Academic literature on the topic 'Forest protection Australia Case studies'

The native eucalypt forests of southeastern Australia are managed for wood production, water protection, human recreation and the conservation of plants and wildlife. One strategy to conserve forest wildlife within wood production areas involves the use of unlogged strips or corridors of habitat. Most corridors are situated in gullies within forest catchments. However, a review of recent studies undertaken in southeastern Australia shows that many species of forest mammals either require habitat outside of gullies to find food and shelter, or make regular movements between forest on different parts of the topographic sequence. These findings illustrate that strategies for the design and implementation of wildlife corridors need to become more sophisticated and ensure: (i) the conservation of forest on ridges and midslopes, and (ii) the linkage of uncut stands on ridges and midslopes with forest in gullies.

This study aims to investigate the role of ecotourism activities and programs in promoting the conservation and protection of the limestone forest at tourism destinations in Langkawi. University students from Malaysia and Australia collaborated in this case study to gather data on the applicability of using ecotourism as a tool for conservation activities in Langkawi. Three field trips were undertaken to the Langkawi limestone forests, where researchers employed onsite observation and face to face interviews with 30 stakeholders from multiple backgrounds. The result indicated that through hands-on experience, ecotourism promotes the conservation and protection of the limestone forest. Keywords: ecotourism, conservation, limestone forest, Langkawi eISSN: 2398-4287 © 2021.. The Authors. Published for AMER ABRA cE-Bs by e-International Publishing House, Ltd., U.K. This is an open access article under the CC BYNC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Peer–review under responsibility of AMER (Association of Malaysian Environment-Behaviour Researchers), ABRA (Association of Behavioural Researchers on Asians) and cE-Bs (Centre for Environment-Behaviour Studies), Faculty of Architecture, Planning & Surveying, Universiti Teknologi MARA, Malaysia. DOI: https://doi.org/10.21834/ebpj.v6iSI6.3047

Abstract. The adage: “There is no such thing as a free lunch”, is relevant to land-use hydrology in Australia. Changes in land use to achieve greater productivity of food and fibre may have an adverse effect on the water balance and hence on the natural resource capital of a catchment. An altered regime of catchment outflow accompanies those land-use changes which, together with land degradation, impairs available water resources in quantity and quality and threatens enterprise sustainability, notwithstanding the initial improvement in productivity. Central to any hydrological change is an altered pattern of seasonal and annual water use by vegetation that has become modified in function with an amended transpiration fraction of daily evapotranspiration. In Australia, since measurement of evapotranspiration became feasible, the hydrological consequences of changes in land use have been determined, allowing the benefits in terms of plant productivity achieved through enhanced water use efficiency to be weighed against changed catchment outflows, diminished in either quantity or quality. Four case studies are presented as examples of ecological and hydrological changes: two deal with the upland forest environment and two with arable lowlands. In an upland eucalypt forest, following wildfire with subsequent regeneration from natural seedling establishment, substantial reduction in water yield occurred throughout a 50-year period of succession in the even-aged stand. In comparison, the effect of converting eucalypt forest to pine plantations was less detrimental to the yield of water from the catchments, with substantial growth increases over 30 years. In the lowlands, agricultural productivity, both as annual pasture and as crop, far exceeds that of natural perennial grassland and woodland. This increase in productivity comes not so much from any change to the yield of total water outflow but at the expense of water quality, compromised with increased material transport in suspension and solution resulting from accelerated erosion in association with outbreaks of soil salinity and acidity. The present study is aimed at optimising management to give plant production outcomes that ensure environmental protection through resource conservation. In the uplands, harvesting of water is the dominant consideration so that conservative management with limited plant productivity is sought. In the lowlands, the objective is to devise novel ecosystems with profitable plant production that exercises due control on outflow in maintaining the chemical and physical integrity of the edaphic environment.

There is considerable uncertainty surrounding the future availability of hardwood timber from state-owned native forests in southern Queensland. The timber industry is becoming increasingly reliant on private native forests, where much is on properties primarily managed for beef cattle grazing. Historically, these forests have been periodically high-grade harvested without silvicultural treatment or cleared to increase pasture production where landholders have the right to do so. This study compares these traditional forest management practices at four case study properties against silvopastoral system alternatives. Merchantable timber, pasture and cattle production was estimated for each management scenario with a native forest silvicultural treatment response model. The net present value of each scenario was estimated over a 20-year management period. For all case study properties, the worst-performing forest management scenario was to clear forest for grazing. Investment in silvopastoral systems in southern Queensland was found to be financially attractive, particularly when silvicultural treatments were implemented in year zero to increase timber production. Silvicultural treatments increased the mean annual increment of merchantable timber over 20 years by an average of 1.3 m3/ha/year relative to the scenario where no management was performed in year zero. Forest management scenarios with silvicultural treatments had better financial performance than scenarios without silvicultural treatment. However, long payback periods and sovereign risk are serious impediments to silvopastoral system adoption in southern Queensland. If these concerns can be overcome, private native forests have the potential to be sustainably managed to improve the financial performance of farms, improve regional employment and income generation, supply Queensland’s future hardwood timber needs, and increase carbon sequestration and biodiversity conservation on private land.

Human interactions with rain-forest on the Australian continent have played, and will continue to play, a vital role in their distribution and survival. The presence and significance of rain-forest in Australia lies in the evolutionary history of the Australian plate since the break-up of the Gondwanan supercontinent. Its continued survival and distribution illustrates and encapsulates the history of plant evolution and biogeography in Australia.Since human arrival in Australia at least 40,000 years ago, human interactions with rain-forest have been marked by a number of phases — ranging from Aboriginal use of rain-forest resources to the impetus given by the hunt for the prized Red Cedar, and from the early European settlement on the east coast of Australia in the midto late-19th century to the wholesale clearing of rain forests for agricultural settlement and dairying in the late 19th century. In more modern times, human interactions with rain-forest have focused on adapting forest management techniques to rain-forest logging, restructuring the native forest timber industry in the face of mechanization, changing markets and resource constraints, convulsions as a result of conservationist challenges in Terania Creek and Daintree, and finally the implications of conserving rain-forests in the context of natural processes including fire, climate change, and the impact of human visitors and their recreation.The course of the controversies over rain-forest conservation in Australia has meant that rain-forest logging either has been dramatically curtailed or is in the process of generally ceasing. The protection of rainforests from logging and forestry operations in the future seems secure, given the widespread community support for rain-forest conservation. Threats to rain-forest conservation in the future are likely to be found in more subtle processes: the impact of fire regimes on the spread and contractions of rain-forests, the impacts of exotic species such as Lantana (Lantana camara) and Camphor Laurel (Cinnamomum camphora), the impacts of human uses through tourism and recreation, the diminution of the viability of isolated pockets by ‘edge effects’, and the damage to the remaining stands on freehold property by conflicting land-uses.Overlying all of these potential threats is the impact of global climate change. Climate change since the Tertiary has reduced the once widespread rain-forest communities of Australia practically to the status of relicts in refugia. Will the remaining rain-forests be able to withstand the projected human-induced climate changes of the future?

This research departs from concerns about an environmental crisis that encompasses deforestation, land-use change, habitat loss, land grabbing, water contamination, and soil degradation that we have faced. Meanwhile, the urgency of an Islamic response to fight those conditions should be more than simple actions like a religious lecture, Friday sermon, or green fatwa for around 1.9 billion Muslim communities around the world. Therefore, this study aims to critically analyze the Sharia contribution today to improve environmental protection by re-Islamization of forest and land law in modern ways, ultimately, to prevent the development and utilization of land and forest resources from continuing to fall into the vicious circle of the past. As an Islamic environmental law research, this study used a multidisciplinary approach, including historical approach, empirical approach, and conceptual approach; it also used a literature review method to synthesize research findings. This paper found that re-Islamized forests and land law could be an ongoing debate due to the differences of national and local legal characteristics that also depend on sharia position if it is an unequivocal discourse. Moreover, accommodating Sharia as an integral part of the state law shown a uniqueness and the flexibilities of Islamic doctrine and an affirmation of Muslim optimism to their faith of course a real contribution to involve in ecological right movement. On the other hand, considering the re-Islamization of forests and land law is an alternative source to enforce the ecological behaviours of the Muslim community to more pro-environment.

Can heritage be practiced and thought outside the binary of exaltation vs. denigration? To answer this question posed by the editors, this paper will analyse the destruction and protection of Indigenous heritage sites in Australia, where the destruction of significant cultural heritage sites, mainly Indigenous heritage sites, is the result of biased and outdated practice of cultural heritage that divides Indigenous heritage (prior 1788) from Australian heritage (after 1788). This rift has caused an immense damage to Indigenous heritage around the country as it shows how in Australia heritage is practiced and thought outside the dualism of celebration versus destruction. In this paper, I will show how the destruction of Indigenous rock art sites has been a constant in the 20th and 21st century and how this destruction has been framed in media as a result of vandalism. By arguing that this framing is perpetuating the dualism of celebration versus destruction, I suggest that we can move out of this binary by considering the concept of iconoclasm to go beyond this dualism.

Although forest devolution has become a key strategy of forestry reforms to mobilise local resources for sustainable forest management, there is growing concern about the legitimacy of this strategy. There have been escalating disputes between forestry agencies and local people as to who receives the rights to forests. Examining the policy of forest land allocation in Vietnam helps us to understand this legitimacy issue. Research findings from three case studies show trade-offs between the two policies’ goals, environmental protection and livelihood improvement, due to locals’ low awareness of the intrinsic values of forests and their lack of knowledge regarding the policy.

Despite growing work on the educational potential of digital media, literacy debates in Australia have remained locked in a banal opposition between serious educational aims and trivial entertainment media. To reinvigorate these debates, this article overviews progressive approaches to media literacy and case studies debates around the sexualisation of girls and young women in popular media. Ultimately, the authors — drawing on their submission to the recent Senate Inquiry on the subject — identify two ways to reset the media education and literacy agenda by incorporating a more productive engagement with digital media literacy.

Social Impact Assessment (SIA) is the process of analyzing, monitoring and managing the social effects of planned or implemented development interventions. The primary purpose of SIA is to bring about a sustainable and equitable biophysical and social environment. SIA is a prerequisite in FAO and World Bank aided projects which cover sectors of mining, agriculture, fishery, dams and transportation. In forestry it has the great potential of enhancing sustainable forest management, taking into account rural development objectives and local needs. SIA can be applied before and after the implementation of projects and programs. In the context of recent policy changes in China, the Natural Forest Protection Program (NFPP) has been implemented in a “top-down” process from 1998 to 2010. A large part of the forests on main river basins in Western regions are being conserved with severe restrictions for commercial use. The social effects of the NFPP are still debatable, indicating a need for conducting a SIA of the NFPP using a systematic conceptual approach. Objectives of the research are: (1) To understand how and to what extent the NFPP affected the local forest-dependent communities and their households; (2) To identify the local strategies currently used to cope up with the impacts; and (3) To develop the optimal strategies likely supported for a better harmonization between livelihood and the NFPP implementation in different regional contexts. The empirical research is approached through quantitative and qualitative social research methods for data collection and analysis. For the case studies, four villages with a total number of 175 respondents were selected for field surveys where questionnaires, interviews and group discussions were employed. The research findings indicate that, the NFPP has significant impacts on the population characteristics, institutional arrangements and infrastructure and public services at the community level and at household level, the income derivation, expenditure, labour time distribution, perceptions on public health/safety and changing values of forests perceived by individuals. The research reveals that, synthesizing de facto impacts of the NFPP makes potential negative social impacts predictable. The policy-makers and project teams implementing the NFPP should be aware that, the NFPP results in dynamic change processes which include the de facto and potential impacts as well as the influence factors; among these, contribution of strategies derived from local communities and households as the spontaneous reactions to cope with the NFPP impacts should be taken into consideration. Recommendations are given referring to a better implementation of the NFPP and the need for future researches concerning the SIA for sustainable forest management in different regional contexts
Social Impact Assessment (SIA) ist ein Prozess, der Analyse, Monitoring und Bewältigung der sozialen Effekte geplanter oder durchgeführter Entwicklungsinterventionen umfasst. Das Hauptanliegen von SIA ist, eine nachhaltige und gerechte biophysische und soziale Umwelt zu schaffen. SIA ist für Projekte der FAO und der Weltbank in den Sektoren Bergbau, Landwirtschaft, Fischerei, Talsperren und Transport eine Grundvoraussetzung. Für die Forstwirtschaft ergibt sich daraus das Potenzial, nachhaltige Waldbewirtschaftung zu stärken und dabei die Ziele ländlicher Entwicklung und lokale Erfordernisse zu berücksichtigen. SIA kann vor und nach der Durchführung von Projekten und Programmen angewendet werden. Im Zusammenhang mit den aktuellen politischen Veränderungen in China wird das Natural Forest Protection Program (NFPP) im Zeitraum von 1998-2010 nach dem top-down-Verfahren durchgeführt. Die sozialen Auswirkungen des NFPP sind noch immer umstritten. Das unterstreicht die Notwendigkeit der SIA unter Anwendung einer systematischen konzeptionellen Herangehensweise. Ein besonders kritischer Faktor dabei ist, dass ein erheblicher Anteil der Wälder in den Wassereinzugsgebieten wichtiger Flussläufe in den westlichen Regionen durch strikte Einschränkungen der kommerziellen Nutzung geschützt wurden. Die Ziele der Forschung sind: (1) Aufzeigen wie und in welchem Ausmaß das NFPP die örtlichen waldabhängigen Gemeinden und ihre Haushalte beeinflusst hat; (2) Identifizieren lokal entwickelter und angewandter Strategien, um die Auswirkungen des NFPP zu bewältigen; und (3) Entwickeln optimaler Strategien für eine bessere Harmonisierung der Lebensgrundlagen mit der Umsetzung des NFPP in unterschiedlichen regionalen Kontexten. Die empirische soziale Forschung bedient sich quantitativer und qualitativer Methoden zur Datensammlung und Datenanalyse. Für die Fallstudie wurden vier Dörfer mit insgesamt 175 Befragten ausgewählt. Bei der Primärdatenerhebung kamen Fragebögen, Interviews und Gruppendiskussionen zur Anwendung. Die Forschungsergebnisse zeigen, dass das NFPP signifikanten Einfluss ausübt auf Größe und Anteil armer Bevölkerung, auf institutionelle Rahmenbedingungen, die Infrastruktur und den öffentlichen Dienstleistungssektor auf Gemeindeebene. Auf Haushaltsebene wurde signifikanter einfluss nachgewiesen für die Generierung von Einkommen, die Ausgaben, die Arbeitszeitverteilung, die Vorstellungen über Gesundheitswesen und Sicherheit als auch auf die Wahrnehmung der sich verändernden Werte des Waldes. Es wird ersichtlich, dass durch Zusammenführen der de facto-Auswirkungen des NFPP potenzielle negative soziale Einflüsse vorhersagbar werden. Entscheidungsträger und Projektteams sollten sich darüber bewusst werden, dass das NFPP zu dynamischen Veränderungsprozessen führt, welche die de facto- und potentiellen Auswirkungen sowie die Einflussfaktoren betreffen. Dies schließt den Beitrag der lokal entwickelten Strategien ein. Empfehlungen betreffen die bessere Umsetzung des NFPP sowie die Notwendigkeit weiterer Forschung hinsichtlich der SIA im Zusammenhang nachhaltiger Waldbewirtschaftung in verschiedenen regionalen Kontexten

La conservation du couvert forestier tropical est essentielle pour assurer la fourniture durable de services écosystémiques. Dans les paysages anthropisés, la conservation des forêts doit également être conciliée avec la productivité agricole. Toutefois, l'accroissement de la démographie, la demande de produits agricoles et les changements dans l'utilisation des terres affectent la durabilité des forêts. Une première étape pour adapter la gestion efficace des forêts par les décideurs locaux consiste à identifier les forêts les plus vulnérables et à caractériser ce qui la génère. L'objectif de cette thèse est de développer une approche multidimensionnelle utilisant la télédétection pour évaluer la dégradation des forêts et les relations avec la dynamique de l'utilisation des terres afin d’estimer la vulnérabilité écologique des forêts. La thèse a été appliquée à Paragominas (Brésil) et Di Linh (Vietnam), où la déforestation à grande échelle due à l'agriculture commerciale a façonné le paysage en mosaïques d'utilisation des terres. A Paragominas, la dégradation est liée à l'accumulation de l’exploitation sélective du bois et au feu impliquant des changements dans la structure forestière. Nous avons estimé le potentiel de la télédétection multisource pour cartographier la biomasse forestière aérienne (AGB) à partir de données de stock de carbone. Nous avons amélioré la précision de la cartographie de l'AGB par rapport aux données pantropicales et révélé que 87 % des forêts étaient dégradées. À une plus petite échelle, nous avons étudié les conséquences de 33 ans de dégradation sur les structures forestières à l'aide de drone. Nous avons constaté que les textures de la canopée capturaient le grain, l'hétérogénéité et les gradients d'ouverture de la canopée, corrélés à la variabilité de la structure forestière et pouvaient être utilisés comme indicateurs pour caractériser les forêts dégradées. Nous avons également évalué le potentiel des images satellites à très haute résolution pour cartographier les structures des forêts dégradées à l'échelle de la municipalité. En nous basant sur des facteurs environnementaux, géographiques et de structure du paysage dérivés de la classification de l'utilisation des terres, nous avons démontré que 80 % de la dégradation des forêts était principalement due à l'accessibilité, la géomorphologie, la fréquence des incendies et à la fragmentation. Les facteurs de dégradation sont interconnectés et agissent en séquence au sein de différentes cascades d'effets. L'évolution de la structure du paysage a permis de reconstituer des trajectoires informant sur la dynamique des frontières agricoles. La combinaison de l'état actuel des forêts, de la dynamique du paysage et de la distribution des facteurs de dégradation permettra d’évaluation la vulnérabilité. A Di Linh, la dégradation concerne principalement les lisières forestières et est due à l'empiètement de l'agriculture (café). L'inventaire sur le terrain des différents types de forêts et d'autres éléments, combiné aux images Sentinel-2, a permis de cartographier avec une grande précision la couverture terrestre actuelle. Nous avons cartographié l'évolution de la couverture terrestre sur 45 ans à l'aide de séries chronologiques Landsat. Nous avons construit des trajectoires de dynamique paysagère afin de caractériser l'expansion de la frontière agricole et mis en évidence l'empiétement agricole sur les zones forestières. Nous avons également identifié des trajectoires de dégradation et de fragmentation qui affectent le couvert forestier à différentes intensités. Ensemble, ces indicateurs ont mis en évidence des points chauds de vulnérabilité. Grâce aux approches et aux indicateurs élaborés à multiples échelles, nous avons fourni un diagnostic holistique des forêts dans les paysages anthropisés, englobant l'état des forêts et des dynamiques à plus larges échelles. Cette thèse vise à orienter une gestion adaptée des forêts dégradées à l'échelle du paysage
The conservation of tropical forest cover is a key to ensuring sustainable provision of multiple ecosystem services. In human-modified landscapes, forest conservation must also be reconciled with agricultural productivity. However, increasing demography, demand for agricultural products and changes in land uses are affecting forest sustainability through degradation processes. A first step to tailor effective forest management by local decision makers is to identify most vulnerable forests and to characterize what is driving this vulnerability. The objective of this thesis is to develop a multidimensional approach using remote sensing to assess forest degradation and the relations with the broader dynamics of land use/cover towards the evaluation of forest ecological vulnerability. The thesis was applied in old-deforestation fronts of Paragominas (Brazil) and Di Linh (Vietnam) where large-scale deforestation driven by commercial agriculture shaped the landscape into land use mosaics with increasing degradation pressures. In Paragominas, degradation is linked with long-term accumulation of selective logging and fire implying changes in forest structure. We estimated the potential of multisource remote sensing to map forest aboveground biomass (AGB) from large-scale field assessment of carbon stock. We improved the accuracy of AGB mapping compared to pantropical datasets and revealed that 87% of forest was degraded. At a lower scale, we investigated the consequences of 33 years of degradation history from Landsat on forest structures using Unmanned Aerial Vehicle. We found that canopy textures captured canopy grain, heterogeneity and openness gradients, correlated with forest structure variability and could be used as proxies to characterize degraded forests. We also assessed the potential of very high resolution satellite images and derived canopy textures to upscale texture-structure relations at the municipality scale. Based on environmental, geographical factors and landscape structure metrics derived from land use/cover classification, we demonstrated that 80% of forest degradation was mainly driven by accessibility, geomorphology, fire occurrence and fragmentation. The drivers of degradation acted together and in sequence and clustering analysis disentangled different cascades of effects. Changes in landscape structure allowed reconstructing trajectories informing on agricultural frontier dynamics. The combination of current forest state, landscape dynamics and distribution of degradation drivers would be at the basis of ecological vulnerability assessment. In Di Linh, degradation mostly concerns forest edges and is driven by encroachment of coffee-based agriculture. Field inventory of the different forest types and other landscape elements combined with Sentinel-2 images allowed to map with high precision the current land cover. We then mapped land cover changes over 45 years using Landsat time series. We constructed trajectories of landscape structure dynamics from which we characterized the expansion of the agricultural frontier and highlighted heterogeneous agricultural encroachment on forested areas. We also identified degradation and fragmentation trajectories that affect forest cover at different rates and intensity. Combined, these indicators pinpointed hotspots of forest ecological vulnerability. Most vulnerable forest areas were experiencing rapid and recent forest cover loss associated with landscape fragmentation, land use competition due to coffee production and degradation. Through the developed remote sensing approaches and indicators at forest and landscape scales, we provided a holistic diagnosis of forests in human-modified landscapes encompassing forest state and broader dynamics and drivers. This thesis aims to pave the way for tailored and prioritized management of degraded forests at the landscape scale

Bibliography: leaves 135-143. An anthropological analysis of an industrial dispute that occurred within the East Gippsland forest industry, 1997-1998 and how the workers strove to acheive better working conditions for themselves, and to share in the wealth they had created.

Social Impact Assessment (SIA) is the process of analyzing, monitoring and managing the social effects of planned or implemented development interventions. The primary purpose of SIA is to bring about a sustainable and equitable biophysical and social environment. SIA is a prerequisite in FAO and World Bank aided projects which cover sectors of mining, agriculture, fishery, dams and transportation. In forestry it has the great potential of enhancing sustainable forest management, taking into account rural development objectives and local needs. SIA can be applied before and after the implementation of projects and programs. In the context of recent policy changes in China, the Natural Forest Protection Program (NFPP) has been implemented in a “top-down” process from 1998 to 2010. A large part of the forests on main river basins in Western regions are being conserved with severe restrictions for commercial use. The social effects of the NFPP are still debatable, indicating a need for conducting a SIA of the NFPP using a systematic conceptual approach. Objectives of the research are: (1) To understand how and to what extent the NFPP affected the local forest-dependent communities and their households; (2) To identify the local strategies currently used to cope up with the impacts; and (3) To develop the optimal strategies likely supported for a better harmonization between livelihood and the NFPP implementation in different regional contexts. The empirical research is approached through quantitative and qualitative social research methods for data collection and analysis. For the case studies, four villages with a total number of 175 respondents were selected for field surveys where questionnaires, interviews and group discussions were employed. The research findings indicate that, the NFPP has significant impacts on the population characteristics, institutional arrangements and infrastructure and public services at the community level and at household level, the income derivation, expenditure, labour time distribution, perceptions on public health/safety and changing values of forests perceived by individuals. The research reveals that, synthesizing de facto impacts of the NFPP makes potential negative social impacts predictable. The policy-makers and project teams implementing the NFPP should be aware that, the NFPP results in dynamic change processes which include the de facto and potential impacts as well as the influence factors; among these, contribution of strategies derived from local communities and households as the spontaneous reactions to cope with the NFPP impacts should be taken into consideration. Recommendations are given referring to a better implementation of the NFPP and the need for future researches concerning the SIA for sustainable forest management in different regional contexts.:TABLE OF CONTENT ACKNOWLEDGEMENTS ..................................................................................................... i LIST OF FIGURES ................................................................................................................ vi LIST OF TABLES ................................................................................................................ viii LIST OF BOXES .................................................................................................................... ix LIST OF ACRONYMS ............................................................................................................ x ABSTRACT ........................................................................................................................... xii ZUSAMMENFASSUNG ..................................................................................................... xiii 1 INTRODUCTION ........................................................................................................ xiii 1.1 Background .................................................................................................................. 1 1.2 Problem statement and justification ............................................................................. 5 1.3 Research objectives ...................................................................................................... 6 1.3.1 General research objectives .................................................................................. 6 1.3.2 Specific research objectives .................................................................................. 7 1.4 Structure of the dissertation ......................................................................................... 8 2 CURRENT STATE OF KNOWLEDGE AND INFORMATION ............................... 10 2.1 General remark .......................................................................................................... 10 2.2 Forestry reforms in China .......................................................................................... 10 2.2.1 China‘s forestry sector since the economic reform in 1978 ................................ 10 2.2.2 Forest tenure and administration ......................................................................... 13 2.2.3 Chronology of sectional reforms in China and their consequences .................... 14 2.2.4 Policy reforms in the forestry sector ................................................................... 18 2.3 The Natural Forest Protection Program ..................................................................... 21 2.3.1 Background and objective .................................................................................. 21 2.3.2 Scale and main contents ...................................................................................... 21 2.3.3 Implementation process ...................................................................................... 22 2.3.4 Budget ................................................................................................................. 23 2.3.5 Legal basis .......................................................................................................... 23 2.3.6 Current implementation status and main achievements ..................................... 23 2.3.7 Various impacts of the NFPP derived from previous researches ........................ 23 2.4 Social Impact Assessment as a development tool ...................................................... 25 2.4.1 Concepts of Social Impact Assessment .............................................................. 25 2.4.2 A brief history of Social Impact Assessment ...................................................... 27 2.4.3 Principles and guidelines for Social Impact Assessment .................................... 29 2.4.4 Basic model of Social Impact Assessment ......................................................... 29 2.4.5 Process of Social Impact Assessment ................................................................. 31 2.4.6 SIA case study examples and matrix of common social indicators .................... 31 3 CONCEPTUAL FRAMEWORK AND THEORETICAL PERSPECTIVES ........... 38 3.1 General remark .......................................................................................................... 38 3.2 Basic settings in the ―Function evaluation‖ approach ............................................... 40 3.3 Integration framework: indirect and direct human impacts ....................................... 42 3.4 Conceptual framework of SIA: focusing on changes in social setting ...................... 46 3.5 Human ecosystem as an organizing concept for SIA ................................................ 47 3.5.1 Concept of human ecology and human ecosystem models ................................ 47 3.5.2 Systems model of human ecology ...................................................................... 48 3.5.3 Concept model of human ecosystems ................................................................. 50 3.5.4 Learning from the two conceptual models of human ecosystem ........................ 51 3.5.5 A local forest-dependent community as a small scale human ecosystem ........... 53 3.6 Framework conceptualizing social impacts in the empirical context ........................ 55 3.7 Research questions ..................................................................................................... 57 4 RESEARCH METHDOLOGY ..................................................................................... 60 4.1 Defining and operationalizing the research indicators .............................................. 60 4.1.1 Foundation of the definition ............................................................................... 60 4.1.2 Defining and operationalizing the selected research indicators .......................... 62 4.2 Selection of case study areas ..................................................................................... 68 4.3 Methods for quantitative and qualitative data collection ........................................... 71 4.3.1 Introduction ......................................................................................................... 71 4.3.2 Field reconnaissance survey ............................................................................... 71 4.3.3 Secondary data collection ................................................................................... 71 4.3.4 Primary data collection ....................................................................................... 72 4.4 Data processing and analysis ..................................................................................... 75 4.5 Research procedure .................................................................................................... 76 4.6 Discussion on the attribution gap ............................................................................... 76 4.7 Reliability and validity of the field research process ................................................. 76 5 SCOPING AND OBSERVATION OF THE STUDY AREAS ..................................... 79 5.1 General remark .......................................................................................................... 79 5.2 Case study area 1: Gansu Xiaolongshan state-owned forest area .............................. 79 5.2.1 General information of Gansu Province ............................................................. 79 5.2.2 Profile of Xiaolongshan state-owned forest area ................................................ 81 5.2.3 Profiles of the villages investigated .................................................................... 84 5.2.4 Characteristics of household respondents in the two villages ............................ 86 5.3 Case Study Area 2: Chongqing collective-owned forest area .................................... 87 5.3.1 General information of Chongqing Municipality ............................................... 87 5.3.2 Information on Dazu County and its collective forest area ................................ 90 5.3.3 Profiles of the villages investigated .................................................................... 92 5.3.4 Characteristics of household respondents in the two villages ............................ 93 6 ASSESSMENT OF SOCIAL IMPACTS AND CAUSAL ANALYSIS ....................... 96 6.1 Social impacts on the local community level ............................................................ 96 6.1.1 Change in the community population characteristics ......................................... 96 6.1.2 Change in the community institutional arrangements ........................................ 99 6.1.3 Change in the community infrastructure and public services ........................... 111 6.2 Social impacts on the household level ..................................................................... 118 6.2.1 Impacts on households and families ................................................................. 118 6.2.2 Impacts on individuals ...................................................................................... 131 7 DIAGNOSIS: COMPARATIVE ANALYSIS AND DISCUSSION .......................... 145 7.1 General remark ........................................................................................................ 145 7.2 The de facto impacts of the NFPP on local communities and households .............. 145 7.2.1 The social change processes in the local community ....................................... 145 7.2.2 Human impacts on the local households ........................................................... 149 7.3 External and internal factors influencing the extent of impact results..................... 152 7.3.1 Introduction ....................................................................................................... 152 7.3.2 The external factors at community level ........................................................... 152 7.3.3 The internal factors at household and individual level ..................................... 154 7.4 Potential impacts of the NFPP on the local community and households................. 154 7.5 Dynamics of de facto and potential impacts, local strategies and influence factors 155 8 CONCLUSION AND RECOMMENDATIONS ........................................................ 157 8.1 General remarks ....................................................................................................... 157 8.2 Recapitulation of major findings and conclusions ................................................... 157 8.3 Scope and limitations of the empirical study ........................................................... 158 8.4 Recommendation for future policy implementation ................................................ 160 8.5 Relationship between theory and findings ............................................................... 163 8.6 A critical review of methodology and implications for SIA research ...................... 165 REFERENCES ..................................................................................................................... 168 APPENDICES ...................................................................................................................... 179 Appendix 1: Some data and background information available in literature ..................... 180 Appendix 2: Supplementary material and material information used in research ............. 195 Appendix 3: Questionnaires used in the field surveys ....................................................... 203 Appendix 4: Part of the data collected in the field ............................................................. 212 Appendix 5: Photos in the fields ........................................................................................ 234
Social Impact Assessment (SIA) ist ein Prozess, der Analyse, Monitoring und Bewältigung der sozialen Effekte geplanter oder durchgeführter Entwicklungsinterventionen umfasst. Das Hauptanliegen von SIA ist, eine nachhaltige und gerechte biophysische und soziale Umwelt zu schaffen. SIA ist für Projekte der FAO und der Weltbank in den Sektoren Bergbau, Landwirtschaft, Fischerei, Talsperren und Transport eine Grundvoraussetzung. Für die Forstwirtschaft ergibt sich daraus das Potenzial, nachhaltige Waldbewirtschaftung zu stärken und dabei die Ziele ländlicher Entwicklung und lokale Erfordernisse zu berücksichtigen. SIA kann vor und nach der Durchführung von Projekten und Programmen angewendet werden. Im Zusammenhang mit den aktuellen politischen Veränderungen in China wird das Natural Forest Protection Program (NFPP) im Zeitraum von 1998-2010 nach dem top-down-Verfahren durchgeführt. Die sozialen Auswirkungen des NFPP sind noch immer umstritten. Das unterstreicht die Notwendigkeit der SIA unter Anwendung einer systematischen konzeptionellen Herangehensweise. Ein besonders kritischer Faktor dabei ist, dass ein erheblicher Anteil der Wälder in den Wassereinzugsgebieten wichtiger Flussläufe in den westlichen Regionen durch strikte Einschränkungen der kommerziellen Nutzung geschützt wurden. Die Ziele der Forschung sind: (1) Aufzeigen wie und in welchem Ausmaß das NFPP die örtlichen waldabhängigen Gemeinden und ihre Haushalte beeinflusst hat; (2) Identifizieren lokal entwickelter und angewandter Strategien, um die Auswirkungen des NFPP zu bewältigen; und (3) Entwickeln optimaler Strategien für eine bessere Harmonisierung der Lebensgrundlagen mit der Umsetzung des NFPP in unterschiedlichen regionalen Kontexten. Die empirische soziale Forschung bedient sich quantitativer und qualitativer Methoden zur Datensammlung und Datenanalyse. Für die Fallstudie wurden vier Dörfer mit insgesamt 175 Befragten ausgewählt. Bei der Primärdatenerhebung kamen Fragebögen, Interviews und Gruppendiskussionen zur Anwendung. Die Forschungsergebnisse zeigen, dass das NFPP signifikanten Einfluss ausübt auf Größe und Anteil armer Bevölkerung, auf institutionelle Rahmenbedingungen, die Infrastruktur und den öffentlichen Dienstleistungssektor auf Gemeindeebene. Auf Haushaltsebene wurde signifikanter einfluss nachgewiesen für die Generierung von Einkommen, die Ausgaben, die Arbeitszeitverteilung, die Vorstellungen über Gesundheitswesen und Sicherheit als auch auf die Wahrnehmung der sich verändernden Werte des Waldes. Es wird ersichtlich, dass durch Zusammenführen der de facto-Auswirkungen des NFPP potenzielle negative soziale Einflüsse vorhersagbar werden. Entscheidungsträger und Projektteams sollten sich darüber bewusst werden, dass das NFPP zu dynamischen Veränderungsprozessen führt, welche die de facto- und potentiellen Auswirkungen sowie die Einflussfaktoren betreffen. Dies schließt den Beitrag der lokal entwickelten Strategien ein. Empfehlungen betreffen die bessere Umsetzung des NFPP sowie die Notwendigkeit weiterer Forschung hinsichtlich der SIA im Zusammenhang nachhaltiger Waldbewirtschaftung in verschiedenen regionalen Kontexten.:TABLE OF CONTENT ACKNOWLEDGEMENTS ..................................................................................................... i LIST OF FIGURES ................................................................................................................ vi LIST OF TABLES ................................................................................................................ viii LIST OF BOXES .................................................................................................................... ix LIST OF ACRONYMS ............................................................................................................ x ABSTRACT ........................................................................................................................... xii ZUSAMMENFASSUNG ..................................................................................................... xiii 1 INTRODUCTION ........................................................................................................ xiii 1.1 Background .................................................................................................................. 1 1.2 Problem statement and justification ............................................................................. 5 1.3 Research objectives ...................................................................................................... 6 1.3.1 General research objectives .................................................................................. 6 1.3.2 Specific research objectives .................................................................................. 7 1.4 Structure of the dissertation ......................................................................................... 8 2 CURRENT STATE OF KNOWLEDGE AND INFORMATION ............................... 10 2.1 General remark .......................................................................................................... 10 2.2 Forestry reforms in China .......................................................................................... 10 2.2.1 China‘s forestry sector since the economic reform in 1978 ................................ 10 2.2.2 Forest tenure and administration ......................................................................... 13 2.2.3 Chronology of sectional reforms in China and their consequences .................... 14 2.2.4 Policy reforms in the forestry sector ................................................................... 18 2.3 The Natural Forest Protection Program ..................................................................... 21 2.3.1 Background and objective .................................................................................. 21 2.3.2 Scale and main contents ...................................................................................... 21 2.3.3 Implementation process ...................................................................................... 22 2.3.4 Budget ................................................................................................................. 23 2.3.5 Legal basis .......................................................................................................... 23 2.3.6 Current implementation status and main achievements ..................................... 23 2.3.7 Various impacts of the NFPP derived from previous researches ........................ 23 2.4 Social Impact Assessment as a development tool ...................................................... 25 2.4.1 Concepts of Social Impact Assessment .............................................................. 25 2.4.2 A brief history of Social Impact Assessment ...................................................... 27 2.4.3 Principles and guidelines for Social Impact Assessment .................................... 29 2.4.4 Basic model of Social Impact Assessment ......................................................... 29 2.4.5 Process of Social Impact Assessment ................................................................. 31 2.4.6 SIA case study examples and matrix of common social indicators .................... 31 3 CONCEPTUAL FRAMEWORK AND THEORETICAL PERSPECTIVES ........... 38 3.1 General remark .......................................................................................................... 38 3.2 Basic settings in the ―Function evaluation‖ approach ............................................... 40 3.3 Integration framework: indirect and direct human impacts ....................................... 42 3.4 Conceptual framework of SIA: focusing on changes in social setting ...................... 46 3.5 Human ecosystem as an organizing concept for SIA ................................................ 47 3.5.1 Concept of human ecology and human ecosystem models ................................ 47 3.5.2 Systems model of human ecology ...................................................................... 48 3.5.3 Concept model of human ecosystems ................................................................. 50 3.5.4 Learning from the two conceptual models of human ecosystem ........................ 51 3.5.5 A local forest-dependent community as a small scale human ecosystem ........... 53 3.6 Framework conceptualizing social impacts in the empirical context ........................ 55 3.7 Research questions ..................................................................................................... 57 4 RESEARCH METHDOLOGY ..................................................................................... 60 4.1 Defining and operationalizing the research indicators .............................................. 60 4.1.1 Foundation of the definition ............................................................................... 60 4.1.2 Defining and operationalizing the selected research indicators .......................... 62 4.2 Selection of case study areas ..................................................................................... 68 4.3 Methods for quantitative and qualitative data collection ........................................... 71 4.3.1 Introduction ......................................................................................................... 71 4.3.2 Field reconnaissance survey ............................................................................... 71 4.3.3 Secondary data collection ................................................................................... 71 4.3.4 Primary data collection ....................................................................................... 72 4.4 Data processing and analysis ..................................................................................... 75 4.5 Research procedure .................................................................................................... 76 4.6 Discussion on the attribution gap ............................................................................... 76 4.7 Reliability and validity of the field research process ................................................. 76 5 SCOPING AND OBSERVATION OF THE STUDY AREAS ..................................... 79 5.1 General remark .......................................................................................................... 79 5.2 Case study area 1: Gansu Xiaolongshan state-owned forest area .............................. 79 5.2.1 General information of Gansu Province ............................................................. 79 5.2.2 Profile of Xiaolongshan state-owned forest area ................................................ 81 5.2.3 Profiles of the villages investigated .................................................................... 84 5.2.4 Characteristics of household respondents in the two villages ............................ 86 5.3 Case Study Area 2: Chongqing collective-owned forest area .................................... 87 5.3.1 General information of Chongqing Municipality ............................................... 87 5.3.2 Information on Dazu County and its collective forest area ................................ 90 5.3.3 Profiles of the villages investigated .................................................................... 92 5.3.4 Characteristics of household respondents in the two villages ............................ 93 6 ASSESSMENT OF SOCIAL IMPACTS AND CAUSAL ANALYSIS ....................... 96 6.1 Social impacts on the local community level ............................................................ 96 6.1.1 Change in the community population characteristics ......................................... 96 6.1.2 Change in the community institutional arrangements ........................................ 99 6.1.3 Change in the community infrastructure and public services ........................... 111 6.2 Social impacts on the household level ..................................................................... 118 6.2.1 Impacts on households and families ................................................................. 118 6.2.2 Impacts on individuals ...................................................................................... 131 7 DIAGNOSIS: COMPARATIVE ANALYSIS AND DISCUSSION .......................... 145 7.1 General remark ........................................................................................................ 145 7.2 The de facto impacts of the NFPP on local communities and households .............. 145 7.2.1 The social change processes in the local community ....................................... 145 7.2.2 Human impacts on the local households ........................................................... 149 7.3 External and internal factors influencing the extent of impact results..................... 152 7.3.1 Introduction ....................................................................................................... 152 7.3.2 The external factors at community level ........................................................... 152 7.3.3 The internal factors at household and individual level ..................................... 154 7.4 Potential impacts of the NFPP on the local community and households................. 154 7.5 Dynamics of de facto and potential impacts, local strategies and influence factors 155 8 CONCLUSION AND RECOMMENDATIONS ........................................................ 157 8.1 General remarks ....................................................................................................... 157 8.2 Recapitulation of major findings and conclusions ................................................... 157 8.3 Scope and limitations of the empirical study ........................................................... 158 8.4 Recommendation for future policy implementation ................................................ 160 8.5 Relationship between theory and findings ............................................................... 163 8.6 A critical review of methodology and implications for SIA research ...................... 165 REFERENCES ..................................................................................................................... 168 APPENDICES ...................................................................................................................... 179 Appendix 1: Some data and background information available in literature ..................... 180 Appendix 2: Supplementary material and material information used in research ............. 195 Appendix 3: Questionnaires used in the field surveys ....................................................... 203 Appendix 4: Part of the data collected in the field ............................................................. 212 Appendix 5: Photos in the fields ........................................................................................ 234

This chapter explores how two middle powers, Sweden and Australia, deploy the politics of protection in different ways. Sweden’s efforts to remake the state is viewed through a gender lens as part of efforts to disentangle its former neutral profile through more robust military applications, whilst embodying a peaceful self-narrative linked to military non-alignment, active internationalism and a ‘feminist foreign policy’. The second case explores efforts to reclaim a bounded concept of the sovereign state in Australia's masculinist and militarized approach to securing its borders with respect to asylum seekers. Australia seeks to reclaim a more traditional imagining of the state, or a return to ‘restoring’ state sovereignty perceived to be under threat by globalising forces. Both case studies explore the inherently gendered and securitized reworking and revisioning of the state, and the tensions and contradictions that emerge in questions of security, sovereignty and identity.

‘Smart infrastructure’, such as smart meters, are innovative, information-based energy technologies designed to promote systemic energy efficiency, cost savings, and to transition energy markets toward sustainable outcomes, including reducing climate change impacts. Smart meters promise innovation in electricity markets–as an enabler of demand-side services and a more distributed energy system. The chapter examines three case studies of legal reform for smart meter introduction in Australia and Germany. It concludes that the realization of the innovation promise of smart infrastructure requires the legal system to address consumer-oriented social and economic changes. While legal responses are growing in sophistication, significant questions around consumer protection remain, although Germany emphasizes consumer privacy more than Australian case studies. Finally, Germany most closely links innovation to climate change and electricity system transitions, whereas, increasingly, Australian policies emphasize the consumer benefits and innovation in the business models for electricity distribution.

Australia is quintessentially a maritime nation where sea travel and transportation have been vitally important. Despite being an island, Australia hasd never completely felt isolated, and the indigenous peoples were never cut off from the rest of the world. This article presents four case studies in order to provide insights into the types and extent of maritime archaeological research that has been conducted over more than three decades in Australia. One of the great influences of Australian maritime archaeology over the years has been the Australasian Institute for Maritime Archaeology. A drawback in Australian maritime archaeology is the lack of funding for academic research. Australia has developed legislation for the protection of the historic shipwreck component of its underwater cultural heritage.

We are currently facing significant challenges in environmental management that must be addressed to maintain the health of our planet and our population. While carbon offsetting in its various forms is widespread globally, few countries have fully legislated and put into operation other offset policies. This edited collection aims to fill the gap of knowledge on environmental offsets, from theory to practice. Environmental Offsets addresses four major forms of environmental offsets – biodiversity offsets, carbon offsets, offsetting the depletion of non-renewable resources and offsetting the destruction of built heritage. The authors discuss their research and provide case studies from around Australia and across the developing world. Using examples such as the Sydney Olympics, the Bakossi Forest Reserve in Cameroon and green roof gardens, this book highlights the strengths and weaknesses of environmental offsetting and illustrates how jobs can be created in the offsetting process. Environmental Offsets is both a historical source in our understanding of environmental offsetting and a guide to the way forward. It illustrates what works, what does not and what can be improved for the future.

Both desertification and forest policies address environmental issues related to land. However, the types of land covered and the ways the issues associated with that land are conceptualized represent opposite ends of a spectrum, with the former policy area focusing on land degradation in areas with limited biodiversity and the latter relating to protection of lands comprising some of the most biologically diverse areas in the world. Moreover, despite their common denominator as issues related to land, the international studies literatures on desertification and forests, like the international policy responses to them, have taken different paths. A number of United Nations (UN)-backed research efforts have sought to define the concept, assess the impacts, and identify possible actions to address the desertification phenomenon. International studies scholarship has also focused on transformations in international policy approaches to deserts, such as the implementation of certain plans of action. Forests, meanwhile, have received renewed attention at the international policy-making level, due to the fact that even though forests themselves fall within the jurisdiction of sovereign states. Historically, deforestation the world over has been associated with conversion of land for agriculture and human settlement. In recent decades, this has been particularly the case in developing countries, though recent deforestation trends have also been traced back to the current global economic system that encourages privatization of forestland.

This chapter highlights the influence of mountain forests on runoff patterns in alpine catchments. We discuss the forest impact at different spatial scales and bridge to the requirements for an integrated natural hazard risk management, which considers forest as an efficient protection measure against floods and other water-related natural hazards. We present results from a wide range of research studies from Austria, which all reveal the runoff-reducing effect of forest vegetation in small and medium-size catchments (< 100 km2). Forests also contribute to runoff reduction in heavy rainfall events in macro-scale catchments (> 100 km2), e.g., by reducing surface runoff and delaying interflow, but above all by stabilising slopes and therefore reducing bedload transport during major runoff events. To avoid that forests become a hazard due to enhanced driftwood release, managing of steep riparian slopes for a permanent forest cover (“Dauerbestockung”) is a basic prerequisite. Often protective effects of forests are impaired by man-made impacts like dense forest road networks, insensitive use (e.g., false design of skid roads, compacting machinery, forest operations during adverse weather on wet and saturated soils), and delayed or omitted reforestation and regeneration. Flood risk management in mountain regions should include Ecosystem-based Disaster Risk Reduction measures, with particular emphasis on sustainable and climate change-adapted management of protective forests. This will require integral and catchment-based approaches such as comprehensive management concepts coordinated with spatial planning, and verifiable, practicable and correspondingly adapted legal guidelines as well as appropriate funding of protective forest research to close the existing knowledge gaps.

Academics and University Extension personnel have experience with soil mapping and providing soil suitability interpretations; however, a more efficient information conveyance to land custodians is desired to support informative land management applications. In the USA each state, in concert with the United States Department of Agriculture, has embarked on developing an online format linking soil survey with ecological site descriptions to provide information for forest and rangeland management to encourage soil protection - health and optimizing ecological services on individual land parcels. In this Missouri-based manuscript, we discuss three cases where soils and their associated ecological site descriptions provide land custodians information concerning their logical reference state vegetation community and detail land management decisions that transform the reference vegetation community to a different vegetation community. With each case, landscapes and their associated vegetations communities are potentially partitioned by soil, physiography, hydrology, and other attributes.

This chapter provides a twenty-year retrospective on non-traditional trademarks, using the European Union, the United Kingdom, Singapore, Japan, and Australia as case studies. It presents findings from an empirical study on the application and registration of non-traditional marks in these jurisdictions from 1996 to present day. It assesses whether the appetite for non-traditional marks differs across jurisdictions and what impact, if any, differing regulatory regimes have on filing and registration activity. The study also canvasses the micro-trends emerging from these data in order to test prevailing assumptions about non-traditional marks. The policy implications of these findings will also be touched upon and contextualized against growing concerns about trademark depletion, which have to date focused on the diminishing number of available words and colors as trademarks, but may well extend to non-traditional marks more generally.

Protection forests can be severely affected by natural disturbances, whose consequences could greatly alter the fundamental ecosystem services they are providing. Assessing and monitoring the status of the protective effects, particularly within disturbed stands, is therefore of vital importance, with timing being a critical issue. Remote sensing technologies (e.g., satellite imagery, LiDAR, UAV) are widely available nowadays and can be effectively applied to quantify and monitor the protective effects of Alpine forests. This is especially important after abrupt changes in forest cover and structure following the occurrence of a disturbance event. In this contribution, we present a brief introduction on remote sensing technologies and their potential contribution to protection forest management, followed by two case studies. In particular, we focus on research areas within protection forests against rockfall affected by windthrow (i.e., the 2018 storm Vaia in the Eastern Italian Alps, where LiDAR and UAV data were used), and forest fires (i.e., the 2017 fall fires in the Western Italian Alps, involving Sentinel-2 image analyses).

Shishigaki (wild boar defense walls), as a part of cultural landscapes in Japan, currently faces serious deterioration. The research aims to identify the characteristics of Shishigaki walls in eight villages located at the foot of Mt. Hira and propose conservation strategies. Interpretation of historical documents and cadastral maps, interviews, and measurement surveys were conducted. As a result, about 4,3 km of Shish-igaki relics are confirmed, of a total length up to12,7 km built in the 18th to 19th century. Shishigaki walls were built by local households collaboratively with different drystone masonry techniques. Based on the field surveys, it was found that although up to 91% of Shishigaki walls located within the village territories were demolished, only half of Shishigaki walls in the forest were deconstructed. Loss of functionality as protection fences with the change of land use is considered as the main reason for the demolition of Shish-igaki walls. It is suggested that Shishigaki relics in the forest could be integrated into existing hiking routes and promoted through collaborative map-making with local residents. The authors contest that heritage interpretation rooted in local historical studies and conservation with community involvement could be adopted in the promotion of cultural landscapes worldwide.

Gas pipelines and networks are subject to multiple regulatory governance arrangements. One regime is economic regulation which is designed to ensure fair access to gas markets and emulate the price pressures of competition in a sector dominated by a few companies. Another regime is technical regulation which is designed to ensure pipeline system integrity is sufficient for the purposes of public safety, environmental protection and physical security of supply. As was highlighted in analysis of the San Bruno pipeline failure, these two regulatory regimes have substantially different orientations towards expenditure on things such as maintenance and inspection which ultimately impact public safety. Drawing on more than 50 interviews, document review and case studies of specific price determinations, we have investigated the extent to which these two regulatory regimes as enacted in Australia may conflict, and particularly whether economic regulation influences long-term public safety outcomes. We also draw on a comparison with how similar regulatory requirements are enacted in the United Kingdom (UK). Analysis shows that the overall orientation towards risk varies between the two regimes. The technical regulatory regime is a typical goal-setting style of risk governance with an overarching requirement that ‘reasonably practicable’ measures are put in place to minimize risk to the public. In contrast, the incentive-based economic regulatory regime requires that expenditure should be ‘efficient’ to warrant inclusion in the determination of acceptable charges to customers. How safety is considered within this remains an open question. Best practice in performance-based safety regimes such as those used in the UK and Australia require that regulators adopt an attitude towards companies based on the principle of ‘trust but verify’ as, generally speaking, all parties aim for the common goal of no accidents. Equally, in jurisdictions that favor prescriptive safety requirements such as the United States (US) the common goal remains. In contrast, stakeholders in the economic regulatory regime have significantly diverse interests; companies seek to maximize their individual financial returns and regulators seek to exert downward price pressures. We argue that these differences in the two regulatory regimes are significant for the management of public safety risk and conclude that minimizing risk to the public from a major pipeline failure would be better served by the economic regulatory regime’s separate consideration of safety-related from other expenditure and informed by the technical regulator’s view of safety.

Under the United Nations Charter, the U.N. Security Council has several important functions and powers, not least with regard to taking binding actions to maintain international peace and security. The ten elected members have the opportunity to influence this area and others during their two-year terms on the Council. In this paper, we aim to illustrate some of these opportunities, identify potential guidance from prior elected members’ experiences, and outline the key procedures that incoming elected members should be aware of as they prepare to join the Council. In doing so, we seek in part to summarize the current state of scholarship and policy analysis in an effort to make this material more accessible to States and, particularly, to States’ legal advisers. We drafted this paper with a view towards States that have been elected and are preparing to join the Council, as well as for those States that are considering bidding for a seat on the Council. As a starting point, it may be warranted to dedicate resources for personnel at home in the capital and at the Mission in New York to become deeply familiar with the language, structure, and content of the relevant provisions of the U.N. Charter. That is because it is through those provisions that Council members engage in the diverse forms of political contestation and cooperation at the center of the Council’s work. In both the Charter itself and the Council’s practices and procedures, there are structural impediments that may hinder the influence of elected members on the Security Council. These include the permanent members’ veto power over decisions on matters not characterized as procedural and the short preparation time for newly elected members. Nevertheless, elected members have found creative ways to have an impact. Many of the Council’s “procedures” — such as the “penholder” system for drafting resolutions — are informal practices that can be navigated by resourceful and well-prepared elected members. Mechanisms through which elected members can exert influence include the following: Drafting resolutions; Drafting Presidential Statements, which might serve as a prelude to future resolutions; Drafting Notes by the President, which can be used, among other things, to change Council working methods; Chairing subsidiary bodies, such as sanctions committees; Chairing the Presidency; Introducing new substantive topics onto the Council’s agenda; and Undertaking “Arria-formula” meetings, which allow for broader participation from outside the Council. Case studies help illustrate the types and degrees of impact that elected members can have through their own initiative. Examples include the following undertakings: Canada’s emphasis in 1999–2000 on civilian protection, which led to numerous resolutions and the establishment of civilian protection as a topic on which the Council remains “seized” and continues to have regular debates; Belgium’s effort in 2007 to clarify the Council’s strategy around addressing natural resources and armed conflict, which resulted in a Presidential Statement; Australia’s efforts in 2014 resulting in the placing of the North Korean human rights situation on the Council’s agenda for the first time; and Brazil’s “Responsibility while Protecting” 2011 concept note, which helped shape debate around the Responsibility to Protect concept. Elected members have also influenced Council processes by working together in diverse coalitions. Examples include the following instances: Egypt, Japan, New Zealand, Spain, and Uruguay drafted a resolution that was adopted in 2016 on the protection of health-care workers in armed conflict; Cote d’Ivoire, Kuwait, the Netherlands, and Sweden drafted a resolution that was adopted in 2018 condemning the use of famine as an instrument of warfare; Malaysia, New Zealand, Senegal, and Venezuela tabled a 2016 resolution, which was ultimately adopted, condemning Israeli settlements in Palestinian territory; and A group of successive elected members helped reform the process around the imposition of sanctions against al-Qaeda and associated entities (later including the Islamic State of Iraq and the Levant), including by establishing an Ombudsperson. Past elected members’ experiences may offer some specific pieces of guidance for new members preparing to take their seats on the Council. For example, prospective, new, and current members might seek to take the following measures: Increase the size of and support for the staff of the Mission to the U.N., both in New York and in home capitals; Deploy high-level officials to help gain support for initiatives; Partner with members of the P5 who are the informal “penholder” on certain topics, as this may offer more opportunities to draft resolutions; Build support for initiatives from U.N. Member States that do not currently sit on the Council; and Leave enough time to see initiatives through to completion and continue to follow up after leaving the Council.

The international community agrees on the urgent need to reduce greenhouse gas emissions from deforestation and forest degradation. With 13 million hectares of forest cleared every year, such efforts are critical to curbing climate change before it reaches a dangerous tipping point. But we are missing a vital opportunity to combat climate change—strengthening the land and resource rights of Indigenous Peoples and local communities whose well-being is tied to their forests. This publication analyzes the growing body of evidence linking community forest rights with healthier forests and lower carbon dioxide emissions from deforestation and forest degradation. It presents a compelling case for expanding and strengthening community forest rights based on evidence drawn from comparative studies, advanced quantitative research, case studies, and original deforestation and carbon analyses by the World Resources Institute. The findings center on examples from 14 forest-rich countries in Latin America, Africa, and Asia. Together, these countries contain about 323 million hectares of government-recognized community forest —68 percent of the estimated total in all low- and middle-income countries—as well as large areas of community forests without legal or official recognition. Our analysis focuses on the links between legal community forest rights (or lack thereof), the extent of government protection of those rights, and forest outcomes.