climate change on UAE - Stockholm Environment Institute-US Center
climate change on UAE - Stockholm Environment Institute-US Center
climate change on UAE - Stockholm Environment Institute-US Center
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
populate itself, and imbalances in the food-web,<br />
meaning that there is either not enough food for<br />
top predators or there are too few predators to<br />
c<strong>on</strong>trol the populati<strong>on</strong> of prey species. In these<br />
circumstances, the imbalances can quickly<br />
stack up synergistically in a positive feedback<br />
cycle: for example, as top predators dwindle,<br />
prey species multiply quickly and begin to<br />
deplete food sources for other species or <str<strong>on</strong>g>change</str<strong>on</strong>g><br />
the physical or chemical properties of their<br />
ecosystem. For example, overfishing of Codfish<br />
in the rich kelp (seaweed) forests of the Gulf of<br />
Maine allowed sea urchins to prosper, which in<br />
turn destroyed the kelp habitat (Jacks<strong>on</strong> et al,<br />
2001). Cod is now extinct in the North Atlantic,<br />
and the habitat has, for all intensive purposes,<br />
<str<strong>on</strong>g>change</str<strong>on</strong>g>d permanently.<br />
Habitat destructi<strong>on</strong> results in the loss of<br />
ecosystem area or an impedance in ecosystem<br />
functi<strong>on</strong>, and is, by far, the most pressing threat<br />
to biodiversity worldwide. Polluti<strong>on</strong> and habitat<br />
misuse can destroy or impede key elements of<br />
an ecosystem, lending to severe imbalances and<br />
loss of ecosystem functi<strong>on</strong>ality. For example,<br />
overgrazing in arid ecosystems comm<strong>on</strong>ly leads<br />
to the trampling of biogenic crusts and the loss<br />
of critical vegetati<strong>on</strong> cover, which, in turn, leads<br />
to increased runoff and erosi<strong>on</strong>, nutrient losses,<br />
and can promote invasive species.<br />
The direct loss of habitat by land use <str<strong>on</strong>g>change</str<strong>on</strong>g> can<br />
also result in the loss of biodiversity as parts of<br />
an ecosystem are transformed for another use,<br />
there is less area for the native ecosystem to<br />
use. The relati<strong>on</strong>ship between species diversity<br />
and area has been recognized since at least<br />
the early 20 th century, and was formalized by<br />
Williams (1964) and, later, Rosenzsweig (1995)<br />
as a logarithmic curve. In numerous studies, as<br />
larger areas are examined, the number of species<br />
increases (i.e. from a small plot to a c<strong>on</strong>tinent).<br />
Geographical c<strong>on</strong>straints, the ability to move,<br />
migrate, and compete, and the ability to<br />
escape small-scale disturbances all govern the<br />
relati<strong>on</strong>ship between area and speciati<strong>on</strong>.<br />
Within a specific type of biome or ecosystem, as<br />
the physical size of the ecosystem is reduced,<br />
the number of species which can be supported<br />
in the ecosystem is also reduced. Expansi<strong>on</strong><br />
of urban areas, deforestati<strong>on</strong>, sedimentati<strong>on</strong>,<br />
and agricultural expansi<strong>on</strong> are all mechanisms<br />
of direct habitat destructi<strong>on</strong>. Fragmentati<strong>on</strong><br />
restricts the ability for species to migrate or<br />
expand. Thus, even if total habitat space is<br />
large, but is subdivided into small fragments,<br />
the net effect results in small, n<strong>on</strong>-diverse (and<br />
often functi<strong>on</strong>ally deficient) ecosystems.<br />
Finally, <str<strong>on</strong>g>climate</str<strong>on</strong>g> <str<strong>on</strong>g>change</str<strong>on</strong>g> may already be<br />
resp<strong>on</strong>sible for some species losses and<br />
threatens to lead to rampant reducti<strong>on</strong>s in<br />
biodiversity globally. Climate <str<strong>on</strong>g>change</str<strong>on</strong>g> shifts the<br />
basic substrates up<strong>on</strong> which ecosystems rely:<br />
as temperatures increase and precipitati<strong>on</strong><br />
patterns are altered, ecosystems which used to<br />
thrive in <strong>on</strong>e regi<strong>on</strong> may be displaced to other<br />
areas or disappear altogether. For many biomes<br />
around the world, this shift may look like a mass<br />
movement of ecosystems towards the poles or<br />
higher elevati<strong>on</strong>s, while ecosystems already<br />
near the poles or at high elevati<strong>on</strong> may be lost<br />
completely.<br />
While the story is both complicated and<br />
uncertain, it is likely that many sedentary<br />
or n<strong>on</strong>-migrating species will be unable to<br />
move at the pace of <str<strong>on</strong>g>climate</str<strong>on</strong>g> <str<strong>on</strong>g>change</str<strong>on</strong>g>, and even<br />
migratory species may find their migratory<br />
routes falling out of synchr<strong>on</strong>y with weather<br />
and food patterns. For all of these reas<strong>on</strong>s, it<br />
is likely that <str<strong>on</strong>g>climate</str<strong>on</strong>g> <str<strong>on</strong>g>change</str<strong>on</strong>g> al<strong>on</strong>e will lead to<br />
significant biodiversity losses (Sala et al., 2000),<br />
and the effect will be compounded where there<br />
are already significant envir<strong>on</strong>mental stresses,<br />
such as those described previously (Thomas et<br />
al, 2004).<br />
8.1. Biodiversity and ecological<br />
thresholds<br />
In 2000, Sala and others predicted that<br />
“Mediterranean <str<strong>on</strong>g>climate</str<strong>on</strong>g> and grassland<br />
ecosystems likely will experience the greatest<br />
proporti<strong>on</strong>al <str<strong>on</strong>g>change</str<strong>on</strong>g> [loss] in biodiversity”<br />
by 2100 due to the combined influence of<br />
<str<strong>on</strong>g>climate</str<strong>on</strong>g> <str<strong>on</strong>g>change</str<strong>on</strong>g>, land use <str<strong>on</strong>g>change</str<strong>on</strong>g>, <str<strong>on</strong>g>change</str<strong>on</strong>g>s in<br />
atmospheric CO 2<br />
, and introduced (invasive)<br />
species. Except for far northern and southern<br />
latitudes, where <str<strong>on</strong>g>climate</str<strong>on</strong>g> <str<strong>on</strong>g>change</str<strong>on</strong>g> is expected to<br />
have the most significant impacts, <str<strong>on</strong>g>change</str<strong>on</strong>g>s in<br />
land use are expected to be resp<strong>on</strong>sible for the<br />
heaviest toll <strong>on</strong> biodiversity. According to the<br />
Sala et al. (2000) analysis, if we assume that<br />
interacti<strong>on</strong>s am<strong>on</strong>gst the drivers of biodiversity<br />
<str<strong>on</strong>g>change</str<strong>on</strong>g> are synergistic and multiplicative,<br />
164<br />
Climate Change Impacts, Vulnerability & Adaptati<strong>on</strong>