Skip to main content
. 2014 Dec 9;29(1):78–87. doi: 10.1111/cobi.12423

Table 3.

Differences between household status and livelihood strategies in 2008 before the commencement of the payments for environmental services (PES) programs for households that participated in the PES programs and households that did not.a

Bird nest participantsb
Ecotourism participantsc
Ibis Rice participantsc
Yes No Pd Yes No Pd Yes No Pd
No. of households 28 219 27 147 50 124
Female-headed households (%) 7 5 11 5 0 8
Well-being variables
 Poverty 9.4 9.4 ns 10.8 10.2 ns 11.1 9.9 *
 Rice harvest (kg) 2154 1935 ns 2811 1926 ** 2707 1804 ***
 Food security (kg) −194 −154 ns 304 −191 (*) 486 −357 **
Livelihood strategies
 Resin tappers (%) 64 55 ns 56 56 ns 54 57 ns
 Rice farmer (%) 89 90 ns 93 88 ns 96 85 (*)
 >1 ha of paddy fields (%) 68 72 ns 93 76 * 94 72 **
 Mini tractor (%) 29 26 ns 33 25 ns 44 19 **
 Rice shifting cultivation (%) 43 31 ns 11 18 ns 10 19 ns
 Employed (%) 0 9 ns 19 7 (*) 14 6 ns
 Service or shop (%) 14 12 ns 19 13 ns 14 14 ns
Average annual payments per household, 132 (18) 225 (14) 413 (41)
US$ (SE)
Percentage of households in the village 7 (616) 12 (499) 24 (616)
engaged in program (total households)
Percentage of households engaged 10 62 54
for > 1 year
a

Data are from the same villages within the protected areas.

b

Data for the Bird Nests program are based on 6 villages (247 households). The Bird Nests program provided direct payments for protection of nests of globally threatened birds.

c

Data for the Ecotourism and Ibis Rice programs are based on 4 villages (174 households). The ecotourism program provided payments conditional on wildlife and habitat protection, and Ibis Rice provided households with premium prices for agricultural goods if they kept to agreed land-use plans.

d

Tests of difference are mixed effects models with a binomial link function. Significance: ns, not significant;

*

P < 0.1; *P < 0.05;

**

P < 0.01;

***

P< 0.001.