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manual for social impact assessment of land-based ... - Forest Trends

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• People in control groups are known to change their behavior when studied (known as the<br />

‘Hawthorne effect’);<br />

• The ethical problem <strong>of</strong> denying people in control groups the future right to participate in an<br />

expanding project;<br />

• Measuring <strong>impact</strong>s at one point <strong>of</strong> time is considered less reliable <strong>for</strong> establishing causality<br />

than a comparison at two points <strong>of</strong> time;<br />

• There is low motivation <strong>for</strong> control groups to cooperate.<br />

In sum, the experimental approach is expensive and does not ensure attribution, due to possible<br />

differences in unobservable characteristics or other causes <strong>of</strong> bias (Tanburn, 2008).<br />

Quasi-experimental methods<br />

The above problems usually mean that a pure statistical approach is not practical or viable <strong>for</strong><br />

<strong>impact</strong> <strong>assessment</strong>. There<strong>for</strong>e a ‘quasi-experimental’ approach involving 'constructed controls' is<br />

<strong>of</strong>ten used. This means trying to find people or groups who are as similar as possible to the project<br />

participants in terms <strong>of</strong> their observable characteristics, possibly living in the same or in nearby<br />

communities. But the problems <strong>of</strong> selecting controls are more or less the same, and it has a lower<br />

level <strong>of</strong> certainty as regards attribution compared to the experimental method.<br />

The quasi-experimental approach can theoretically be used with or without a starting conditions or<br />

‘baseline’ study, but it is more reliable with a baseline – sometimes called the be<strong>for</strong>e-and-aftercontrol-<strong>impact</strong><br />

(BACI) design. Assuming a baseline is used, it is necessary to ‘over-sample’ by 50%<br />

according to some sources – and possibly a higher percentage among the controls if there are few<br />

incentives <strong>for</strong> them to remain in their communities. This allows <strong>for</strong> the natural decline or ‘attrition’<br />

(e.g. outmigration, death, etc.) <strong>of</strong> respondents.<br />

A cheaper but less reliable alternative to the above approaches is a 'be<strong>for</strong>e and after' comparison by<br />

project participants, known as 'reflexive comparison'. In this case the ‘control’ element is provided<br />

by the original conditions or be<strong>for</strong>e project situation. Again it is more effective and reliable with a<br />

baseline. If used without a baseline, it depends entirely on memory recall, and is there<strong>for</strong>e more<br />

subjective and open to bias. It is again important to 'over-sample' if a baseline is undertaken.<br />

Data collection methods<br />

As well as appropriate indicator selection, ‘matching methods’ need to be accompanied by carefully<br />

chosen and designed data collection methods which are described in the subsequent sections <strong>of</strong> the<br />

Toolbox. Thus, <strong>for</strong> example, the Basic Necessities Survey (BNS) is a cost-effective approach to<br />

measuring changes in poverty in control and project communities (Section T6.1), while several <strong>of</strong> the<br />

Participatory Impact Assessment (PIA) methods are relevant <strong>for</strong> matching methods (Section T6.2).<br />

Social Impact Assessment <strong>of</strong> Land-Based Carbon Projects (1.0) – Part II | 33

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