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Rural Restructuring and the Regulation of Farm Pollution

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Abstract

In this paper the emergence during the 1980s of a water pollution problem associated with intensive livestock production is examined. Farm pollution is socially constructed and is shaped by rural social change. Rural areas are experiencing social and economic restructuring with a resultant shift in emphasis from production to consumption concerns. 'New' people are living in the countryside, with ideas about how its resources should be managed that often differ from those with traditional production interests. At the same time, the debates surrounding the privatisation of the water industry opened up the issue of water pollution in the countryside to greater critical scrutiny. It is in this context that pollution from farm 'wastes' (termed here 'farm pollution') has gone from being a 'nonproblem' in the 1970s to an issue of greater public and political concern and regulatory activity since the late 1980s. Based on evidence from a study of dairy farming in Devon, it is argued in this paper that the farm pollution problem and its regulation are as much a function of social change in the countryside as of environmental change in rivers.

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... We then consider the influence of these factors on the effective regulation of farmers' conduct and on the organisations involved in implementation. This chapter builds on insights gained from previous studies that focused on the views of farmers or farmer interests in the implementation of pollution control and agri-environmental schemes (Ward et al. 1995;Kaljonen 2006;Blackstock et al. 2007;Dupraz et al. 2009). This study differs in engaging farming and other actors at the next tier of social organisation, through agri-political organisations (referred to hereafter as farmer industry groups), in environmental governance. ...
... Related sources of ambiguity include the often unacknowledged and competing political motivations behind target setting and policy objectives. Ward et al. (1995), writing about the UK Control of Pollution Act 1974, described how the 'control objectives' of the regulations were left unclear. In this instance, they pointed to the emerging value-based conflict between farmers and environmentalists. ...
... It is also seen as contributing towards resolving conflicting policy imperatives (Moss 2004;Carter et al. 2005) which are part and parcel of neoliberal policy settings in Australia. One particular regulatory strategy is that of cooperatively developed standards or targets, tailored to local conditions (Ward et al. 1995;Sabel et al. 2000;Brouwer et al. 2003). In our study, these cooperatively developed targets and standards play a central but partial approach to co-regulation of agriculture in the Great Barrier Reef. ...
Book
Risk and Social Theory in Environmental Management marks a timely contribution, given that environmental management is no longer just about protecting pristine ecosystems and endangered species from anthropogenic harm; it is about calculating and managing the risks to human communities of rapid environmental and technological change. First, the book provides a solid foundation of the social theory underpinning the nature of risk, then presents a re-thinking of key concepts and methods in order to take more seriously the biophysical embeddedness of human society. Second, it presents a rich set of case studies from Australia and around the world, drawing on the latest applied research conducted by leading research institutions. In so doing, the book identifies the tensions that arise from decision-making over risk and uncertainty in a contested policy environment, and provides crucial insights for addressing on-ground problems in an integrated way.
... Increased consumption also affects rural communities through agricultural production itself. Ward et al (1995Ward et al ( , 1193 contend that the role of agricultural production is diminishing in association with a secular redefinition of the social functions of rural space to encompass distinctive consumption roles (such as residence, recreation, leisure, and environmental conservation). Marsden (1992, 219) agrees, seeing a decline in the "productivist system of agriculture" at the same time as the development of a much more diverse set of "privatized consumption relations." ...
... People are migrating in and out of rural communities in response to the pressures of the global market. These migration flows have reshaped rural society (Ward et al 1995(Ward et al , 1194. ...
... In-migration has been associated with and helped to catalyze a major shift in public attitudes to agriculture and the countryside, which has produced a growing gap between public perceptions of the function of the countryside and those of the farming community on questions of pesticide and land use (Ward et al 1995(Ward et al , 1194. Salamon and Tornatore (1994, 638) found that in-migration also resulted in tensions between local residents and newcomers with more wealth and education than established residents. ...
... Increased consumption also affects rural communities through agricultural production itself. Ward et al (1995Ward et al ( , 1193 contend that the role of agricultural production is diminishing in association with a secular redefinition of the social functions of rural space to encompass distinctive consumption roles (such as residence, recreation, leisure, and environmental conservation). Marsden (1992, 219) agrees, seeing a decline in the "productivist system of agriculture" at the same time as the development of a much more diverse set of "privatized consumption relations." ...
... People are migrating in and out of rural communities in response to the pressures of the global market. These migration flows have reshaped rural society (Ward et al 1995(Ward et al , 1194. ...
... In-migration has been associated with and helped to catalyze a major shift in public attitudes to agriculture and the countryside, which has produced a growing gap between public perceptions of the function of the countryside and those of the farming community on questions of pesticide and land use (Ward et al 1995(Ward et al , 1194. Salamon and Tornatore (1994, 638) found that in-migration also resulted in tensions between local residents and newcomers with more wealth and education than established residents. ...
... Ward and Lowe's (1994) analysis noted the importance of succession and noted that 'sceptics' were most likely, and the 'radicals' least likely, to be planning for family farm succession. Drawing on the same sample, Ward et al. (1995) set farm pollution incidents in wider social context, noting how the presence of non-farming 'newcomers' might be leading to a re-evaluation of environmental management in the countryside as well as farmers' roles within it. ...
... This paper has considered farmers' understandings of rivers and riparian environments and examined how these sit within notions of good farming. Whilst the paper echoes previous studies which have observed some confusion amongst respondents relating to both ownership of, and responsibility for, riparian environments (Popp et al., 2007;Barnes et al., 2009) it has also observed a change in the two decades since Ward et al.'s (1995) study -with farmers being acutely aware of their responsibilities in relation to avoiding pollution. Clear, and strict, regulatory control has meant that all farmers were aware of their responsibilities to not, knowingly at least, pollute rivers. ...
Article
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A vibrant literature has emerged around Bourdieusian-inspired notions of the ‘good farmer’ and how such concepts might aid our understandings of agriculture and agricultural change. To date, however, studies of the good farmer have been framed largely in relation to land management, with little consideration given to riparian environments which make up a significant part of the farmed landscape. Drawing on in-depth interviews with farmers in a river catchment in the North of England (UK), this paper considers how farmers' engagement with riparian environments on their farms feature in, and are (re)shaped by, notions of good farming. The paper observes how riparian environments' (im)materiality, unpredictability and untidiness limit their ability to generate and exhibit capital(s) and how an infrequency of direct engagement with rivers – arguably reinforced through recent regulatory changes on what farmers can and cannot do to riparian environments – mean that farmers have often not developed skills and capitals associated with rivers in the same way that they have for land. These observations are used to consider farmers' engagement with more recently introduced river health-enhancing managements and to consider whether, when taken together, we might be witnessing a shift in how riparian environments contribute to good farming and good farmer status.
... Col- lectively, these changes undermine farm- ers' economic and political standing. Al- though not a new concern (Pahl 1965; Newby et al. 1978), it is now felt more intensely and is more widespread ( Ward et al. 1995). Farmers' control over local change is diminishing at the same time as society is devaluing their technical exper- tise, learned over two generations, di- rected toward producing ever more food. ...
... These de- mands are internalized by agricultural science and agribusiness, who interpret sustainability as a combination of "clean" technical fixes and a progressive integra- tion of environmental policies into exist- ing practices (Frouws and Van Tatenhove 1993). The new protocols present farmers with incentives and constraints on farm practices, all of which have particular geographies (Bishop and Phillips 1993;Ward et al. 1995). These issues raise important questions for agrarian political economy. ...
Article
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In this paper, we review recent developments in political economy approaches to agricultural geography. During the last decade, the main areas of debate have shifted from materialist concerns about uneven development, transformation of the family farm, and the role of the state to the related questions of consumption and social nature. We emphasize the common challenges faced by economic geographers addressing the embeddedness of economic relations in social, political, and cultural practices, including the need for theoretical approaches which examine the differential constitution of "structural" processes, their articulation in localities, and the role of actors. To illustrate, we recount recent changes in British farming that demonstrate the continuous repositioning of agriculture within restructured rural spaces and an increasingly integrated, corporate agro-food chain. From these changes new themes emerge. These include those of nature, specifically relations between "natural" and "social" processes, contested meanings of the natural world, and the environmental regulation of agriculture, and the growing need to address aspects of consumption, ranging from food safety to the delivery of amenity, landscape, and ecological "improvements."
... Rosenau (1990) argues that while the nation-state has traditionally buffered civil society from the excesses of capital, there is no such protection at the global level. Ward et al (1995) contend that the role of agricultural protection is diminishing in association with a secular redefinition of the social functions of rural space to encompass distinctive consumption roles (such as residence, recreation, leisure, and environmental conservation). ...
Conference Paper
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The main purpose of this descriptive-survey research is to identify green marketing strategies in Iran and also to investigate the level of awareness of organic agricultural producers in Iran about mixed marketing strategies. The statistical population of this study is all producers of organic products in Iran (N=۸۳) that all these units were considered as a research sample. Research tools include a questionnaire in three sections of general characteristics questions (۷ questions), green marketing strategies (۹ items) in three dimensions (organizational, environmental, and consumer) and a survey of producers’ awareness of the green marketing mix (۱۶ items) in four dimensions (green product, green price, green place, and green promotion) was developed for organic agricultural producers. The validity of the questionnaire was proofed by face and content validity. Likewise, the reliability of the questionnaire was tested employing Cronbach’s alpha. Data analysis was accomplished using SPSS۲۵ software at two levels of descriptive and inferential statistics. Mean and correlation coefficients were used to analyze the data. Findings revealed that the strategy of organic producers in Iran is more focused on its environmental aspect. The results also revealed that the majority of producers are highly aware of the green marketing mix. There is no positive and significant relationship between manufacturers’ awareness of the green marketing mix and research variables. There was no significant difference between contextual variables and producers’ awareness of the green marketing mix.
... In terms of agriculture, as this sector has industrialized and intensified, public perceptions of farmers have become more complex. For example, pollution from farms has become more of a concern, the economic role of agriculture within local industries has become less important, and rural land use change toward amenity and recreation uses have intensified (e.g., Butt 2013; Cabot et al. 2004;Caldwell 1998;Smithers et al. 2005;Ward et al. 1995). Increasing pressure to change public policy to address environmental degradation from a public whose livelihoods do not depend on agriculture (e.g., Freshwater and Deavers 1992) was noted decades ago, but this problem has yet to be addressed. ...
Article
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Urban and agricultural communities are interdependent but often differ on approaches for improving water quality impaired by nutrient runoff waterbodies worldwide. Current water quality governance involves an overlapping array of policy tools implemented by governments, civil society organizations, and corporate supply chains. The choice of regulatory and voluntary tools is likely to influence many dimensions of the relationship between urban and agricultural actors. These relationships then influence future conditions for collective decision-making since many actors participate for multiple years in water quality improvement. In this policy analysis, we draw on our professional experiences and research, as well as academic and practitioner literatures, to investigate how different types of water quality interventions influence urban-agricultural relationships, specifically examining policy tools on a regulatory to voluntary spectrum. Interactions between farmers and other rural agricultural interests on one hand, and urban residents and their stormwater managers and wastewater treatment plants on the other, influence dynamics relevant for water quality improvement. We suggest that the selection of policy tools within complex governance contexts influence urban–agricultural relationships through financial exchange, political coalitions, knowledge exchange, interpersonal relationships, and shared sense of place. Policy tools that provide a means to build relationships and engage with people’s emotions and identities have potential to influence personal and community change and adaptive capacity, while processes such as lawsuits can catalyze structural change. Engaging these relationships is particularly critical given the need to move out of polarized positions to solve collective problems.
... Such patterns have significant implications for the existing farms, since land prices may rise in response to accelerated demand from 'lifestyles' migrating from urban centers and/or non-permanent second homeowners [154]. These processes can be regarded as a sort of rural gentrification leading to fragmented land ownership, increasing human impact and greater disturbance of local ecosystems [155]. In such contexts, native population and migrants (with temporary or permanent second homes) may occupy a 'shared but separate' geographic space with considerable consequences for resilience of local communities, counting environmental and political issues, and long-term sustainability [156][157][158]. ...
Article
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A complex interplay between socioeconomic transformations and demographic dynamics has characterized the long-term development of European countries. As a characteristic example of such linkage, the present study focuses on the spatial relationship between metropolitan growth and population age structure. Preferences for urban and suburban locations reflect complex socioeconomic phenomena such as sprawl, class segregation, gentrification and filtering. However, the spatial linkage between sprawl and demographic transitions was relatively poorly analyzed, and should be more extensively investigated in relation with population dynamics and socioeconomic structures at local scale. By reviewing pertinent literature, this study outlines how space exerts a non-neutral impact on population age structures in Europe, shaping housing needs and influencing settlement patterns and processes of urban transformation. While suburban locations have concentrated younger families and larger households in Northern and Western Europe, the socio-demographic composition of new settlements is increasingly dominated by older inhabitants in the Mediterranean region. Results of this work suggest how discontinuous urban expansion was specifically associated with an elder, wealthy population with high standard of living and a preference for specific housing locations such as detached villas with gardens and swimming pools.
... In the 1970s, the government began to see livestock waste as a pollution problem and legislated for its abatement. In the 1980s, it envisaged AD as enhancing the farm's environmental sustainability (Ward et al., 1995). The government's farm waste-management plans helped stimulate around 30 farm-based AD units from the late 1980s to 1995 (Bywater, 2011;Sanders et al., 2010). ...
Article
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To implement EU climate policy, the UK’s New Labour government (1997–2010) elaborated an ecomodernist policy framework. It promoted technological innovation to provide low-carbon renewable energy, especially by treating waste as a resource. This framework discursively accommodated rival sociotechnical imaginaries, understood as visions of feasible and desirable futures available through technoscientific development. According to the dominant imaginary, techno-market fixes stimulate low-carbon technologies by making current centralized systems more resource-efficient (as promoted by industry incumbents). According to the alternative eco-localization imaginary, a shift to low-carbon systems should instead localize resource flows, output uses and institutional responsibility (as promoted by civil society groups). The UK government policy framework gained political authority by accommodating both imaginaries. As we show by drawing on three case studies, the realization of both imaginaries depended on institutional changes and material-economic resources of distinctive kinds. In practice, financial incentives drove technological design towards trajectories that favour the dominant sociotechnical imaginary, while marginalizing the eco-localization imaginary and its environmental benefits. The ecomodernist policy framework relegates responsibility to anonymous markets, thus displacing public accountability of the state and industry. These dynamics indicate the need for STS research on how alternative sociotechnical imaginaries mobilize support for their realization, rather than be absorbed into the dominant imaginary.
... Not only in high-income countries, but also in middle-income countries (Karali et al., 2014;Paolisso & Maloney, 2000), a shift is induced by the changing rural population and more generally by the pressure of public opinion, which results in emphasis on health and consumption concerns over production. The gap between conventional farming practices and people's awareness of the impact of the 'productivist' model on environment and food quality has been continuously increasing since the 1980s and the 1990s (Ward et al., 1995). In other terms, the structuring concept of "good farmer" is now evolving to meet consumers' expectations. ...
... Not only in high-income countries, but also in middle-income countries (Karali et al., 2014;Paolisso & Maloney, 2000), a shift is induced by the changing rural population and more generally by the pressure of public opinion, which results in emphasis on health and consumption concerns over production. The gap between conventional farming practices and people's awareness of the impact of the 'productivist' model on environment and food quality has been continuously increasing since the 1980s and the 1990s (Ward et al., 1995). In other terms, the structuring concept of "good farmer" is now evolving to meet consumers' expectations. ...
Chapter
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EXECUTIVE SUMMARY When dominant or mainstream perceptions and concepts have an undesired impact on nature and its contributions to people, promoting alternative perceptions and concepts may transform practices towards more desired impacts (established but incomplete). Individual perceptions of the surrounding world are organized into concepts that vary depending on the knowledge, norms, values and beliefs of the community to which an individual belongs (Figure 2.1). These perceptions and concepts influence the way a society builds its own reality and acts on it (well established) {2.1, 2.2.1.2}. The dominant worldviews of a given society or community can affect, positively or negatively, nature and nature’s contributions to people {2.2.2, 2.2.3, 2.2.4}. To achieve Sustainable Development Goal 15.3 of a land degradation neutral world, a shift in worldviews in necessary: from one where land degradation is seen as collateral damage or an externality of desired development, to one where land degradation to achieve development is unacceptable {2.2.1.5, 2.3.3). Sustainable development is based on three pillars: social, environmental and economic. In its implementation, however, economic growth is often considered as the overarching driver of social and environmental progress (well established). Land degradation is sometimes perceived as a result of underdevelopment, while the impacts of development on land degradation tend to be disregarded (e.g., public policies supporting export crops or huge infrastructures) {Box 2.4}. For example, in 2012, 26 out of 40 Agenda 21 targets were “far from being reached” and six were in recession {2.2.4}. Among the six were “fighting global climate change” and “changing consumption patterns” {2.2.4}. Development and economic activity can also cause negative externalities and degradation {2.2.1.5}. A successful example of creating disincentives for negative externalities is the “polluter pays principle” {2.2.1.5}. Widening the scope of this principle to make it more broadly applicable to land degradation might be considered. People are often uninformed about the undesirable environmental impacts of goods and commodities (well established). Raising awareness on how individual consumption choices can have unintended consequences in distant locations is a necessity (well established) {2.2.1.3}. Marketing disinformation about environmental impacts is a rule, not an exception {2.2.3.3, 2.3.2, 2.3.1.3, 2.3.1.4}. Trade competition externalizes social-environmental impacts to lower the prices {2.2.1.5, 2.2.3}. Internalizing the environmental costs of staple, clothes and other goods would raise public awareness, create a strong demand for low-impact products and promote more equity between people in developed and developing countries {2.2.1.5, 2.2.2.3}. Farmers and agribusiness corporations have a major role to play in inventing products and practices reflecting people’s expectation for low footprint agriculture (2.2.3). When land degradation affects cultural diversity and its associated biodiversity, not only are unique socialecological systems threatened, but society also risks losing the local cultural knowledge that can inspire more sustainable practices (well established). The pervasive absorption or loss of traditional knowledge and management systems, which have proven sustainable over decades or centuries, affects cultural, biological, agricultural diversity and ecosystem services {2.2.2.1}. Land and water degradation in or around traditional territories is mainly caused by external population pressure and development programmes such as dams or monoculture {2.2.2.3, 2.3.1.1}. The precarious situation of many indigenous and local people, and their knowledge systems, is an environmental as well as a social issue. Indigenous and local practices and values are embedded in worldviews and can provide alternatives to mainstream practices. For example, indigenous and local value that link the “good life” or “Buen Vivir” {2.2.2.1} to a fulfilling social life in a non-degraded environment point to more sustainable pathways through new worldviews, such as the expansion of traditional and/or agroecological practices along with new conscious consumption patterns. These have already been adopted by growing segments of civil society around the world and could be further promoted {2.3.1.2, 2.3.2.1}. High and rising population numbers in many parts of the world pose profound challenges for environmental sustainability in both developed and developing countries (well established). While human demography is predominantly seen as a matter of 2. CONCEPTS AND PERCEPTIONS OF LAND DEGRADATION AND RESTORATION 56 THE ASSESSMENT REPORT ON LAND DEGRADATION AND RESTORATION poverty and underdevelopment to be dealt with by increasing food production, it is nonetheless a crucial but tabooed environmental issue (unresolved). Successful closing of the transnational development gap and eradication of the difference in per capita consumption highlights the importance of the population size. Thus, the focus on reducing consumption might be extended to embrace an inclusive demographic policy. In 1972, the declaration of Stockholm acknowledged the environmental problems caused by overpopulation and stated that countries should control their demography without affecting basic human rights. Soon after Stockholm, however, the population problem was deemed a social and educational problem, and was addressed as an underdevelopment issue. Measures to curb population growth are available and can deliver significant and lasting environmental and social benefits. These include improved access to education, family planning and gender equality (well established), and improved access to social welfare to support ageing populations (established but incomplete). The role of subsidies that may be further stimulating population growth in more developed nations should also come under scrutiny as one of the measures to curb population growth {2.2.4.2, 2.3.1.4}. The short-term financial costs of restoration are easy to quantify and may seem high, while the short-, medium-, and long-term effects of restoration on nature’s contributions to people are less easy to perceive and value (well established). The benefits of avoiding and reversing land degradation are undeniable and go beyond monetary valuation (well established). Raising awareness of the multiple benefits of both avoiding land degradation and restoring ecosystems might justify raising the resources to achieve restoration and land degradation neutrality targets. Moreover, a more holistic approach to nature’s contributions to people could embrace and meet the expectations of a part of the civil society with knowledge systems that place social-ecological harmony above other considerations. While economic valuation of ecosystem services is common, many of the nature’s contributions to people have no market prices {2.2.1.3, 2.2.1.5} and are therefore undervalued, if valued at all. This practice diminishes not only the economic, but also the multiple non-monetary and intrinsic values associated with nature and nature’s contributions to people, be it spiritual, cultural or ethical {2.2.2.1, 2.3.1.2}. In addition, the concrete benefits of restoration might take longer to be achieved, while the costs of restoration are rather immediate {2.2.1.3, 2.3.1}. Costs and benefits of degrading or restoring can be defined in monetary terms {2.2.1.5}, but the question is multidimensional and includes the imperative to maintain biological and cultural diversity {2.2.2.1}. Benefits will be underestimated when the concept of “good quality of life” is limited to purchasing power (well established) {2.2.4.3, 2.3.2, 2.3.2.2}. These benefits would be easier to perceive if the dominant systems of value focused on the good quality of life with individuals having a fulfilling social life in a non-degraded environment {2.2.2.1, 2.3}. The international community has recognized that a collapse of ecosystem functions would not be restrained by sovereign national borders. However, decisions to address urgent environmental problems are still guided by the incremental and discretionary jurisprudence of international conventions (well established). Since the 1970s, international environmental law has been constantly developed and enriched to account for both the progress of science and environmental degradation. Nonetheless, global ecological deterioration, including climate change, is continuing (well established). Creating a proactive, new ground for international negotiation could be a first step to facilitate reversing land degradation, from which new jurisprudence could arise. This would include overcoming the old “environment versus development” dilemma and foster cooperation policies motivated by a common interest {2.2.4.1}. “Ecological solidarity” is a promising legal principle, which could renew the perception of the links between humans and their environment {2.2.4.3}. This principle embraces three dimensions: it recognizes the planetary interconnectedness of ecosystems and ecological process {2.2.1.3}; it may foster intergovernmental negotiations based on global and mutual solidarity; and it has a fundamental moral meaning emphasizing the common fate of humankind and all living beings {2.3.1.2}. If human progress was understood through these dimensions, efforts to prevent land degradation and to restore degraded land might be facilitated. A global consensus on the definition and baseline for land degradation does not exist (well established), precluding sound scientific assessment of the extent and severity of global degradation, as well as the possibility of measuring success towards quantitative restoration targets such as Aichi Biodiversity Target 15 reinforced in Sustainable Development Goal 15 (established but incomplete). Quantifying land degradation and its reversal through restoration requires assessment of the geographic extent and severity of damage at the current and restored state of the ecosystem, against a baseline (well established) {2.2.1.1}. Lack of consensus over baselines has led to debates over what constitutes degradation and subsequently to inconsistent estimates of the extent and severity of land degradation {2.2.1.2} (Figure 2.5, Figure 2.7, Figure 2.8). This, in its turn, resulted in differing interpretations of the consequences of degradation for human well-being. To overcome this challenge, a shared global baseline could be adopted (well established) and a good candidate would be 2. CONCEPTS AND PERCEPTIONS OF LAND DEGRADATION AND RESTORATION 57 THE ASSESSMENT REPORT ON LAND DEGRADATION AND RESTORATION the natural state of ecosystems, deviation from which would be degradation {2.2.1.1} (Figure 2.5) (established but incomplete). Adopting natural state of ecosystems as the baseline against which to measure the extent and severity of degradation ensures a comparable assessment of land degradation in general, and a fair assessment of success in meeting the Aichi Biodiversity Targets across countries at different stages of economic and social development. Without this, more developed countries – that have transformed much of their environment centuries ago – are able, in practice, to assume much less ambitious restoration measures than less developed countries {2.2.1.1} (Figure 2.5). For the aspiration to achieve land degradation neutrality by 2030, as agreed in SDG 15.3, the baseline for assessing success is different, namely the state of the ecosystems at 2030.
... Rosenau (1990) argues that while the nation-state has traditionally buffered civil society from the excesses of capital, there is no such protection at the global level. Ward et al (1995) contend that the role of agricultural protection is diminishing in association with a secular redefinition of the social functions of rural space to encompass distinctive consumption roles (such as residence, recreation, leisure, and environmental conservation). ...
Article
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Globalization, as a process, analyzed in consideration of communicative instruments, development possibilities, and the expanded nature of capitalism. The purpose of this study was to investigate impacts of globalization on economical and cultural aspects of rural communities in Kermanshah Township. The study represented correlation research. The statistical population of this research was selected among 700 villages located in Kermanshah Township. Among these, 30 villages were selected in three different regions for gathering data by multi-stage sampling. For data analysis multivariate procedures were used. This research examined eight factors of agro-industrialization, increasing in poverty and inequality, change in employment patterns, economic restructuring, role of nation-state, role of media, cultural universalism, cultural particularize and their impacts on rural communities progress. The results showed that there was a significant correlation between independent and dependent variables (p<0.01). On the base of regression analysis independent variables can be predicted 62 percent of changes in dependent variable. Structural Equation Modeling (SEM) certificated regression analysis results. Path analysis results showed that the model fitted the data with acceptable fit indices: chi square=5.341, p=0.376, RMSEA=0.013, CFI=1.000, NFI=0.992.
... Há modos de conhecimento competitivos, que representam compreensões parciais da realidade. 9 Ver Lowe (1992), Clark et al. (1994), Lowe et al. (1993), , Ward et al. (1995); Ward (1995) e Clark & Lowe (1992). ambiental; a das políticas públicas, numa integração de grupos de pressão, políticos, representantes das agroindústrias, funcionários do governo; e a arena científico-tecnológica, que integra membros dos institutos de pesquisa, cientistas trabalhando para a agroindústria e indústrias agroquímicas. ...
... Some have gone as far as to claim that the independent nation state is now a totally redundant category for understanding contemporary economic change in a globalised world economy (for a fuller discussion see Fagan & Le Heron 1994). Even if one assumes that the actions of the state are still effective in regulating local economic systems, the friction between prescribed policy and real effect is often significant or even overwhelming (Ward et al. 1995). More specifically for this study, identifying the state as a primary actor in agricultural change is probably less relevant for New Zealand than for the European situation which informs much of this discussion. ...
... Regionalization, we argue, has challenged the political -economic position of these interest groups in the system of agri-environmental governance, altering their access to funds, their corporatist status with governments and their own internal sectoral politics and practices of representation. Experience in Europe and the UK has shown that national farmer unions can be effective in their efforts to obstruct, prevent or pay lipservice to agricultural development or environment programmes they believe do not meet their political goals, including ones that rely on regionalization (Trouve & Berriet-Solliec, 2010;Ward et al., 1995Ward et al., , 1998. As such, the conflicts between sectoral and regional modes of operation we explore in this paper have important implications for the prospect of effective implementation of environmental policy involving organized rural interests. ...
Article
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Investigations of agri-environmental programmes and their implementation often overlook the contribution of agri-political organizations (APOs). They focus instead upon the experiences of individual farmers, or the potential of farmers to be environmental stewards, the strategies or particular policy instruments employed by governments, or the workings of cooperative planning committees at river basin scales. Over the last decade in Australia, the influence and involvement of APOs in initiatives such as regional natural resource planning and the implementation of water quality policies has increased markedly but has remained largely under-researched. This paper indicates the ways these groups are becoming more embedded in the politics and operation of environmental governance and outlines the new and contested roles these groups are now playing in Australian rural landscapes. Using the case of the ongoing implementation of the Reef Water Quality Protection Plan, the paper explores tensions in the current arrangements and considers implications for ongoing participation of the farming sector in environmental governance. These tensions revolve around challenges to APOs’ traditional dialogic practices; interest-based models of representation; and their capacity to align with and operate within new territorial spaces of policy implementation, such as regions.
... Ward et al. suggested that farmers responded in an 'addon' and 'end-of-pipe' way rather than seriously engaging with the sources of pollution. Similarly, Ward et al. (1995;1207) reported that "the group felt that agricultural pollution was far less of a problem than industrial pollution and suspected that farmers were being more strictly regulated because they were 'easy targets'. This refusal to accept the 'pollution' framing for farming activities is not restricted to the dairy farms studied by Ward et al. (1998). ...
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Methane emissions from sheep and cattle production have gained increasing profile in the context of climate change. Policy and scientific research communities have suggested a number of technological approaches to mitigate these emissions. This paper uses the concept of co-production as an analytical framework to understand farmers’ evaluation of a 'good animal’. It examines how technology and sheep and beef cattle are co-produced in the context of concerns about the climate change impact of methane. Drawing on 42 semi-structured interviews, this paper demonstrates that methane emissions are viewed as a natural and integral part of sheep and beef cattle by farmers, rather than as a pollutant. Sheep and beef cattle farmers in the UK are found to be an extremely heterogeneous group that need to be understood in their specific social, environmental and consumer contexts. Some are more amenable to appropriating methane reducing measures than others, but largely because animals are already co-constructed from the natural and the technical for reasons of increased production efficiency.
... Few would argue against the notion that environmental regulations in agriculture have increased in the last two decades, especially with regard to farm pollution controls (Ward et al., 1995;Lowe et al., 1997), and more formally established (but not necessarily effective) protection of wildlife sites (Adams, 1986;Winter, 1996;Evans, 2000). Even here, progress is far from even. ...
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Abstract It has become,fashionable to conceptualiserecent shifts in agrarian priorities as a „post- productivist‟ transition from a previously „productivist‟ agriculture. This notion has become,more popular throughout the 1990s as a way to capture in one convenient package the complex,changes experienced by both the agricultural sector specifically and rural areas more generally. However, the widespread and uncritical use of such an all- encompassing,term is rather surprising given debates elsewhere in human geography,on the rejection of dualistic thinking. Yet, in agricultural and rural studies, the active creation and reinforcement of a productivist / post-productivist dualism has emerged,as a means of explaining the uneven development,of rural areas. This paper develops a critique of post-productivism to demonstrate its invalidity, presenting empirical evidence to refute five supposed characteristics relating to quality food, pluriactivity;
... For example, the price of agricultural land may be in ated by high demand from 'life-stylers' migrating from urban centres, while rural gentri cation may lead to fragmented land ownership and increased human presence and disturbance of local ecosystems (Riebsame et al. 1996). In such situations, local populations and migrants (second home, temporary and permanent) may occupy a 'shared but separate' geographic space with substantial implications for local community institutions (Halseth 1993;Lowe et al. 1993;Phillips 1993), including environmental and political issues (Halseth and Rosenberg 1995;Ward To ur ism a nd m igrat io n rel at io ns hi ps 19 et al. 1995) and longer-term sustainability (Flynn and Marsden 1995). For example, viticultural practices (including the use of bird-scarers and helicopters) may not be welcome by second home owners who are attracted by tranquil images of vineyards in pleasant rural areas. ...
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... Such constructions of rurality have wider currency, bearing close resemblance, for instance, to aspects of both the 'move-in for self' and 'move-in and join-in' households identified by Cloke et al (1995; and, even more generally, to Short's (1991, p. xvi) 'environmental myths' of 'wilderness' and 'countryside'. Other work has highlighted how some rural residents value 'green views' (Phillips 2001a;Phillips et al. 2001), evaluating the countryside as an aesthetic landscape and in some cases supporting the development of highly manufactured green spaces such as golfcourses and leisure complexes as a means of retaining and even enhancing rurality (see also Thrift 1987), while other rural residents very much view the countryside as a place of ecological nature, valuing its 'wild' flora and fauna and the 'purity' of its atmosphere and waterways (see Lowe et al. 1997;Macnaghten and Urry 1998;Phillips and Mighall 2000;Ward et al. 1998;Ward et al. 1995).Yet other people value spaces of nature of nature in the countryside for amenity functions and the facilitation of companionship, friendship, and senses of community, tradition, identity and spirituality (Etzioni 1998;Harrison 1991;Schama 1995). Smith and Phillips' (2001, p. 460) claim that greentrifiers are attracted to "village and landscapes synonymous with working farms, country lanes, green fields and sheep" may furthermore connect to the broader arguments of people such as Tovey (2003) and Jones (2003) about the significance of domesticated animals within rural life. ...
... Secondly, there has been a brief phase attempting to establish the characteristics of the PPT. According to Ilbery and Evans (1996), the remaining characteristics of the PPT encompasses: a shift in emphasis away from quantity towards quality in food production Marsden, 1998b); the growth of alternative farm enterprises, conceptualised as 'pluriactivity' (Ilbery, 1991;Evans and Ilbery, 1993); state efforts to encourage a return to more traditional, sustainable farming systems through agri-environmental policy (Wilson, 1996;Ilbery et al. 1997); the growing environmental regulation of agriculture (Robinson, 1991;Ward et al., 1995); and the progressive withdrawal of support for agriculture (Winter, 1996), this latter characteristic being predominantly relegated to a contextual position within agri-environmental research. Thirdly, the PPT has most recently become the subject of process-oriented theorization. ...
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... The question for many of the local residents becomes one of spatial resistance -through , for instance the use of and participation in the planning system and formal preservation societies --to potential forms of development. Ward et al. (1995) and Flynn and Lowe (1995) describe vividly, for instance, how in the contested countryside of rural Devon, agricultural concerns are increasingly voiced by the newer rural non-farming residents as more of them adopt a preservationist and conservationist position, involving the newer environmental agencies like the National River Authority (now the Environmental Agency). ...
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