As with the measurement of housing need, the status of environmental health infrastructure requires a detailed assessment of functionality and adequacy set against agreed normative criteria. However, at the time of writing no secondary source of data was readily available with which to adequately establish change in the findings of the 1997 Environmental Health Survey, nor to establish, in a comprehensive way, the existing status of environmental health infrastructure. The most recent source of data is from the 2001 CHINS, and while this includes information on such issues as water supply, sewerage, drainage and solid waste disposal, this is more in the form of simply noting the existence or otherwise of infrastructure rather than assessing its functionality and adequacy. Likewise, CHINS data do not allow for the proper assessment of activities related to such issues as dust control, animal health and quality of waterways. For example, with regard to dust control, all that is available from the CHINS is the fact that a certain number of permanent dwellings in the region were located on sealed roads. Thus, while this provides some indication of the likely extent of dust mitigation as an issue, it is far from adequate as an indicator of progress.
The idea that Aboriginal community housing and infrastructure should be designed, constructed and maintained to support healthy living practices is now firmly embedded in policy following the pioneering work of Pholeros, Rainow and Torzillo (1993) in the Pitjantjatjara Lands. A total of nine such practices are identified, in descending order of priority in terms of impact on health outcomes: capacity to wash people, wash clothes and bedding, remove waste safely, improve nutrition, reduce crowding, separate people from animals, reduce dust, control temperature, and reduce trauma. Each of these refers to different aspects of the functionality of dwellings and their related infrastructure. For example, if the focus is on improving nutritional standards and practices, then ‘healthy home hardware’ refers to the provision of adequate facilities to store, prepare and cook food. It also extends to water quality and quantity as a lack of these may lead individuals to purchase bottled water or other beverages, thereby adding to expenditure and increasing reliance on soft drinks and cordials.
The National Indigenous Housing Guide (Commonwealth of Australia 1999) includes a range of detailed design and functionality guidelines to address each of these nine healthy living practices. The key functional area with most guidelines is that involving the supply, usage and removal of water: six of the nine healthy living practices are dependent on these. However, even seemingly obscure health-related housing functions include a wide range of design, maintenance and infrastructural features that require attention (Commonwealth of Australia 1999: 49-57). For example, guidelines for improved nutrition include consideration of the following factors:
Different ways of cooking: Given often-crowded dwellings and failure of cooking equipment, it is common for many different age groups to share the cooking facilities of a house. At the same time, each group may have a different preference for cooking. For example, younger people may use a microwave oven; middle-aged people may use a stove or drum oven and barbecue, older people may prefer the ground and a fire for cooking. To this extent, there is a need to consider how many ‘kitchens’ each house may need.
Electric cooking: stoves and hotplates. Electric hotplate cooking is one of the major sources of energy use in a house. To control costs, stove timer switches can be installed to cut off power after a set period. It has also been found that solid hotplates are more robust than coil elements.
Operational fridges: Poorly performing fridges can lead to food spoiling and food poisoning as well as to high energy costs. A number of simple directives can be applied to assist in overcoming these problems, for example ensuring that the fridge is located in a thermally efficient area and that door seals are regularly maintained. However, one problem with fridges in overcrowded households is frequent use, and the only solution here is provide either more fridges or lower density housing.
Kitchen cleaning and maintenance: The design and detailed specification of the kitchen area, joinery, and appliances can make cleaning easier by reducing cleaning effort and access for insects and vermin.
Food storage: Low shelves and cupboards are easily accessed by dogs and children, or are unused or used to store non-food items. Consideration should be given to providing high shelves and cupboards and lock-up pantries that are insect-proof and well ventilated.
The main, and most recent, source of data regarding the functionality of dwelling facilities remains the 1997 Environmental Health Needs Survey. For the Wunan ATSIC Region, this revealed that on average some 30% of the dwelling facilities surveyed were absent from dwellings in the region (Table 6.7), the most noticeable being laundry-floor waste outlets. However, if consideration is also given to facilities that are present but not working, then hot water systems were also effectively absent from as many as 48% of dwellings, more than 30% of dwellings had no effective toilet cistern, more than one-third had no effective laundry trough, and 30% had no kitchen sink, bath or shower. Overall, one-third of dwellings was either without facilities, or had facilities that were dysfunctional. Northern East Kimberley communities that stood out as lacking or requiring major repairs to three or more facilities included Oombulgurri, Nulleywah, Glen Hill, Wurrenranginy, Red Hill, Nicholson Camp, Cockatoo Springs, Mud Springs, Darlu Darlu, Crocodile Hole, Nulla Nulla, Baulu Wah, RB River Junction, Yirralallem, Dillon Springs, Woolah, Bow River, Guda Guda, and Molly Springs (Government of Western Australia 1998: 94).
Table 6.7. Functionality of dwelling facilities in Wunan ATSIC Region, 1997
|
Dwelling facility |
% of dwellings with facility absent |
% of dwellings with facility working |
% of dwellings with facility not working |
Total dwellings |
|
External plumbing connection |
26.3 |
70.9 |
2.8 |
100.0 |
|
On-site sewerage disposal |
27.6 |
70.8 |
1.6 |
100.0 |
|
Hot water system |
30.7 |
52.6 |
16.8 |
100.0 |
|
Kitchen sink |
26.7 |
70.0 |
3.3 |
100.0 |
|
Bath/shower |
27.4 |
70.1 |
2.5 |
100.0 |
|
Toilet cistern |
28.8 |
67.8 |
3.4 |
100.0 |
|
Toilet bowl |
27.4 |
70.6 |
2.0 |
100.0 |
|
Laundry trough |
32.2 |
65.3 |
2.5 |
100.0 |
|
Laundry waste outlet |
41.4 |
55.0 |
3.6 |
100.0 |
|
Source: Government of Western Australia 1998: 91 |
||||
However, aside from the constant need to ensure that maintenance funds are available and sufficient to ensure minimum environmental health standards, the main challenge for the future management of housing stock now seems to be to ensure that adequate and planned expansion occurs to accommodate new household formation for a rapidly growing population.