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7.3<br />

CoMPENSATING FoR LoSSES:<br />

oFFSETS AND BIoDIvERSITy BANKS<br />

Developments linked to economic growth often lead<br />

to habitat loss and degradation, pollution, disturbance<br />

and over-exploitation. These impacts can often be<br />

avoided or substantially reduced through measures<br />

at the design stage (see Chapter 4) and during opeand<br />

adaptive management).<br />

Even with avoidance and other measures, it is<br />

to avoid ongoing cumulative<br />

losses of bio-diversity and ecosystem services.<br />

offsets and biodiversity banks are the main instruments<br />

for this purpose. They are suited for use in<br />

habitats that can be restored within a reasonable timeframe<br />

and/or may benefit from additional protection<br />

(see Box 7.6). offsets can play a key role in delivering<br />

‘no net loss’ policies (Bean et al. 2008). They are<br />

implicitly required as part of an overall policy package<br />

where biodiversity policy targets aim to halt the loss<br />

of biodiversity (such as in the EU).<br />

“measurable conservation outcomes resulting from actions designed to compensate<br />

for significant residual adverse biodiversity impacts arising from project development and persisting after<br />

appropriate prevention and mitigation measures have been implemented. The goal of biodiversity offsets<br />

is to achieve no net loss, or preferably a net gain, of biodiversity on the ground with respect to species<br />

composition, habitat structure and ecosystem services, including livelihood aspects”.<br />

a market system, based on biodiversity offsets, for the supply of biodiversity credits<br />

and demand for those credits to offset damage to biodiversity (debits). Credits can be produced in advance<br />

of, and without ex-ante links to, the debits they compensate for, and stored over time. Such banks include<br />

habitat banks and species banks, and are often known as conservation banks.<br />

Biodiversity banking resembles carbon trading to some extent but is more complex because<br />

(i) there is no such thing as a unit of biodiversity as there is for carbon;<br />

(ii) the location of biodiversity damage and/or compensation matter can present constraints; and<br />

(iii) while there are policy instruments and regulations supporting carbon trading, regulations controlling<br />

biodiversity loss are weak and therefore demand for biodiversity trading is low.<br />

<strong>TEEB</strong> FoR NATIoNAL AND INTERNATIoNAL PoLICy MAKERS - ChAPTER 7: PAGE 11

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