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Spillover Effects in Irrigated Agriculture from the Groundwater Commons

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Abstract

This study examines irrigation spillover effects within the groundwater commons of the San Luis Valley in Colorado. We investigate the common pool competition predicted by a theoretical model of crop production through water-use intensity, acreage size choices, and production intensity among irrigators. By specifying Spatial Probit and regular Spatial Durbin Models, we empirically measure not only the effects of these choices on neighbors, but also the effect of other factors that affect water use and cultivation choices at neighboring farming units. For all three response variables, the results show that irrigators consider neighbors’ responses, with the strength of spatial dependency being highest for production intensity. Additionally, there are significant spillover effects from changes in key covariates, demonstrating the inadequacy of estimating direct effects only. For example, a one-foot increase in depth-to-water has both direct and indirect positive effects on water-use intensity, but the indirect effect constitutes over 81% of the total effect.

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Notes

  1. A notable USGS aquifer study (Lyford 1979) investigated the nearby San Juan Basin and found that “[t]ransmissivities of the sandstones range from 50 to 300 squared feet per day.” Unfortunately, the study area abuts the SLV but does not overlap it enough to generate the needed data.

  2. The Targeted Aquifer Recharge Project conducted an electrical resistivity study, which identifies soil types and improves transmissivity knowledge, with very limited sample sites (Ziegler 2020).

  3. See Mayo (2020) for a technical background on geologic history and groundwater flow; the northern portion of the SLV (and our main study area) is “a region of internal drainage due to...a sedimentary wedge” (pgs. 988–989).

  4. Recently, water managers have focused more on aquifer recharge, funding an ongoing pilot project where irrigators in targeted, optimized locations irrigate in a specific manner so as to make it easier for water used in crops to make it back down to the aquifer. This Targeted Aquifer Recharge Project is run by the Mosca-Hooper Conservation District (Mosca-Hooper Conservation District 2022), while the Closed Basin Project is managed by the Rio Grande Water Conservation District.

  5. It is important to note that the division of the subdistricts was completed taking cognizance of the spatial interconnectedness among wells in the same sub-district. Wells in a particular subdistrict were determined to be hydrologically independent of wells in other subdistricts (Smith et al. 2017).

  6. Our single-stage game could be repeated over time; from folk theorems, we know that repeating the Nash equilibrium of this single-stage game (a withdrawal plan as a function of scarcity) can be a sub-game perfect Nash equilibrium of the repeated game. We leave other potential equilibria to future research.

  7. \(\frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2} \cdot \frac{\partial s^i(\cdot )}{\partial w^j_m} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} < \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \left| \frac{\partial ^2\,s^i(\cdot )}{\partial w^j_m \partial w^i_k} \right|\) and \(\frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2} \left( \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) ^2 < \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \left| \frac{\partial ^2\,s^i(\cdot )}{\partial {w^i_k}^2} \right|\)

  8. Irrigators will face the same tax rate if and only if \(E^i = E^j\), where \(i\ne j\).

  9. Including year dummies that vary over t and not n, as notationally recommended by Wooldridge (2019).

  10. See eg. Kapoor et al. (2007); Miranda et al. (2017, 2018) for detailed treatment of spatial correlated random effects model.

  11. The decomposition of the effects has gain much traction particularly among studies that seek to examine spatial dependence as well as peer effects through social networks (see for example, LeSage and Pace 2009; Bramoullé et al. 2009; Gibson et al. 2017; Ragoubi and El Harbi 2019)

  12. In fact, the non-IV regression underestimates the effect depth-to-water has on acre-feet pumped, and using lagged depth-to-water has a significantly greater effect on pumping.

  13. Prior to 2009, a number of wells do not have measures of certain variables, including the elevations used to calculate the depth-to-water.

  14. We follow Smith et al. (2017) in using 1998 as the baseline, “when all units had the largest expanse of irrigated crops” (pg. 1001).

  15. Results on the split data for subdistrict with pumping fee and subdistricts without the pumping fee in the robustness check section indicate similar competitive posture amount neighboring irrigating units.

  16. Weakly positive, because the effect could be zero in a non-transmissive setting, but it is extremely unlikely for the sign to be negative.

  17. In a dynamic game, we would expect zero land sale in equilibrium. With homogeneous agents, we expect no land sale quickly, while with heterogeneous agents, there may be a longer adjustment period.

References

  • Anselin L (2002) Under the hood issues in the specification and interpretation of spatial regression models. Agric Econ 27(3):247–267

    Google Scholar 

  • Arellano M (2003) Predetermined variables. Panel data econometrics. Oxford University Press, Oxford

    Google Scholar 

  • Belotti F, Hughes G, Mortari AP (2017) Spatial panel-data models using Stata. Stata J 17(1):139–180

    Google Scholar 

  • Bramoullé Y, Djebbari H, Fortin B (2009) Identification of peer effects through social networks. J Econom 150(1):41–55

    Google Scholar 

  • Bredehoeft JD, Young R-A (1970) The temporal allocation of ground water—A simulation approach. Water Resour Res 6(1):3–21

    Google Scholar 

  • Brozović N, Sunding D-L, Zilberman D (2010) On the spatial nature of the groundwater pumping externality. Resour Energy Econ 32(2):154–164

    Google Scholar 

  • Brueckner JK (2003) Strategic interaction among governments: an overview of empirical studies. Int Reg Sci Rev 26(2):175–188

    Google Scholar 

  • Burness H-S, Brill T-C (2001) The role for policy in common pool groundwater use. Resour Energy Econ 23(1):19–40

    Google Scholar 

  • Chamberlain G (1980) Analysis of covariance with qualitative data. Rev Econ Stud 47(1):225–238

    Google Scholar 

  • Chamberlain G (1984) Panel data. In: Griliches Z, Intriligator M (eds) Handbook of econometrics. North Holland, Amsterdam

    Google Scholar 

  • Dasgupta P-S, Heal G-M (1979) Economic theory and exhaustible resources. Cambridge University Press, Cambridge

    Google Scholar 

  • Edwards E-C (2016) What lies beneath? Aquifer heterogeneity and the economics of groundwater management. J Assoc Environ Res Econ 3(2):453–491

    Google Scholar 

  • Eswaran M, Lewis T (1984) Appropriability and the extraction of a common property resource. Economica 51(204):393–400

    Google Scholar 

  • Fulton J, Norton M, Shilling F (2019) Water-indexed benefits and impacts of California almonds. Ecol Ind 96:711–717

    Google Scholar 

  • Gibson J (2019) Are you estimating the right thing? An editor reflects. Appl Econ Perspect Policy 41(3):329–350

    Google Scholar 

  • Gibson J, Datt G, Murgai R, Ravallion M (2017) For India’s rural poor, growing towns matter more than growing cities. World Dev 98:413–429

    Google Scholar 

  • Gisser M (1983) Groundwater: focusing on the real issue. J Polit Econ 91(6):1001–1027

    Google Scholar 

  • Gisser M, Sanchez D-A (1980) Competition versus optimal control in groundwater pumping. Water Resour Res 16(4):638–642

    Google Scholar 

  • Halaby C-N (2003) Panel models for the analysis of change and growth in life course studies. Handbook of the life course. Springer, Berlin, pp 503–527

    Google Scholar 

  • Hardin G (1968) The tragedy of the commons. Science 162(3859):1243–1248

    Google Scholar 

  • Ito J (2012) Collective action for local commons management in rural Yunnan, China: empirical evidence and hypotheses using evolutionary game theory. Land Econ 88(1):181–200

    Google Scholar 

  • Ivers C (2022) Closed Basin Project. Rio Grande Water Conservation District. https://www.rgwcd.org/closed-basin-project

  • Kapoor M, Kelejian H-H, Prucha I-R (2007) Panel data models with spatially correlated error components. J Econom 140(1):97–130

    Google Scholar 

  • Kotani K, Kakinaka M, Matsuda H (2008) Optimal escapement levels on renewable resource management under process uncertainty: some implications of convex unit harvest cost. Environ Econ Policy Stud 9(2):107–118

    Google Scholar 

  • Koundouri P (2004) Potential for groundwater management: Gisser-Sanchez effect reconsidered. Water Resour Res. https://doi.org/10.1029/2003WR002164

    Article  Google Scholar 

  • Koundouri P, Xepapadeas A (2004) Estimating accounting prices for common pool natural resources: a distance function approach. Water Resour Res. https://doi.org/10.1029/2003WR002170

    Article  Google Scholar 

  • LeSage J, Pace R (2009) Introduction to spatial econometrics. Taylor and Francis, Boca Raton

    Google Scholar 

  • LeSage J-P (2008) An introduction to spatial econometrics. Rev Econom Ind 123:19–44

    Google Scholar 

  • Leszczensky L, Wolbring T (2022) How to deal with reverse causality using panel data? Recommendations for researchers based on a simulation study. Sociol Methods Res 51(2):837–865

    Google Scholar 

  • Lyford F-P (1979) Ground water in the San Juan Basin, New Mexico and Colorado (Vol 79) (no 73). Department of the Interior, Geological Survey, Water Resources Division

  • Mayo AL (2020) Mapping paleo-lacustrine environments and long-term climate trends using groundwater chemistry. Hydrogeol J 28(3):987–1002

    Google Scholar 

  • Miranda K, Martínez-Ibañez O, Manjón-Antolín M (2017) Estimating individual effects and their spatial spillovers in linear panel data models: public capital spillovers after all? Spat Stat 22:1–17

    Google Scholar 

  • Miranda K, Martínez Ibáñez O, Manjón Antolín M-C. (2018) A correlated random effects spatial Durbin model

  • Moore M-R, Gollehon N-R, Carey M-B (1994) Multicrop production decisions in western irrigated agriculture: the role of water price. Am J Agric Econ 76(48):59–874

    Google Scholar 

  • Mosca-Hooper Conservation District (2022 ) SLV Aquifer Targeted Recharge Project—Identifying “sweet spots” on the landscape for targeted recharge via ditches and ponds. State of Colorado. https://mhcd.colorado.gov/projects

  • Msangi S-M (2004) Managing groundwater in the presence of asymmetry: three essays. University of California, Davis

    Google Scholar 

  • Mundlak Y (1978) On the pooling of time series and cross section data. Econometrica J Econom Soc 46:69–85

    Google Scholar 

  • Negri D-H (1989) The common property aquifer as a differential game. Water Resour Res 25(1):9–15

    Google Scholar 

  • Noel JE, Gardner BD, Moore CV (1980) Optimal regional conjunctive water management. Am J Agric Econ 62(3):489–498

    Google Scholar 

  • Ostrom E (1990) Governing the commons: the evolution of institutions for collective action. Cambridge University Press, Cambridge

    Google Scholar 

  • Papke LE, Wooldridge JM (2008) Panel data methods for fractional response variables with an application to test pass rates. J Econom 145(1–2):121–133

    Google Scholar 

  • Pfeiffer L, Lin C-YC (2012) Groundwater pumping and spatial externalities in agriculture. J Environ Econ Manag 64(1):16–30

    Google Scholar 

  • Provencher B, Burt O (1993) The externalities associated with the common property exploitation of groundwater. J Environ Econ Manag 24(2):139–158

    Google Scholar 

  • Ragoubi H, El Harbi S (2019) Entrepreneurship and income inequality: a dynamic spatial panel data analysis. Tékhne 17(1):10–30

    Google Scholar 

  • RGWCD (2022) Subdistricts. Rio Grande Water Conservation District. https://www.rgwcd.org/subdistricts

  • RGWCD Subdistrict No. 1 (2017) Rio Grande Water Conservation District. https://www.rgwcd.org/attachments/subdistrict1/Plan%20Revisions/Plan%20Water%20Management%20AMENDED%206Jun17_draft.pdf

  • Rouhi Rad M, Manning DT, Suter JF, Goemans C (2021) Policy leakage or policy benefit? Spatial spillovers from conservation policies in common property resources. J Assoc Environ Resour Econ 8(5):923–953

    Google Scholar 

  • Rubio SJ, Casino B (2003) Strategic behavior and efficiency in the common property extraction of groundwater. Environ Resour Econ 26(1):73–87

    Google Scholar 

  • Saak AE, Peterson JM (2007) Groundwater use under incomplete information. J Environ Econ Manag 54(2):214–228

    Google Scholar 

  • Schoengold K, Sunding DL, Moreno G (2006) Price elasticity reconsidered: panel estimation of an agricultural water demand function. Water Resour Res. https://doi.org/10.1029/2005WR004096

    Article  Google Scholar 

  • Schunck R (2013) Within and between estimates in random-effects models: advantages and drawbacks of correlated random effects and hybrid models. Stata J 13(1):65–76

    Google Scholar 

  • Schworm WE (1983) Monopsonistic control of a common property renewable resource. Can J Econ 16:275–287

    Google Scholar 

  • Sears L, Caparelli J, Lee C, Pan D, Strandberg G, Vuu L, Lin Lawell CYC (2018) Jevons’ paradox and efficient irrigation technology. Sustainability. https://doi.org/10.3390/su10051590

    Article  Google Scholar 

  • Sears L, Lim D, Lawell CYCL (2018) The economics of agricultural groundwater management institutions: the case of California. Water Econ Policy 4(03):1850003

    Google Scholar 

  • Simonds W J (2015) The San Luis Valley Project. US Bureau of Reclamation. https://www.usbr.gov/history/sanluisv.html

  • Smith SM (2018) Economic incentives and conservation: crowding-in social norms in a groundwater commons. J Environ Econ Manag 90:147–174

    Google Scholar 

  • Smith SM, Andersson K, Cody KC, Cox M, Ficklin D (2017) Responding to a groundwater crisis: the effects of self-imposed economic incentives. J Assoc Environ Resour Econ 4(4):985–1023

    Google Scholar 

  • Theis CV (1938) The significance and nature of the cone of depression in ground-water bodies. Econ Geol 33(8):889–902. https://doi.org/10.2113/gsecongeo.33.8.889

    Article  Google Scholar 

  • Tobler WR (1970) A computer movie simulating urban growth in the Detroit region. Econ Geogr 46(sup 1):234–240

    Google Scholar 

  • Wang C, Segarra E (2011) The economics of commonly owned groundwater when user demand is perfectly inelastic. J Agric Resour Econ 36:95–120

    Google Scholar 

  • Wooldridge JM (2010) Econometric analysis of cross section and panel data. MIT Press, Cambridge

    Google Scholar 

  • Wooldridge JM (2014) Quasi-maximum likelihood estimation and testing for nonlinear models with endogenous explanatory variables. J Econom 182(1):226–234

    Google Scholar 

  • Wooldridge JM (2019) Correlated random effects models with unbalanced panels. J Econom 211(1):137–150

    Google Scholar 

  • Yu J, de Jong R, fei Lee L (2008) Quasi-maximum likelihood estimators for spatial dynamic panel data with fixed effects when n and t are large. J Econom 146(1):118–134

    Google Scholar 

  • Ziegler K (2020) Geologic background. Soil Carbon Coalition, Mosca-Hooper Conservation District. https://soilcarboncoalition.org/html/slv/rop.html

Download references

Acknowledgements

The authors thank Megan Brown for hydrogeology detail, Maria Ponomareva for econometric advice, and Steven Smith for data advice and willingness to support a graduate student working in the same area. The authors also gratefully acknowledge the work of three anonymous reviewers.

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Appendices

Appendix 1 Additional Derivations

1.1 Individual Problem

The first order conditions from irrigator j’s Nash equilibrium problem are as follows:

$$\begin{aligned} \begin{aligned} \frac{\partial {\varvec{\Uppi }^{j}}}{\partial w^j_k}&= \sum _{\ell =0}^K \frac{\partial \varvec{\pi }^{j*}_\ell \big (p_\ell , {\textbf {r}}, B^j(s^j(w^j, w^i),b), n^{j*}_\ell (\cdot ); {\textbf {x}}\big )}{\partial w^j_k} \\&= \sum _{\ell =0}^{K} \left[ \left( \frac{\partial \varvec{\pi }^{j*}_\ell (\cdot )}{\partial B^j(\cdot )} + {\frac{\partial \varvec{\pi }^{j*}_\ell (\cdot )}{\partial n^{j*}_\ell (\cdot )} \cdot } \frac{\partial n^{j*}_\ell (\cdot )}{\partial B^j(\cdot ) } \right) \left( \frac{\partial B^j(\cdot )}{\partial s^j(\cdot )} \cdot \frac{\partial s^j(\cdot )}{\partial w^j_k} \right) \right] \le 0 \\ \end{aligned} \end{aligned}$$
(9)

with equality if water withdrawal is positive, i.e. \(w_k^j > 0\).

Using the Implicit Function Theorem, we see:

$$\begin{aligned} \frac{d w^i_k}{d w^j_m} = - \frac{ \displaystyle \frac{\partial }{\partial w^j_m}\left[ \frac{\partial {\varvec{\Uppi }^{i}}}{\partial w^i_k}\right] }{\displaystyle \frac{\partial }{\partial w^i_k}\left[ \frac{\partial {\varvec{\Uppi }^{i}}}{\partial w^i_k}\right] } = - \frac{\displaystyle \frac{\partial ^2 {\varvec{\Uppi }^{i}}}{\partial w^i_k \partial w^j_m }}{\displaystyle \frac{\partial ^2 {\varvec{\Uppi }^{i}}}{\partial {w^i_k}^2}}. \end{aligned}$$
(10)

The strategic effect of j’s total withdrawal will be made up of these individual effects, which are the cross-partial and the second order condition of own withdrawal on profits. Because of the external negative sign, the strategic effect will be positive if either numerator or denominator (but not both) is positive, while it would be negative if numerator and denominator match in sign. The effect will be small in absolute terms if the own second order condition is larger in magnitude than that due to the opponent, while the effect will be large if the other-directed second order condition is larger. The full second order conditions, with respect to \(w^j_m\) and \(w^i_k\) are as follows:

$$\begin{aligned}& \frac{\partial }{\partial w^j_m} \left[ \frac{\partial {\varvec{\Uppi }^{i}}}{\partial w^i_k}\right]= \sum _{\ell =0}^K \Bigg \{ \left( \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{ \partial B^i(\cdot )^2 } + \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )^2} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}\cdot \frac{\partial ^2 n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 } \right) \nonumber \\ &\quad\quad\quad\quad\quad\quad\; \cdot \left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \right) ^2 \left( \frac{\partial s^i(\cdot )}{\partial w^j_m} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) + \left( \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \\ &\quad\quad\quad\quad\quad\quad\; {\cdot} \left. {\left( {\frac{{\partial ^{2} B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )^{2} }} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{m}^{j} }} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{k}^{i} }} + \frac{{\partial B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )}} \cdot \frac{{\partial ^{2} s^{i} ( \cdot )}}{{\partial w_{m}^{j} \partial w_{k}^{i} }}} \right)} \right\} \end{aligned}$$
(11)
$$\begin{aligned}\frac{\partial }{\partial w^i_k} \left[ \frac{\partial {\varvec{\Uppi }^{i}}}{\partial w^i_k}\right]&= \sum _{\ell =0}^K \Bigg \{ \left( \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{ \partial B^i(\cdot )^2 } + \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )^2} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}\cdot \frac{\partial ^2 n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 } \right) \nonumber \\& \quad\;\cdot \left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) ^2 + \left( \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \nonumber \\&\quad\;\cdot \left( \frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2} \left( \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) ^2 + \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial ^2 s^i(\cdot )}{\partial {w^i_k}^2} \right) \Bigg \} \end{aligned}$$
(12)

Using Eqs. (11) and (12), we can write \(-\frac{d w^i_k}{d w^j_m}\) as:

$$\frac{{ {\sum\limits_{{l = 0}}^{K} \begin{gathered} \left\{ {\left( {\frac{{\partial ^{2} \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )^{2} }} + \frac{{\partial ^{2} \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )^{2} }} \cdot \frac{{\partial n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}} + \frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )}} \cdot \frac{{\partial ^{2} n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )^{2} }}} \right)\left( {\frac{{\partial B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )}}} \right)^{2} \left( {\frac{{\partial s^{i} ( \cdot )}}{{\partial w_{m}^{j} }} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{k}^{i} }}} \right)} \right. \hfill \\ \left. {\quad \quad + \left( {\frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}} + \frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )}} \cdot \frac{{\partial n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}}} \right)\left( {\frac{{\partial ^{2} B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )^{2} }} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{m}^{j} }} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{k}^{i} }} + \frac{{\partial B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )}} \cdot \frac{{\partial ^{2} s^{i} ( \cdot )}}{{\partial w_{m}^{j} \partial w_{k}^{i} }}} \right)} \right\} \hfill \\ \end{gathered} } }}{{ {\sum\limits_{{l = 0}}^{K} \begin{gathered} \left\{ {\left( {\frac{{\partial ^{2} \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )^{2} }} + \frac{{\partial ^{2} \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )^{2} }} \cdot \frac{{\partial n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}} + \frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )}} \cdot \frac{{\partial ^{2} n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )^{2} }}} \right)\left( {\frac{{\partial B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )}} \cdot \frac{{\partial s^{i} ( \cdot )}}{{\partial w_{k}^{i} }}} \right)^{2} } \right. \hfill \\ \left. {\quad \quad \left( {\frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}} + \frac{{\partial \pi _{\ell }^{{i*}} ( \cdot )}}{{\partial n_{\ell }^{{i*}} ( \cdot )}} \cdot \frac{{\partial n_{\ell }^{{i*}} ( \cdot )}}{{\partial B^{i} ( \cdot )}}} \right)\left( {\frac{{\partial ^{2} B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )^{2} }}\left( {\frac{{\partial s^{i} ( \cdot )}}{{\partial w_{k}^{i} }}} \right)^{2} + \frac{{\partial B^{i} ( \cdot )}}{{\partial s^{i} ( \cdot )}} \cdot \frac{{\partial ^{2} s^{i} ( \cdot )}}{{\partial w_{k}^{{i2}} }}} \right)} \right\} \hfill \\ \end{gathered} } }}$$
(13)

With regard to the individual first derivative terms, we assumed for all crops k that an increase in the total marginal cost of water decreases profits, \(\frac{\partial \varvec{\pi }^i_k(\cdot )}{\partial B^i(\cdot )} < 0\), while profits are non-decreasing in land allocation, \(\frac{\partial \varvec{\pi }^i_k(\cdot )}{\partial n^{i*}_k(\cdot )} \ge 0\). Because of lift cost, increasing depth-to-water increases total marginal cost, \(\frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} > 0\). We assume that an agent’s own water use weakly increases their scarcity measure, \(\frac{\partial s^i(\cdot )}{\partial w^i_k(\cdot )}\ge 0\); we also assume that another agent’s water use weakly increasesFootnote 16 agent i’s scarcity, \(\frac{\partial s^i(\cdot )}{\partial w^j_m} \ge 0\). Less obvious, however, is how total marginal cost of water affects the land dedicated to various crops, \(\frac{\partial n^{i*}_k (\cdot )}{\partial B^i(\cdot )}\): the farmer may decrease land for water-intensive crops and increase the allocation for fallowing or other crops, or there may be no reaction at all. In a particular growing season, it is unlikely the farmer will be able to purchase land quickly enough to grow additional crops that season. If we also assume that land is sold outside of the growing season (listed after a previous season), then we can see that in a particular game, total land is fixed, \(\sum _{k=0}^K n^i_k = N^i\). Thus, when examining the derivatives, we know that their sum must add up to a constant, which is zero in the case of the one-stage gameFootnote 17 with no land sale: \(\sum _{k=0}^K \frac{\partial n^i_k}{\partial B^i} = 0\).

With regard to the second derivative terms, we assumed convex profits, meaning \(\frac{\partial ^2 \pi ^{i*}_k(\cdot )}{\partial B^i(\cdot )^2} \ge 0\). Resource cost functions are often convex, i.e. accelerating in cost (Schworm 1983; Kotani et al. 2008), and so we assume \(\frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2} \ge 0\). Unfortunately, a priori, we cannot say much about the remaining second derivatives. There are two derivatives about the second order effect of water withdrawal—both i’s and j’s—on i’s depth-to-water. While we are comfortable assuming the first derivative is weakly positive (taking out water increases scarcity), we are unsure whether this effect is increasing, constant, or decreasing. The own second order effect, \(\frac{\partial ^2\,s^i(\cdot )}{\partial w^i_k(\cdot )^2}\), reflects the curvature with regard to water withdrawal for only the farmer in question, while the cross-partial, \(\frac{\partial ^2\,s^i(\cdot )}{\partial w^j_m \partial w^i_k(\cdot )}\), reflects how another farmer’s withdrawals change the marginal cost of withdrawal for farmer i. Additionally, we will remain agnostic on the second derivative of land allocation for crop k with respect to water cost, \(\frac{\partial ^2 n^{i*}_k (\cdot )}{\partial B^i(\cdot )^2}\).

Examining the numerator of Eq. (13), an individual term in the summation is:

$$\begin{aligned} \begin{aligned}&\left( \underbrace{\frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 }}_{\ge 0} + \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )^2} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}}_{\ge 0}\cdot \frac{\partial ^2 n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 } \right) \underbrace{\left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \right) ^2}_{>0} \underbrace{\left( \frac{\partial s^i(\cdot )}{\partial w^j_m} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) }_{>0} \\&\quad+ \left( \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )}}_{<0} + \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}}_{\ge 0} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \left( \underbrace{\frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2}}_{\ge 0} \cdot \underbrace{\frac{\partial s^i(\cdot )}{\partial w^j_m} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k}}_{>0} + \underbrace{\frac{\partial B^i(\cdot )}{\partial s^i(\cdot )}}_{>0} \cdot \frac{\partial ^2 s^i(\cdot )}{\partial w^j_m \partial w^i_k} \right) \end{aligned} \end{aligned}$$
(14)

Meanwhile, an individual term in the denominator is:

$$\begin{aligned} \begin{aligned}&\left( \underbrace{\frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 }}_{\ge 0} + \frac{\partial ^2 \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )^2} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )} + \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}}_{\ge 0}\cdot \frac{\partial ^2 n^{i*}_\ell (\cdot )}{\partial B^i(\cdot )^2 } \right) \underbrace{\left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) ^2}_{>0} \\&\quad+ \left( \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial B^i(\cdot )}}_{<0} + \underbrace{\frac{\partial \varvec{\pi }^{i*}_\ell (\cdot )}{\partial n^{i*}_\ell (\cdot )}}_{\ge 0} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \left( \underbrace{\frac{\partial ^2 B^i(\cdot )}{\partial s^i(\cdot )^2}}_{\ge 0} \underbrace{\left( \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) ^2}_{>0} + \underbrace{\frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} }_{>0} \cdot \frac{\partial ^2 s^i(\cdot )}{\partial {w^i_k}^2} \right) \end{aligned} \end{aligned}$$
(15)

The first thing to note is that the sign of \(\frac{d w^i_k}{d w^j_m}\) will depend on the signs of in Eqs. (14) and (15) added up over K. For each crop, these only differ according to curvature of profits with respect to land allocation and land reallocation with respect to water cost. The first terms of both Eqs. (14) and (15) will match in sign, so the second term that will determine the sign of the strategic effect. This second term is the change in profits per crop scaled by the adjustments in scarcity due to withdrawals and water’s cost due to scarcity.

The second thing to note is how these two expressions differ from each other: the denominator has a squared term \(\left( \frac{\partial s^i(\cdot )}{\partial w^i_k}\right) ^2\), where the numerator has a product of matching signs but potentially not magnitudes, \(\frac{\partial s^i(\cdot )}{\partial w^j_m} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k}\). Additionally, the final term in the numerator has the cross-partial of withdrawal, while that term in the denominator has the own second order effect. These terms are where potential differences in sign and magnitude arise.

1.2 Coordinated Problem

The first order conditions of the coordinated problem with respect to i’s water choices are as follows:

$$\begin{aligned}\begin{aligned} & \frac{\partial {\varvec{\Uppi }^{sp}}}{\partial w^i_k}= \sum _{\ell =0}^{K} \left( \frac{\partial \varvec{\pi }^i_\ell \big (p_\ell , {\textbf {r}}, B^i(s^i(w^i, w^j),b), n^{i*}_\ell (\cdot ); {\textbf {x}}\big )}{\partial w^i_k} + \frac{\partial \varvec{\pi }^j_\ell \big (p_\ell , {\textbf {r}}, B^j(s^j(w^i, w^j),b), n^{j*}_\ell (\cdot ); {\textbf {x}}\big )}{\partial w^i_k} \right) \\& \quad\quad\;= \sum _{\ell =0}^{K} \left( \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial B^i(\cdot )} \cdot \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} + \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial n^{i*} _\ell (\cdot )} \cdot \frac{\partial n^{i*} _\ell (\cdot )}{\partial B^i(\cdot ) }\cdot \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) \\&\quad\quad\quad\;+\sum _{\ell =0}^{K} \left( \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial B^j(\cdot )} \cdot \frac{\partial B^j(\cdot )}{\partial s^j(\cdot )} \cdot \frac{\partial s^j(\cdot )}{\partial w^i_k} + \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial n^{j*} _\ell (\cdot )} \cdot \frac{\partial n^{j*} _\ell (\cdot )}{\partial B^j(\cdot ) }\cdot \frac{\partial B^j(\cdot )}{\partial s^j(\cdot )} \cdot \frac{\partial s^j(\cdot )}{\partial w^i_k} \right) \\&\quad\quad\;= \sum _{\ell =0}^{K} \left( \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial n^{i*} _\ell (\cdot )} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^i_k} \right) \\&\quad\quad\quad\;+ \sum _{\ell =0}^{K} \hspace{-5.69054pt}\underbrace{ \left( \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial B^j(\cdot )} + \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial n^{j*} _\ell (\cdot )} \cdot \frac{\partial n^{j*}_\ell (\cdot )}{\partial B^j(\cdot ) } \right) \left( \frac{\partial B^j(\cdot )}{\partial s^j(\cdot )} \cdot \frac{\partial s^j(\cdot )}{\partial w^i_k} \right) }_{ E^i_k } \le 0 \\ \end{aligned} \end{aligned}$$
(16)

with equality if water withdrawal is positive, i.e. \(w_k^i > 0\).

Again, assuming the irrigators are symmetric, we have for \(w^j_k\)

$$\begin{aligned} \begin{aligned} & \frac{\partial {\varvec{\Uppi }^{sp}}}{\partial w^j_k}= \sum _{\ell =0}^{K} \left( \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial B^j(\cdot )} + \frac{\partial \varvec{\pi }^j_\ell (\cdot )}{\partial n^{j*} _\ell (\cdot )} \cdot \frac{\partial n^{j*}_\ell (\cdot )}{\partial B^j(\cdot ) } \right) \left( \frac{\partial B^j(\cdot )}{\partial s^j(\cdot )} \cdot \frac{\partial s^j(\cdot )}{\partial w^j_k} \right) \\& \quad\quad\quad\;\;+ \sum _{\ell =0}^{K} \hspace{-5.69054pt}\underbrace{ \left( \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial B^i(\cdot )} + \frac{\partial \varvec{\pi }^i_\ell (\cdot )}{\partial n^{i*} _\ell (\cdot )} \cdot \frac{\partial n^{i*}_\ell (\cdot )}{\partial B^i(\cdot ) } \right) \left( \frac{\partial B^i(\cdot )}{\partial s^i(\cdot )} \cdot \frac{\partial s^i(\cdot )}{\partial w^j_k} \right) }_{ E^j_k } \le 0 \\ \end{aligned} \end{aligned}$$
(17)

with equality if water withdrawal is positive, i.e. \(w_k^j > 0\).

Appendix 2 Additional Tables

We include tables for results for the larger 2- and 5-mile radii for all three regression specifications, as well as production intensity (share of acreage cropped) broken out by subdistrict. See Table 7, 8, 9, 10 and 11.

Table 7 Direct, Indirect and Total Effects for Water Use (acre-foot/acre) for 2- and 5-mile radii
Table 8 Direct, indirect and total effects for acreage irrigated for 2- and 5-mile radii
Table 9 Average partial direct and indirect effects for proportion of total available acres irrigated for 2- and 5-mile radii
Table 10 Production intensity for subdistrict with pumping fee—half-mile radius
Table 11 Production intensity for subdistrict with no pumping fee—half-mile radius

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Ekpe, G.K., Klis, A.A. Spillover Effects in Irrigated Agriculture from the Groundwater Commons. Environ Resource Econ 86, 469–507 (2023). https://doi.org/10.1007/s10640-023-00801-6

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