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7.2 Adaptive water resource<br />

management<br />

The history of water management is, <strong>in</strong> many<br />

ways, a history of searches for universally<br />

applicable solutions (Moench, 1999).<br />

The “development era” focused on construction<br />

of large-scale <strong>in</strong>frastructure projects such as dams<br />

and municipal supply schemes. In a similar<br />

manner, many now advocate economic pric<strong>in</strong>g,<br />

bas<strong>in</strong> approaches, <strong>in</strong>tegrated plann<strong>in</strong>g, the<br />

development of participatory water management<br />

<strong>in</strong>stitutions and demand management as “the”<br />

solution to management needs. The pr<strong>in</strong>ciple of<br />

adaptive management turns many current debates<br />

on resource management on their head. Instead of<br />

gett<strong>in</strong>g bogged down debat<strong>in</strong>g whether or not<br />

decentralised participatory approaches are better<br />

than centralised ones for water management, the<br />

pr<strong>in</strong>ciple of adaptive management <strong>in</strong>volves<br />

work<strong>in</strong>g from the specifics of a given problem<br />

outwards, to the best solution for address<strong>in</strong>g it.<br />

Some problems may be best addressed through<br />

decentralised participatory approaches; others may<br />

require more centralised forms of plann<strong>in</strong>g and<br />

<strong>in</strong>tervention (Moench, 1999, Batchelor 2001).<br />

Adaptive management is also a process by<br />

which management actions and directions are<br />

adjusted <strong>in</strong> the light of new <strong>in</strong><strong>format</strong>ion on<br />

current and likely future conditions. It recognises<br />

the limitations of current knowledge and the<br />

potential impacts of current resource management<br />

strategies and also recognises that there is a<br />

disjuncture between the <strong>in</strong>herent variability of<br />

natural and social systems and the tendency for<br />

management approaches to cluster around a<br />

few management models. New management<br />

paradigms emerge <strong>in</strong> response to the limitations<br />

<strong>in</strong> earlier ones. When these new paradigms<br />

become dom<strong>in</strong>ant, their <strong>in</strong>herent limitations<br />

emerge and they are gradually discarded <strong>in</strong><br />

favour of new “better” paradigms.<br />

The rapid pace of technical, social and<br />

economic change <strong>in</strong> Andhra Pradesh is such that<br />

it is very difficult to predict future patterns of<br />

water supply and demand with any great<br />

confidence. The possible impacts of short and<br />

long term climate changes add further<br />

uncerta<strong>in</strong>ty. This be<strong>in</strong>g the case, resource<br />

management systems are required that are flexible<br />

and able to adapt to new challenges.<br />

7.3 Integrated water resource<br />

management<br />

In many areas, competition and equitable<br />

access to water resources was not an issue as long<br />

as the size of the “cake” was grow<strong>in</strong>g. Now,<br />

however, competition over access is emerg<strong>in</strong>g as a<br />

major issue <strong>in</strong> semi-arid areas and one that has<br />

the potential to have a serious long-term impact<br />

on the livelihoods of people liv<strong>in</strong>g <strong>in</strong> these areas.<br />

Lack of <strong>in</strong>tegration between the sectors<br />

<strong>in</strong>volved <strong>in</strong> water resources plann<strong>in</strong>g and<br />

management is a fundamental impediment to<br />

improved water resource management. In general,<br />

there is little <strong>in</strong>tegration between the watershed<br />

development, water supply and sanitation (WSS)<br />

and power sectors despite the fact that all three<br />

sectors impact hugely on the availability and<br />

access to water resources and, hence, on the<br />

livelihoods of urban and rural communities. For<br />

example, <strong>in</strong> semi-arid India, an un<strong>in</strong>tended<br />

impact of watershed development and RWSS<br />

source protection measures is an <strong>in</strong>crease <strong>in</strong><br />

groundwater extraction for irrigation that can<br />

lead to an <strong>in</strong>creas<strong>in</strong>g risk of resource-related<br />

failure of village water supplies. A potential<br />

un<strong>in</strong>tended impact of power sector reform is also<br />

a big <strong>in</strong>crease <strong>in</strong> groundwater extraction that may<br />

also impact adversely on rural dr<strong>in</strong>k<strong>in</strong>g water<br />

supplies. Given that the profitability of<br />

“commercial” irrigated cropp<strong>in</strong>g is so high, new<br />

tariffs are unlikely to limit groundwater<br />

extraction by larger farmers. However, they are<br />

likely to make pump<strong>in</strong>g costs too high for poor<br />

and marg<strong>in</strong>al farmers that are grow<strong>in</strong>g subsistence<br />

crops. In contrast to the previous two examples,<br />

<strong>in</strong> many areas, the livelihoods of all farmers<br />

(i.e. the relatively rich and the poor and marg<strong>in</strong>al<br />

farmers) are be<strong>in</strong>g affected by the reallocation of<br />

water resources, that they were us<strong>in</strong>g for<br />

irrigation, to meet the ever <strong>in</strong>creas<strong>in</strong>g demands of<br />

urban areas.<br />

Regardless of official policy (or norms), access<br />

and allocation issues tend to have major political<br />

and economic ramifications. Furthermore the<br />

mechanisms used for allocation, touch deep<br />

cultural, ethical and often religious sensitivities.<br />

Clearly <strong>in</strong>tegrated water resource management is<br />

needed that <strong>in</strong>volves identification of the multiple<br />

impacts and trade-offs result<strong>in</strong>g from current or<br />

proposed sectoral policies. Once these impacts<br />

and trade-offs are identified (by water audit<strong>in</strong>g or<br />

other procedures) it is then up to the political<br />

process to make <strong>in</strong>formed decisions.<br />

78

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