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Box 17. Water-related myths<br />

Water-related myths that were found to be relatively common dur<strong>in</strong>g the Water Audit<br />

<strong>in</strong>cluded:<br />

. Water harvest<strong>in</strong>g is a totally benign technology. Although water harvest<strong>in</strong>g technologies<br />

can produce huge benefits, <strong>in</strong>tensive dra<strong>in</strong>age l<strong>in</strong>e treatment, <strong>in</strong> particular, can<br />

significantly reduce water resource availability to “downstream” communities. In some<br />

cases, this negative trade-off does not matter; <strong>in</strong> others, severe hardship can result.<br />

. Plant<strong>in</strong>g trees <strong>in</strong>creases local ra<strong>in</strong>fall and runoff. The reality is that forests exert a<br />

small, almost <strong>in</strong>significant <strong>in</strong>fluence on local ra<strong>in</strong>fall and, notwithstand<strong>in</strong>g a small<br />

number of exceptions, catchment experiments generally <strong>in</strong>dicate reduced runoff from<br />

forested areas as compared to those under shorter vegetation.<br />

. Runoff <strong>in</strong> semi-arid areas is 30-40% of annual ra<strong>in</strong>fall. Although localised runoff and<br />

runoff from <strong>in</strong>dividual storms can be high, annual runoff at the micro-watershed<br />

scale (or greater) <strong>in</strong> semi-arid areas tends to be much lower than 30-40%.<br />

. Ra<strong>in</strong>fall has decreased <strong>in</strong> recent years. With few exceptions, studies of long-term<br />

ra<strong>in</strong>fall records, that have used data from a s<strong>in</strong>gle set of ra<strong>in</strong> gauges, have not shown<br />

a significant decrease (or <strong>in</strong>crease) <strong>in</strong> mean annual ra<strong>in</strong>fall.<br />

. Aquifers are underground lakes. The reality is that check dams and other waterharvest<strong>in</strong>g<br />

structures usually only have localised impacts on groundwater levels and<br />

aquifers rarely behave like underground lakes. Or put another way, localised recharge <strong>in</strong><br />

one place rarely leads to an immediate rise <strong>in</strong> groundwater levels many kilometres away.<br />

. Water use of crops depends ma<strong>in</strong>ly on crop type. A common misconception is that the<br />

daily water use of crops is directly related to the crop type and that evaporation rates are<br />

many times higher from some crops as compared to others. The reality is that, assum<strong>in</strong>g<br />

that a crop is well supplied by water and has a <strong>full</strong> canopy (i.e. the crop completely<br />

shades the ground), the daily rate of evaporation is driven primarily by the<br />

meteorological conditions (e.g. radiation, w<strong>in</strong>d speed, dryness of the air).<br />

. Aquifers once depleted stay depleted. A pessimistic view of aquifer depletion is that this<br />

is an irreversible process. The reality is that, <strong>in</strong> most cases, aquifers can be re-established<br />

or replenished as long as the balance between recharge and extraction is swung towards<br />

recharge. This can occur as a result of <strong>in</strong>creased recharge, decreased extraction or both.<br />

6.2 Water-related risks<br />

Experience <strong>in</strong> the region has shown that there<br />

are a number of water-related risks associated with<br />

watershed development and with the source<br />

protection measures implemented as part of rural<br />

water supply programmes. These<br />

<strong>in</strong>clude:<br />

. Increased borewell construction and<br />

<strong>in</strong>creased irrigation by <strong>in</strong>dividual<br />

landowners: In most cases, the prime<br />

motivation of farmers to become <strong>in</strong>volved<br />

<strong>in</strong> soil and water conservation programmes<br />

and the construction of water<br />

harvest<strong>in</strong>g structures is not altruistic. It is<br />

to <strong>in</strong>crease the water resources that are<br />

available to them for irrigation.At the<br />

watershed scale, this is justified only if the<br />

resources that are be<strong>in</strong>g “harvested” do not<br />

have a higher value if they are put to<br />

other uses.<br />

· Increased borewell construction and<br />

<strong>in</strong>creased irrigation by “poor” landowners:<br />

Successful watershed development projects<br />

often improve the f<strong>in</strong>ancial status of<br />

relatively poor farmers such that they are<br />

able to take loans for construct<strong>in</strong>g<br />

borewells and <strong>in</strong>stall<strong>in</strong>g pumps. As above,<br />

this is f<strong>in</strong>e as long as the water they<br />

“harvest” does not have alternative<br />

higher-value uses (e.g. as a source of<br />

domestic water supply).<br />

74

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