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Month: September 2017

Reduction in exposure to arsenic from drinking well-water in Bangladesh limited by insufficient testing and awareness

Alexander Pfaff, Amy Schoenfeld, Kazi Matin Ahmed, Alexander van Geen
Journal of Water, Sanitation and Hygiene for Development 07.2 doi: 10.2166/washdev.2017.136

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This study considers potential policy responses to the still very high levels of exposure to arsenic (As) caused by drinking water from shallow tubewells in rural Bangladesh. It examines a survey of 4,109 households in 76 villages of Araihazar upazila conducted two years after a national testing campaign swept through the area. The area is adjacent to the region where a long-term study was initiated in 2000 and where households are periodically reminded of health risks associated with well-water elevated in As. Results confirm that testing spurs switching away from unsafe wells, although the 27% fraction who switched was only about half of that in the long-term study area. By village, the fraction of households that switched varied with the availability of safe wells and the distance from the long-term study area. Lacking follow-up testing, two years only after the campaign 21% of households did not know the status of their well and 21% of households with an unsafe well that switched did so to an untested well. Well testing is again urgently needed in Bangladesh and should be paired with better ways to raise awareness and the installation of additional deep community wells.

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Spillovers from Conservation Programs

Alexander Pfaff, Juan Robalino
Annual Review of Resource Economics 9:299-315

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Conservation programs have increased significantly, as has the evaluation of their impacts. However,the evaluation of their potential impacts beyond program borders has been scarce.Such spillovers can significantly reduce or increase net impacts. In this review, we discuss how conservation programs might affect outcomes beyond their borders and present some evidence of when they have or have not. We focus on five major channels by which spillovers can arise:(1) input reallocation; (2) market prices; (3) learning; (4) nonpecuniary motivations; and (5) ecological-physical links. We highlight evidence for each channel and emphasize that estimates often may reflect multiple channels. Future research could test for spillovers within different contexts and could separate the effects of different channels.

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