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Economics of Groundwater Depletion: Need for Demand Management

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Replenishment becomes problem if non-renewable groundwater is used. ... gaj limestone: 780 mt. weathered basalt: 720 mt. Externality context ... – PowerPoint PPT presentation

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Title: Economics of Groundwater Depletion: Need for Demand Management


1
Economics of Groundwater Depletion Need for
Demand Management
  • V. Ratna Reddy
  • CESS, Hyderabad.

2
Water Related Issues Concerns
  • Declining Surface water sources like canal and
    tank irrigation
  • Increased groundwater exploitation
  • Increased Depletion of groundwater
  • Replenishment becomes problem if non-renewable
    groundwater is used.
  • Resource preservation would not be in the best
    interest of the region

3
Source Wise Area Under Irrigation (India)
4
Economics of Groundwater
  • Groundwater is a public good
  • Groundwater use and depletion has externalities
  • Costs of depletion related externalities could be
    high and disproportionately distributed
  • Rationale for mitigating (replenishment) measures
    in terms of private / social costs and benefits.
  • Internalising the externalities could result in
    net social welfare

5
Groundwater Externalities 
                                    
 
APPROPRIATION EXTERNALITIES
Add heterogeneity in technology. And
heterogeneity in access to technology or capital.
Add heterogeneity in spatial distribution
Add private property rights to a complimentary
resource
Assignment problems
Legislative Externalities
Technological Externalities
6
Types of Externalities
  • Negative Externalities Stock (over
    exploitation), technological (higher pumping
    costs) and strategic (over extraction by few).
  • Positive externalities of resource investments
    (percolation tanks/replenishment mechanisms)
  • - Recharge normal Percolation Tank 7.87 mm/day
  • De-silted Percolation Tank 20.40 mm/day
  • - Impact radius miliolite limestone 1100 mt.
  • gaj limestone 780 mt.
  • weathered basalt 720 mt.

7
Externality context
  • ?rt ?pt --- Short run due to technological or
    strategic externalities as (Drt-1) gt (Dpt-1).
    Resource rich farmers tend to appropriate more
    resources using their resource position
  • ?rt ?pt --- long run due to stock
    externalities. Over exploitation resulting in use
    of non-renewable resource and tragedy of commons
    in the absence of cooperative strategy.


8
Externalities of GW Depletion Open wells
  • Drying up of open wells range from 45 in good
    to 85 in scarcity conditions (decline in no. of
    open wells)
  • Drying up of open wells is more prominent among
    marginal small farmers, especially in the
    moderate and scarcity conditions.
  • SM farmers are the first victims of
    externalities due to location disadvantages and
    poor quality soils.

9
Externalities of GW Depletion Bore wells
  • Many fold increase in no. of Bore wells- rate of
    increase directly linked to resource status.
  • Significant increase in the depth of bore wells
    directly linked to resource status
  • SM farmers are also investing in bore wells,
    especially in the moderate scarcity conditions.

10
Externalities Area irrigated
  • Decline in NIA GIA in all situations, but the
    decline progresses as we move from good to scarce
    resource condition.
  • Decline is more in the case rabi (where
    dependence on GW is more).
  • Decline in kharif is noticed in moderate and
    scarcity conditions.
  • Decline is more among marginal farmers,
    especially in moderate and scarcity conditions.

11
Externalities Crop shifts
  • Decline in area under paddy (kharif rabi),
    which is a water intesive crop.
  • Cotton (ID), gingelly, etc., crops have replaced
    paddy though they are not remunerative.
  • Decline in the rabi paddy area is the highest
    among the SM farmers, especially in moderate and
    scarcity conditions.

12
Externalities Yields
  • Decline in yield rates of paddy (khaif rabi) in
    all the situations.
  • Declines as high as 17 percent.
  • Decline is more for SM farmers.
  • ID crops also have recorded a decline.

13
Nature of Costs
  • Direct Costs
  • -Loss due to drying of open wells (sunk)
  • -Investment in borewells / well deepening
    (replacement)
  • Indirect Costs
  • -Loss due to decline in productivity
  • -crop shifts (high remunerative to low
    remunerative)

14
Costs of Depletion
  • Total Costs of degradation range from Rs. 3349
    (US85) per acre (good availability) to Rs. 15069
    (US425) (scarcity conditions).
  • These costs compare favourably with the costs of
    renovating the tanks.
  • Both direct (sunk) and indirect (cropping pattern
    changes) costs are disproportionately borne by
    small and marginal farmers.

15
Costs of Degradation (Good Availability)
  • Average cost /acre 3349 (US85)
  • Large farmers Rs. 2362
  • (US60) / acre
  • Medium farmers Rs. 5723 (US115) / acre
  • Small farmers Rs. 6374 (US160) / acre
  • Marginal Farmers Rs. 1379
  • (US35) / acre

16
Costs of Degradation (Moderate Availability)
  • Average cost /acre 5539 (US140)
  • Large farmers Rs. 4125
  • (US 105) / acre
  • Medium farmers Rs. 6882 (US170) / acre
  • Small farmers Rs. 14279 (US350) / acre
  • Marginal Farmers Rs. 2362 (US60) / acre

17
Costs of Degradation(Scarcity conditions)
  • Average cost /acre 15069
  • (US425)
  • Large farmers Rs. 8159
  • (US205) / acre
  • Medium farmers Rs. 13427 (US335) / acre
  • Small farmers Rs. 19787 (US480) / acre
  • Marginal Farmers Rs. 44602 (US1110 / acre

18
Costs Degradation vs Abatement
  • Lower costs of degradation in resource condition
    is due to the availability of replenishing
    mechanisms (percolation tank).
  • Differential losses range from above Rs. 2000
    (US50) to above Rs. 11000 (US275) per acre per
    year.
  • Abatement costs range between Rs. 4000 Rs. 6000
    (US100-150) per acre depending on the size of
    the tank (with out de-silting) with a life of
    10-15 years.
  • Investments in mitigation makes economic as well
    as ecological sense.

19
GW A Mismanaged Resource
  • Clear case of market failure due the absence of
    clearly defined property rights, as access to
    water is based on riparian laws resulting in over
    exploitation by some.
  • Absence of Institutions in GW management has
    aggravated the problem (institutional failure)
  • Absence of any policies for GW management (policy
    failure)

20
Demand management of Groundwater
  • Managing Demand Low priority for
  • -Water demand functions
  • -Water productivity
  • -Water use efficiency
  • Instruments
  • -Market Based
  • -Technological
  • -Institutional

21
Market based Instruments
  • Pricing of water economic as well as scarcity
    value
  • Pricing increases use efficiency and cuts
    wastage
  • - Pricing is inversely related to demand but
    inelastic
  • - Income positively related and inelastic
  • - Reasonably high willingness and ability to pay
    as farmers spend as much as 50 of their GVP when
    they buy groundwater for irrigation as against 2
    in the case of public irrigation

22
Market based Instruments-II
  • Pricing of complementary goods (power)
  • -In the event of high transaction costs, adding
    the scarcity price of water to the electricity
    would be efficient for raising resources. This
    would not only internalise the externalities at
    the regional level but also minimise the adverse
    impacts.
  • Other related pricing policies
  • Incentive / dis-incentive strategies

23
Technological Instruments
  • Technology is the key for expanding the supplies
  • Technology can help in reducing wastage and
    increase use efficiency
  • Micro irrigation systems can save up to 67 of
    water, energy and up to 60 of labour.
  • Micro irrigation systems are economically viable
    for a number of crops
  • Technology promotion through policy support

24
Institutional Options
  • Property rights institutions-clearly defined and
    equitable rights in water
  • Collective action institutions-bringing
    groundwater under the management regime viz.,
    WUAs
  • Institutional arrangements are required to make
    groundwater a common pool resource in the true
    sense of the term. In this regard de-linking of
    water rights from land rights would help
    addressing the equity issues effectively
    (vertical externalities).

25
Need for an Integrated Approach
  • Integration at the resource front Groundwater
    surface water bodies should be treated as
    complements rather than substitutes.
  • Integration at the policy level Supply side and
    demand side management approaches need to be
    integrated.
  • The experience of APFAMGS and similar initiatives
    would go a long way in helping designing better
    policies

26
Thank You
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