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Water policy changes in Turkey’s agriculture sector

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WATER POLICY CHANGES IN

TURKEY’S AGRICULTURAL

SECTOR:

CHALLENGES AND

RESPONSES

AYSEGÜL KIBAROGLU PROF. DR.

DEPT. OF POLITICAL SCIENCE AND INTERNATIONAL

RELATIONS

MEF UNIVERSITY ISTANBUL, TURKEY

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KEY DETERMINANTS

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STRUCTURAL FACTORS

Structural factors comprise macro-level planning for policy changes and

investments in infrastructure and techniques:

improving the competitiveness of agricultural sector through

sustainable use of soil and water resources

expansion of irrigation infrastructure

land consolidation

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MAIN INSTITUTIONS

Ministry of Forestry and Water Affairs

DG State Hydraulic Works (DSI)

Ministry of Food, Agriculture and Livestock

DG Agrarian Reform

Ministry of

Interior

Provincial Administrations

Water User Organizations (Irrigation

Associations)

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INSTITUTIONAL RESTRUCTURING

DG Rural Services (abolished,

2005)

DG Land and Water (abolished,

1984)

This institutional restructuring in

water and land management

became disruptive and ended up

with delays and failures in the

efforts for land consolidation and

increasing irrigation ratio and

irrigation efficiency.

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IRRIGATION ASSOCIATIONS

Irrigation Associations has helped to overcome some of the problems such as

collection of irrigation fees and operation of the irrigation network.

However, an increase in water use efficiency remains a challenge.

Moreover, maintenance and rehabilitation become even more critical, because about one-third of the irrigation network is over 40 years old.

Over the next decades Turkey will likely face a rapidly growing repair and renewal challenge and corresponding investment requirements.

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TECHNOLOGICAL FACTORS

Since water scarcity is a pressing issue for all water-user

sectors, the diffusion of water-saving irrigation methods

such as drip and sprinkle irrigation is promoted,

especially by the DSI and the DG Agrarian Reform.

Successful implementation of this instrument depends on the farmers’

adoption, which is related to training and extension services, suitable

irrigation infrastructure and economic incentives

(Özerol et al., “Irrigated

agriculture and environmental sustainability: an alignment perspective” Environmental Science & Policy 23, 2012, p. 63)

.

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IRRIGATION INFRASTRUCTURE

Regarding the infrastructure, 92 percent of the irrigation infrastructure is open canals, which is not suitable for direct installment of drip or sprinkle systems.

However, since 2003, DSI has been constructing piped irrigation systems. If expanded on larger areas, these systems can facilitate water-metering and contribute to the diffusion of water-saving irrigation methods by eliminating the extra energy costs (Özerol et al., “Irrigated agriculture and environmental sustainability: an alignment

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ECONOMIC INCENTIVES

The pricing of irrigation water by the state and WUOs does not support the diffusion of water-saving methods. WUOs collect irrigation fees to cover the operation,

maintenance and administration costs; there is no charge for the amount of water used by the farmers.

In many regions, the irrigation fee is based on the type of the cultivated crop and the size of the irrigated land.

With the existing canal irrigation systems, it is impossible to measure the water consumption at the farm level and to implement volumetric prices.

Thus, the widespread adoption of water-saving technologies does not seem probable in the short-term due to the lack of an enabling combination of training, economic incentives and infrastructure (Özerol et al., “Irrigated agriculture and environmental sustainability: an alignment perspective” Environmental Science & Policy 23, 2012, p. 64).

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IRRIGATION RATIO

At the national level, the irrigation ratio is reported to be 65 percent.

Despite the low irrigation ratio, the DSI targets to open all the irrigable

land to irrigation, which implies tremendous amount of irrigation

investments. The main argument of the DSI with sticking to its target is

that the economic benefits of irrigated agriculture justify the cost of

investments.

However, there is no mention to the negative social or environmental impacts of

irrigation, which are also the ‘costs’ of irrigation. It is essential to evaluate and reflect on social and environmental factors so that the irrigation ratio can be improved. Then the rationality of the target to irrigate all the irrigable land can be revisited (Özerol et al., “Irrigated agriculture and environmental sustainability: an alignment perspective” Environmental Science & Policy 23, 2012, p. 64).

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CONCLUSION

In many countries there is a substantial gap between what is stated at macro level

and what actually is happening on the ground. Turkey is no exception to that.

We identify this as the policy-implementation gap, which means that the

institutional arrangements, incentives and resources mobilized are not properly

aligned resulting in a gap that is the difference between what is stated in the law

and related policies and in their actual implementation.

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