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Community-based management

From Wikipedia, the free encyclopedia

Community-based management (CBM) is a bottom up approach of organization which can be facilitated by an upper government or NGO structure but it aims for local stakeholder participation in the planning, research, development, management and policy making for a community as a whole.[1][2] The decentralization of managing tactics enables local people to deal with the unique social, political and ecological problems their community might face and find solutions ideal to their situation.[3][4][5] Overwhelming national or local economic, political and social pressures can affect the efficiency of CBM as well as its long term application.[6] CBM varies across spatial and temporal scales to reflect the ever-changing distinctive physical and/or human environment it is acting within. While the specifics of each practice might differ, existing research maintains that community based management, when implemented properly, is incredibly beneficial not only for the health of the environment, but also for the well-being of the stakeholders.[7][8][9][10][11]

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  • Hazard, Risk & Safety - Understanding Risk Assessment, Management and Perception
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Transcription

Hazard, Risk & Safety We all hear these terms on a daily basis. So and so a chemical, physical or a biological agent poses a risk; This or that product is a hazard or behaving a certain way is unsafe. A lot of the time “hazard” and “risk” are freely used to mean the same thing. However they are not. Hazard is the potential to cause harm. Risk on the other hand is the likelihood of harm in defined circumstances. But what does this actually mean? Let’s look at two examples First, Potassium Dichromate: it sounds scary and it is indeed a hazardous substance that is both toxic and carcinogenic. It is used in some cases to analyse exhaled breath for alcohol. For this purpose it is sealed in a tube. Therefore although it is intrinsically a hazardous substance, if used and managed as described, it presents little or no risk to people or the environment. Now let’s look at the opposite case. Flour would not be considered by many to be a hazardous substance. However, if a baker were to be exposed over a period of time to airborne flour, he/she could develop dermatitis, conjunctivitis, rhinitis and even asthma. So even something that is considered a low hazard can present substantial risk and vice versa. Risk is always a probability, influenced by the level of exposure. To evaluate the risk we have to take many factors into consideration. How, where, how much and how long one can be exposed to the hazard are all things to be taken into account. Toxicological research can map the potentially harmful properties of a product, be it chemical, physical or biological and it can also set a limit under which exposure will have no effect. Based on this research, a risk can be calculated based on frequency, conditions and length of exposure. However, some types of risks are hard to quantify, either because of the complexity of a system, like in the case of climate change, or because we still lack some of the tools to measure it, like in the case of nano-materials. When there is no consensus on the level of risk, policy makers sometimes who have the responsibility to decide on safety levels apply a precautionary principle. “When sufficiently established elements suggest that an activity is seriously expected to potentially produce irreversible damage to health or the environment, measures should be taken even if the definite proof or the causal link is not yet formally established with absolute certainty.” (Communication of the EU in 2000) It is best to err on the side of caution. Nevertheless, the precautionary decisions should remain proportional to this potential but uncertain risk, and be reevaluated when new data become available. Indeed The Proportionality Principle is and should be at the base of most legal thinking. Now, how can we manage a risk? Risk can thus be managed by limiting exposure to a danger and by the adoption of risk-reduction measures. Prevention might be a better idea to reduce risk. For example driving has been made safer by speed limits, the use of seatbelts, bumpers, airbags, driver assistance systems etc. But what is considered safe? Acceptable safety levels greatly depend on where you are on the planet, culture, socio-economic criteria and the sector. Similarly, the safety limit adopted for a pesticide like DDT has to be balanced with its importance in safeguarding health or food resources in some regions of the world. For each specific case, an acceptable safety level has to be determined. This is thus not only a technical, but also a “political” decision. Even if the previous steps are logical, what is considered safe has to take into account the perception and acceptance of risk. These tend to be emotional and rational at the same time. For example flying is commonly considered a greater risk than driving although all statistics point to the contrary. Moreover, once a perception of risk sets in, it is very hard to change. Even if all evidence points to the opposite. For example: fear can be fuelled by debatable science and poor or even sensationalist interpretation of a study by the media. A very limited study that indicates that Substance A could be harmful to mice and would merit further research quickly turns into a ‘Substance A kills’ headline. Once fear sets in, even if risk is not proven, the precautionary principle is often pulled out of the hat. In a nutshell, risk and perception of risk are not always aligned; this can make political decisions difficult to make, in these cases it is especially important to base them on facts rather than on opinions. These facts can be gathered from scientific reports published by reference institutions, but these reports are often written in a technical language that is not accessible to anyone but the specialists. GreenFacts offers faithful summaries of those reports so that non-specialists can get the information they need to build their own opinion.

Cultural change and sustainability

Social ideologies and cultural divides between regions and often within regions challenge the implications of CBM.[12] The process of identifying stakeholders and maintaining policies needs to fluctuate culturally to imply the sustainability of CBM.[13] Scrutiny of inequality issues and the level of self-management a community will take on needs to be evaluated for each CBM implementation.[14] Therefore, cultural beliefs can be communicated politically whether the community agrees with CBM or not.[15]

Natural resources

The community-based management concept is often integrated into the conservation and development projects of natural resources.[16] Referred to as community-based natural resources management (CBNRM), these projects aim to develop a partnership between wildlife and communities while generating a revenue to benefit the community as well as its resources management.[17]

See also

References

  1. ^ Senyk, J. "Lessons from the Equator initiative: Community-based Management by Pred Nai Community Forestry Group in the Mangroves of Southeastern Thailand" (PDF). Winnipeg: Natural Resources Institute. University of Manitoba. Retrieved 30 October 2012.
  2. ^ Balint, P.J.; Mashinya, J. (2005). "The decline of a model Community-based conservation project: Governance, capacity, and devolution in Mahenye, Zimbabwe" (PDF). Geoforum. 37: 805–815. doi:10.1016/j.geoforum.2005.01.011.
  3. ^ Hackel, J.D. (1999). "Community Conservation and the Future of Africa's Wildlife". Conservation Biology. 13: 726–734. doi:10.1046/j.1523-1739.1999.98210.x.
  4. ^ Tocconi, L. (2007). "Decentralization, forests and livelihoods: Theory and narrative". Global Environmental Change. 17: 338–348. doi:10.1016/j.gloenvcha.2007.01.002.
  5. ^ Senyk, J. "Lessons from the Equator initiative: Community-based Management by Pred Nai Community Forestry Group in the Mangroves of Southeastern Thailand" (PDF). Winnipeg: Natural Resources Institute. University of Manitoba. Retrieved 30 October 2012.
  6. ^ Hackel, J.D. (1999). "Community Conservation and the Future of Africa's Wildlife". Conservation Biology. 13: 726–734. doi:10.1046/j.1523-1739.1999.98210.x.
  7. ^ Wollenberg, R.; Edmunds, D.; Buck, L. (2000). "Using Scenarios to Make Decisions About the Future: anticipatory learning for the adaptive co-management of Community Forests". Landscape and Urban Planning. 47: 65–77. doi:10.1016/s0169-2046(99)00071-7.
  8. ^ Sultana, P.; Abeyasekera, S. (2008). "Effectiveness of Participatory Planning for Community Management of Fisheries in Bangladesh". Journal of Environmental Management. 86: 201–213. doi:10.1016/j.jenvman.2006.12.027.
  9. ^ Banks, T.; Richard, C.; Ping, L.; Zhaoli, Y. (2003). "Community-Based Grassland Management in Western China". Mountain Research and Development. 23 (2): 132–140. doi:10.1659/0276-4741(2003)023[0132:cgmiwc]2.0.co;2.
  10. ^ Ellis, E.; Porter-Bolland, L. (2008). "Is Community-Based Forest Management More Effective than Protected Areas? A comparison of land use/land cover change in Two Neighboring study areas of the Yucatan Peninsula, Mexico". Forest Ecology & Management. 256: 1971–1983. doi:10.1016/j.foreco.2008.07.036.
  11. ^ Olsson, P.; Folke, C. (2001). "Local Ecological Knowledge and Institutional Dynamics for Ecosystem Management: A Study of Lake Racken Watershed, Sweden". Ecosystems. 4: 85–104. doi:10.1007/s100210000061.
  12. ^ Green, Maureen G.; Springer (2007). "Uneven Environmental Management: A Canadian Perspective". Environ Manage. 39 (1): 30–49. doi:10.1007/s00267-005-0159-5.
  13. ^ Green, Maureen G.; Springer (2007). "Uneven Environmental Management: A Canadian Perspective". Environ Manage. 39 (1): 30–49. doi:10.1007/s00267-005-0159-5.
  14. ^ Green, Maureen G.; Springer (2007). "Uneven Environmental Management: A Canadian Perspective". Environ Manage. 39 (1): 30–49. doi:10.1007/s00267-005-0159-5.
  15. ^ Green, Maureen G.; Springer (2007). "Uneven Environmental Management: A Canadian Perspective". Environ Manage. 39 (1): 30–49. doi:10.1007/s00267-005-0159-5.
  16. ^ Balint, P.J.; Mashinya, J. (2005). "The decline of a model Community-based conservation project: Governance, capacity, and devolution in Mahenye, Zimbabwe" (PDF). Geoforum. 37: 805–815. doi:10.1016/j.geoforum.2005.01.011.
  17. ^ Balint, P.J.; Mashinya, J. (2005). "The decline of a model Community-based conservation project: Governance, capacity, and devolution in Mahenye, Zimbabwe" (PDF). Geoforum. 37: 805–815. doi:10.1016/j.geoforum.2005.01.011.

External links

  • Community Based Eco Tourism Project in Cambodia Started by Wildlife Alliance (NGO) but mostly managed by a local committee. Wildlife Alliance aims to withdraw completely within a few years.
  • From the David Suzuki Foundation website: Fisheries That Work: Sustainability Through Community-Based Management [1]
This page was last edited on 12 August 2023, at 16:17
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