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· Deterioration <strong>in</strong> village water supplies:<br />

There is a high risk that project<br />

<strong>in</strong>terventions will reduce runoff <strong>in</strong>to tanks<br />

or other structures that are important<br />

sources of recharge of the aquifers that<br />

meet urban water requirements. Project<br />

<strong>in</strong>terventions can also lead <strong>in</strong>directly to<br />

<strong>in</strong>creased pump<strong>in</strong>g of groundwater<br />

for irrigation <strong>in</strong> urban and peri-urban<br />

areas, thereby, <strong>in</strong>creas<strong>in</strong>g the risk of<br />

failure of village water supplies dur<strong>in</strong>g<br />

the summer months. F<strong>in</strong>ally, project<br />

<strong>in</strong>terventions can lead to <strong>in</strong>creased<br />

consumption of water: per household, by<br />

livestock, by horticulture with<strong>in</strong> the village<br />

and by non-land-based activities.<br />

Wait<strong>in</strong>g for water at a water po<strong>in</strong>t <strong>in</strong><br />

Yapad<strong>in</strong>ne, Dhone<br />

· Conflicts with<strong>in</strong> villages and between<br />

villages: Some <strong>in</strong>terventions, that <strong>in</strong>volve<br />

chang<strong>in</strong>g land use or patterns of water<br />

availability and use, result <strong>in</strong> dist<strong>in</strong>ct<br />

w<strong>in</strong>ners and losers. If there is a risk of this<br />

happen<strong>in</strong>g, conflicts should be managed by<br />

ensur<strong>in</strong>g that losers are compensated <strong>in</strong><br />

some way. As above, decisions on whether<br />

an <strong>in</strong>tervention should take place should<br />

be based on economic and social value.<br />

· Reduction <strong>in</strong> net productivity: There is a<br />

risk that promotion of <strong>in</strong>terventions with<br />

a high social value will lead to reductions<br />

<strong>in</strong> net productivity at the village or<br />

watershed scale. For example, use of water<br />

for irrigation on marg<strong>in</strong>al lands (usually<br />

owned by poorer farmers) will tend to be<br />

less productive than use of the same water<br />

on better quality land (usually owned by<br />

relatively richer farmers). Ultimately,<br />

determ<strong>in</strong><strong>in</strong>g the balance between<br />

acceptable social and economic value is<br />

a political decision.<br />

Kocheruvu open well, Dhone<br />

. Increase <strong>in</strong> environmental degradation:<br />

It is generally assumed that an <strong>in</strong>crease<br />

<strong>in</strong> forestry equates to environmental<br />

improvement <strong>in</strong> watersheds and that this<br />

is sufficient <strong>in</strong> terms of meet<strong>in</strong>g<br />

environmental susta<strong>in</strong>ability targets. In<br />

many cases, <strong>in</strong>creased forestry will lead to<br />

significant improvements <strong>in</strong> biodiversity,<br />

particularly if <strong>in</strong>digenous tree species are<br />

planted. There are risks, however, that<br />

chang<strong>in</strong>g patterns of land and water use<br />

and, hence, the hydrology of watersheds<br />

will lead to reduction <strong>in</strong> biodiversity <strong>in</strong><br />

areas other than forested areas (e.g. <strong>in</strong><br />

wetland areas, <strong>in</strong> ephemeral streams,<br />

<strong>in</strong> and around tanks). There is also a risk<br />

that project <strong>in</strong>terventions will adversely<br />

affect water quality (e.g. pollution result<strong>in</strong>g<br />

from: <strong>in</strong>creased use of agro chemicals).<br />

75

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