srijeda, veljače 25, 2015

Conservation prioritization

The time has come to do some more research on my thesis, which deals with identifying conservation priorities in the Galapagos Islands.

http://www.galapagostours.net/images/galapagos-map.jpg


The field of identifying conservation priorities is known as conservation prioritization, and can be defined as “the process of using spatial analysis of quantitative data to identify locations for conservation investment”[1], which isn’t applied only to protected areas, but can also pertain to management strategies and conservation activities outside them. One of the more important considerations in conservation prioritization is that of comprehensiveness, by which the ideal conservation area should contain the composition, structure and function representative of the biodiversity feature. The complementarity principle should also be considered, since it states that costs should be optimized while ensuring that all biodiversity features receive benefit; furthermore, prioritization should be designed for the long term, with considerations for cost-effectiveness and taking into account threats that biodiversity faces.

The prioritization is a socio-political process, in which the goals are determined by societal considerations, but one in which science is the key provider of technical information and options. Even though mapping of the relevant factors is in itself an important aspect of this process, it should not focus solely on this tool in order to design a successful conservation strategy, but also include stakeholders opinions, development of scenarios, of decision support systems, social marketing, facilitation and conflict resolution, institutional establishment, monitoring and management, to name a few. The scope of the current work, however, only includes the production of the prioritization map due to technical, political and economic restraints.

http://i.telegraph.co.uk/multimedia/archive/01692/galapagos_1692336c.jpg


The identification of conservation goals is the initial phase of the process, followed by identifying the variables (factors or system attributes) to be considered, which is a scientific and technical stage involving the understanding and describing of the dynamic relations that define the ecology of a system. The next phase requires the gathering of information of the previously defined factors, which should principally be spatial information; in the absence of georeferenced data, carefully selected proxies can be used. The final and critical phase is to perform the prioritization analysis itself by means of one of the two basic principles: scoring of factors or complementarity based approach.

A variety of software has been designed with the purpose of aiding in the process of conservation prioritization analysis, such as MARXAN, Zonation, C-Plan, Res-Net, and this current work will use one such tool (Environmental Risk Surface, ERS) in order to determine priority conservation areas in the Galapagos Islands. Literature pertaining to the ERS software is extremely limited, therefore the main basis for this investigation is the work of McPherson et al. (2008) and Lessmann et al. (2014), both assessing human impact on conservation. McPherson et al. use GIS tools to assign weight and distance of influence to several human activities and map its impacts, in order to identify optimal conservation areas in Jamaica. Lessmann et al., on the other hand, use GIS map the distribution of target species, include conservation feasibility costs, in order to identify conservation gaps in Ecuador. Both articles focus on conservation efforts while evaluating and mapping the effect of such human influences as population, roads, tourism, agriculture, mining, and will thus offer guidance in the judgment of their impact.

References
Ferrier, S., & Wintle, B. A. (2009). Quantitative approaches to spatial conservation prioritization : matching the solution to the need. In Spatial Conservation Prioritization. Quantitative Methods and Computational Tools (p. 328). New York: Oxford University Press. 
Knight, A. T., Cowling, R. M., Possingham, H., & Wilson, K. A. (2009). From theory to practice: designing and situating spatial prioritization approaches to better implement conservation action. In Spatial Conservation Prioritization. Quantitative Methods and Computational Tools (p. 328). New York: Oxford University Press.
Lessmann, J., Muñoz, J., & Bonaccorso, E. (2014). Maximizing species conservation in continental Ecuador: a case of systematic conservation planning for biodiverse regions. Ecology and Evolution, n/a–n/a. doi:10.1002/ece3.1102
McPherson, M., Schill, S., Raber, G., John, K., Zenny, N., Thurlow, K., & Sutton, H. (2008). GIS-based Modeling of Environmental Risk Surfaces (ERS) for conservation planning in Jamaica. Journal of Conservation Planning, 4, 60–89.

[1] Wilson, Cabeza, & Klein, C., 2009, pg. 16

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I may not have gone where I wanted to go, but I'm sure I ended up where I needed to be.