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El supuesto origen del texto hebreo y su relación con otras versiones del tratado

Ecosystems on the South African west coast provide a number of resources including food, minerals and oil and gas. The west coast therefore supports large commercial fishing and mining industries highlighting the economic importance of this area (Sink et al. 2012).

However, these commercial activities also present a threat to biodiversity. It is therefore

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imperative to reach a compromise which allows for both the protection of biodiversity and the continuation of commercial activities.

Commercial activities on the west coast include diamond mining, oil and gas exploration and demersal trawl fishing. The effects of diamond mining and demersal trawl fishing have been quantified on the west coast (Savage et al. 2001, Steffani 2007, Atkinson et al. 2011).

However, these impact studies highlighted concerns about the lack of baseline information.

Differences between impacted and control sites could not be assessed in the context of the general variation in biological communities on the continental shelf since this has not yet been investigated (Steffani 2007). In addition a baseline is lacking, since diamond mining and the demersal trawl fishery have been in operation since the early 1900s and the 1920s respectively (Griffiths et al. 2005). The lack of foundational understanding of macrofaunal community or species distributions has made it difficult to properly assess the impacts of various human activities (Steffani 2007, Atkinson et al. 2011).

The spatial extent of each user or threat has been mapped for the entire Exclusive Economic Zone of South Africa based on the best available data (Sink et al. 2012). Activities other than fishing and mining include naval activities, dumping of waste, placement of submarine cables and shipping. These mapped layers will be combined into a single cost layer which quantifies the cost of rezoning a particular area for conservation rather than the current use, commercial or not. This map will be developed in Chapter 8, where it will be incorporated into a systematic conservation plan.

Currently, a very small fraction of the west coast is formally protected in marine protected areas (MPAs) or management zones (Sink et al. 2012). Marine protected areas are limited to Cape Point, the West Coast National Park and Sixteen-mile beach (Fig. 2.8). All these MPAs are coastal, in depths shallower than 30 m, which leaves the entire offshore region of the west coast unprotected (Sink et al. 2012). The South African National Protected Area Expansion Strategy aims to expand the protection to 20 % of each habitat over the next 20 years by proclaiming new MPAs (Government of South Africa 2010) especially in the offshore and the northern part of the west coast where there is no protection at all (Sink et al. 2012).

A previous attempt to proclaim an MPA off the west coast (which was proposed in 2004) was met with great resistance from the fishing and mining industries operating in the area,

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as well as the Department of Minerals and Energy (Sink 2007). One of the objections raised by industry was that the scientific basis for the nominated area was not clear or robust. It is thus pertinent to conduct foundational research in order to develop a more scientifically robust nomination for a west coast MPA.

Figure 2.8: Marine protected areas on the South African West Coast (Sink et al.

2012). “Other MPAs” refer to management areas where some extraction activities are allowed.

No-take MPAs Other MPAs

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Systematic conservation planning in the marine environment is improving as better models are developed and tested (Carwardine et al. 2008, Game et al. 2008) and in South Africa as data are constantly added to these plans. The first South African National Marine and Coastal (SANMC) habitat classification system and integrated maps were recently developed (Sink et al. 2012). Thus far, most targets have been based on heuristics due to the limited data available, however it is a national priority to undertake scientific research to support conservation target setting for marine habitats in South Africa (Sink et al. 2012, Harris et al.

in press), for example Harris et al. (in press). In addition, marine unconsolidated sediment habitats were not considered vulnerable, so they were included in biodiversity plans for representation only (Clark and Lombard 2007, Lombard et al. 2007). A national beach classification has recently been developed (Harris et al. 2010), which was verified and tested with biological data (Harris 2012). Harris (2012) revealed that despite the perception of robustness/resilience, South African beaches were under significant threat. Through a data intensive exercise, the standard 20 % biodiversity target was deemed too low to ensure the protection of South Africa’s beaches, and a 27 % target was derived instead.

Harris (2012) then produced the first ecosystem-based conservation plan for South African beaches. This thesis will produce the first systematic conservation plan for the South African west coast subtidal unconsolidated sediments.

In this thesis, the South African west coast is used as a case study for the development of habitat classifications, setting of habitat-specific targets and production of an ecosystem-based systematic conservation plan for marine unconsolidated sediments. Since the physical processes on the west coast are similar to that of other Eastern Boundary Upwelling Regions, the results of this study will be applicable elsewhere.

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Defining seascapes for marine unconsolidated shelf