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Journal articles on the topic 'Sustainable forestry Western Australia'

Author: Grafiati
Published: 4 June 2021
Last updated: 1 February 2022

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1

C. Calver, M., and J. Dell. "Conservation status of mammals and birds in southwestern Australian forests. II. Are there unstudied, indirect or long-term links between forestry practices and species decline and extinction?" Pacific Conservation Biology 4, no. 4 (1998): 315. http://dx.doi.org/10.1071/pc980315.

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There is little evidence in the literature for past or current negative impacts of forestry practices on the mammals and birds of the south-west forests of Western Australia, although there are few relevant, detailed studies. For the conclusion of no major negative impact of forestry practices to be accepted, it must be shown that there are no indirect connections between forestry practices and established causes of fauna decline and that it is unlikely that forestry practices will have delayed impacts on the conservation status of mammals and birds. This paper reviews the literature relevant to these issues and concludes: (i) past forestry practices are linked to the changed fire regimes implicated in the decline of several species, indirectly connecting forestry practices with an established cause of fauna decline, (ii) there are plausible links between forestry and long-term causes of fauna decline that have not been investigated thoroughly. However, these findings need not mean that a native timber industry is incompatible with conservation in the south-west forests. Rather, they highlight the need for mediation between parties in the forest management debate, perhaps using some of the approaches developed recently in eastern Australia and North America. Concurrently, research effort could be directed towards determining the effectiveness of management initiatives already in place to ameliorate forestry impacts, while identifying actions successful elsewhere and setting research priorities to enable their effective implementation in the south-west. Forest managers, past and present, have good reason to be proud of their efforts. Even during earlier eras, when the focus of forest management was largely on timber supply, the need to ensure successful regeneration after logging has acted to conserve the whole jarrah and karri forest ecosystem. Abbott and Christensen (1994). The challenges posed by old growth eucalypt forest management in Australia are unique and by virtue of historical events, lie with our generation. To our advantage is an appreciation of what reforms are required, the availability of adequate knowledge and technology, and an understanding of what is at stake. A move towards ecologically sustainable forest use in Australia's remaining eucalypt forests requires a combination of initiatives including an enhanced conservation reserve network, and markedly enhanced protective measures in unreserved forest ecosystems, irrespective of land tenure. Significant reductions in logging quotas and major changes to current codes of forest practice are required if stated biodiversity conservation goals are to be achieved. Institutional reforms are required to support these changes as is support for long-term ecological research and monitoring. Norton (1996).
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2

Wardell-Johnson, Grant W., Michael Calver, Neil Burrows, and Giovanni Di Virgilio. "Integrating rehabilitation, restoration and conservation for a sustainable jarrah forest future during climate disruption." Pacific Conservation Biology 21, no. 3 (2015): 175. http://dx.doi.org/10.1071/pc15026.

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The environment of the northern jarrah (Eucalyptus marginata) forest (NJF) of Mediterranean-climate, south-western Australia is characterised by deeply weathered soil profiles and low fertility, reflecting long geological stasis. This fire-prone environment is characterised by primary forests of low productivity but high biomass. Since European settlement (1829), the NJF has been structurally transformed by deforestation and resource extraction, including logging and mining (principally for bauxite). Rainfall has declined by 15–20% since 1970, with projections for further decline. A new hydrological regime foreshadows regolith drying, with a changed climate leading to more unplanned, intense fires. Declining productivity, coupled with rehabilitation more suited to a wetter climate, places stress on tree growth and compromises biodiversity. Thus, ecological disruption likely follows from interactions between climate change and historical exploitation. The complex challenges posed by these interactions require multifaceted and novel solutions. We argue that under drying conditions, maintenance of productivity while conserving biodiversity can best be achieved by changing the focus of rehabilitation to the understorey. This would coincide with protecting and restoring surrounding unmined forest with emphasis on the overstorey. Presently, state-of-the-science rehabilitation seeks to restore jarrah forest, following bauxite mining. This goal is unlikely to be achievable across extensive areas under climate change projections. Rather, a focus on restoring understorey following mining would provide a more positive water balance in the wider forest matrix. This approach recognises loss of forest values through mining, but anticipates conservation of biodiversity and important elements of forest structure by minimising ecologically unacceptable disturbance to surrounding forest.
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3

Wilson, Geoff A., and P. Ali Memon. "Indigenous Forest Management in 21st-Century New Zealand: Towards a ‘Postproductivist’ Indigenous Forest–Farmland Interface?" Environment and Planning A: Economy and Space 37, no. 8 (August 2005): 1493–517. http://dx.doi.org/10.1068/a37144.

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The critique of indigenous forest management in New Zealand in this paper contextualises the discussion in light of recent Eurocentric debates on the transition towards ‘postproductivist’ and ‘multifunctional’ agricultural and forestry regimes. The research findings confirm recent criticisms of Australian writers with regard to the direct transferability of the notion of a transition towards postproductivism developed by European researchers and also lend support to Holmes's (2002) notion of productivist and postproductivist occupance. Long-standing productivist demands continue to be made on New Zealand's indigenous forests, especially from economically marginalised stakeholder groups who depend on the continuation of logging for economic survival. We argue that the tension between the recent adoption of a ‘postproductivist’ conservation policy at government level and the continuing ‘productivist’ attitudes among some stakeholder groups explains why the protection of remaining indigenous forests continues to be contested. The New Zealand findings also provide further evidence for those persons criticising the implied linearity and dualism inherent in the Eurocentric postproductivist transition model. We argue that processes at the New Zealand forest–farmland interface support Wilson's (2001) notion of a territorialisation of productivist and postproductivist territories into a ‘multifunctional’ territory. From a social constructionist perspective, the results highlight the fact that a clear separation into productivist and postproductivist occupance may not be easy to conceptualise as our view of agricultural land as ‘productivist’ territory and unlogged or sustainably managed indigenous forest as ‘postproductivist’ territory is largely based on a Euro–American ‘deep green’ view of unaltered ‘nonhuman’ nature. This supports Mather's (2001) suggestion that postproductivism should be cast as part of a shifting mode of social regulation of forestry with particular stakeholder groups constructing images of nature according to their interests, and where western ideas of nature as a (postproductivist) wilderness embody cultural politics which arguably serve to marginalise the interests of indigenous communities.
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4

Fraser, D., and E. M. Davison. "Stem cankers ofEucalyptus salignain Western Australia." Australian Forestry 48, no. 4 (January 1985): 220–26. http://dx.doi.org/10.1080/00049158.1985.10674449.

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5

Behn, G., F. H. McKinnell, P. Caccetta, and T. Vernes. "Mapping forest cover, Kimberley Region of Western Australia." Australian Forestry 64, no. 2 (January 2001): 80–87. http://dx.doi.org/10.1080/00049158.2001.10676169.

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6

Radomiljac, Andrew M., Syd R. Shea, F. H. McKinnell, and Jen A. McComb. "Potential for irrigated tropical forestry in northern Western Australia." Australian Forestry 61, no. 2 (January 1998): 70–75. http://dx.doi.org/10.1080/00049158.1998.10674722.

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7

Abbott, Ian, and Per Christensen. "Objective knowledge, ideology and the forests of Western Australia." Australian Forestry 59, no. 4 (January 1996): 206–12. http://dx.doi.org/10.1080/00049158.1996.10674690.

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8

Calver, M. C., C. R. Dickman, M. C. Feller, R. J. Hobbs, P. Horwitz, H. F. Recher, and G. Wardell-Johnson. "Towards resolving conflict between forestry and conservation in Western Australia." Australian Forestry 61, no. 4 (January 1998): 258–66. http://dx.doi.org/10.1080/00049158.1998.10674750.

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9

Bradshaw, F. J. "Trends in silvicultural practices in the native forests of Western Australia." Australian Forestry 62, no. 3 (January 1999): 255–64. http://dx.doi.org/10.1080/00049158.1999.10674790.

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10

Ecker, S., A. Karafilis, and R. Taylor. "Challenges of the Blackwood Basin, Western Australia." Water Science and Technology 43, no. 9 (May 1, 2001): 37–44. http://dx.doi.org/10.2166/wst.2001.0504.

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Growing concern about the declining state of the catchment and river led to the formation of the Blackwood Basin Group in 1992. Funded primarily by the Natural Heritage Trust and using the river as the focus, the group aims to provide leadership and support to achieve sustainable management of natural resources in the catchment. Through an Integrated Catchment Management approach, the Blackwood Basin Group has managed a range of projects to improve the community's understanding and management of the Blackwood River and its catchment. A number of research, education, demonstration and on-ground action activities relating to river management have been undertaken in partnership with community and local, state and federal government organisations. Activities include demonstrations and evaluations of riparian restoration, funding riparian restoration activities, protection of high conservation value remnant vegetation, a flood risk study, zone action planning and monitoring the condition of the river and its tributaries.
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11

Burrows, ND. "Patch-Burning Desert Nature Reserves in Western Australia Using Aircraft." International Journal of Wildland Fire 1, no. 1 (1991): 49. http://dx.doi.org/10.1071/wf9910049.

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Fire management in desert nature reserves in Western Australia aims to restrict the spread of wildfires and to re-introduce a spatial and temporal mosaic of firecreated patches. Aerial ignition is well suited to patchburning the large, remote and poorly accessible desert reserves. The Weather Factor, a function incorporating wind speed, temperature and relative humidity, dxectly influenced the ignition rate, the range of sizes of burnt patches and the area burnt. During the trials described here, some 140,000 ha of spinifex fuels in the Gibson Desert Nature Reserve were patch-burnt using aircraft at a total cost of A$O.32 ha-1.
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12

Strelein, G. J. "Gum leaf skeletoniser moth, Uraba lugens,in the forests of Western Australia." Australian Forestry 51, no. 3 (January 1988): 197–204. http://dx.doi.org/10.1080/00049158.1988.10676042.

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13

Ritson, P., N. E. Pettit, and J. F. McGrath. "Fertilising Eucalypts at Plantation Establishment on Farmland in south-west Western Australia." Australian Forestry 54, no. 3 (January 1991): 139–47. http://dx.doi.org/10.1080/00049158.1991.10674570.

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14

Abbott, Ian, and Per Christensen. "Application of ecological and evolutionary principles to forest management in Western Australia." Australian Forestry 57, no. 3 (January 1994): 109–22. http://dx.doi.org/10.1080/00049158.1994.10676125.

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15

Williamson, Jim, Kate Rodger, Susan A. Moore, and Carol Warren. "An exploratory study of community expectations regarding public forests in Western Australia." Australian Forestry 75, no. 2 (January 2012): 100–106. http://dx.doi.org/10.1080/00049158.2012.10676391.

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16

Moores, Len, and Sean Dolter. "Forest management planning in Newfoundland and Labrador: The Western Newfoundland Model Forest contribution." Forestry Chronicle 78, no. 5 (October 1, 2002): 655–57. http://dx.doi.org/10.5558/tfc78655-5.

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The management of forests has dramatically changed in the past few decades. Forest managers no longer can prepare and implement forest management plans in isolation of other resource values and local citizens. Today, the economic, ecological and social values are blended together into sustainable forest management. Finding a balance among these values in Newfoundland and Labrador is done through local district planning teams. The team participants need to understand the principles of sustainable forest management and the overall planning process. A primary focus of the Western Newfoundland Model Forest has been to support planning teams through the development of management tools to enhance management of the Province’s forest ecosystems. The Model forest program will continue to test, document and transfer new and innovative management options to forest managers. Key words: adaptive management, consensus, sustainable forest management, planning teams, public involvement, model forests
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17

Curtis, Carey, and John Punter. "Design-led sustainable development: The Liveable Neighbourhoods experiment in Perth, Western Australia." Town Planning Review 75, no. 1 (March 2004): 31–65. http://dx.doi.org/10.3828/tpr.75.1.3.

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18

Hart, Jason C. "Dutch Disease and the Sustainable Management of Royalty Wealth in Western Australia*." Economic Papers: A journal of applied economics and policy 29, no. 4 (December 2010): 421–31. http://dx.doi.org/10.1111/j.1759-3441.2010.00087.x.

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19

Conacher, A., M. Tonts, and J. Conacher. "Education and land-use planning for sustainable agricultural development in Western Australia." Land Degradation & Development 15, no. 3 (May 2004): 299–310. http://dx.doi.org/10.1002/ldr.616.

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20

Goeft, Ute, and Jackie Alder. "Sustainable Mountain Biking: A Case Study from the Southwest of Western Australia." Journal of Sustainable Tourism 9, no. 3 (September 29, 2001): 193–211. http://dx.doi.org/10.1080/09669580108667398.

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21

Grant, C. D., J. M. Koch, D. T. Bell, and W. A. Loneragan. "Tree species response to prescribed burns in rehabilitated bauxite mines in Western Australia." Australian Forestry 60, no. 2 (January 1997): 84–89. http://dx.doi.org/10.1080/00049158.1997.10674702.

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22

Abbott, Ian, and Neil Burrows. "Biodiversity conservation in the forests and associated vegetation types of southwest Western Australia." Australian Forestry 62, no. 1 (January 1999): 27–32. http://dx.doi.org/10.1080/00049158.1999.10674759.

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23

Dumbrell, I. C., and J. F. McGrath. "Growth and nutrient relationships of juvenilePinus pinastergrown on ex-farmland in Western Australia." Australian Forestry 66, no. 2 (January 2003): 137–44. http://dx.doi.org/10.1080/00049158.2003.10674903.

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24

Brand, David G. "Forest management in New South Wales, Australia." Forestry Chronicle 73, no. 5 (October 1, 1997): 578–85. http://dx.doi.org/10.5558/tfc73578-5.

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Forest management policy in New South Wales, Australia, has been dramatically changing during the past two decades in response to public controversy and widening expectations of the values that the forest should provide to society. The nature of NSW forest management today is a reflection of the unique Australian forest ecology, the nature of the forest sector, and the emergence of conflict and polarized views on forest management in the past two decades. Recent efforts have made progress in resolving the forest debate. The key elements have included an expanded protected areas reserve system, expanded reliance on plantation forests for wood supply, increased wood security for native forest industries in return for a commitment to value-adding and the implementation of an ecologically sustainable forest management framework. Like other Australian States, NSW is currently negotiating Regional Forest Agreements with the Commonwealth Government that will set the stage for future directions in forest management. Key words: forest policy, Australia, New South Wales forest management
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25

Spinelli, Raffaele, Mark Brown, Rick Giles, Dan Huxtable, Ruben Laina Relaño, and Natascia Magagnotti. "Harvesting alternatives for mallee agroforestry plantations in Western Australia." Agroforestry Systems 88, no. 3 (May 16, 2014): 479–87. http://dx.doi.org/10.1007/s10457-014-9707-4.

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26

Howard, Trevor, Neil Burrows, Tony Smith, Glen Daniel, and Lachlan McCaw. "A framework for prioritising prescribed burning on public land in Western Australia." International Journal of Wildland Fire 29, no. 5 (2020): 314. http://dx.doi.org/10.1071/wf19029.

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A risk-based framework for targeting investment in prescribed burning in Western Australia is presented. Bushfire risk is determined through a risk assessment and prioritisation process. The framework provides principles and a rationale for programming fuel management with indicators to demonstrate that bushfire risk has been reduced to an acceptable level. Indicators provide targets for fuel management that are applicable throughout the state and can be customised to meet local circumstances. The framework identifies eight bushfire risk management zones having broad consistency of land use, fire environment and management approach, which combine to create a characteristic risk profile. Thirteen fuel types based primarily on structural attributes of the vegetation that influence fire behaviour are recognised and used to assign models for fuel accumulation and fire behaviour prediction. Each bushfire risk management zone is divided into fire management areas, based on the management intent. These are areas where fuels will be managed primarily to minimise the likelihood of fire causing adverse impacts on human settlements or critical infrastructure, to reduce the risk of bushfire at the landscape scale or to achieve other land management outcomes. Indicators of acceptable bushfire risk are defined for each fire management area and are modified according to the distribution of assets and potential fire behaviour in the landscape. Risk criteria established in the framework can be converted to spatially represented targets for fuel management in each zone and can be reported against to measure the effectiveness of the fuel management program. In areas where the primary intent is to reduce the risk of bushfire at the landscape scale, managers have flexibility to apply prescribed fire in ways that maintain and enhance ecosystem services, nature conservation and landscape values through variation in the seasonality, intensity and scale of planned burning.
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27

Wood, P. J. "Sustainable forestry and certification in the Commonwealth." Forestry Chronicle 72, no. 6 (December 1, 1996): 599–603. http://dx.doi.org/10.5558/tfc72599-6.

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Sustainable forest management is the goal of most foresters and of the informed public and it is the main mission of the Commonwealth Forestry Association. Certification of forest products is a recent market phenomenon, driven partly by Non-Government Organizations and partly by retailers; it is largely a western initiative with parallels in agricultural and pharmaceutical products. Certification does not guarantee sustainability—it only defines what the buyer demands, like lumber dimensions. Environmental or social certification is a contractual specification and the European market seems currently to be the furthest forward with such schemes. Without such market pull, interest in certification would collapse. There are now many initiatives world wide; the Forest Stewardship Council began as an accrediter of independent certifiers, but countries are now developing their own criteria and especially seeking approaches through the International Standards Organization (ISO), an ISO 14000 or ISO 9000 approach. The relevance of certification to many smaller tropical Commonwealth countries is limited, since international trade is of little concern, and many newcomers to the international market have not yet adopted certification requirements. The challenge for the future is to find norms of country-specific good forest stewardship and certifiers are now turning their attention to other objects of trade.
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28

Byrne, J. J., M. Anda, and G. E. Ho. "Water sustainable house: water auditing of 3 case studies in Perth, Western Australia." Water Practice and Technology 14, no. 2 (April 16, 2019): 435–43. http://dx.doi.org/10.2166/wpt.2019.028.

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Abstract Householders in cities face water-related issues due to the increasing cost and restrictions in water use, especially during drought. They respond in many different ways, ranging from installing water efficient appliances, adopting water-saving behavior and implementing greywater reuse, to being water self reliant (off-mains supply). The latter approach should consider using only rainwater falling on the property boundaries, and if self-supply is from groundwater it should be derived from rainwater falling on the property. Therefore, sustainability depends on the annual rainfall, size of property and availability of storage for water to be used during periods without rainfall. In principle any house can be retrofitted to rely solely on rainwater, because technologies exist to treat subsequent wastewater to any quality desired for reuse. However, the energy requirement and investment needed may negate overall sustainability. Very few studies have assessed water use in households to determine whether relying solely on rainwater is practical or sustainable in the long-term. Three case studies in Perth, Western Australia are reported here, where water auditing has been used for sustainability assessment.
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29

Cozens, P. "Crime prevention through environmental design in Western Australia: planning for sustainable urban futures." International Journal of Sustainable Development and Planning 3, no. 3 (August 19, 2008): 272–92. http://dx.doi.org/10.2495/sdp-v3-n3-272-292.

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30

Burrows, N. D., Y. C. Woods, B. G. Ward, and A. D. Robinson. "Prescribing low intensity fire to kill wildings in Pinus radiata plantations in Western Australia." Australian Forestry 52, no. 1 (January 1989): 45–52. http://dx.doi.org/10.1080/00049158.1989.10674535.

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31

Biggs, P. H., and R. D. Spencer. "New approaches to extensive forest inventory in Western Australia using large-scale aerial photography." Australian Forestry 53, no. 3 (January 1990): 182–93. http://dx.doi.org/10.1080/00049158.1990.10676076.

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32

Hathurusingha, Subhash, Nanjappa Ashwath, Kolitha Wijesekara, and David Midmore. "Reproductive phenology of Calophyllum inophyllum in Yeppoon, Australia and Meegoda Western Province, Sri Lanka." Journal of Forestry Research 22, no. 4 (May 13, 2011): 615–19. http://dx.doi.org/10.1007/s11676-011-0169-5.

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33

Biggs, P. H. "Aerial tree volume functions for eucalypts in Western Australia." Canadian Journal of Forest Research 21, no. 12 (December 1, 1991): 1823–28. http://dx.doi.org/10.1139/x91-251.

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Large-scale, fixed-base aerial photography is being used together with ground sampling in a major inventory of eucalypt forest in Western Australia. This paper describes the aerial tree volume functions derived for that inventory, covering species in the jarrah (Eucalyptusmarginata) forest. The equations, derived from ground measurements, predict gross bole volume from estimates of total height and vary with the site quality of the forest. They are used to predict volume from photomeasurements of total height that have been corrected for measurement error. The functions appear suitable for this forest type, although the volumes of veteran trees with severely damaged crowns are underestimated.
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34

Butcher, T. B. "Achievements in forest tree genetic improvement in Australia and New Zealand 7: Maritime pine and Brutian pine tree improvement programs in Western Australia." Australian Forestry 70, no. 3 (January 2007): 141–51. http://dx.doi.org/10.1080/00049158.2007.10675014.

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35

Christensen, Per, and Ian Abbott. "Impact of fire in the eucalypt forest ecosystem of southern Western Australia: a critical review." Australian Forestry 52, no. 2 (January 1989): 103–21. http://dx.doi.org/10.1080/00049158.1989.10674542.

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36

Brand, J. E., P. C. Ryan, and M. R. Williams. "Establishment and growth of sandalwood (Santalum spicatum) in south-western Australia: the Northampton pilot trial." Australian Forestry 62, no. 1 (January 1999): 33–37. http://dx.doi.org/10.1080/00049158.1999.10674760.

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37

Mazanec, R. "Nine year results from aEucalyptus camaldulensisDehnh. provenance trial in the Wellington catchment of Western Australia." Australian Forestry 62, no. 2 (January 1999): 166–72. http://dx.doi.org/10.1080/00049158.1999.10674779.

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38

Mazanec, R. A., M. L. Mason, and C. Vellios. "Performance of spotted gum provenances for timber production on former bauxite mines in Western Australia." Australian Forestry 66, no. 2 (January 2003): 129–36. http://dx.doi.org/10.1080/00049158.2003.10674902.

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39

McGrath, J. F., I. C. Dumbrell, R. A. Hingston, and B. Copeland. "Nitrogen and phosphorus increase growth of thinned late-rotationPinus radiataon coastal sands in Western Australia." Australian Forestry 66, no. 3 (January 2003): 217–22. http://dx.doi.org/10.1080/00049158.2003.10674915.

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40

Koch, J. M., and S. C. Ward. "Thirteen-year growth of jarrah (Eucalyptus marginata) on rehabilitated bauxite mines in south-western Australia." Australian Forestry 68, no. 3 (January 2005): 176–85. http://dx.doi.org/10.1080/00049158.2005.10674963.

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41

Robinson, Richard. "Forest health surveillance in Western Australia: a summary of major activities from 1997 to 2006." Australian Forestry 71, no. 3 (January 2008): 202–11. http://dx.doi.org/10.1080/00049158.2008.10675036.

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42

Myers, Norman. "Forestland farming in western Amazonia: Stable and sustainable." Forest Ecology and Management 15, no. 2 (June 1986): 81–93. http://dx.doi.org/10.1016/0378-1127(86)90138-6.

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43

Growns, IO, and JA Davis. "Effects of forestry activities (clearfelling) on stream macroinvertebrate fauna in south-western Australia." Marine and Freshwater Research 45, no. 6 (1994): 963. http://dx.doi.org/10.1071/mf9940963.

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The effects of forestry activities on macroinvertebrate community structure were examined in the headwaters of Carey Brook in the south-west of Australia. The fauna at four sites on an upland stream that ran through a logging coupe were compared, before and after clearfelling, with the fauna at four nearby undisturbed sites. Mean species richness and mean total abundance declined at the treatment sites relative to the control sites after the commencement of clearfelling activities. The composition of the macroinvertebrate fauna in the disturbed stream changed in comparison with that in the undisturbed sites after logging started but returned to the pre-logging composition after winter and spring rains had stopped. The observed changes in the macroinvertebrate fauna occurred during the periods of high loads of suspended inorganic solids at the treatment sites. The possible reasons for the observed results are discussed.
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44

Trayler, K. M., and J. A. Davis. "Forestry impacts and the vertical distribution of stream invertebrates in south-western Australia." Freshwater Biology 40, no. 2 (September 1998): 331–42. http://dx.doi.org/10.1046/j.1365-2427.1998.00337.x.

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45

Stoneman, Geoff L. "‘Ecological forestry’ and eucalypt forests managed for wood production in south-western Australia." Biological Conservation 137, no. 4 (July 2007): 558–66. http://dx.doi.org/10.1016/j.biocon.2007.03.008.

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46

Schoknecht, Noel. "Report card on sustainable natural-resource use in the agricultural regions of Western Australia." Soil Research 53, no. 6 (2015): 695. http://dx.doi.org/10.1071/sr14267.

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A ‘Report Card’, which summarises the current knowledge of the status and trend in land condition in the agricultural areas of the south-west of Western Australia, was published in 2013 by the Department of Agriculture and Food, Western Australia. The Report Card draws on best available evidence from government and industry on the current condition and trend of 10 soil- and water-related natural resource themes relevant to agriculture, and discusses the implications of these results for the agricultural industries. The report also discusses the three main factors driving the performance of the land, namely climate, land characteristics and land management. The first two factors are largely out of the control of land managers, but in a drying and warming climate of the agricultural areas of Western Australia, land-management practices need to be able to respond to these changing conditions. The paper briefly explains the methodologies used to assess the seven soil-related themes in the Report Card and summarises the major findings. The results indicate that, for soils, the situation and outlook for our natural resources is mixed. Although there has been progress in some areas, such as managing wind and water erosion, the status and trend in many indicators of resource condition, such as soil acidity, soil compaction and water repellence, are adverse. The predicted growth in global demand for food and fibre brings many opportunities to the Western Australian agri-food sector but also challenges, especially in light of the Report Card findings. One of these challenges is our need to achieve agricultural productivity growth while ensuring our natural resources are healthy and resilient.
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47

Ramsden, Robyn, Richard Colbran, Tricia Linehan, Michael Edwards, Hilal Varinli, Carolyn Ripper, Angela Kerr, et al. "Partnering to address rural health workforce challenges in Western NSW." Journal of Integrated Care 28, no. 2 (November 4, 2019): 145–60. http://dx.doi.org/10.1108/jica-06-2019-0026.

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Purpose While one-third of Australians live outside major cities, there are ongoing challenges in providing accessible, sustainable, and appropriate primary health care services in rural and remote communities. The purpose of this paper is to explore a partnership approach to understanding and addressing complex primary health workforce issues in the western region of New South Wales (NSW), Australia. Design/methodology/approach The authors describe how a collaboration of five organisations worked together to engage a broader group of stakeholders and secure commitment and resources for a regional approach to address workforce challenges in Western NSW. A literature review and formal interviews with stakeholders gathered knowledge, identified issues and informed the overarching approach, including the development of the Western NSW Partnership Model and Primary Health Workforce Planning Framework. A stakeholder forum tested the proposed approach and gained endorsement for a collaborative priority action plan. Findings The Western NSW Partnership Model successfully engaged regional stakeholders and guided the development of a collaborative approach to building a sustainable primary health workforce for the future. Originality/value Given the scarcity of literature about effective partnerships approaches to address rural health workforce challenges, this paper contributes to an understanding of how to build sustainable partnerships to positively impact on the rural health workforce. This approach is replicable and potentially valuable elsewhere in NSW, other parts of Australia and internationally.
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48

Abbott, I., P. Van Heurck, T. Burbidge, and A. Wills. "Factors influencing the performance of jarrah leafminer (Lepidoptera) within stands of jarrah forest of Western Australia." Australian Forestry 57, no. 4 (January 1994): 165–70. http://dx.doi.org/10.1080/00049158.1994.10676133.

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49

Norwood, C., G. Wardell-Johnson, J. D. Majer, and M. Williams. "Short-term influences of edge and gap creation on bird populations in jarrah forest, Western Australia." Australian Forestry 58, no. 2 (January 1995): 48–57. http://dx.doi.org/10.1080/00049158.1995.10674644.

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50

Mazanec, R. A. "Thirteen year results from a Spotted Gum provenance trial in the Wellington catchment of Western Australia." Australian Forestry 62, no. 4 (January 1999): 315–19. http://dx.doi.org/10.1080/00049158.1999.10674798.

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