Need for external expertise/management |
Usually a significant external
input into the design, operation and management of these systems |
Usually a significant external
input into the design, operation and management of these systems |
External expertise for
the design is normally required. Management can be local or centralised |
External expertise for technology
selection and design is normally appropriate. Management can be on-site
or centralised |
| Community change | ||||
| Pressure for future growth | Stimulates urban growth, including
commercial and industrial growth |
Stimulates urban growth, including commercial and industrial growth | The cluster system will enable
domestic localised growth. Less conducive to commercial and industrial growth |
Local geophysical and hydrological conditions can restrict urban growth. Recent systems can overcome some of these constraints |
| Capacity to absorb growth |
Depends on both total system design
capacity and individual capacity for each component. Modern systems can be designed to accommodate future growth |
Depends on both total system design
capacity and individual capacity for each component. Modern systems can be designed to accommodate future growth |
Cluster systems tend to be
designed for a given cluster of homes. May be possible to absorb some
growth, or additional cluster systems may be require. |
Growth will be dependent on the
suitability of the property's site for on-site management. However,
growth within site boundaries is very rarely an issue |
| Other potential benefits | ||||
| Leisure and recreation |
Restored wetlands may be integrated
with an urban park. Health risks would have to be minimised by appropriate pre-treatment prior to wetland re-entry |
Restored wetlands may be integrated
with an urban park. Health risks would have to be minimised by appropriate pre-treatment prior to wetland re-entry |
Restored wetlands may be
integrated with an urban park. Health risks would have to be minimised by appropriate pre-treatment prior to wetland re-entry |
N A |
| Education |
Opportunities to develop community
education activities centred on wastewater, and social and ecological issues |
Opportunities to develop community
education activities centred on wastewater and social and ecological issues |
Opportunities to involve
local community in educational activities centred on wastewater and social and ecological issues |
Opportunities to educate community
to take greater responsibility for their waste |
| Research |
Many research opportunities to
study the resource value of wastewater |
Many research opportunities at
the centralised level to study the resource value of wastewater |
Many research opportunities
at the local level to study the resource values of wastewater |
Many research opportunities at
the individual level to study the resource values of wastewater |
| Formal processes | ||||
| Familiarity to decision-makers |
Decision-makers are familiar with
these types of systems and traditionally place confidence in them |
Decision-makers are less familiar
with these types of systems but normally have confidence in them because
of the final centralised management |
Decision-makers are less
familiar with these types of systems and subject such systems to greater scrutiny |
Decision-makers are familiar
with on-site systems, but often very unfamiliar with recent innovations
and the benefits of inspection and management programmes |
| Technical demands |
Requires expert engineeering input
for design. Requires skilled operators |
Requires expert engineeering input
for design. Requires skilled operators |
Requires expert engineeering
input for design Requires skilled operators |
Requires expert engineeering
input for design Requires trained inspection, operation and maintenance personnel |
| Public health service |
Strict health standards |
Strict health standards |
Strict health standards |
Strict health standards |
| Ease of the consent process
|
Site and system dependent. Consenting
process usually well resourced |
Site and system dependent. Consenting
process usually well resourced |
Site and system dependent.
Consenting process usually less well resourced |
Consent under council building
controls. |