Naturally, at your service: - RSPB
Naturally, at your service: - RSPB
Naturally, at your service: - RSPB
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Two key fe<strong>at</strong>ures of the ecosystem<br />
<strong>service</strong> approach are th<strong>at</strong> <strong>service</strong>s<br />
only exist if somebody benefits and<br />
th<strong>at</strong> those beneficiaries include future<br />
gener<strong>at</strong>ions. On the l<strong>at</strong>ter point,<br />
tropical forests today provide the<br />
benefit of maintaining a liveable<br />
clim<strong>at</strong>e for future gener<strong>at</strong>ions. In<br />
terms of geography, <strong>service</strong>s deliver<br />
over multiple sp<strong>at</strong>ial scales.<br />
Identifying and valuing them depends<br />
on knowing how the <strong>service</strong>s are<br />
supplied and where the beneficiaries<br />
are loc<strong>at</strong>ed. The benefits of some<br />
<strong>service</strong>s can only be realised in the<br />
same place they are gener<strong>at</strong>ed.<br />
Other <strong>service</strong>s provide benefits, <strong>at</strong><br />
various scales, beyond their point of<br />
production. For example, the flood<br />
mitig<strong>at</strong>ion <strong>service</strong>s provided by<br />
saltmarshes benefit communities<br />
adjacent to the marsh, pollin<strong>at</strong>ion may<br />
have local or regional benefits while<br />
carbon sequestr<strong>at</strong>ion and biodiversity<br />
protection gener<strong>at</strong>e benefits globally.<br />
These possibilities are shown in the<br />
illustr<strong>at</strong>ion to the right.<br />
For management, it is also important<br />
to know how site-specific <strong>service</strong>s<br />
are. Some <strong>service</strong>s, like food<br />
production or recre<strong>at</strong>ional<br />
opportunities, can be delivered <strong>at</strong><br />
varying scales and in different<br />
loc<strong>at</strong>ions. Many regul<strong>at</strong>ory and<br />
supporting <strong>service</strong>s, on the other<br />
hand, rely on complex ecological<br />
processes so the scale and loc<strong>at</strong>ion<br />
cannot be easily influenced. For<br />
example, the maintenance of w<strong>at</strong>er<br />
regul<strong>at</strong>ory <strong>service</strong>s requires a<br />
landscape and land-use management<br />
approach across an entire w<strong>at</strong>ershed.<br />
Such <strong>service</strong>s pose particular<br />
challenges for planning, given their<br />
immovability and the fact th<strong>at</strong> their<br />
provision will seldom m<strong>at</strong>ch existing<br />
political boundaries.<br />
A similar challenge arises from<br />
ecosystem degrad<strong>at</strong>ion or potential<br />
restor<strong>at</strong>ion. Rarely will solutions<br />
respect political boundaries or be<br />
achievable over short time horizons.<br />
Establishing rules, rights and<br />
responsibilities <strong>at</strong> the range of<br />
sp<strong>at</strong>ial and temporal scales <strong>at</strong> which<br />
ecosystem <strong>service</strong>s deliver is a<br />
major challenge. Effective<br />
management requires a sp<strong>at</strong>ially<br />
explicit approach, working across<br />
boundaries. Success will depend<br />
on collabor<strong>at</strong>ion <strong>at</strong> several levels,<br />
from the local to the global.<br />
Diagram 2. The delivery of ecosystem <strong>service</strong>s<br />
1 2<br />
P/B<br />
3 4<br />
P<br />
B<br />
For environmental management,<br />
knowing wh<strong>at</strong> <strong>service</strong>s regions<br />
provide and how they flow over the<br />
landscape is necessary to balance<br />
the different demands – food, energy,<br />
clim<strong>at</strong>e change mitig<strong>at</strong>ion and<br />
adapt<strong>at</strong>ion, w<strong>at</strong>er reliability, flood risk<br />
management or conserv<strong>at</strong>ion – we<br />
place on our land and seas. Knowing<br />
how and where <strong>service</strong>s are<br />
delivered is also important for<br />
identifying potential opportunities for<br />
developing payment schemes for<br />
ecosystem <strong>service</strong>s or effective<br />
means of capturing the benefits.<br />
Possible sp<strong>at</strong>ial rel<strong>at</strong>ionship between <strong>service</strong> production areas (P)<br />
and <strong>service</strong> benefit areas (B). In panel 1, both the <strong>service</strong> provision<br />
and benefit occur <strong>at</strong> the same loc<strong>at</strong>ion (e.g. soil form<strong>at</strong>ion, provision<br />
of raw m<strong>at</strong>erial). In panel 2 the <strong>service</strong> is provided omni-directionally<br />
and benefits the surrounding landscape (e.g, pollin<strong>at</strong>ion, carbon<br />
sequestr<strong>at</strong>ion). Panel 3 and 4 demonstr<strong>at</strong>e <strong>service</strong>s th<strong>at</strong> have<br />
specific directional benefits. In panel 3, <strong>service</strong>s provided in uphill<br />
areas, for example w<strong>at</strong>er regul<strong>at</strong>ion <strong>service</strong>s provided by forested<br />
slopes, deliver benefits down stream. In panel 4, the <strong>service</strong><br />
provision unit could be coastal wetlands providing storm and flood<br />
protection to a coastline. (Reproduced from Fisher et al. 2008)<br />
P<br />
B<br />
P<br />
B<br />
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