Different groups of people will often have different reasons for conserving specific habitats and species. Some people will value a tree for its beauty whereas others may value it for the resources it provides e.g. fruit and timber.
There are also different approaches that can be taken to the conservation of biodiversity such as:
Many conservation strategies will incorporate a number of these approaches to maximize the probability of success.
The resources available to help conservation also vary from place to place. More economically developed countries (MEDCs) can afford to spend more money on biodiversity conservation. They have more advanced technological tools and are often home to world leading institutes on biological conservation. The world’s biodiversity is not distributed evenly, a large amount of the biodiversity is located in biological hotspots within less economically developed countries (LEDCs). To attempt to address this inequity, various conservation groups have formed to help share resources and expertise.
Figure 1. Map illustrating distribution of LEDCs and biodiversity hotspots.
It can be difficult to keep conservation continually on the political agenda and ensure that there is sufficient funding. We live in a world where marketing, advertising, peer pressure and individual desire encourage many of us to use large amounts of resources at the expense of our environment. We often fail to see the link between consumerism, environmental degradation and the loss of biodiversity. The conservation of a threatened species in a remote part of the world may be considered of little value by some people.
Figure 2. Tiger species under threat from extinction.
Would the loss of tigers in the wild be of concern to you? What are the reasons for your response?
To effectively use the limited resources we need to ensure there are collaboration and cooperation at international, national and local level.
This is a question that is frequently asked. Why be concerned about our biodiversity and spend resources, time and effort to preserve it? As discussed in subtopic 3.1, we are dependent on this biodiversity, both directly and indirectly. Our lives and well-being are inextricably linked to the natural world. If you have not already, watch the CSIRO video 'What is biodiversity and why is it important?' shown in the introduction to biodiversity.
The reasons given for conservation of biodiversity vary and will depend on Environmental Value Systems. For example, deep ecologist with an ecocentric view would argue that it is our moral duty to conserve biodiversity and that every species has biorights, the right to exist. Deep ecologists adopt a holistic world view, valuing how biodiversity is interconnected and believe that the spiritual and aesthetic value is important to human well-being. At the other extreme of the scale, Cornucopians with a technocentric view would argue that exploitation and loss of biodiversity is acceptable and that human ingenuity will help replace any lost resources. Environmental managers with an anthropocentric view would consider the ecological environment, economic and social aspects with the aim of achieving sustainable development.
Figure 1. Sustainable development is achieved through consideration of interaction of environment, economic and social factors.
The reasons for biodiversity conservation can be grouped into various categories. Environmental managers often adopt an economic approach and divide the reasons according to their utilitarian and non-utilitarian values. Utilitarian value is where there is an economic value associated with the use of resources and non-utilitarian value is when use does not have any economic value.
Utilitarian values include:
Non-utilitarian values include:
The Millennium Ecosystem Assessment (2005) explicitly linked biodiversity to human well-being. The report categorized the values of biodiversity into the following groups:
You will find an image illustrating this here.
Who should take responsibility for conserving biodiversity? We all benefit from biodiversity and also contribute to its demise.
Often for conservation initiatives to be effective they need to:
Decisions to conserve biodiversity are often made at international or national level and then implemented at local level. International agreements are vital in some situations, for example where:
Figure 1. Animal crossing the Mara River during the great migration between Tanzania and Kenya.
There are many organizations around the world that campaign and work towards conserving biodiversity. These include intergovernmental organizations and non-governmental organizations.
Non-governmental organizations (NGOs) are non-profit, voluntary organizations usually funded by charitable donations and membership fees. The can vary from being focused on one specific problem in one location (e.g. Brainforest is focused on protecting rainforest in Gabon) to working at an international level focusing on a range of related concerns e.g. WWF, Birdlife International, Greenpeace and Friends of the Earth.
Important
You should have knowledge of a NGO that is local to you. What are its aims and how does it hope to achieve them? Have they achieved any successes to date and if so, what key aspects have contributed to these successes?
As previously discussed in subtopic 1.1, the emergence of environmental NGOs began in the 1960s, when there were clear signs of the damage we humans were doing to the environment.
NGOs often try to change policies, legislation and behavior at the individual level in a variety of ways:
Figure 2. Protest against fracking activity which also gains media attention and raises public awareness.
Figure 3. On-site environmental education.
Intergovernmental organizations (IGOs) consist of members from different countries. They are funded by its members. E.g. the United Nations (UN) founded in 1945 currently consist of 193 members and has specialized agencies that are independent international organizations with their own specific aims e.g.:
The International Union for Conservation for Nature and Natural Resources (IUCN) is another IGO, whose members include 74 countries, 105 governmental agencies and 647 NGOs. The IUCN vision 'is a just world that values and conserves nature'.
Key features of IGOs include:
Examiner Tip
Ensure you are able to compare and contrast the roles of a named NGO and IGO in conserving biodiversity.
As global resources and biodiversity are finite and human activities in one area can have consequences elsewhere, we need to ensure we work together and take a holistic approach to biodiversity conservation. Intergovernmental organizations often attempt to address global issues through agreements on policy and action to be taken. However, not all nations have to agree to comply or may at a later stage decide to withdraw which could undermine the action that is taken elsewhere. In addition, the level of enforcement within each nation can vary; with limited resources available for some countries conservation of biodiversity may be lower down on their list of national priorities.
In addition to obtaining agreement from nations to take action within their own country, the conventions above are increasingly promoting collaboration between nations to help conserve biodiversity. Examples from the Convention on Biological Diversity (CBD) include (i) consortium of scientific partners, (ii) South-south cooperation and (iii) triangular cooperation.
In order to help achieve targets within the CBD strategic plan, a consortium of scientific partners was set up in 2006. This originally consisted of six leading scientific institutions that were able to share their expertise and experience to help develop education and training opportunities in less economically developed countries (LEDCs). More than 20 scientific institutes from across the world have now become partners of this consortium.
Figure 1. Member of consortium of scientific partners: Royal Botanical Gardens, Kew in London has one of the largest plant and seed collections in the world.
The CBD strategic plan for 2011-2020 includes the need of south-south and triangular cooperation. ‘South’, refers to less economically developed countries (LEDCs) and ‘north’ to more economically developed countries (MEDCs).
Figure 2. Countries designated as either north or south.
The CBD strategic plan recognizes that through traditional north-south countries, some LEDCs countries have built up considerable knowledge, experience and expertise on biodiversity conservation. Hence these countries are now in a position to also help other LEDCs, though exchange of knowledge, technology and resources.
Triangular cooperation consists of collaboration between two or more LEDCs and a third party which could be a MEDCs or organization with the appropriate knowledge and resources.
Species conservation has received significant attention over the years. For more than half a century environmental movements have used large species such as whales and tigers to raise public awareness about the threats to biodiversity and the environment.
Figure 1. The World wildlife fund for Nature uses the Giant Panda as its emblem.
Species used as symbols of conservation are known as flagship species. They are typically charismatic and large animals. Action taken to improve the survival of flagship species can also benefit the whole ecosystem.
Other important groups of species in conservation biodiversity include:
Figure 2. Wolves are a keystone species, in their absence deer numbers increase preventing seedlings growing into trees and providing habitats for birds and other species.
When species numbers are low, how can we try to conserve them? Approaches taken to conservation are wide ranging and two approaches include:
To prevent a species becoming extinct, the reasons for species loss need to be addressed. For example, if poaching is the main threat, it is necessary to stop the poachers. In some situations where the habitat has been degraded or lost, habitat restoration could be required which can be a difficult and lengthy process.
The role of legislation including international agreements to remove threats to species was discussed in the previous section. In subtopic 3.3 we also considered the conservation of humpback whales and Lear’s MaCaw parrot that demonstrate how international agreements and legislation can reduce over-exploitation. In summary:
Poaching activities can be very difficult to stop. For those living in poverty, it could be one of only a few ways they are able to earn any money. For others the deterrent of fines and imprisonment is not sufficient to compete with high potential profits.
CITES aims to ensure international trade does not endanger threatened species. It is a tool that can be used to support conservation strategies.
Strengths of CITES:
Weaknesses of CITES:
The African savanna elephant is the world’s largest terrestrial mammal and is categorized as ‘vulnerable’ by the IUCN Red List.
In the past colonists in Africa hunted elephants for trophies and tusks and by the 1940s elephants had become endangered in some regions. The solution to declining numbers was to exclude local people and develop game reserves that attracted tourist from around the world. Revenue from tourism helped conserve these new parks.
In the 1970s the price of ivory rose and in some countries such as Kenya the associated increase in ivory poaching resulted in numbers of elephants falling dramatically. The WWF estimated that between 1973 and 1989, the number of elephants in Kenya declined by 85%. Richard Leakey (at the time Head of Wildlife Services) established a "shoot to kill poacher policy" and lobbied to ban the ivory trade. In 1989 against opposition from some countries, elephants were moved to Appendix I of CITES and trade in ivory banned. The demand for ivory fell and so did poaching. Where there was adequate protection, elephant numbers started to recover. However, in areas where the elephants are not so securely protected an illegal market for ivory and elephant meat has continued. In recent years there has been an increase in poaching and illegal trading through organized crime syndicates.
In southern Africa, elephant populations are large and continuing to grow. This increasing elephant population in some areas has led to competition with the growing human populations. Elephants can be highly destructive, destroying crops, properties and killing people. Where elephants exceed the carrying capacity, the high feeding rate (average of 200Kg of vegetation per day) is resulting in damage to the habitat and a decline in overall biodiversity.
Control of elephant numbers to conserve biodiversity is important. Methods used have included:
In the past money from ivory sales has been used to run and manage national parks. Countries in southern Africa want to lift the CITES ban so they can use the money raised for conservation projects. However, there is concern that if the ban is removed poaching will increase in areas such as East Africa, where the populations are not so healthy. Some people also believe it is morally wrong to lift the ivory ban.
Figure 3. African savanna elephant populations - ivory ban is opposed in some countries where population numbers are large and expanding.
This can be a long and expensive process in which organisms are taken out of their natural habitat in order to be conserved. The application of ex-situ conservation to plants and animals is discussed below.
Samples of plant species under threat may be removed from their habitat and placed in botanical gardens or herbariums. Organizations involved with ex-situ plant conservation are able to maintain the genetic stock and are usually extensively involved with biodiversity conservation programmes (e.g. role of Royal Botanical Gardens, Kew in the CBD Consortium of Scientific Partners discussed in the previous section). Scientists are able to conduct research and extend our knowledge and understanding about these plants.
The dormant stage of seeds also allows for long term storage and they can be preserved for future use. The Millennium seed bank project at Kew and the Nordic Gene Bank for seeds in Svalbard, Norway, both have extensive on-going seed collections. Where appropriate for some plants, pollen preservation or tissue preservation is used.
This usually involves removal of the species from their natural habitat and placing them into captivity (e.g. zoo or aquarium) as part of a breeding programme to increase numbers. In some cases reproductive technology can be used to achieve greater success rates. The aim is to reintroduce the species back into the wild where they can help repopulate the area.
Often species loss has occurred as a consequence of habitat degradation or loss. Therefore habitat restoration and protection must occur prior to re-introducing the animals back. The animals are unlikely to survive if the original threats are not eradicated.
Figure 4. Captive breeding and reintroduction programme has increased the number of Golden Lion Tamarins in the wild.
In order to protect species diversity, their habitats also need to be protected. In 2008 the International Union for Conservation of Nature (IUCN) defined a protected area as:
‘… a clearly defined geographical space, recognised, dedicated and managed, through legal or other effective means, to achieve the long term conservation of nature with associated ecosystem services and cultural values’.
There are many different types of protected areas around the world such as national parks, nature reserves and wilderness areas, each with varying levels of protection. The number of protected areas has increased over time rising from 13.4 million km2 in 1990 to more than 32 million km2 in 2014. They cover more than 15% of the earth's land surface and over 3% of the ocean area.
Reasons for designating a protected area include:
Two of the biggest sites are the Chagos Marine Protected Area south of the Maldives and Northeast Greenland National Park.
Figure 1. Location of Chagos and Northeast Greenland National Park
Protected areas play a vital role in conserving biodiversity. It is now also recognized the important functions ecosystems perform in the stability of our environment.
How can you maximize biodiversity conservation through design of a protected area? In 1975 Jared Diamond attempted to answer this question and his suggestions were adopted in 1980 by the IUCN in their World Conservation Strategy. Key features include reducing edge effect, selecting optimal shape and size, having a single large reserve rather than several small reserves, close proximity of reserves to each other and connections between reserves. It is also important to consider proximity of the reserve of any potential human influence.
Sometimes there is dramatic change in the composition of the vegetation at the boundary e.g. where an area is fenced and cleared around the reserve creating an ‘abrupt edge’. This clearance of land at the forest edge increases sunlight to the lower forest levels, increases temperature, lowers humidity and can result in an increase of air movement. These changes in abiotic factors can adversely affect the habitat conditions and threaten some species. Also the risk from predation and hunting by humans can increase near the edge.
To avoid the dramatic change in abiotic conditions at the edge of a reserve, a gradual change in vegetation away from the reserve is more favourable than an abrupt change.
The UNESCO Man and Biosphere Programme recommend the use of three distinct zones in designing protected areas:
Figure 2. UNESCO recommended zonation within a protected area.
The optimal shape is a circle because it has a minimum edge to area ratio. Also within a circle the centre will be further away from the edge than any other shapes of the same area.
Figure 3. Circle has the lowest perimeter and therefore the lowest amount of edge effect.
Larger reserves can in theory support more ecosystems, habitats and species so generally the larger the reserve the better. Also large or migratory animal species need bigger areas to provide adequate resources to support a viable population. Sometimes, small reserves are fragments of larger ecosystems and need to be carefully managed. For example, in the case of migratory species, movement between reserves may need to be considered and planned e.g. by examining past migratory routes and using this information to create suitable routes between reserves.
There has been considerable debate between scientists over whether a single large or several small (SLOSS) reserves covering the same area is better? The answer varies for individual species. Large species like elephants require large areas whereas for small plants and insects smaller areas could be suitable. Some species may be able to attain all their requirements for a viable population by moving between the smaller reserves. Notably, with several small reserves there will be a greater edge effect than having one large reserve.
Reserves can be connected using wildlife corridors which are areas of habitats that are retained or created for animals to move through.
Figure 4. Example of a wildlife corridor, a bridge connecting two forested areas within the Banff National Park, Canada.
Linking the reserves has various advantages:
There are also some disadvantages associated with wildlife corridors connecting reserves:
Activities within nearby human settlements may adversely affect behaviour of some species within the reserve. This can vary from noise disturbances, light pollution at night to atmospheric and aquatic pollution of a shared watershed. If reserves are near to human settlements, large animals may venture out of the reserve and raid crops and even attack people. Hence the proximity of reserves to urban areas needs to be carefully considered in the planning stages, with consideration of a buffer zone.
Establishing and running a protected area can be financially expensive, from the cost of buying the land to its management.
Historically creation of protected areas has often resulted in removal of people and communities. Compensation has varied but in some cases people have been left homeless and without any livelihood. In addition the heritage and culture of a community may be inextricably linked to the ecosystems they have been removed from. Attitudes have now changed and it is recognized that plans for protected areas should not increase the hardship of local people but consider them as partners, often with extensive knowledge about the ecosystem. Conservation strategies that utilize the knowledge and services of local communities are now becoming more popular.
Watch the following video and make notes on the activities and characteristics which contribute to the success of the Kristianstads Vattenrike Biosphere Reserve.
Figure 5. Location of Kristianstads Vattenrike biosphere reserve in Sweden.Kristianstads Vattenrike biosphere reserve in Sweden.
Source: Tuvendal, M., and T. Elmqvist. 2011. Ecosystem services linking social and ecological systems: river brownification and the response of downstream stakeholders. Ecology and Society 16(4): 21.
Can you give examples of the following using Kristianstads Vattenrike as a case study:
Examiner Tip
Ensure you are familiar with at least one example of a protected area which can be used to illustrate key characteristics of a successful project.
Key features of a successful protected area: