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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 />

15

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