Building Nature’s Safety Net 2014 : A decade of protected area achievements in Australia

The single most important asset for the conservation of Australia’s unique and globally significant biodiversity is the National Reserve System, a mosaic of over 10,000 discrete protected areas on land on all tenures: government, Indigenous and private,including on-farm covenants, as well as state, territory and Commonwealth marine parks and reserves.THE NATIONAL RESERVE SYSTEMIn this report, we cover major National Reserve System initiatives that have occurred in the period 2002 to the present and highlight issues affecting progress toward agreed national objectives. We define a minimum standard for the National Reserve System to comprehensively, adequately and representatively protect Australia’s ecosystem and species diversity on sea and land. Using government protected area, species and other relevant spatial data, we quantify gaps: those areas needing to move from the current National Reserve System to one which meets this standard. We also provide new estimates of financial investments in protected areas and of the benefits that protected areas secure for society. Protected areas primarily serve to secure Australia’s native plants and animals against extinction, and to promote their recovery.BENEFITSProtected areas also secure ecosystem services that provide economic benefits forhuman communities including water, soil and beneficial species conservation, climatemoderation, social, cultural and health benefits. On land, we estimate these benefitsare worth over $38 billion a year, by applying data collated by the Ecosystem ServicesPartnership. A much larger figure is estimated to have been secured by marineprotected areas in the form of moderation of climate and impact of extreme eventsby reef and mangrove ecosystems. While these estimates have not been verified bystudies specific to Australia, they are indicative of a very large economic contributionof protected areas. Visitors to national parks and nature reserves spend over $23.6 billion a year in Australia, generating tax revenue for state and territory governments of $2.36 billion a year. All these economic benefits taken together greatly exceed the aggregate annual protected area expansion and management spending by all Australian governments, estimated to be ~$1.28 billion a year. It is clear that Australian society is benefiting far greater than its governments’ investment into strategic growth and maintenance of the National Reserve System.Government investment and policy settings play a leading role in strategic growth of the National Reserve System in Australia, and provide a critical stimulus fornon-government investment. Unprecedented expansion of the National Reserve System followed an historic boost in Australian Government funding under Caring for Our Country 2008–2013. This expansion was highly economical for the Australian Government, costing an average of only $44.40 per hectare to buy and protect land forever. State governments have contributed about six times this amount toward the expansion of the National Reserve System, after including in-perpetuity protected area management costs. The growth of Indigenous Protected Areas by the Australian Government has cost ~$26 per hectare on average, including management costs capitalised in-perpetuity, while also delivering Indigenous social and economic outcomes. The aggregate annual investment by all Australian governments has been ~$72.6 million per year on protected area growth and ~$1.21 billion per year on recurrent management costs. For the first time in almost two decades, however, the Australian Government’s National Reserve System Program, comprising a specialist administrative unit and funding allocation, was terminated in late 2012. This program was fundamental in driving significant strategic growth in Australia’s protected area estate. It is highly unlikely that Australia can achieve its long-standing commitments to an ecologically representative National Reserve System, and prevent major biodiversity loss, without this dedicated funding pool. The Australian Government has budgeted ~$400 million per year over the next five years (2013-2018) under the National Landcare and related programs. This funding program should give high priority to delivery of national protected area commitments by providing a distinct National Reserve System funding allocation. Under the Convention on Biological Diversity (CBD), Australia has committed to bringing at least 17 percent of terrestrial and at least 10 per cent of marine areas into ecologically representative, well-connected systems of protected areas by 2020 (Aichi Target 11).BIODIVERSITY CONSERVATIONAustralia also has an agreed intergovernmental Strategy for developing a comprehensive, adequate and representative National Reserve System on land andsea that, if implemented, would deliver on this CBD target. Due to dramatic recent growth, the National Reserve System covers 16.5 per cent of Australia’s land area, with highly protected areas, such as national parks, covering 8.3 per cent. The marine National Reserve System extends over one-third of Australian waters with highly protected areas such as marine national parks, no-take or green zones covering 13.5 per cent. Growth has been uneven however, and the National Reserve System is still far from meeting Aichi Target 11, which requires that it also be ecologically representative and well-connected. On land, 1,655 of 5,815 ecosystems and habitats for 138 of 1,613 threatened species remain unprotected. Nonetheless, 436 terrestrial ecosystems and 176 threatened terrestrial species attained minimum standards of protection due to growth of the National Reserve System on land between 2002 and 2012. The gap for ecosystem protection on land – the area needed to bring all ecosystems to the minimum standard of protection – closed by a very substantial 20 million hectares (from 77 down to 57 million hectares) between 2002 and 2012, not including threatened species protection gaps. Threatened species attaining a minimum standard for habitat protection increased from 27 per cent to 38 per cent over the decade 2002–2012. A low proportion of critically endangered species meeting the standard (29 per cent) and the high proportion with no protection at all (20 per cent) are cause for concern, but one which should be relatively easy to amend, as the distributions of these species tend to be small and localised. Protected area connectivity has increased modestly for terrestrial protected areas in terms of the median distance between neighbouring protected areas, but this progress has been undermined by increasing land use intensity in landscapes between protected areas.A comprehensive, adequate and representative marine reserve system, which meetsa standard of 15 per cent of each of 2,420 marine ecosystems and 30 per cent of thehabitats of each of 177 marine species of national environmental significance, wouldrequire expansion of marine national parks, no-take or green zones up to nearly 30per cent of state and Australian waters, not substantially different in overall extentfrom that of the current marine reserve system, but different in configuration.Protection of climate change refugia, connectivity and special places for biodiversityis still low and requires high priority attention. FINANCING TO FILL GAPS AND MEET COMMITMENTSIf the ‘comprehensiveness’ and ‘representativeness’ targets in the agreed terrestrial National Reserve System Strategy were met by 2020, Australia would be likely to have met the ‘ecologically representative’ requirement of Aichi Target 11. This would requireexpanding the terrestrial reserve system by at least 25 million hectares. Considering that the terrestrial ecosystem protection gap has closed by 20 million hectares over the past decade, this required expansion would be feasible with a major boost in investment and focus on long-standing priorities. A realistic mix of purchases, Indigenous Protected Areas and private land covenants would require an Australian Government National Reserve System investment of ~$170 million per year over the five years to 2020, representing ~42 per cent of the $400 million per year which the Australian Government has budgeted for landcare and conservation over the next five years. State, territory and local governments, private and Indigenous partners wouldlikewise need to boost financial commitments to both expand and maintain newprotected areas to meet the agreed National Reserve System strategic objectives.The total cost of Australia achieving a comprehensive, adequate and representativemarine reserve system that would satisfy Aichi Target 11 is an estimated $247 million.

The Probe, Issue 204 - September 1999

USFWS to Explore Canada Goose Management Strategies -- from a press release issued Aug. 3 by the US. Fish & Wildlife Service, written by Chris Tollefson. Anti-Trapping Measure Passes House Oregon Legislature Moves To Ensure Safety Of Its Citizens Against Cougars Acord Promoted Away From Wildlife Services New State Director US DA/APHIS in Mississippi is Kristina Godwin BOOk R e v i e w : "Living With Wildlife: How to Enjoy, Cope With, and Protect North America's Wild Creatures Around Your Home and Theirs," The California Center for Wildlife, with Diana Landau and Shelley Stump. San Francisco: A Sierra Club Book. 1994. 340 pp. + index $15.00. French Shepherds Protest Predators Rabbit Calicivirus Kills 65% of Rabbit Population Abstracts from the 2nd International Wildlife Management Congress, Hungary Crop Damage by Wildlife in Northern Ghana – O. I. Aalangdon* and A.S. Langyintuo, *Dept. of Renewable Natural Resources, University for Development Studies, Tamale Northern Region, Ghana Large Predators in Slovenia On the Way from Near Extermination to Overprotection and Back: Is Conservation Management of Large Predators in Cultural Landscapes Possible At All? -- M. Adamic, Chair of Wildlife Ecology, Biotechnical Faculty, University of Ljubljana, Slovenia Human-wolf Conflicts in the East Baltic: Past, Present, and Future -- Z. Andersone*, L. Balciauskas, and H. Valdmann., *Kemeri National Park, KemeriJurmala, Latvia Gray Wolf Restoration in the Northwestern United States -- E.E. Bangs*, J.A. Fontaine, D.W. Smith, C. Mack, and C. C. Niemeyer, *U.S. Fish & Wildlife Service, Helena, MT The Impact of Changing U.S. Demographics on the Future of Deer Hunting -- R. D. Brown, Wildlife & Fisheries Sciences, Texas A&M University, College Station, TX Management of Overabundant Marcropods in Nature Reserves: 6 Case Studies from Southeastern Australia -- G. Coulson, Dept. of Zoology,University of Melbourne,Parkville, Victoria, Australia

Can Roads Be Used as Transects for Primate Population Surveys?

Line transect distance sampling (LTDS) can be applied to either trails or roads. However, it is likely that sampling along roads might result in biased density estimates. In this paper, we compared the results obtained with LTDS applied on trails and roads for two primate species (Callithrix penicillata and Callicebus nigrifrons) to clarify whether roads are appropriate transects to estimate densities. We performed standard LTDS surveys in two nature reserves in south-eastern Brazil. Effective strip width and population density were different between trails and roads for C. penicillata, but not for C. nigrifrons. The results suggest that roads are not appropriate for use as transects in primate surveys, at least for some species. Further work is required to fully understand this issue, but in the meantime we recommend that researchers avoid using roads as transects or treat roads and trails as covariates when sampling on roads is unavoidable. Copyright (C) 2012 S. Karger AG, Basel

Are land sparing and land sharing real alternatives for European agricultural landscapes?

There is a lively debate on whether biodiversity conservation and agricultural production could be better reconciled by land sparing (strictly separating production fields and conservation areas) or by land sharing (combining both, agricultural production and biodiversity conservation on the same land). The debate originates from tropical countries, where agricultural land use continues to increase at the expense of natural ecosystems. But is it also relevant for Europe, where agriculture is withdrawing from marginal regions whilst farming of fertile lands continues to be intensified? Based on recent research on farmland biodiversity we conclude that the land sharing – land sparing dichotomy is too simplistic for Europe. Instead we differentiate between productive and marginal farmland. On productive farmland, semi-natural habitats are required to yield ecosystem services relevant for agriculture, to promote endangered farmland species which society wants to conserve even in intensively farmed regions, and to allow migration of non-farmland species through the agricultural matrix. On marginal farmland, high-nature value farming is a traditional way of land sharing, yielding high quality agricultural products and conserving specialized species. To conserve highly disturbance-sensitive species, there is a need for nature reserves. In conclusion, land sparing is not a viable olution for Europe in both productive and marginal farmland but because of different reasons in each type of farmland.

Diversidad étnica e identidad en la llanura costera del istmo oaxaqueño

En este artículo se desarrollan una serie puntos para entender al istmo oaxaqueño como una zona de convergencia cultural diversa, múltiple y por lo tanto diferenciada tanto en el ámbito de la historia de los pueblos que en ella viven, como en el ámbito de la estructura económica que permite su reproducción no sólo como grupos étnicos, sino como comunidades. El autor plantea que las manifestaciones culturales de cada grupo se confunden, se entrelazan se influencian mutuamente y en una lógica asociada a la perdurabilidad de dichos procesos, terminan por imponerse. Para comprender las relaciones interétnicas no basta con dar cuenta de las características generales de estos grupos sino que es necesario actualizar la información que se ha obtenido de ellos, sobre todo ahora que nuevos procesos nacionales o internacionales están afectando de manera irreversible la composición y la estructura de estas culturas. Aspectos como la falta de vías de comercialización de productos agrícolas y pesqueros, la marginación sempiterna, la falta de empleo a escala regional, la migración, etc.. son entre otros, las aristas de una realidad que se revela en su irremediable avance frente a comunidades que ponen en funcionamiento estrategias de reproducción y de sobreviviencia para mantenerse como comunidad. Las manifestaciones de las relaciones interétnicas aquí se definen como asimétricas horizontales en virtud de una diferenciación entre etnias y las relaciones entre ellas, de tal forma que así como se ha analizado la relación grupos étnicos-sociedad nacional, en la que se constatan desigualdades flagrantes a nivel del acceso a la riqueza generada en el país, calidad de vida, educación, comunicación, y otras variables importantes, de la misma manera se constata que en los grupos étnicos hay unos que tienen una posición privilegiada en el acceso a vías de comunicación, redes comerciales e influencia política, entre otros aspectos, mientras que otros se encuentran excluidos de ellos, no sólo por su condición de indígenas, sino también como consecuencia de la dominación entre etnias que existe en la región. Finalmente, el autor enfatiza que en esta zona del estado de Oaxaca existe una gama considerable de recursos naturales cuya apropiación y explotación para beneficios económicos está en el centro de la discusión actual. En efecto, el sistema de lagunas del Golfo de Tehuantepec, las reservas de la biodiversidad como la selva de los Chimalapas, o la actividad ganadera agrícola en la zona mixe son, entre otras, no sólo zonas importantes de explotación económica, que han fortalecido a grupos de poder locales. También son espacios de control estratégico para el futuro desarrollo del país pues en el istmo oaxaqueño se ha ubicado una fuente importante de riqueza en agua, bosques, especies endémicas, etc... que puede tener un papel importante en la vida económica regional y nacional. La cuestión es saber qué dispositivos sociales o legales se han puesto en marcha para definir a los beneficiarios de esa riqueza natural.

Diversidad étnica e identidad en la llanura costera del istmo oaxaqueño

En este artículo se desarrollan una serie puntos para entender al istmo oaxaqueño como una zona de convergencia cultural diversa, múltiple y por lo tanto diferenciada tanto en el ámbito de la historia de los pueblos que en ella viven, como en el ámbito de la estructura económica que permite su reproducción no sólo como grupos étnicos, sino como comunidades. El autor plantea que las manifestaciones culturales de cada grupo se confunden, se entrelazan se influencian mutuamente y en una lógica asociada a la perdurabilidad de dichos procesos, terminan por imponerse. Para comprender las relaciones interétnicas no basta con dar cuenta de las características generales de estos grupos sino que es necesario actualizar la información que se ha obtenido de ellos, sobre todo ahora que nuevos procesos nacionales o internacionales están afectando de manera irreversible la composición y la estructura de estas culturas. Aspectos como la falta de vías de comercialización de productos agrícolas y pesqueros, la marginación sempiterna, la falta de empleo a escala regional, la migración, etc.. son entre otros, las aristas de una realidad que se revela en su irremediable avance frente a comunidades que ponen en funcionamiento estrategias de reproducción y de sobreviviencia para mantenerse como comunidad. Las manifestaciones de las relaciones interétnicas aquí se definen como asimétricas horizontales en virtud de una diferenciación entre etnias y las relaciones entre ellas, de tal forma que así como se ha analizado la relación grupos étnicos-sociedad nacional, en la que se constatan desigualdades flagrantes a nivel del acceso a la riqueza generada en el país, calidad de vida, educación, comunicación, y otras variables importantes, de la misma manera se constata que en los grupos étnicos hay unos que tienen una posición privilegiada en el acceso a vías de comunicación, redes comerciales e influencia política, entre otros aspectos, mientras que otros se encuentran excluidos de ellos, no sólo por su condición de indígenas, sino también como consecuencia de la dominación entre etnias que existe en la región. Finalmente, el autor enfatiza que en esta zona del estado de Oaxaca existe una gama considerable de recursos naturales cuya apropiación y explotación para beneficios económicos está en el centro de la discusión actual. En efecto, el sistema de lagunas del Golfo de Tehuantepec, las reservas de la biodiversidad como la selva de los Chimalapas, o la actividad ganadera agrícola en la zona mixe son, entre otras, no sólo zonas importantes de explotación económica, que han fortalecido a grupos de poder locales. También son espacios de control estratégico para el futuro desarrollo del país pues en el istmo oaxaqueño se ha ubicado una fuente importante de riqueza en agua, bosques, especies endémicas, etc... que puede tener un papel importante en la vida económica regional y nacional. La cuestión es saber qué dispositivos sociales o legales se han puesto en marcha para definir a los beneficiarios de esa riqueza natural.

Diversidad étnica e identidad en la llanura costera del istmo oaxaqueño

En este artículo se desarrollan una serie puntos para entender al istmo oaxaqueño como una zona de convergencia cultural diversa, múltiple y por lo tanto diferenciada tanto en el ámbito de la historia de los pueblos que en ella viven, como en el ámbito de la estructura económica que permite su reproducción no sólo como grupos étnicos, sino como comunidades. El autor plantea que las manifestaciones culturales de cada grupo se confunden, se entrelazan se influencian mutuamente y en una lógica asociada a la perdurabilidad de dichos procesos, terminan por imponerse. Para comprender las relaciones interétnicas no basta con dar cuenta de las características generales de estos grupos sino que es necesario actualizar la información que se ha obtenido de ellos, sobre todo ahora que nuevos procesos nacionales o internacionales están afectando de manera irreversible la composición y la estructura de estas culturas. Aspectos como la falta de vías de comercialización de productos agrícolas y pesqueros, la marginación sempiterna, la falta de empleo a escala regional, la migración, etc.. son entre otros, las aristas de una realidad que se revela en su irremediable avance frente a comunidades que ponen en funcionamiento estrategias de reproducción y de sobreviviencia para mantenerse como comunidad. Las manifestaciones de las relaciones interétnicas aquí se definen como asimétricas horizontales en virtud de una diferenciación entre etnias y las relaciones entre ellas, de tal forma que así como se ha analizado la relación grupos étnicos-sociedad nacional, en la que se constatan desigualdades flagrantes a nivel del acceso a la riqueza generada en el país, calidad de vida, educación, comunicación, y otras variables importantes, de la misma manera se constata que en los grupos étnicos hay unos que tienen una posición privilegiada en el acceso a vías de comunicación, redes comerciales e influencia política, entre otros aspectos, mientras que otros se encuentran excluidos de ellos, no sólo por su condición de indígenas, sino también como consecuencia de la dominación entre etnias que existe en la región. Finalmente, el autor enfatiza que en esta zona del estado de Oaxaca existe una gama considerable de recursos naturales cuya apropiación y explotación para beneficios económicos está en el centro de la discusión actual. En efecto, el sistema de lagunas del Golfo de Tehuantepec, las reservas de la biodiversidad como la selva de los Chimalapas, o la actividad ganadera agrícola en la zona mixe son, entre otras, no sólo zonas importantes de explotación económica, que han fortalecido a grupos de poder locales. También son espacios de control estratégico para el futuro desarrollo del país pues en el istmo oaxaqueño se ha ubicado una fuente importante de riqueza en agua, bosques, especies endémicas, etc... que puede tener un papel importante en la vida económica regional y nacional. La cuestión es saber qué dispositivos sociales o legales se han puesto en marcha para definir a los beneficiarios de esa riqueza natural.

Policies for saving a rare Australian glider: economics and ecology

This paper considers the economics of conserving a species with mainly non-use value, the endangered mahogany glider. Three serial surveys of Brisbane residents provide data on the knowledge of respondents about the mahogany glider. The results supply information about the attitudes of respondents to the mahogany glider, to its conservation and relevant public policies, and about variations in these factors as the knowledge of participants of the mahogany glider alters. Similarly, data are provided and analysed about the willingness to pay of respondents to conserve the mahogany glider and how it changes. Population viability analysis is applied to estimate the required habitat area for a minimum viable population of the mahogany glider to ensure at least a 95% probability of its survival for 100 years. Places are identified in Queensland where the requisite minimum area of critical habitat can be conserved. Using the survey results as a basis, the likely willingness of groups of Australians to pay for the conservation of the mahogany glider is estimated and consequently their willingness to pay for the minimum required area of its habitat. Methods for estimating the cost of protecting this habitat are outlined. Australia-wide benefits are estimated to exceed the costs. Establishing a national park containing the minimum viable population of the mahogany glider is an appealing management option. This would also be beneficial in conserving other endangered wildlife species and ecosystems. Therefore, additional economic benefits to those estimated on account of the mahogany glider itself can be obtained. (C) 2004 Elsevier Ltd. All rights reserved.

A new method for conservation planning for the persistence of multiple species

Although the aim of conservation planning is the persistence of biodiversity, current methods trade-off ecological realism at a species level in favour of including multiple species and landscape features. For conservation planning to be relevant, the impact of landscape configuration on population processes and the viability of species needs to be considered. We present a novel method for selecting reserve systems that maximize persistence across multiple species, subject to a conservation budget. We use a spatially explicit metapopulation model to estimate extinction risk, a function of the ecology of the species and the amount, quality and configuration of habitat. We compare our new method with more traditional, area-based reserve selection methods, using a ten-species case study, and find that the expected loss of species is reduced 20-fold. Unlike previous methods, we avoid designating arbitrary weightings between reserve size and configuration; rather, our method is based on population processes and is grounded in ecological theory.

Vegetation dynamics and their implications for the management of wetlands in the lowlands of Nepal

The maintenance of species richness is often a priority in the management of nature reserves, where consumptive use of resources is generally prohibited. The purpose of this research was to improve management by understanding the vegetation dynamics in the lowlands of Nepal. The objectives were to determine vegetation associations in relation to environments and human-induced disturbances that affect vegetation dynamics on floodplains, where upstream barrages had altered flooding patterns, and consumptive use of plant resources was influencing natural processes. Floodplain vegetation in relation to physical environments and disturbances were studied along transects, perpendicular to the course of the Mahakali River in the western Terai, Nepal. Forest structural changes were studied for three years in ten plots. A randomized split-block experiment with nine burning and grazing treatments was performed in seasonally flooded grasslands. A semi-structured questionnaire was used to assess people's socio-economic status, natural resource use patterns and conservation attitudes. ^ Elevation, soil organic matter, nitrogen, percentage of sand and grazing intensity were significant in delineating herbaceous vegetation assemblages, whereas elevation and livestock grazing were significant in defining forest type boundaries. On the floodplain islands, highly grazed Dalbergia sissoo-Acacia catechu forests were devoid of understory woody vegetation, but the lightly grazed D. sissoo-mixed forests had a well-developed second canopy layer, comprising woody species other than D. sissoo and A. catechu. In grasslands, species richness and biomass production were highest at intermediate disturbance level represented by the lightly grazed and ungrazed early-burned treatments. Ethnicity, education and resource use patterns were important in influencing conservation attitudes. A succession towards the mixed forests would occur in D. sissoo-dominated floodplain forests, where dams and barrages reduce flooding and associated fluvial processes, and if livestock grazing is stopped, as occasionally suggested by nature conservationists. In seasonally flooded grasslands, early burning with moderate grazing would enhance the species diversity and productivity. There is a need to implement a participatory integrated wetland management plan, to include community development, education and off farm income generation, to assure participatory conservation and management of wetlands in Nepal. ^

Förbättring av tillgänglighet i tillgänglighetsanpassade naturreservat

More than half a million people in Sweden are affected by some sort of disability. During recreational activities in nature areas, these people might encounter difficulties such as inadequate accessibility. The Swedish society requires that all citizens should have the same possibilities. The purpose of this thesis is to improve the accessibility for people with disabilities. The aim is to examine occurring flaws in accessible nature reserves and suggest possible improvements.The questions that will be answered are as follows:• What flaws do accessible nature reserves have, and how do they affect the visitors?• What improvements can be made in nature reserves to increase accessibility?To answer the questions, a case study was done, where five different nature areas were visited. During the case study, various flaws in the accessibility were observed and analysed. Prior to the case study, requirements and scientific research regarding accessibility was studied. Using this, suggestions for improving the accessibility were made. . Most of the improvements that could be made in the studied nature reserves were presumed to be applicable in other nature reserves in Sweden.With the case study in mind, the accessibility was considered in need of various improvements. The accessibility was studied from three out of four of the Swedish disability association’s categories; physical, communicative, and informative accessibility. The flaws that were encountered in the studied areas were due to incorrect design, or insufficient maintenance. Most of the flaws could be corrected in simple ways, but the flaws that were due to incorrect design or planning would require more work. After the case study it was discovered that supposedly “accessible” trails, according to different websites, had varying levels of accessibility. An accessible recreational area will benefit all types of visitors, not only people with disabilities. It will be more convenient and enables visits with strollers. An area cannot be made accessible for all types of visitors, but can be made accessible for as many visitors as possible.

Green planning heritage/industrial nature : the park lands or 'regeneration reserves' of Broken Hill

Freestone (1989+) has extensively surveyed town planning visions and model communities for Australia, but one settlement has been forgotten. The significant mining settlement of Broken Hill in far western New South Wales does not figure in his thematic and historical analyses yet its park lands are so integral to its physical cultural legacy and human health that it warrants enhanced standing. In the last 2 years the Commonwealth has been considering the potential nomination of the municipality of Broken Hill for inclusion onto the National Heritage List principally due to its mining, social and economic contributions to Australia’s heritage and identity. A component in their deliberations is the Park Lands, or ‘Regeneration Reserves’, that encompass this urban settlement and its mine leaseholds. Within these Regeneration Reserves, international arid zone ecological restoration theory and practice was pioneered by Albert and Margaret Morris in the 1930s that serves as the method for all mining revegetation practice in Australia today. This paper reviews the theory and evolution of the Broken Hill Regeneration Reserves, having regard to the Adelaide Park Lands and Garden City discourses of the 1920s-30s, arguing that the Broken Hill Regeneration Reserves have a valid and instrumental position in the planning and landscape architectural histories of Australia.