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This chapter analyzes the building of environmental governance in two post-socialist countries of Southeastern Europe, Albania, and Croatia, with a focus on forest policy reforms. After the end of the socialist era, the countries have rapidly adopted new policies and legislation directed at sustainable forest management. The main driver of policy reform is the European and international influence. Yet the developments in the countries cannot be adequately described as a mere adoption of Western-style methods and solutions, as suggested in arguments on the catch-up development of transition states. The capacities needed in post-socialist countries to deal with environmental issues differ from those in industrial societies. On the contrary, there is no essentialistic link between environmental problems and solutions to these problems in post-socialist countries. The outline of the policy reforms in Croatia and Albania reveals very different approaches to sustainable forest management and different paths in the post-socialist transition process. It is argued that capacity development in forestry in transition states needs to be based on country-specific socio-political, economic, and cultural features to be successful.

According to a report by Food and Agriculture Organization, total forest area in the world as of 2005 is estimated at 3,952 million hectares (9,766 acres) or 30 percent of total land area (FAO, 2005a). The area of forest is unevenly distributed (FAO, 2005b). At the regional level, South America is the region with the highest percentage of forest cover, followed by Europe and North and Central America. Asia is the region with the lowest percentage of forest cover (FAO, 2005c). The forest environments are changing globally. Climate change is one of the reasons, and it affects world forest management. More attention has been devoted to timber as the major commercial aspect of forests rather than to other noncommercial resource values (Barnard et al., 1985). The purpose of forest management was once as simple as taking timbers, but it is now more complicated. When the forest environments change, the key trends of world forest management must also change. Now, generally speaking, the extent of forest resources refers to an overall maintaining of adequate forest cover and stocking of various forest types and characteristics, and the ultimate aim of monitoring the extent and characteristics of forest resources is to reduce unplanned deforestation, restore and rehabilitate degraded forest landscapes, manage forests sustainably, and evaluate the important function of carbon sequestration by forests, other wooded land, and trees outside forests, thereby contributing to moderating the global climate (FAO, 2005d).

The 1990s have been the decade of state decentralisation both in India and in Sweden. Decentralisation of political power has been accompanied by the rhetoric of community participation in natural resource management and rural development initiatives. In light of this, questions about whom or what constitutes the ‘community’ and ‘the local’ take on important connotations. Women and men living in many rural areas (often peripheral in relation to State and other decision-making structures) have sought to ‘redefine’ community citizenship and their relationships with the forests and nature around them. They have tried to play a more active and responsible role in the relationships that they already share by virtue of living together with the forests. Although considerable research has now turned to look at these processes, the gendered nature of these efforts is often subsumed in all-encompassing terms such as community, state or forests. Research with women in two forest communities, one in Sweden and the other in India illustrated that natural resource management is clearly gendered and has tangible effects on the gendering of citizenship in rural areas.

Mangrove has the potential to adapt climate change threats like sea level rise, extreme high water events, and coastal erosions. The large stretched root systems of the mangrove acts as a natural barrier to catch hold of the run off soil, leading to accretion of coastal areas. Due to human and other natural activities, mangroves in different parts of the world are being degraded. Citing examples from India, this chapter provides ways of unique mangrove comanagement system with the involvement of local communities, NGOs, and local governments.

Climate change during the next century is likely to significantly influence forest ecosystems in the western United States, including indirect effects on forest and shrubland fire regimes. Further exacerbation of fire hazards by the warmer, drier summers projected for much of the western U.S. by climate models would compound already elevated fire risks caused by 20th century fire suppression. This has potentially grave consequences for the urban–wildland interface in drier regions, where residential expansion increasingly places people and property in the midst of fire-prone vegetation. Understanding linkages between climate variability and change, therefore, are central to our ability to forecast future risks and adapt land management, allocation of fire management resources, and suburban planning accordingly. To establish these linkages we review previous research and draw inferences from our own retrospective work focused on 20th century climate–fire relationships in the U.S. Pacific Northwest (PNW). We investigated relationships between the two dominant modes of climate variability affecting the PNW, which are Pacific Decadal Oscillation (PDO) and El Niño/Southern Oscillation (ENSO), and historic fire activity at multiple spatial scales. We used historic fire data spanning most of the 20th century for USDA Forest Service Region 6, individual states (Idaho, Oregon, and Washington), and 20 national forests representative of the region's physiographic diversity. Forest fires showed significant correlations with warm/dry phases of PDO at regional and state scales; relationships were variable at the scale of individual national forests. Warm/dry phases of PDO were especially influential in terms of the occurrence of very large fire events throughout the PNW. No direct statistical relationships were found between ENSO and forest fires at regional scales, although relationships may exist at smaller spatial scales. However, both ENSO and PDO were correlated with summer drought, as estimated by the Palmer Drought Severity Index (PDSI), and PDSI was correlated with fire activity at all scales. Even moderate (±0.3°C decadal mean) fluctuations in PNW climate over the 20th century have influenced wildfire activity based on our analysis. Similar trends have been reported for other regions of the western U.S. Thus, forest fire activity has been sensitive to past climate variability, even in the face of altered dynamics due to fire suppression, as in the case of our analysis. It is likely that fire activity will increase in response to future temperature increases, at the same or greater magnitude as experienced during past climate variability. If extreme drought conditions become more prevalent we can expect a greater frequency of large, high-intensity forest fires. Increased vulnerability to forest fires may worsen the current fire management problem in the urban–wildland interface. Adaptation of fire management and restoration planning will be essential to address fire hazards in areas of intermingled exurban development and fire-prone vegetation. We recommend: (1) landscape-level strategic planning of fire restoration and containment projects; (2) better use of climatic forecasts, including PDO and ENSO related predictions; and (3) community-based efforts to limit further residential expansion into fire-prone forested and shrubland areas.

Forests and the goods and services they provide are essential for human well-being (Seppälä, Buck, & Katila, 2009). Forests provide three types of ecosystem services that directly support human well-being: provisioning services such as food, fuelwood, medicine, etc.; regulating services such as water purification, climate regulation, erosion control, etc.; and cultural services, including recreation, spiritual, and religious values (Millennium Ecosystem Assessment, 2003). About 1.6 billion people live in predominantly forest ecosystems or in their vicinity. Forest communities include indigenous peoples (IPs) who have been living since time immemorial in forest areas and other local groups including the more recent settlers or immigrants. In the tropics, over 800 million people are living in forests and woodlands, which makes these areas a very important resource for the rural poor (Chomitz, Buys, De Luca, Thomas, & Wertz-Kanounnikoff, 2007). Based on ADB's (2009a) estimates, half of the world's poorest of the poor are IPs, and more than half live in Asia. Sixty million of these IPs are forest dependent.

By bringing together aspects of sustainable forest management, population health, and local livelihoods, the purpose of this study was to characterize how household dependence on forest resources changes through three phases: the period before HIV became a problem in the household, the period during HIV-related morbidity, and after AIDS-related mortality.

Sixty semi-structured interviews were conducted with members of unaffected and HIV/AIDS-affected households in four case study districts in Malawi.

This study demonstrates that the relationship between HIV/AIDS and dependence on specific forest resources appears to correspond closely with the stage of the disease. Firewood and water were consistently ranked as being one of the three most important resources, regardless of HIV-affectedness. During the morbidity phase, respondents reported their need for medicinal plants increased substantially, along with other resources. The importance of timber increased significantly after HIV-related mortality.

Interview respondents themselves suggested key interventions that would assist households in the HIV/AIDS-mortality phase, in particular, to obtain the forest resources they require. These interventions could address the impacts of HIV/AIDS on the sustainability of important resources, compensate for a decreased availability of household labor, and foster greater access to these resources for vulnerable households in the four study sites.

In spite of the fact that forest resources can play a crucial role in enabling a household to control and adapt to the disease, research on the environmental dimensions of HIV/AIDS remains limited. This chapter helps to address this knowledge gap, suggests practical, innovative interventions that could alleviate some of the disease burden on rural Malawian households, and offers insight into potential areas of further inquiry in this research domain.

Forests too thick with fuels that are too continuously spread to resist fire are common throughout the west. After a century or more of actively working to suppress fire across the landscape, we now recognize that fire is a part of our forests, shrublands, and range, and that it will come whether we wish it or not. At last, managers must realize forests cannot be fire-proofed (DellaSala, Williams, Williams, & Franklin, 2004). We must work with fire rather than against it.

Indonesia is one of the world’s “megadiverse” countries, providing ecosystem services that accrue at the global scale. However, control over access to and use of natural resources has historically been a source of tension between the central government and local communities, with the latter usually being marginalized by the former. Since the fall of the authoritarian Suharto regime in 1998, however, a grassroots movement supports the revitalization of customary communities and their traditional systems of social organization (adat). A major part of this quest for legitimacy is the portrayal of indigenous people as environmentally benign. This chapter describes how indigenous systems have been influenced by political processes over time. We then describe how the changing political–administrative landscape has given rise to a national indigenous rights movement. We also analyze international factors that have contributed to the emergence of the indigenous movement before discussing potential challenges facing the movement in the future. This chapter seeks to get beyond the simplistic conflation of indigenous peoples and environmentalism by understanding the strategic articulation of indigeneity and environmentalism.

Community-based fire management (CBFiM) integrates community action with the standard elements of fire management and mitigation, such as prescribed fire (managed beneficial fires for reducing hazardous fuel loads, controlling weeds, preparing land for cultivation, reducing the impact of pests and diseases, etc.), mechanical fuel treatment, defensible space planning, wildfire awareness and prevention, preparedness planning, and suppression of wildfires. In developed examples of CBFiM, communities are empowered to have effective input into land and fire management and problem solving and to self regulate to respond to fire and other emergencies. Its premise is that local people usually have most at stake in the event of a harmful fire, so they should clearly be involved in mitigating these unwanted events.