It is very important to specify carefully the exact target for the program. Is it drought- affected households? Is it poor households? Or is it chronically food deficit households? The commodity or service being delivered by the program may also be relevant to he choice of targeting indicator. This is likely to be different if a program is delivering food as opposed to health services. The ranking of EPAs in Malawi is very sensitive to the choice of indicators, as examination of the following maps shows. Figure 1 shows the impact of the short rainfall RURAL HOUSEHOLD FOOD SECURITY INDEX in 1994/95, in terms of the percentage FOOD SECURITY variation of actual production of crops, j measured in kilocalories, from the historical average kilocalorie production, by EPA. The dark areas showed significant production shortfalls of up to 150 percent reductions. The light areas were less affected, and some had significant production increases. The worst-affected areas are spread fairly evenly throughout the country. In fact, a variation on this was used to target the 1994/95 drought relief programme. EPAs whose production was less than 1800 kilocalories per person per -- day, and had suffered a fall in production over the historical average, were targeted for '""" - emergency relief. This identified areas where the production shortfall took the EPA below a minimum coping level. FEWS has been developing an indicator of overall vulnerability, which is F e based on a principal component analysis of data series on food availability, cropping patterns, health, education, infrastructure and demographic variables. This has not yet been finalised, but Figure 2 shows its current status. This shows clusters of vulnerable EPAs along the borders with Mozambique and Zambia, with better-off EPAs along the lakeshore and in the North of the country. This gives a very different picture from the drought map, partly because the aim is to identify chronic, rather transitory status, and also because of the inclusion of data on health and education variables. This type of indicator would be useful for programs where there was a strong community element, such as the MASAF program. If, however, the program under consideration provided some kind of resource transfer to the household, such as food, then it might be more appropriate to rank EPAs on the basis of