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Sunday, February 25, 2024

Fisheries management

From Wikipedia, the free encyclopedia
A signboard listing fishing regulations at Horton Creek, Arizona

The goal of fisheries management is to produce sustainable biological, environmental and socioeconomic benefits from renewable aquatic resources. Wild fisheries are classified as renewable when the organisms of interest (e.g., fish, shellfish, amphibians, reptiles and marine mammals) produce an annual biological surplus that with judicious management can be harvested without reducing future productivity. Fishery management employs activities that protect fishery resources so sustainable exploitation is possible, drawing on fisheries science and possibly including the precautionary principle.

Modern fisheries management is often referred to as a governmental system of appropriate environmental management rules based on defined objectives and a mix of management means to implement the rules, which are put in place by a system of monitoring control and surveillance. An ecosystem approach to fisheries management has started to become a more relevant and practical way to.  According to the Food and Agriculture Organization of the United Nations (FAO), there are "no clear and generally accepted definitions of fisheries management". However, the working definition used by the FAO and much cited elsewhere is:

The integrated process of information gathering, analysis, planning, consultation, decision-making, allocation of resources and formulation and implementation, with necessary law enforcement to ensure environmental compliance, of regulations or rules which govern fisheries activities in order to ensure the continued productivity of the resources and the accomplishment of other fisheries objectives.

Objectives

Political

According to the FAO, fisheries management should be based explicitly on political objectives, ideally with transparent priorities. Political goals can also be a weak part of fisheries management, since the objectives can conflict with each other. Typical political objectives when exploiting a commercially important fish resource are to:

For the most recent several decades, the political goals in fisheries management of commercially important species have been rapidly evolving, primarily driven by (1) a recognition of the response of fish and other target animals to changing climate, (2) new technologies for fishing particularly on the high seas, (3) development of competing policy priorities for aquatic environments leading to a more ecosystem-based approach to fisheries management, and (4) new scientific insights about the processes affecting fish population size and recruitment. The political objectives operative in recreational fisheries management are often substantially different from those prevalent in commercial fisheries management. For example, catch-and-release regulations are common in some types of recreational fisheries. Thus, biological yield is of less important.

International objectives

Fisheries objectives need to be expressed in concrete management rules. In most countries fisheries management rules should be based on the internationally agreed, though non-binding, Code of Conduct for Responsible Fisheries, agreed at a meeting of the U.N.'s Food and Agriculture Organization FAO session in 1995. The precautionary approach it prescribes is typically implemented in concrete management rules as minimum spawning biomass, maximum fishing mortality rates, etc. In 2005 the UBC Fisheries Centre at the University of British Columbia comprehensively reviewed the performance of the world's major fishing nations against the Code.

Management mechanisms

Many countries have set up Ministries/Government Departments, named "Ministry of Fisheries" or similar, controlling aspects of fisheries within their exclusive economic zones. Four categories of management means have been devised, regulating either input/investment, or output, and operating either directly or indirectly:


Inputs Outputs
Indirect Vessel licensing Catching techniques
Direct Limited entry Catch quota and technical regulation

Technical measures may include:

  • prohibiting devices such as bows and arrows, and spears, or firearms
  • prohibiting nets
  • setting minimum mesh sizes
  • limiting the average potential catch of a vessel in the fleet (vessel and crew size, gear, electronic gear and other physical "inputs".
  • prohibiting bait
  • snagging
  • limits on fish traps
  • limiting the number of poles or lines per fisherman
  • restricting the number of simultaneous fishing vessels
  • limiting a vessel's average operational intensity per unit time at sea
  • limiting average time at sea

Catch quotas

Systems that use individual transferable quotas (ITQ), also called individual fishing quota limit the total catch and allocate shares of that quota among the fishers who work that fishery. Fishers can buy/sell/trade shares as they choose.

A large scale study in 2008 provided strong evidence that ITQ's can help to prevent fishery collapse and even restore fisheries that appear to be in decline. Other studies have shown negative socio-economic consequences of ITQs, especially on small-sclale fisheries. These consequences include concentration of quota in that hands of few fishers; increased number of inactive fishers leasing their quotas to others (a phenomenon known as armchair fishermen); and detrimental effects on coastal communities.

Elderly maternal fish

Old, fat, female rockfish are the best producers.

Traditional management practices aim to reduce the number of old, slow-growing fish, leaving more room and resources for younger, faster-growing fish. Most marine fish produce huge numbers of eggs. The assumption was that younger spawners would produce plenty of viable larvae.

However, 2005 research on rockfish shows that large, elderly females are far more important than younger fish in maintaining productive fisheries. The larvae produced by these older maternal fish grow faster, survive starvation better, and are much more likely to survive than the offspring of younger fish. Failure to account for the role of older fish may help explain recent collapses of some major US West Coast fisheries. Recovery of some stocks is expected to take decades. One way to prevent such collapses is to establish marine reserves, where fishing is not allowed and fish populations age naturally.[

Precautionary principle

A Fishery Manager's Guidebook issued in 2002 by the FAO advises that a set of working principles should be applied to "highlight the underlying key issues" of fisheries management." There are 8 principles that should be considered as a whole in order to best manage a fishery. The first principle focuses on the finite nature of fish stocks and how potential yields must be estimated based on the biological constraints of the population.

In a paper published in 2007, Shertzer and Prager suggested that there can be significant benefits to stock biomass and fishery yield if management is stricter and more prompt. This is supported by recent work on the management of North Sea fisheries in accordance with ranges of acceptable fishing, where fishing at the top of the "acceptable" ranges is many times more risky than fishing near the bottom, but delivers only 20% more yield. In addition there is growing evidence – and growing recognition by both fishery scientists and small-scale fishermen – that coastal marine protected areas do favour the biodiversity and resilience of ecosystems nearby, significantly enhancing the density, biomass and size of commercially exploited species in local waters.

Human factors

Fishermen in the harbor of Kochi, India

Managing fisheries is about managing people and businesses, and not about managing fish. Fisheries are managed by regulating the actions of people. If fisheries management is to be successful, then associated human factors, such as the reactions of anglers and harvesters, are of key importance, and need to be understood.

Management regulations must also consider the implications for stakeholders. Commercial fishermen rely on catches to provide for their families just as farmers rely on crops. Commercial fishing can be a traditional trade passed down from generation to generation. Most commercial fishing is based in towns built around the fishing industry; regulation changes can impact an entire town's economy. Cuts in harvest quotas can have adverse effects on the ability of fishermen to compete with the tourism industry.

Effective management of fisheries includes involving all stakeholders in the fishery. To do this successfully, stakeholders need to feel empowered enough to make meaningful contributions to the management process.

Empowerment has a wide application but in this context it refers to a tool that gives people within the fishing communities an opportunity to shape their own future in order to cope with the impacts from large-scale commercial fishing, competition of resources, and other threats that impact fishing communities.

However, there are limits to empowerment in the fisheries management process. Empowerment maintains an involvement on the part of the state in fisheries management and no matter how empowered the other stakeholders are, the success of fisheries is not possible without the legislative powers, financial resources, educational support, and research the government provides.

This concept is not accepted by all, as some communities and individuals argue that the state should withdraw completely and let the local communities handle their own fishery management based on cultural traditions and established practices. Additionally, others have argued that co-management only empowers the wealthy and powerful which in turn solidifies and validates the already existing inequalities of fisheries management.

Empowerment working as a function of co-management, carried out correctly, will not only enable but it will authorize individuals and communities to make meaningful contributions to fisheries management. It is a mechanism that works in a loop, where an individual gains empowerment and encouragement from being a part of the group and the collective action is only successful because of its empowered individuals. In order to effectively and successfully use empowerment as co-management, it is imperative that study programs, guidelines, reading materials, manuals, and checklists are developed and incorporated into all fisheries management.

Corruption

Fisheries mismanagement is due, in part, to corruption. Corruption and bribery influence the number of fishing licenses that are distributed and to whom, as well as the negotiation of fishing access agreements. There is evidence of industrial fisheries corruption among the Small Island Developing States of the Pacific Ocean as well as the fisheries off the coast of West Africa. In small-scale fisheries, inspectors who are charged with regulating catch are bribed to give advance notice of surprise inspections and to relax enforcement standards. Some standards are not enforced at all due to bribery, while other infractions may result in smaller fines than mandated. Fishing gear seized during an investigation can also be returned in exchange for a bribe. Corruption of small-scale fisheries has been documented in South Africa and Lake Victoria.

Data quality

According to fisheries scientist Milo Adkison, the primary limitation in fisheries management decisions is the absence of quality data. Fisheries management decisions are often based on population models, but the models need quality data to be effective. He asserts that scientists and fishery managers would be better served with simpler models and improved data.

The most reliable source for summary statistics is the FAO Fisheries Department.

Fisheries law

Fisheries law is an emerging and specialized area of law which includes the study and analysis of different fisheries management approaches, including seafood safety regulations and aquaculture regulations. Despite its importance, this area is rarely taught at law schools around the world, which leaves a vacuum of advocacy and research.

Fisheries legislation on a national level differs greatly between countries Fisheries may also be managed on an international level. One of the first laws enacted was the "United Nations Convention on the Law of the Sea of 10 December 1982 (LOS Convention)", which entered into force in 1994. This law set the foundation for all international agreements related to oceans that followed.

Effects of climate change

In the past, changing climate has affected inland and offshore fisheries and such changes are likely to continue. From a fisheries perspective, the specific driving factors of climate change include rising water temperature, alterations in the hydrologic cycle, changes in nutrient fluxes, and relocation of spawning and nursery habitat. Further, changes in such factors would affect resources at all levels of biological organization, including the genetic, organism, population, and ecosystem levels. Understanding how these factors affect fisheries at a more nuanced level stand as challenges that fisheries scientists, across multiple fields, still need to face.

Population dynamics

Population dynamics describes the growth and decline of a given fishery stock over time, as controlled by birth, death and migration. It is the basis for understanding changing fishery patterns and issues such as habitat destruction, predation and optimal harvesting rates. The population dynamics of fisheries has been traditionally used by fisheries scientists to determine sustainable yields.

The basic accounting relation for population dynamics is the BIDE model:

N1 = N0 + BD + IE

where N1 is the number of individuals at time 1, N0 is the number of individuals at time 0, B is the number of individuals born, D the number that died, I the number that immigrated, and E the number that emigrated between time 0 and time 1. While immigration and emigration can be present in wild fisheries, they are usually not measured.

Care is needed when applying population dynamics to real world fisheries. In the past, over-simplistic modelling, such as ignoring the size, age and reproductive status of the fish, focusing solely on a single species, ignoring bycatch and physical damage to the ecosystem, has accelerated the collapse of key stocks.

Environmental impact of fishing

The environmental impact of fishing includes issues such as the availability of fish, overfishing, fisheries, and fisheries management; as well as the impact of industrial fishing on other elements of the environment, such as bycatch. These issues are part of marine conservation, and are addressed in fisheries science programs.

Fisheries also have an evolutionary impact on species, especially related to the implementation of minimum landing sizes.

Ecosystem based fisheries

We propose that rebuilding ecosystems, and not sustainability per se, should be the goal of fishery management. Sustainability is a deceptive goal because human harvesting of fish leads to a progressive simplification of ecosystems in favour of smaller, high turnover, lower trophic level fish species that are adapted to withstand disturbance and habitat degradation.

According to marine ecologist Chris Frid, the fishing industry points to pollution and global warming as the causes of unprecedentedly low fish stocks in recent years, writing, "Everybody would like to see the rebuilding of fish stocks and this can only be achieved if we understand all of the influences, human and natural, on fish dynamics." Overfishing has also had an effect. Frid adds, "Fish communities can be altered in a number of ways, for example they can decrease if particular sized individuals of a species are targeted, as this affects predator and prey dynamics. Fishing, however, is not the sole perpetrator of changes to marine life – pollution is another example [...] No one factor operates in isolation and components of the ecosystem respond differently to each individual factor."

In contrast to the traditional approach of focusing on a single species, the ecosystem-based approach is organized in terms of ecosystem services. Ecosystem-based fishery concepts have been implemented in some regions. In 2007 a group of scientists offered the following "ten commandments":

* Keep a perspective that is holistic, risk-averse and adaptive.

  • Maintain an "old growth" structure in fish populations, since big, old and fat female fish have been shown to be the best spawners, but are also susceptible to overfishing.
  • Characterize and maintain the natural spatial structure of fish stocks, so that management boundaries match natural boundaries in the sea.
  • Monitor and maintain seafloor habitats to make sure fish have food and shelter.
  • Maintain resilient ecosystems that are able to withstand occasional shocks.
  • Identify and maintain critical food-web connections, including predators and forage species.
  • Adapt to ecosystem changes through time, both short-term and on longer cycles of decades or centuries, including global climate change.
  • Account for evolutionary changes caused by fishing, which tends to remove large, older fish.
  • Include the actions of humans and their social and economic systems in all ecological equations.
  • Report to Congress (2009): The State of Science to Support an Ecosystem Approach to Regional Fishery Management National Marine Fisheries Service, NOAA Technical Memorandum NMFS-F/SPO-96.
  • Ecosystem modelling software

    Ecopath, with Ecosim (EwE), is an ecosystem modelling software suite. It was initially a NOAA initiative led by Jeffrey Polovina, later primarily developed at the UBC Fisheries Centre of the University of British Columbia. In 2007, it was named as one of the ten biggest scientific breakthroughs in NOAA's 200-year history. The citation states that Ecopath "revolutionized scientists' ability worldwide to understand complex marine ecosystems". Behind this lies two decades of development work by Villy Christensen, Carl Walters, Daniel Pauly, and other fisheries scientists. As of 2010 there are 6000 registered users in 155 countries. Ecopath is widely used in fisheries management as a tool for modelling and visualising the complex relationships that exist in real world marine ecosystems.

    Performance

    The biomass of certain global fish stocks have been allowed to run down. The biomass of many species have now diminished to the point where it is no longer possible to sustainably catch the amount of fish that could be caught. According to a 2008 UN report, titled The Sunken Billions: The Economic Justification for Fisheries Reform, the world's fishing fleets incur a "$US 50 billion annual economic loss" through depleted stocks and poor fisheries management. The report, produced jointly by the World Bank and the UN Food and Agriculture Organization (FAO), asserts that half the world's fishing fleet could be scrapped with no change in catch.

    "By improving governance of marine fisheries, society could capture a substantial part of this $50 billion annual economic loss. Through comprehensive reform, the fisheries sector could become a basis for economic growth and the creation of alternative livelihoods in many countries. At the same time, a nation's natural capital in the form of fish stocks could be greatly increased and the negative impacts of the fisheries on the marine environment reduced."

    The most prominent failure of fisheries management in recent times has perhaps been the events that lead to the collapse of the Atlantic northwest cod fishery. More recently, the International Consortium of Investigative Journalists produced a series of journalistic investigations called Looting the seas. These detail investigations into the black market for bluefin tuna, the subsidies propping up the Spanish fishing industry, and the overfishing of the Chilean jack mackerel.

    History

    Fisheries have been explicitly managed in some places for hundreds of years. More than 80 percent of the world's commercial exploitation of fish and shellfish are harvested from natural occurring populations in the oceans and freshwater areas. For example, the Māori people, New Zealand residents for about 700 years, had prohibitions against taking more than what could be eaten and about giving back the first fish caught as an offering to sea god Tangaroa. Starting in the 18th century attempts were made to regulate fishing in the North Norwegian fishery. This resulted in the enactment of a law in 1816 on the Lofoten fishery, which established in some measure what has come to be known as territorial use rights.

    "The fishing banks were divided into areas belonging to the nearest fishing base on land and further subdivided into fields where the boats were allowed to fish. The allocation of the fishing fields was in the hands of local governing committees, usually headed by the owner of the onshore facilities which the fishermen had to rent for accommodation and for drying the fish."

    In Europe, governmental resource protection-based fisheries management is a relatively new idea, first developed for North European fisheries after the first Overfishing Conference held in London in 1936. In 1957 British fisheries researchers Ray Beverton and Sidney Holt published a seminal work on North Sea commercial fisheries dynamics. In the 1960s the work became the theoretical platform for North European management schemes. In North America, both commercial and recreational fisheries have been actively managed for over 150 years. All U.S. states and Canadian provinces have fisheries agencies and their employees implement state, provincial, and federal laws using a broad suite of tools and procedures for both freshwater and marine fisheries.

    After some years away from the field of fisheries management, Beverton criticized his earlier work in a paper given at the first World Fisheries Congress in Athens in 1992. "The Dynamics of Exploited Fish Populations" expressed his concerns, including the way his and Sidney Holt's work had been misinterpreted and misused by fishery biologists and managers during the previous 30 years. Nevertheless, the institutional foundation for modern fishery management had been laid.

    In 1996, the Marine Stewardship Council was founded to set standards for sustainable fishing. In 2010, the Aquaculture Stewardship Council was created to do the same for aquaculture.

    A report by Prince Charles' International Sustainability Unit, the New York-based Environmental Defense Fund and 50in10 published in July 2014 estimated global fisheries were adding $270 billion a year to global GDP, but by full implementation of sustainable fishing, that figure could rise by an extra amount of as much as $50 billion.

    Landscape-scale conservation

    From Wikipedia, the free encyclopedia
    Landscape scale conservation attempts to reconcile competing pressures on the designated Areas of Outstanding Natural Beauty across the United Kingdom.

    Landscape-scale conservation is a holistic approach to landscape management, aiming to reconcile the competing objectives of nature conservation and economic activities across a given landscape. Landscape-scale conservation may sometimes be attempted because of climate change. It can be seen as an alternative to site based conservation.

    Many global problems such as poverty, food security, climate change, water scarcity, deforestation and biodiversity loss are connected. For example, lifting people out of poverty can increase consumption and drive climate change. Expanding agriculture can exacerbate water scarcity and drive habitat loss. Proponents of landscape management argue that as these problems are interconnected, coordinated approaches are needed to address them, by focussing on how landscapes can generate multiple benefits. For example, a river basin can supply water for towns and agriculture, timber and food crops for people and industry, and habitat for biodiversity; and each one of these users can have impacts on the others.

    Landscapes in general have been recognised as important units for conservation by intergovernmental bodies, government initiatives, and research institutes.

    Problems with this approach include difficulties in monitoring, and the proliferation of definitions and terms relating to it.

    Definitions

    Bureau of Land Management using fire to maintain a landscape in Western Oregon

    There are many overlapping terms and definitions, but many terms have similar meanings. A sustainable landscape, for example, meets "the needs of the present without compromising the ability of future generations to meet their own needs."

    Approaching conservation by means of landscapes can be seen as "a conceptual framework whereby stakeholders in a landscape aim to reconcile competing social, economic and environmental objectives". Instead of focussing on a single use of the land it aims to ensure that the interests of different stakeholders are met.

    The starting point for all landscape-scale conservation schemes must be an understanding of the character of the landscape. Landscape character goes beyond aesthetic. It involves understanding how the landscape functions to support communities, cultural heritage and development, the economy, as well as the wildlife and natural resources of the area. Landscape character requires careful assessment according to accepted methodologies. Landscape character assessment will contribute to the determination of what scale is appropriate in which landscape. "Landscape scale" does not merely mean acting at a bigger scale: it means conservation is carried out at the correct scale and that it takes into account the human elements of the landscape, both past and present.

    History

    Highland cow helping to maintain the landscape near Hilversum in the Netherlands

    The word 'landscape' in English is a loanword from Dutch landschap introduced in the 1660s and originally meant a painting. The meaning a "tract of land with its distinguishing characteristics" was derived from that in 1886. This was then used as a verb as of 1916.

    The German geographer Carl Troll coined the German term Landschaftsökologie–thus 'landscape ecology' in 1939. He developed this terminology and many early concepts of landscape ecology as part of this work, which consisted of applying aerial photograph interpretation to studies of interactions between environment, agriculture and vegetation.

    In the UK conservation of landscapes can be said to have begun in 1945 with the publication of the Report to the Government on National Parks in England and Wales. The National Parks and Access to the Countryside Act 1949 introduced the legislation for the creation Areas of Outstanding Natural Beauty (AONB). Northern Ireland has the same system after adoption of the Amenity Lands (NI) Act 1965. The first of these AONB were defined in 1956, with the last being created in 1995.

    The Permanent European Conference for the Study of the Rural Landscape was established in 1957. The European Landscape Convention was initiated by the Congress of Regional and Local Authorities of the Council of Europe (CLRAE) in 1994, was adopted by the Committee of Ministers of the Council of Europe in 2000, and came into force in 2004.

    The conservation community began to take notice of the science of landscape ecology in the 1980s.

    Efforts to develop concepts of landscape management that integrate international social and economic development with biodiversity conservation began in 1992.

    Landscape management now exists in multiple iterations and alongside other concepts such as watershed management, landscape ecology and cultural landscapes.

    International

    The UN Environment Programme stated in 2015 that the landscape approach embodies ecosystem management. UNEP uses the approach with the Ecosystem Management of Productive Landscapes project. The scientific committee of the Convention on Biological Diversity also considers the perspective of a landscape the most important scale for improving sustainable use of biodiversity. There are global fora on landscapes. During the Livelihoods and Landscapes Strategies programme the International Union for Conservation of Nature applied this approach to locations worldwide, in 27 landscapes in 23 different countries.

    Examples of landscape approaches can be global or continental, for example in Africa, Oceania and Latin America. The European Agricultural Fund for Rural Development plays an important part in funding landscape conservation in Europe.

    Relevance to international commitments

    Some argue landscape management can address the Sustainable Development Goals. Many of these goals have potential synergies or trade-offs: some therefore argue that addressing these goals individually may not be effective, and landscape approaches provide a potential framework to manage them. For example, increasing areas of irrigated agricultural land to end hunger could have adverse impacts on terrestrial ecosystems or sustainable water management. Landscape approaches intend to include different sectors, and thus achieve the multiple objectives of the Sustainable Development Goals – for example, working within catchment area of a river to enhance agricultural productivity, flood defence, biodiversity and carbon storage.

    Climate change and agriculture are intertwined so production of food and climate mitigation can be a part of landscape management. The agricultural sector accounts for around 24% of anthropogenic emissions. Unlike other sectors that emit greenhouse gases, agriculture and forestry have the potential to mitigate climate change by reducing or removing greenhouse gas emissions, for example by reforestation and landscape restoration. Advocates of landscape management argue that 'climate-smart agriculture' and REDD+ can draw on landscape management.

    The marketing of products from specific landscapes can assist conservation. This is apple juice from Tukuche village in the Kali Gandaki Gorge, Nepal

    Regional

    Germany

    Because a large proportion of the biodiversity of Germany was able to invade from the south and east after human activities altered the landscape, maintaining such artificial landscapes is an integral part of nature conservation. The full name of the main nature conservation law in Germany, the Bundesnaturschutzgesetzes, is thus titled in its entirety Gesetz über Naturschutz und Landschaftspflege, where Landschaftspflege translates literally to "landscape maintenance" (see reference for more). Related concepts are Landschaftsschutz, "landscape protection/conservation", and Landschaftsschutzgebiet, a "nature preserve", or literally a (legally) "protected landscape area". The Deutscher Verband für Landschaftspflege is the main organisation which protects landscapes in Germany. It is an umbrella organisation which coordinates the regional landscape protection organisations of the different German states. Classically, there are four methods which can be done in order to conserve landscapes' maintenance, improvement, protection and redevelopment. The marketing of products such as meat from alpine meadows or apple juice from traditional Streuobstwiese can also be an important factor in conservation. Landscapes are maintained by three methods: biological - such as grazing by livestock, manually (although this is rare due to the high cost of labour) and commonly mechanically.

    The Netherlands

    The ladybird spider, Eresus sandaliatus lives on inland shifting dunes, created by forest clearance and overgrazing on poor, sandy soils. Today backhoe loaders can scrape off topsoil, maintaining the low-nutrient soil that such heath and dune species need.

    Staatsbosbeheer, the Dutch governmental forest service, considers landscape management an important part of managing their lands. Landschapsbeheer Nederland is an umbrella organisation which promotes and helps fund the interests of the different provincial landscape management organisations, which between them include 75,000 volunteers and 110,000 hectares of protected nature reserves. Sustainable landscape management is being researched in the Netherlands.

    Peru

    An example of a producer movement managing a multi-functional landscape is the Potato Park in Písac, Peru, where local communities protect the ecological and cultural diversity of the 12,000ha landscape.

    A variety of Peruvian potatoes from the Andes

    Sweden

    In Sweden, the Swedish National Heritage Board, or Riksantikvarieämbetet, is responsible for landscape conservation. Landscape conservation can be studied at the Department of Cultural Conservation (at Dacapo Mariestad) of the University of Gothenburg, in both Swedish and English.

    Thailand

    An example of cooperation between very different actors is from the Doi Mae Salong watershed in northwest Thailand, a Military Reserved Area under the control of the Royal Thai Armed Forces. Reforestation activities led to tension with local hill tribes. In response, an agreement was reached with them on land rights and use of different parts of the reserve.

    Doi Mae Salong landscape in Thailand is managed by agreement between the army and local hill tribes.

    United Kingdom

    Among the leading exponents of UK landscape scale conservation are the Areas of Outstanding Natural Beauty (AONB). There are 49 AONB in the UK. The International Union for Conservation of Nature has categorised these regions as "category 5 protected areas" and in 2005 claimed the AONB are administered using what the IUCN coined the "protected landscape approach". In Scotland there is a similar system of national scenic areas.

    The UK Biodiversity Action Plan protects semi-natural grasslands, among other habitats, which constitute landscapes maintained by low-intensity grazing. Agricultural environment schemes reward farmers and land managers financially for maintaining these habitats on registered agricultural land. Each of the four countries in the UK has its own individual scheme.

    Studies have been carried out across the UK looking at much wider range of habitats. In Wales the Pumlumon Large Area Conservation Project focusses on upland conservation in areas of marginal agriculture and forestry. The North Somerset Levels and Moors Project addresses wetlands.

    Other

    The landscape to the left is known as satoyama; a traditional human-influenced secondary forest bordering agricultural fields in Japan. The satoyama conservation movement spread in the 1980s in Japan and by 2001 there were more than 500 environmental groups involved.

    Landscape approaches have been taken up by governments in for example the Greater Mekong Subregion project and in Indonesia's climate change commitments, and by international research bodies such as the Center for International Forestry Research, which convenes the Global Landscapes Forum.

    The Mount Kailash region is where the Indus River, the Karnali River (a major tributary of the Ganges River), the Brahmaputra River and the Sutlej river systems originate. With assistance from the International Centre for Integrated Mountain Development, the three surrounding countries (China, India and Nepal) developed an integrated management approach to the different conservation and development issues within this landscape.

    Six countries in West Africa in the Volta River basin using the 'Mapping Ecosystems Services to Human well-being' toolkit, use landscape modelling of alternative scenarios for the riparian buffer to make land-use decisions such as conserving hydrological ecosystem services and meeting national SDG commitments.

    Variations

    Ecoagriculture

    In a 2001 article published by Sara J. Scherr and Jeffrey McNeely, soon expanded into a book, Scherr and McNeely introduced the term "ecoagriculture" to describe their vision of rural development while advancing the environment, claim that agriculture is the dominant influence on wild species and habitats, and point to a number of recent and potential future developments they identified as beneficial examples of land use. They incorporated the non-profit EcoAgriculture Partners. in 2004 to promote this vision, with Scherr as President and CEO, and McNeely as an independent governing board member. Scherr and McNeely edited a second book in 2007. Ecoagriculture had three elements in 2003.

    Integrated landscape management

    In 2012 Scherr invented a new term, integrated landscape management(ILM), to describe her ideas for developing entire regions, not at just a farm or plot level. Integrated landscape management is a way of managing sustainable landscapes by bringing together multiple stakeholders with different land use objectives. The integrated approach claims to go beyond other approaches which focus on users of the land independently of each other, despite needing some of the same resources. It is promoted by the conservation NGOs Worldwide Fund for Nature, Global Canopy Programme, The Nature Conservancy, The Sustainable Trade Initiative, and EcoAgriculture Partners. Promoters claim that integrated landscape management will maximise collaboration in planning, policy development and action regarding the interdependent Sustainable Development Goals. It was defined by four elements in 2013:

    1. Large scale: It plans land uses at the landscape scale. Wildlife population dynamics and watershed functions can only be understood at the landscape scale. Assuming short-term trade-offs may lead to long-term synergies, conducting analyses over long time periods is advocated.
    2. Emphasis on synergies: It tries to exploit "synergies" among conservation, agricultural production, and rural livelihoods.
    3. Emphasis on collaboration: It can not be achieved by individuals. The management of landscapes require different land managers with different environmental and socio-economic goals to achieve conservation, production, and livelihood goals at a landscape scale.
    4. Importance of both conservation and agricultural production: bringing conservation into the agricultural and rural development discourse by highlighting the importance of ecosystem services in supporting agricultural production. It supports conservationists to more effectively conserve nature within and outside protected areas by working with the agricultural community by developing conservation-friendly livelihoods for rural land users.

    By 2016 it had five elements, namely:

    1. stakeholders come together for cooperative dialogue and action;
    2. they exchange information systematically and discuss perspectives to achieve a shared understanding of the landscape conditions, challenges and opportunities;
    3. collaborative planning to develop an agreed action plan;
    4. implementation of the plan;
    5. monitoring and dialogue to adapt management.

    Ecosystem approach

    The ecosystem approach, promoted by the Convention on Biological Diversity, is a strategy for the integrated ecosystem management of land, water, and living resources for conservation and sustainability.

    Ten Principles

    This approach includes continual learning and adaptive management: including monitoring, the expectation that actions take place at multiple scales and that landscapes are multifunctional (e.g. supplying both goods, such as timber and food, and services, such as water and biodiversity protection). There are multiple stakeholders, and it assumes they have a common concern about the landscape, negotiate change with each other, and their rights and responsibilities are clear or will become clear.

    Criticisms

    A literature review identified five main barriers, as follows:

    1. Terminology confusion: the variety of definitions creates confusion and resistance to engage. This resistance has emerged, often independently, from different fields. As stated by Scherr et al.: "People are talking about the same thing ... This can lead to fragmentation of knowledge, unnecessary re-invention of ideas and practices, and inability to mobilize action at scale. ... this rich diversity is often simply overwhelming: they receive confusing messages" This problem is not unique to landscape approaches: since the 1970s it has been recognised that the constant emergence of new terminology can be harmful if they promote rhetoric at the expense of action. Because landscapes approaches develop from, and aim to integrate, a wide variety of sectors, makes it vulnerable to overlapping definitions and parallel concepts. Like other approaches to conservation, it may be a fad.
    2. Time lags: substantial time and resources are invested in developing and planning, while resources are inadequate for implementation.
    3. Operating silos: Each sector pursues its goals without giving consideration to the others. This may arise because of a lack in established objectives, operating norms and funding that effectively bridge different sectors. Working across sectors at the landscape scale requires a range of skills, different from those traditionally used by conservation organisations.
    4. Engagement: Stakeholders may not desire to be engaged in the process, engagement may be trivial or inaccessible, and the discussions may hinder efficient decision-making.
    5. Monitoring: There is lack of monitoring to check whether the objectives have been achieved.

     

    Anthropogenic biome

    From Wikipedia, the free encyclopedia
     
    Anthropogenic biomes, also known as anthromes, human biomes or intensive land-use biome, describe the terrestrial biosphere (biomes) in its contemporary, human-altered form using global ecosystem units defined by global patterns of sustained direct human interaction with ecosystems. Anthromes are generally composed of heterogeneous mosaics of different land uses and land covers, including significant areas of fallow or regenerating habitats.

    Origin and evolution of the concept

    Anthromes were first named and mapped by Erle Ellis and Navin Ramankutty in their 2008 paper, "Putting People in the Map: Anthropogenic Biomes of the World". Anthrome maps now appear in numerous textbooks. and in the National Geographic World Atlas. The most recent version of anthrome maps were published in 2021.

    In a recent global ecosystem classification, anthropogenic biomes have been incorporated into several distinct functional biomes in the terrestrial and freshwater realms, and additional units have been described for the freshwater, marine, subterranean and transitional realms to create a more comprehensive description of all ecosystems created and maintained by human activities. The intensive land-use biome comprises five distinct terrestrial ecosystem functional groups: pastures, crops, plantations, urban and semi-natural ecosystem functional group. The artificial wetlands biome in the freshwater realm includes large reservoirs and other constructed wetlands, rice paddies, aquafarms and networks of canals and ditches. The anthropogenic marine biome in the marine realm includes submerged artificial structures and marine aquafarms. The anthropogenic subterranean voids biome includes industrial excavations or artificial cave-like systems. There are two additional biomes in transitions between realms: the anthropogenic shoreline biome includes artificial shorelines; the anthropogenic subterranean freshwaters biome includes water pipes, subterranean canals and flooded mines.

    Anthropogenic transformation of the Biosphere

    For more than a century, the biosphere has been described in terms of global ecosystem units called biomes, which are vegetation types like tropical rainforests and grasslands that are identified in relation to global climate patterns. Considering that human populations and their use of land have fundamentally altered global patterns of ecosystem form, process, and biodiversity, anthropogenic biomes provide a framework for integrating human systems with the biosphere in the Anthropocene.

    Before 1700

    Humans have been altering ecosystems since we have evolved. Evidence suggests that our ancestors were burning land to clear it at one million years ago. 600,000 years ago, humans were using spears to kill horses and other large animals in Great Britain and China. For the past tens of thousands of years, humans have greatly changed the plant and animal life around the globe, from what type of wildlife and plant life dominated to what type of ecosystems dominate. Examples include Native Americans; they altered the forest, burnt land to clear it, settled in cities, disrupting forests and other ecosystems, and built monuments that required moving large amounts of earth, such as the Cahokia Monuments. More examples are the civilizations of the ancient world; they mined large amounts of material, made roads, and especially for the Romans, when mining lead, released large amounts of mercury and lead into the air. A recent study showed that nearly three quarters of Earth's land was already inhabited and reshaped by human societies as long as 12,000 years ago.

    Agriculture (1700–present)

    Humans have been altering ecosystems since before agriculture first developed, and as the human population has grown and become more technologically advanced over time, the land use for agricultural purposes has increased significantly. The anthropogenic biome in the 1700s, before the industrial revolution, was made up of mostly wild, untouched land, with no human settlement disturbing the natural state. In this time period, most of the Earth's ice-free land consisted of wildlands and natural anthromes, and it wasn't until after the industrial revolution in the 19th century that land use for agriculture and human settlements started to increase. With technology advancing and manufacturing processes becoming more efficient, the human population was beginning to thrive, and was subsequently requiring and using more natural resources. By the year 2000, over half of the Earth's ice free land was transformed into rangelands, croplands, villages and dense settlements, which left less than half of the Earth's land untouched. Anthropogenic changes between 1700 and 1800 were far smaller than those of the following centuries, and as such the rate of change has increased over time. As a result, the 20th century had the fastest rate of anthropogenic ecosystem transformation of the past 300 years.

    Land distribution

    As the human population steadily increased in numbers throughout history, the use of natural resources and land began to increase, and the distribution of land used for various agricultural and settlement purposes began to change. The use of land around the world was transformed from its natural state to land used for agriculture, settlements and pastures to sustain the population and its growing needs. The distribution of land among anthromes underwent a shift away from natural anthromes and wildlands towards human-altered anthromes we are familiar with today. Now, the most populated anthromes (dense settlements and villages) account for only a small fraction of the global ice-free land. From the year 1700-2000, lands used for agriculture and urban settlements increased significantly, however the area occupied by rangelands increased even more rapidly, so that it became the dominant anthrome in the 20th century. As a result, the biggest global land-use change as a result of the industrial revolution, was the expansion of pastures.

    Human population

    Following the industrial revolution, the human population experienced a rapid increase. The human population density in certain anthromes began to change, shifting away from rural environments to urban settlements, where the population density was much higher. These changes in population density between areas shifted global patterns of anthrome emergence, and also had wide-spread effects on various ecosystems. Half of the Earth's population now lives in cities, and most people reside in urban anthromes, with some populations dwelling in smaller cities and towns. Currently, human populations are expected to grow until at least midcentury, and the transformation of the Earth's anthromes are expected to follow this growth.

    Current state of the anthropogenic biosphere

    The present state of the terrestrial biosphere is predominantly anthropogenic. More than half of the terrestrial biosphere remains unused directly for agriculture or urban settlements, and of these unused lands still remaining, less than half are wildlands. Most of Earth's unused lands are now within the agricultural and settled landscapes of semi-natural, rangeland, cropland and village anthromes.

    Anthromes map for 2017 with timeline of anthrome changes from 10,000 BCE to 2017 CE. From Ellis et al. (2021)

    Major anthromes

    Anthromes include dense settlements (urban and mixed settlements), villages, croplands, rangelands and semi-natural lands and have been mapped globally using two different classification systems, viewable on Google Maps and Google Earth. There are currently 18 anthropogenic biomes, the most prominent of which are listed below.

    Dense settlements

    Dense settlements are the second most densely populated regions in the world. They are defined as areas with a high population density, though the density can be variable. The population density, however, never falls below 100 persons/km, even in the non-urban parts of the dense settlements, and it has been suggested that these areas consist of both the edges of major cities in underdeveloped nations, and the long standing small towns throughout western Europe and Asia. Most often we think of dense settlements as cities, but dense settlements can also be suburbs, towns and rural settlements with high but fragmented populations.

    Villages

    Villages are densely populated agricultural landscapes, many of which have been inhabited and intensively used for centuries to millennia.

    Croplands

    Croplands are another major anthrome throughout the world. Croplands include most of the cultivated lands of the world, and also about a quarter of global tree cover. Croplands which are locally irrigated have the highest human population density, likely due to the fact that it provides crops with a constant supply on water. This makes harvest time and crop survival more predictable. Croplands that are sustained mainly from the local rainfall are the most extensive of the populated anthromes, with annual precipitation near 1000 mm in certain areas of the globe. In these areas, there is sufficient water supplied by the climate to support all aspects of life without hardly any irrigation. However, in dryer areas, this method of agriculture would not be as productive.

    Rangelands

    Rangelands are a very broad anthropogenic biome group that has been described according to three levels of population density: residential, populated and remote. The Residential rangeland anthrome has two key features: its population density is never below 10 persons per square kilometre, and a substantial portion of its area is used for pasture. Pastures in rangelands are the most dominant land cover. Bare earth is significant in this anthrome, covering nearly one third of the land for every one square kilometer. Rangeland anthromes are less altered than croplands, but their alteration tends to increase with population. Domesticated grazing livestock are typically adapted to grasslands and savannas, so the alteration of these biomes tends to be less noticeable.

    Cultured lands

    Cultured anthromes are landscapes shaped by low levels of intensive land use and substantial to very low density populations. The Cultured anthrome classification was introduced in 2021to replace analogous classifications, "Seminatural" (2010 classification) and "Forested" (original 2008 classification). Cultured woodland anthromes are woodland biomes shaped by land use and human inhabitation, and their population densities are usually less than 3 persons/km². Many cultured woodlands are secondary forests that act as carbon sinks as a result of ongoing regrowth of woody vegetation. Some cultured woodlands are partially cleared for agriculture, including domestic livestock, and to utilize timber. Cultured dryland anthromes are dryland biomes shaped by land use and human inhabitation.

    Anthromes are mosaics of intensively used and cultured lands

    Indoor

    Very few biologists have studied the evolutionary processes at work in indoor environments. Estimates of the extent of residential and commercial buildings range between 1.3% and 6% of global ice-free land area. This area is as extensive as other small biomes such as flooded grass-lands and tropical coniferous forests. The indoor biome is rapidly expanding. The indoor biome of Manhattan is almost three times as large, in terms of its floor space, as is the geographical area of the island itself, due to the buildings rising up instead of spreading out. Thousands of species live in the indoor biome, many of them preferentially or even obligatorily. The only action that humans take to alter the evolution of the indoor biome is with cleaning practices. The field of indoor biomes will continue to change as long as our culture will change.

    Aquatic

    Managed aquatic biomes or aquatic anthromes have rarely been studied as such. They range from fish ponds, marine shrimp and benthic farming sites to large tracts of land such as parts of the Guadalquivir Marshes in Andalusia, Spain.

    Implications of an anthropogenic biosphere

    Humans have fundamentally altered global patterns of biodiversity and ecosystem processes. It is no longer possible to explain or predict ecological patterns or processes across the Earth without considering the human role. Human societies began transforming terrestrial ecology more than 50 000 years ago, and evolutionary evidence has been presented demonstrating that the ultimate causes of human transformation of the biosphere are social and cultural, not biological, chemical, or physical. Anthropogenic biomes offer a new way forward by acknowledging human influence on global ecosystems and moving us toward models and investigations of the terrestrial biosphere that integrate human and ecological systems.

    Challenges facing biodiversity in the anthropogenic biosphere

    Extinctions

    Over the past century, anthrome extent and land use intensity increased rapidly together with growing human populations, leaving wildlands without human population or land use in less than one quarter of the terrestrial biosphere. This massive transformation of Earth's ecosystems for human use has occurred with enhanced rates of species extinctions. Humans are directly causing species extinctions, especially of megafauna, by reducing, fragmenting and transforming native habitats and by overexploiting individual species. Current rates of extinctions vary greatly by taxa, with mammals, reptiles and amphibians especially threatened; however there is growing evidence that viable populations of many, if not most native taxa, especially plants, may be sustainable within anthromes. With the exception of especially vulnerable taxa, the majority of native species may be capable of maintaining viable populations in anthromes.

    Conservation

    Anthromes present an alternative view of the terrestrial biosphere by characterizing the diversity of global ecological land cover patterns created and sustained by human population densities and land use while also incorporating their relationships with biotic communities. Biomes and ecoregions are limited in that they reduce human influences, and an increasing number of conservation biologists have argued that biodiversity conservation must be extended to habitats directly shaped by humans. Within anthromes, including densely populated anthromes, humans rarely use all available land. As a result, anthromes are generally mosaics of heavily used lands and less intensively used lands. Protected areas and biodiversity hotspots are not distributed equally across anthromes. Less populated anthromes contain a greater proportion of protected areas. While 23.4% of remote woodland anthrome is protected, only 2.3% of irrigated village anthrome is protected. There is increasing evidence that suggests that biodiversity conservation can be effective in both densely and sparsely settled anthromes. A combination of land sharing and land sparing in working landscapes and multifunctional landscapes are increasingly popular as conservation strategies.

    Saturday, February 24, 2024

    Human rights defender

    From Wikipedia, the free encyclopedia

    A human rights defender or human rights activist is a person who, individually or with others, acts to promote or protect human rights. They can be journalists, environmentalists, whistleblowers, trade unionists, lawyers, teachers, housing campaigners, participants in direct action, or just individuals acting alone. They can defend rights as part of their jobs or in a voluntary capacity. As a result of their activities, human rights defenders (HRDs) are often subjected to reprisals including smears, surveillance, harassment, false charges, arbitrary detention, restrictions on the right to freedom of association, physical attack, and even murder. In 2020, at least 331 HRDs were murdered in 25 countries. The international community and some national governments have attempted to respond to this violence through various protections, but violence against HRDs continues to rise. Women human rights defenders and environmental human rights defenders (who are very often indigenous) face greater repression and risks than human rights defenders working on other issues.

    In 1998, the United Nations issued their Declaration on Human Rights Defenders to legitimise the work of human rights defenders and extend protection for human rights activity. Following this Declaration, increasing numbers of activists have adopted the HRD label; this is especially true for professional human rights workers.

    Definition

    The term human rights defender (HRD) became commonly used within the international human rights community after the UN General Assembly issued the Declaration on the Right and Responsibility of Individuals, Groups and Organs of Society to Promote and Protect Universally Recognised Human Rights and Fundamental Freedoms (A/RES/53/144, 1998), commonly known as the Declaration on Human Rights Defenders. Prior to this Declaration, activist, worker, or monitor were more common terms for people working to defend human rights. The Declaration on Human Rights Defenders created a very broad definition of human rights defenders to include anyone who promotes or defends human rights. This broad definition presents both challenges and benefits to stakeholders and donors seeking to support HRD protection programs, as more precise definitions exclude some categories of HRDs, but such broad definition also leaves much room for interpretation and can make it difficult to establish HRD status for some at-risk individuals.

    In 2004, the Office of the United Nations High Commissioner for Human Rights issued Fact Sheet 29 to further define and support human rights defenders. This document states that, "no 'qualification' is required to be a human rights defender," but that the minimum standards for HRDs are acceptance of the universality of human rights and non-violent action.

    Some researchers have attempted to demarcate categories of human rights defenders for the purpose of better understanding patterns of HRD risks. Such categorisation may discern professional vs. non-professional activity, or differentiate based on the specific rights that are being defended such as the rights of women, or indigenous land rights.

    Self identification

    Self-identification as a human rights defender is more common among professional human rights advocates who work within established institutions, governments, or NGOs. Individuals who work outside of these systems commonly self-identify as 'activists', 'leaders', or by a broad range of other terms instead of human rights defenders, even when their activity falls clearly within the scope outlined by the UN Declaration on Human Rights Defenders. Use of the HRD identity could benefit human rights activists by legitimising their work and facilitating access to protective measures. Use of the HRD identity can also be counterproductive by directing attention to particular individuals rather than focusing on the collective nature of their work, which may also have the effect of further endangering these individuals.

    Threats to human rights defenders

    Human rights defenders (HRDs) face severe repression and retaliation from government and private actors including the police, military, local elites, private security forces, right-wing groups, and multi-national corporations. Abuses include threats, arbitrary arrest and detainment, harassment, defamation, dismissal from jobs, eviction, disappearance, and murder. HRDs who work on women's rights (WHRDs) or who challenge cultural gender norms run increased risks compared to other HRDs, as do less prominent workers in remote areas. Environmental human rights defenders (EHRDs) who work on environmental rights, land rights, and indigenous rights issues also face greater threats than other HRDs; in 2020 69% of the HRDs killed globally were working on these issues.

    A report published by Front Line Defenders in 2020 found that at least 331 HRDs were murdered that year in 25 countries. Although indigenous people only account for about 6% of the global population, approximately 1/3 of these murdered HRDs were indigenous. In 2019, 304 HRDs were murdered in 31 countries. Global Witness reported that 1,922 EHRDs were killed in 52 countries between 2002 and 2019. 80% of these deaths were in Latin America. Approximately 1/3 of the EHRDs reported killed between 2015 and 2019 were indigenous. Documentation of this violence is incomplete, and for every death there may be as many as a hundred cases of severe repression such as detainment, eviction, defamation, etc.

    Research conducted by the Business and Human Rights Resource Center documented a 34 percent increase worldwide in attacks against human rights activists in 2017. The figures included 120 suspected murders and hundreds of incidents that involved assault, bullying, and threats. There were 388 attacks in 2017 compared to only 290 in 2016. The same study identified human rights defenders connected to agribusiness, mining, and renewable energy sectors (EHRDs) as those in greatest danger. Lawyers and members of environmental groups were also at risk.

    UN Declaration on Human Rights Defenders

    The United Nations Declaration on the Right and Responsibility of Individuals, Groups and Organs of Society to Promote and Protect Universally Recognized Human Rights and Fundamental Freedoms (A/RES/53/144) on December 9, 1998, commonly known as the Declaration on Human Rights Defenders, is the first UN instrument to legitimise and define human rights defenders, as well as the right and responsibility for everyone to protect human rights.

    The Declaration is not legally binding, but it articulates rights established by existing human rights treaties and applies them to human rights defenders in order to legitimise their work and extend protection of HRDs. Under the Declaration, a human rights defender is anyone who works to promote or protect human rights: whether professionally or non-professionally; alone or as part of group or institution.

    The Declaration articulates existing rights in a way that makes it easier to apply them to human rights defenders. The rights protected under the Declaration include, among others, the right to develop and discuss new human rights ideas and to advocate their acceptance; the right to criticise government bodies and agencies and to make proposals to improve their functioning; the right to provide legal assistance or other advice and assistance in defence of human rights; the right to observe fair trials; the right to unhindered access to and communication with non-governmental and intergovernmental organisations; the right to access resources for the purpose of protecting human rights, including the receipt of funds from abroad; and the rights of free expression, association and assembly.

    The Declaration indicates that states have a responsibility to implement and respect the provisions of the Declaration and emphasises the duty of the state to protect HRDs from violence, retaliation and intimidation as a consequence of their human rights work. The Declaration also places responsibility to protect human rights at the individual level and especially upon individuals in professions that may affect human rights such as law enforcement, judges, etc.

    Women human rights defenders

    Women human rights defenders (WHRDs) are women who defend human rights, and defenders of all genders who defend the rights of women and rights related to gender and sexuality. Their work and the challenges they face have been recognized by a United Nations (UN) resolution in 2013, which calls for specific protection for women human rights defenders.

    This is the logo for the Women Human Rights Defenders International Coalition that represents the coming together and discussing problematic issues dealing with human rights for all.

    A woman human rights defender can be an Indigenous woman fighting for the rights of her community, a woman advocating against torture, an LGBTQI rights campaigner, a sex workers’ rights collective, or a man fighting for sexual and reproductive rights.

    Like other human rights defenders, women human rights defenders can be the target of attacks as they demand the realization of human rights. They face attacks such as discrimination, assault, threats, and violence within their communities. Women human rights defenders face additional obstacles based on who they are and the specific rights they defend. This means they are targeted just because they are women, LGBTI people or for identifying with their struggles. They also face additional obstacles connected with Institutional discrimination and inequality and because they challenge, or are seen to be challenging, patriarchal power and social norms. They are more at risk of facing gender based violence in the home and the community, and sexist, misogynistic, homophobic, trans-phobic threats, smears and stigmatization, as well as exclusion from resources and power.  International Women Human Rights Defenders Day has been celebrated each 29 November since 2006.

    In 2017, female activists who were killed because of their advocacies and activities in defending human rights were honored during the International Women Human Rights Defenders' Day. Those murdered criticized corruption and other forms of injustice, protect their lands from governments and multinational corporations, and upheld the rights of lesbians, gays and transgender individuals.

    Environmental human rights defenders

    Environmental human rights defenders or simply environmental defenders, have been defined by the UN Environment Programme as, "defenders carrying out a vast range of activities related to land and environmental rights, including those working on issues related to extractive industries, and construction and development projects." They also state that environmental defenders are, "defending environmental rights, including constitutional rights to a clean and healthy environment, when the exercise of those rights is being threatened whether or not they self-identify as human rights defenders. Many environmental defenders engage in their activities through sheer necessity."

    The use of the term Environmental defender (or Environmental human rights defender) by human rights organizations, the media, and academia is recent and associated with the UN Declaration on Human Rights Defenders. However, the approach and role of environmental defenders is closely related to earlier concepts developed as early as the 1980s such as environmental justice and environmentalism of the poor. Although these different terms have different origins, they converge around the re-establishment of land-based cultures, re-making of place for marginalized people, and protection of land and livelihood from activities such as resource extraction, dumping of toxic waste, and land appropriation. Since the 1998 UN Declaration, the term environmental defenders is increasingly used by global organizations and media to refer to this convergence of goals and analysis.

    Protection instruments

    Following the adoption of the Declaration on Human Rights Defenders in 1998, a number of initiatives were taken, both at the international and regional level, to increase the protection of defenders and contribute to the implementation of the Declaration. In this context, the following mechanisms and guidelines were established:

    In 2008, the Observatory for the Protection of Human Rights Defenders, a joint programme of the International Federation for Human Rights (FIDH) and the World Organisation Against Torture (OMCT), took the initiative to gather all the human rights defenders' institutional mandate-holders (created within the United Nations, the African Commission on Human and Peoples' Rights, the Inter-American Commission on Human Rights, Council of Europe, the Organisation for Security and Cooperation in Europe, the European Union) to find ways to enhance coordination and complementarities among themselves and with NGOs. In 2010, a single inter-mechanisms website was created, gathering all relevant public information on the activities of the different human rights defenders' protection mandate-holders. It aims to increase the visibility of the documentation produced by the mechanisms (press releases, studies, reports, statements), as well as of their actions (country visits, institutional events, trials observed).

    In 2016, the International Service for Human Rights published the 'Model National Law on the Recognition and Protection of Human Rights Defenders'. This document provides authoritative guidance to states on how to implement the UN Declaration on Human Rights Defenders at the national level. It was developed in collaboration with hundreds of defenders and endorsed by leading human rights experts and jurists.

    Several countries have introduced national legislation or policies to protect human rights defenders including Colombia, Brazil, Mexico, and Guatemala; however, key challenges in implementation remain.

    Awards for human rights defenders

    Electronic mapping

    Electronic mapping is a newly developed tool using electronic networks and satellite imagery and tracking. Examples include tactical mapping, crisis mapping and geo-mapping. Tactical mapping has been primarily used in tracking human rights abuses by providing visualization of the tracking and implementation monitoring.

    Examples of HRDs

    In 2017, Human rights lawyer Emil Kurbedinov, a Crimean Tatar, won the 2017 Award for Frontline Human Rights Defenders at Risk. Kurbedinov has been an avid defender of civil society militants, mistreated Crimean Tatars, and members of the media. He documents violations of human rights during searches of activists' residences as well as emergency responses. In January 2017, the Crimean Center for Counteracting Extremism arrested and detained the lawyer. He was taken to a local facility of the Russian Federal Security Service for questioning. A district tribunal ruled that Kurbedinov was guilty of doing propaganda work for terrorist groups and organizations. He was sentenced to 10 days of imprisonment.

    See also

    Lie group

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