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Optimizing Adjustments to Transboundary Water Sharing Plans: A Multi-Basin Approach

Abstract

Afghanistan contributes water supplies to Iran, Pakistan, Tajikistan, Turkmenistan, and Uzbekistan. However, with the exception of the Helmand Basin, Afghanistan has negotiated transboundary water sharing agreements with no downstream country. This paper describes a constrained optimization framework to minimize economic costs within each of nine Afghan transboundary basins of adapting to potential water sharing agreements. Model results show impacts of water agreements on farm income and food security for each Afghan basin. Our results show that unrestricted trading reduces the economic costs of adapting to water sharing treaties by two to 6 % compared to the conventional water sharing system. A higher scale of reservoir storage capacity as well as market trading of water among regions moderates costs of water shortages, both with and without water agreements in place.

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Acknowledgements

The authors gratefully acknowledge support by the New Mexico Agricultural Experiment Station and US Geological Survey International Division. Neither organization is responsible for errors in this document.

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Corresponding author

Correspondence to Frank A. Ward.

Appendix

Appendix

Overview.

The appendix summarizes relevant mathematical documentation of the multi-basin hydro-economic model design to inform water policy decisions in Afghanistan. It outlines the mathematical framework of the optimization model built using General Algebraic Modeling Systems to include sets, parameters, variables, equations and the objective function specification. The complete model show hydrological, economic and institutional constraints. The code for the hydro-economic model and spreadsheet results are available at the New Mexico State University web page at https://water-research.nmsu.edu/

Sets.Sets characterize the foundation of the multi-basin framework. Each set constitute elements as described below. In our model, sets and corresponding elements are defined for all studied transboundary river basins in Afghanistan.

sets

set name

description

set elements

k

crop

Crop selection is an important choice variable for farm income, food security, and policy assessment that influences both.

/ Alfalfa, Cotton, Melon, Potato, Pulses, Rice, Tomato, Wheat/

t

Year

Year reflect a 20-year horizon

/year1 * year 20/

i

Region by basin

Each basin divided into 3 regions

/upper, middle, lower/

j

Water right priority

Priority among regions inside each basin

/j1, j2, j3/

r

Water allocation rule

Water right systems for sharing water shortages when they occur

/Upstream priority, free market/

s

Storage reservoir capacity scale

Scale at which new reservoirs could be built. None reflects base condition and has no storage.

/none, small, medium, large/

b

River Basin

Lists of all river basins studied in the country

/Balkh, Patika, Helmand, Farah, Kabul, Kokcha Kunduz, Murghab, Upper_Harirud

y

Treaty

Treaty agreement on transboundary river basins.

/Without treaty, With treaty/

rji(r,j,i)

Mapping set

Assigns priorities to regions in a basin to vary water right regime

us_priority.j1.upper,us_priority.j2.middle,us_priority.j3.lower

free_mkt.j1.upper,free_mkt.j1.middle,free_mkt.j1.lower

rwa(r)

Upstream priority

Upstream users receive priority when shortages occur

upstream priority

rfm(r)

free_market

No restrictions on water reallocations from baseline

free market

Parameters.

Terms ending in _p refer to parameters, data read by the model. They are:

Parameter

sets

Label

units

Nat_supp_p

(b)

Natural runoff inflow to basin

MCM / year

Nat_suppl_p

(b,t)

Stochastic water supply by year with set mean and standard deviation

MCM / Year

Nat_supply_p

(b,t,y)

Natural water supply adjusted by downstream delivery treaty requirement

MCM / Year

Pop_p

(b,t)

Forecast population by basin and years

thousands

Popratio_p

(b,t)

Ratio of given year population to base year

1 and above

Rho_p

 

Discount rate (1%)

unitless

Capacity_p

(b,s)

Maximum reservoir storage capacity

MCM

Com_cost_mcm

(b,s)

Construction cost per million cubic meters storage capacity

$US/MCM

Prop_right_p

(b,i)

Proportion of right to water compared by region within basin

0–1

Right_p

(b,i)

Customary absolute right to water supply by region

MCM / year

Shortage_p

(b,r,i,t,s,y)

Water storage relative to full supply right

0–1

Basin_use_p

(b,r, t,s,y)

Total water use in the basin

MCM / year

Change_store_p

(b,r, t,s,y)

Total change in storage

MCM / year

Bc_p

(b,i,k)

Water use per unit land (irrigation depth)

M / year

Land_p

(b,i,k)

Observed land in production

Ha / year

Price_p

(k,b)

Observed crop prices

$US per metric ton

Price_elast_p

(k,b)

Price elasticity of demand

unitless

Yield_p

(b,i,k)

Observed crop yield

Metric tons/ha

Cost_p

(b,i,k)

Production costs

$US per ha

A0_p

(b,k,t)

Intercept in price-dependent demand function

$US per metric ton

A1_p

(b,k,t)

Slope of price-dependent demand function

$US per metric ton

B0_p

(b,k,t)

Intercept in crop water production function (PMP)

Metric tons/ha

B1_p

(b,k,t)

Slope in crop water production function (PMP)

Metric tons/ha

Variables.

As characterized in the multi-basin model, variables are endogenous (unknown) and end in _v to distinguish the unknown data from parameters. These variables are optimized by the model, while respecting all important bounds. The most important variables are:

Variables

sets

label

units

Hectares_v

(b,r,i,k,t,s,y)

Land use

1000 ha

T_hectares_v

(b,r,i, t,s,y)

Total land use

1000 ha

Uses_v

(b,r,i, t,s,y)

Water use

MCM/year

Sum_uses_v

(b,r, t,s,y)

Summed water use

MCM/year

Production_v

(b,r,i,k,t,s,y)

Land in production details

1000 ha

Yield_v

(b,r,i,k,t,s,y)

Crop yields

Tons/ha

Crop_price_v

(b,r, k,t,s,y)

Crop price

$US/ton

Netrev_v

(b,r,i,k,t,s,y)

Net revenue per unit land

$US/ha

Con_surp_v

(b,r, k,t,s,y)

Consumer surplus (willingness to pay in excess of price)

$US 1000 / year

Tgrossrev_v

(b,r,i,k,t,s,y)

Total gross revenue over all lands

$US 1000 / year

Ag_ben_j_v

(b,r,i,k,t,s,y)

Discounted ag benefits with details

$US 1000 / year

Tot_wel_v

(b,r, t,s,y)

Discounted total welfare

$US 1000 / year

Wel_wo_cd_v

(b,r, s,y)

Discounted total welfare without reservoir capacity expansion

$US 1000 / year

Ttot_wel_v

(b,r, s,y)

Discounted total welfare with reservoir capacity expansion

$US 1000 / year

Equations

Mathematical expressions connecting the relationship between variables and parameters used in the optimization frame to characterize the most important indicators such as hydrology, land in production, crop production, and economic policy choices.

Hydrology Block

$$ \mathrm{X}\left(\mathrm{t}\right)\sim \mathrm{N}\left(\upmu, {\upsigma}^2\right). $$
(1)

Basin headwater supply for the year t, X(t)

$$ \mathrm{X}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\kern0.5em =\kern1em \mathrm{Bc}\_\mathrm{p}{\left(\mathrm{b},\mathrm{i},\mathrm{k}\right)}^{\ast }\ \mathrm{hectares}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(2)

Crop water use equation calculated based on land in production

$$ \mathrm{Uses}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right)\kern0.5em =\mathrm{sum}\left(\mathrm{k},\mathrm{X}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(3)

Water use summed over crops

$$ \mathrm{sum}\_\mathrm{uses}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\left(\mathrm{i},\mathrm{Uses}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(4)

It calculates water use summed over canals

Agronomy Block

$$ \mathrm{T}\_\mathrm{hectares}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\left(\mathrm{k},\mathrm{hectares}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(5)

Land in production summed over crops

$$ \mathrm{Yield}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{B}0\_\mathrm{p}\left(\mathrm{b},\mathrm{i},\mathrm{k}\right)+\kern0.5em \mathrm{B}1\_\mathrm{p}{\left(\mathrm{b},\mathrm{i},\mathrm{k}\right)}^{\ast }\ \mathrm{hectares}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(6)

Crop yields declines as acreage in production increases

$$ \mathrm{Production}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{Yield}\_\mathrm{v}\ {\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)}^{\ast }\ \mathrm{hectares}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(7)

It calculates crop production based on crop yield and acreage in production.

$$ \mathrm{Tot}\_\mathrm{prod}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\left(\mathrm{i},\mathrm{production}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(8)

Total crop production summed over regions.

Economics Block

$$ \mathrm{crop}\_\mathrm{p}\mathrm{rice}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{BB}0\_\mathrm{p}\ \left(\mathrm{b},\mathrm{k},\mathrm{t}\right)+\left[\mathrm{BB}1\_\mathrm{p}{\left(\mathrm{b},\mathrm{k},\mathrm{t}\right)}^{\ast }\ \mathrm{Tot}\_\mathrm{p}\mathrm{rod}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right] $$
(9)

Linear demand function of crop price for each basin as influence by water right systems, region, time, storage capacity and treaty

$$ \mathrm{con}\_\mathrm{surp}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)={0.5}^{\ast }\ \left[{\left[\mathrm{BB}0\_\mathrm{p}\left(\mathrm{b}\mathrm{b},\mathrm{k},\mathrm{t}\right)-\mathrm{crop}\_\mathrm{p}\mathrm{rice}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right]}^{\ast }\ \mathrm{Tot}\_\mathrm{p}\mathrm{rod}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right] $$
(10)

Consumer surplus representing gains in economic benefits to the Afghan people as water right systems, treaty agreement and storage capacities are varied.

$$ \mathrm{Netrev}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{crop}\_\mathrm{p}\mathrm{rice}\_\mathrm{v}{\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)}^{\ast }\ \mathrm{Yield}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)-\mathrm{Cost}\_\mathrm{p}\left(\mathrm{b},\mathrm{i},\mathrm{k}\right) $$
(11)

Net revenue per unit land is price times yield minus costs per unit land

$$ \mathrm{Ag}\_\mathrm{Ben}\_\mathrm{j}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{Netrev}\_\mathrm{v}{\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)}^{\ast }\ \mathrm{hectares}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(12)

Agricultural benefits by river basin, water right systems, agricultural region, crop, time period, storage capacity and treaty.

$$ \mathrm{To}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\ \left[\mathrm{i},\mathrm{ag}\_\mathrm{ben}\_\mathrm{j}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right]+\mathrm{con}\_\mathrm{surp}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(13)

Discounted net present value of total economic welfare

$$ \mathrm{Tot}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\ \left(\mathrm{k},\mathrm{To}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(14)

Summed total welfare over crops

$$ \mathrm{Wel}\_\mathrm{wo}\_\mathrm{cd}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\ \left(\mathrm{t},\mathrm{DF}{\left(\mathrm{t}\right)}^{\ast }\ \mathrm{Tot}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{t},\mathrm{s},\mathrm{y}\right)\right) $$
(15)

Net present value of farm income plus consumer surplus

$$ \mathrm{Ttot}\_\mathrm{wel}\_\mathrm{v}\ \left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)=\mathrm{Wel}\_\mathrm{wo}\_\mathrm{cd}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)-\mathrm{Tot}\_\mathrm{COM}\_\mathrm{cost}\_\mathrm{p}\left(\mathrm{b},\mathrm{s}\right) $$
(16)

Total net benefits after subtracting dam construction cost

$$ \mathrm{Tot}\_\mathrm{b}\_\mathrm{v}=\mathrm{sum}\ \left(\left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right),\mathrm{Ttot}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)\right) $$
(17)

Total benefits looped over all changeable indices

$$ \mathrm{shad}\_\mathrm{p}\mathrm{rice}\_\mathrm{p}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{uses}\_\mathrm{v}.\mathrm{m}\ \left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(18)

Shadow prices for all water allocation rules except unrestricted trading

$$ \mathrm{shad}\_\mathrm{p}\mathrm{rice}\_\mathrm{p}\left(\mathrm{b},\mathrm{rfm},\mathrm{i},\mathrm{t},\mathrm{s},\mathrm{y}\right)=\mathrm{sum}\_\mathrm{uses}\_\mathrm{v}.\mathrm{m}\left(\mathrm{b},\mathrm{rfm},\mathrm{t},\mathrm{s},\mathrm{y}\right) $$
(19)

Shadow prices for unrestricted trading

$$ \mathrm{Storage}\_\mathrm{Capacity}\_\mathrm{p}=\mathrm{scale}\_{\mathrm{p}}^{\ast }\ \mathrm{natural}\_\mathrm{supply}\_\mathrm{p}. $$
(20)

Water storage capacity is defined by natural supply at various values of the scale parameter (scale_p)

$$ \mathrm{Tot}\_\mathrm{Com}\_\mathrm{cost}\_\mathrm{p}\left(\mathrm{b},\mathrm{s}\right)=\mathrm{Cost}\_\mathrm{Per}\ \mathrm{Unit}\ \mathrm{Storage}\_{\mathrm{p}}^{\ast }\ \mathrm{Storage}\_\mathrm{Capacity}\_\mathrm{p}. $$
(21)
$$ \mathrm{Ttot}\_\mathrm{wel}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)=\mathrm{Wel}\_\mathrm{wo}\_\mathrm{cd}\_\mathrm{v}\left(\mathrm{b},\mathrm{r},\mathrm{s},\mathrm{y}\right)\hbox{--} \mathrm{Tot}\_\mathrm{Com}\_\mathrm{cost}\_\mathrm{p}\left(\mathrm{b},\mathrm{s}\right). $$
(22)

Total net benefits obtained after dam cost.

Bounds.

Bounds characterize constraints on institutions, technology, and water user behavior, while also producing realistic responses to future climate or policy adaptations to climate. A lower bound (.lo) on each water flows and land used assures no crop production or water supplies have negative values. An upper bound (.up) guards against a variable exceeding that set level.

$$ \mathrm{hectares}\_\mathrm{v}.\mathrm{lo}\left(\mathrm{b},\mathrm{r},\mathrm{i},\mathrm{k},\mathrm{t},\mathrm{s},\mathrm{y}\right)=0. $$
(23)

Agricultural land in production cannot be negative.

$$ \mathrm{uses}\_\mathrm{v}.\mathrm{up}\ \left(\mathrm{b},\mathrm{rwa},\mathrm{i},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{Without}\_{\mathrm{treaty}}^{'}\right)={1.0}^{\ast }\ \mathrm{wet}\_\mathrm{wat}\_\mathrm{use}\left(\mathrm{b},\mathrm{rwa},\mathrm{i},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{Without}\_{\mathrm{treaty}}^{'}\right) $$
(24)

uses_v . up (b, rwa, i, t, s, 'With_treaty) = 0.8* wet_wat_use(b, rwa, i, t, s, 'With_treaty) (25)

Bounds water use in production, with use in the face of a treaty set to 80% of without treaty level

$$ \mathrm{sum}\_\mathrm{use}\mathrm{s}\_\mathrm{v}.\mathrm{up}\left(\mathrm{b},\mathrm{rfm},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{Without}\_{\mathrm{treaty}}^{'}\right)={1.0}^{\ast }\ \mathrm{basin}\_\mathrm{use}\_\mathrm{p}\left(\mathrm{b},\mathrm{rfm},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{Without}\_{\mathrm{treaty}}^{'}\right) $$
(26)
$$ \mathrm{sum}\_\mathrm{use}\mathrm{s}\_\mathrm{v}.\mathrm{up}\left(\mathrm{b},\mathrm{rfm},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{With}\_{\mathrm{treaty}}^{'}\right)={0.8}^{\ast }\ \mathrm{basin}\_\mathrm{use}\_\mathrm{p}\left(\mathrm{b},\mathrm{rfm},\mathrm{t},\mathrm{s},{}^{\hbox{'}}\mathrm{With}\_{\mathrm{treaty}}^{'}\right) $$
(27)

When water trading is allowed among regions in each basin, only total water use is bounded.

Objective.

The objective of the model is to maximize discounted net present value subject to the hydrologic and institutional constraints described above.

The objective function Ttot_wel_v(b,r,s,y) specified above is maximized for each basin, water shortage sharing rule, treaty agreement and storage capacity level. A total of 144 model runs are optimized.

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Acquah, S., Ward, F.A. Optimizing Adjustments to Transboundary Water Sharing Plans: A Multi-Basin Approach. Water Resour Manage 31, 5019–5042 (2017). https://doi.org/10.1007/s11269-017-1794-3

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Keywords

  • Economic benefit
  • transboundary water resources
  • constrained optimization
  • water treaties