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Investment-driven mixed firms: partial privatization by local governments

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Abstract

We analyze partial privatization by local governments, driven by investment and credit constraints, and provide a theory of monopolistic mixed firms based on strategic interaction between local politicians and private shareholders. Minority participation by private investors—as empirically observed—arises endogenously in the model to prevent investment expropriation. We consider the example of water supply with perfectly inelastic demand and fixed-price regulation, coupled with price discretion at a local level. Welfare-maximizing local governments face a trade-off between the increase in consumers’ surplus and the reduction in costly public funds. Therefore, private shareholders choose investment to keep the government share at a threshold such that the politician always sticks to the price-cap and dividends are then maximized. To consider normative issues, we compare investment by mixed firms and by a social planner.

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Notes

  1. To the extent that “off-budget enterprises” were exempted from limits imposed on municipal budgets, an important wave of corporatizations took place in countries like Italy and Germany as a result.

  2. These firms are included in the larger population of 2009 municipal firms concerning towns with more than 50,000 inhabitants.

  3. Bognetti and Robotti (2007) observe that in Italy partial privatization by local utilities involved in water supply was accompanied by new investments in 70 % of cases.

  4. Our result is also consistent with empirical evidence (Bortolotti and Faccio 2004), showing that partial privatization of firms where governments do not relinquish control rights does not negatively affect stock market valuation as frequently expected.

  5. From the theoretical point of view, mixed firms should be distinguished from Public Private Partnerships (PPPs) which have been extensively analyzed in the economic literature.

  6. Empirical studies consistently indicate a price-inelastic demand for water: a meta-analysis of almost 300 price elasticity studies reports a mean price elasticity of \(-0.41\) (Dalhuisen et al. 2003). Olmstead et al. (2007) consider the bias that could be due to estimations based on linear prices. They also consider nonlinear tariffs with separate estimates, finding a higher value for price elasticity, though equal to \(-0.59\). Interestingly, they fail to identify a price elasticity significantly different from zero for the uniform-price households.

  7. Motivations for a perfectly inelastic demand, up to price \(P^{\max }\)—implying a discontinuity at \(P^{\max }\) such that for \(P>P^{\max }\), water consumption becomes zero—may also include the opportunity of switching to substitutes such as water distribution carried out by tank trucks (as happens in areas not reached by the network).

  8. Water leaks in the distribution network and the related investment to detect and reduce them are one of the most important issues currently facing the water industry. Cfr. Egenhofer et al. (2012) for an assessment concerning European countries.

  9. Actually leaks negatively affect network pressure with bad effects on the water flow for final users. Reductions in pressure can be compensated by increasing the quantity of water injected into the network. Water waste may not be sustainable, especially in some local areas affected by water scarcity.

  10. The assumption of decreasing return to scale appears to be rather intuitive in this case and has been already used in similar frameworks (e.g., see Chakravorty et al. 1995).

  11. An increased water injection in the network due to water leaks implies greater pumping efforts, giving rise to increased energy costs. The latter can amount to a considerable share of total provision costs. Additional chemicals for water treatment may also be necessary, thereby raising variable costs.

  12. Actually any water undertaking with an efficiency parameter \(i>\underline{i}\) , when investing K it can get a further reduction in variable costs with respect to the level implied by the price-cap. Therefore, the price-cap allows more efficient firms to increase their revenues by the following amount: \(\beta \left[ \left( 2iK-\frac{(iK)^{2}}{L_{0}}\right) -\left( 2\underline{i}K-\frac{(\underline{i}K)^{2}}{L_{0}}\right) \right] =\beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right] >0\)

  13. In the specific case of water provision such an assumption can capture the fact that the private firms involved in the business of water provision (through partial or complete privatization) may be multinational firms.

  14. For example, with \(\lambda =0.01\) the ownership share of the local government in the mixed firms will be around 77 %.

  15. As what matters for the analysis of the first stage is simply the assumption that \(\alpha \rho >r\), one can notice that, as far as the choice of debt is concerned, the assumptions about the timing structure of the game are not crucial for the final equilibrium results.

  16. The intuition about welfare being strictly increasing in c—for any P—can be explained as follows. Let us consider firstly the case of \(P=\widehat{P}\). In this case \(U_{s}=\alpha \rho S^{\circ }\) [cfr. (10)], the variation of c affects welfare only through its effect on \(\widehat{P}\), which can be conveniently written as \(\widehat{P}=S^{\circ }\alpha \rho +(1-c)K\alpha \rho +K+crK+\beta \left( 1+L_{0}-2iK+\frac{(iK)^{2}}{L_{0}}\right) \). One can easily check that an increase in c has two opposite effects on \(\widehat{P}\). On the one hand, it increases the cost of capital in proportion to r; on the other hand, by reducing the private shareholders’ contribution to the corporation stock, it reduces their ownership share and the minimum dividends to be granted to them in proportion to \(\alpha \rho \). If the second effect more than compensates the first, due to \(\alpha \rho >r\), then any increase in c leads to a price reduction and thereby to an increase in welfare. Now let us consider the case of \(P=\overline{P}\). The regulator rewards all the amount of capital at a rate of \(\rho \), regardless of the financial source [cfr. (12)], so a variation of c affects welfare only through the effect on the local government dividends \(U_{s}\), as they are devoted to the reduction in distortionary taxation. By considering that \(U_{s}=s\varPi \), with \(\varPi =\overline{P}-\beta \left( 1+L_{0}-2iK+\frac{(iK)^{2}}{L_{0}}\right) -K-crK\), one can check that an increase in c has two opposite effects on the dividends cashed by the local government, and thereby on welfare. On the one hand, it increases the share of profits gained by the local government through s, which in turn leads to an increase in \(U_{s}\), a reduction in distortionary taxation and, thereby, to a welfare increase. On the other hand, any increase in c reduces the amount of corporation profits in proportion to r, leading to a lower reduction in distortionary taxation which negatively affects welfare. Notice that \(\rho >r\) is a sufficient condition for making the first effect greater than the second one, and thereby letting social welfare to increase in c.

  17. According to available empirical studies, \(\lambda \) is not expected to be greater than 0.3 (Snow and Warren 1996).

  18. Estimation of social damages due to water leaks appears to be quite difficult. To the best of our knowledge, there are no references in the literature, and evaluating the value of wasted water may be an arbitrary exercise. Our estimation is then based on the sum of: (1) Environmental costs due to the increase in energy use implied by greater pumping effort. This part of the damage can be evaluated by resorting to carbon prices or more generally to carbon values. (2) The value of a tax imposed by the French government on all water users to finance a national fund devoted to investments in water supply. According to Dore et al. (2004), this tax was set at a rate of FF 0.105/m3 in 1992.

References

  • Bennet, J. T., & Dilorenzo, T. J. (1982). Off-budget activities of local government: The bane of the tax revolt. Public Choice, 39(3), 333–342.

    Article  Google Scholar 

  • Bognetti, G., & Robotti, L. (2007). The provision of local public services through mixed enterprises: The Italian case. Annals of Public and Cooperative Economics, 78(3), 415–437.

    Article  Google Scholar 

  • Bortolotti, B., & Faccio, M. (2004). Reluctant privatization. Fondazione ENI Enrico Mattei, NOTA DI LAVORO, 130, 2004.

    Google Scholar 

  • Boycko, M., Shleifer, A., & Vishny, R. W. (1996). A theory of privatisation. The Economic Journal, 106, 309–319.

    Article  Google Scholar 

  • Chakravorty, U., Hochman, E., & Zilberman, D. (1995). A spatial model of optimal water conveyance. Journal of Environmental Economics and Management, 29(1), 25–41.

    Article  Google Scholar 

  • Dalhuisen, J. M., Florax, R. J. G. M., de Groot, H. L. F., & Nijkamp, P. (2003). Price and income elasticities of residential water demand: A meta-analysis. Land Economics, 79(2), 292–308.

    Article  Google Scholar 

  • Dore, M. H. I., Kushner, J., & Zumer, K. (2004). Privatization of water in the UK and France: What can we learn? Utilities Policy, 12(1), 41–50.

    Article  Google Scholar 

  • Egenhofer, C., Alessi, M., Teusch, J., & Nunez-Ferrer, J. (2012). Which economic model for a water-efficient Europe? CEPS Task Force Reports. SSRN: http://ssrn.com/abstract=2181382

  • Garcia, S., & Thomas, A. (2003). Regulation of public utilities under asymmetric information. Environmental and Resource Economics, 26, 145–162.

    Article  Google Scholar 

  • Joulfaian, D., & Marlow, M. L. (1991). The relationship between on-budget and off-budget government. Economic Letters, 35(3), 307–310.

    Article  Google Scholar 

  • Matsumura, T. (1998). Partial privatization in mixed duopoly. Journal of Public Economics, 70(3), 473–483.

    Article  Google Scholar 

  • Mediobanca (2015). Economia e finanza delle principali società partecipate dai maggiori Enti locali (2006–2013). www.mbres.it/it/publications/companies-owned-local-entities

  • Newbery, D. M. (1999). Privatization, restructuring, and regulation of network industries. Cambridge: MITPress.

    Google Scholar 

  • Noll, R. G., Shirley, M. M., & Cowan, S. (2000). Reforming urban water systems in developing countries. In A. O. Krueger (Ed.), Economic policy reform: The second stage (pp. 243–289). Chicago and London: The University of Chicago Press.

    Google Scholar 

  • Noll, R. G. (2002). The economics of urban water systems. In M. M. Shirley (Ed.), Thirsting for efficiency: The economics and politics of urban water system reform (pp. 43–64). Washington: The World Bank.

    Google Scholar 

  • OECD. (2011). Water governance in OECD Countries: A multi-level approach. OECD Studies on Water, OECD Publishing. doi:10.1787/9789264119284-en.

  • Olmstead, S., Hanemann, W. M., & Stavins, R. N. (2007). Water demand under alternative price structures. Journal of Environmental Economics and Management, 54(2), 181–198.

    Article  Google Scholar 

  • Perotti, E. (1995). Credible privatization. American Economic Review, 85(4), 847–859.

    Google Scholar 

  • Richter, P., Edeling, T., & Reichard, C. (2006). Kommunale Betriebe in größeren Städten. In W. Kilian, P. Richter, & J. H. Trapp (Eds.), Ausgliederung und Privatisierung in Kommunen (pp. 56–84). Berlin: Empirische Befunde zur Struktur kommunaler Aufgabenwahrnehmung.

    Google Scholar 

  • Shleifer, A., & Vishny, R. W. (1994). Politicians and firms. Quarterly Journal of Economics, 109, 133–150.

    Article  Google Scholar 

  • Snow, A., & Warren, R. S. (1996). The marginal welfare cost of public funds: Theory and estimates. Journal of Public Economics, 61(2), 289–305.

    Article  Google Scholar 

  • Venkatesh, G. (2012). Cost-benefit analysis—leakage reduction by rehabilitating old water pipelines: Case study of Oslo (Norway). Urban Water Journal, 9(4), 277–286.

    Article  Google Scholar 

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Correspondence to A. Cavaliere.

Appendices

Appendix 1

In this appendix, we study the monotonicity of the function V with respect to K.

$$\begin{aligned} V=\left\{ \begin{array} [c]{l} (1-p)\left[ \beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0} }\right] +(\rho -rc)K+\rho S^{\circ }\right] -(1-c)\alpha \rho K,\\ \mathrm {if}\ K\le S^{\circ }\frac{\lambda }{1-c}\\ 0,\mathrm {if}\ K>S^{\circ }\frac{\lambda }{1-c} \end{array} \right. \end{aligned}$$

When \(K\le S^{\circ }\frac{\lambda }{1-c}\), the complete form of V is

$$\begin{aligned} V= & {} \frac{(1-c)K}{S^{\circ }+(1-c)K}\left[ \beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right] +(\rho -rc)K+\rho S^{\circ }\right] \nonumber \\&-(1-c)\alpha \rho K \end{aligned}$$

which can be written as

$$\begin{aligned} V=\frac{(1-c)K}{S^{\circ }+(1-c)K}\left[ \beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right] +(\rho -rc-(1-c)\alpha \rho )K+\rho (1-\alpha )S^{\circ }\right] \end{aligned}$$

where the two factors are positive:

$$\begin{aligned}&\frac{(1-c)K}{S^{\circ }+(1-c)K}=1-s>0,\\&\beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right]>0\ \mathrm {if}\ K<2\frac{L_{0}}{i+\underline{i}},\ \mathrm {where} \ 2\frac{L_{0}}{i+\underline{i}}>2\frac{L_{0}}{i+i}=\frac{L_{0}}{i},\\&(\rho -rc-(1-c)\alpha \rho )=\rho [1-(1-c)\alpha ]-rc\underbrace{>} _{\rho>r}r[1-(1-c)\alpha -c]=r(1-\alpha )(1-c)>0,\\&\rho (1-\alpha )S^{\circ }>0 \end{aligned}$$

The first factor \(\frac{(1-c)K}{S^{\circ }+(1-c)K}\) has a positive derivative \(\frac{(1-c)S^{\circ }}{[S^{\circ }+(1-c)K]^{2}}\), whereas the second factor has the derivative

$$\begin{aligned} 2\beta (i-\underline{i})+\rho -rc-(1-c)\alpha \rho -2\beta \frac{i^{2} -\underline{i}^{2}}{L_{0}}K, \end{aligned}$$

which is positive when

$$\begin{aligned} K<\frac{2\beta (i-\underline{i})+\rho -rc-(1-c)\alpha \rho }{2\beta \frac{i^{2}-\underline{i}^{2}}{L_{0}}}=\frac{L_{0}}{i+\underline{i}}+\frac{\rho -rc-(1-c)\alpha \rho }{2\beta (i^{2}-\underline{i}^{2})}. \end{aligned}$$

This shows that an analytic conclusion about the monotonicity of V cannot be easily found. A sufficient condition is that for \(K<\frac{L_{0}}{i+\underline{i}}\), the function V is strictly increasing in K. However, we obtained an interesting result by simulation as follows:

  • We randomly generate 100,000 parameter sets in the ranges, \(\underline{i} = 0.074925\);

  • We computed the \(K^{\circ }\) that maximizes V in the range \(K\in \left( 0,2\frac{L_{0}}{i}\right) \).

  • We computed the number of times when \(K^{\circ }< \frac{S^{\circ }\, \lambda }{1-c}\) and \(K^{\circ }< \frac{L_{0}}{i}\). We found that this number is 0.

We are therefore reasonably sure that the function V is strictly increasing for \(K\in \left( 0,\frac{S^{\circ }\,\lambda }{1-c}\right) \).

Appendix 2

In this appendix, we formally prove that local welfare is strictly increasing in c for any P.

  1. 1.

    \(P=\widehat{P}\). By substituting and \(U_{s}(\widehat{P})=\alpha \rho S^{\circ }\) [see eq. (10)] in (8) we get the maximization problem

    $$\begin{aligned} \max _{c}W&=\max _{c}\left\{ P^{\max }-\widehat{P}-d\left[ L_{0} -2iK+\frac{(iK)^{2}}{L_{0}}\right] +(1+\lambda )\alpha \rho S^{\circ }\right\} \\ \mathrm {s.t.}&\widehat{P}=\left( \frac{1-c}{1-s}\,\alpha \rho +1+cr\right) K+\beta \left( 1+L_{0}-2iK+\frac{(iK)^{2}}{L_{0}}\right) \\&c\le \overline{c}. \end{aligned}$$

    By substitution of \((1-s)=\frac{(1-c)K}{S^{\circ }+(1-c)K}\) in \(\widehat{P}\), we obtain

    $$\begin{aligned} \widehat{P}=S^{\circ }\alpha \rho +(1-c)K\alpha \rho +K+crK+\beta \left( 1+L_{0}-2iK+\frac{(iK)^{2}}{L_{0}}\right) , \end{aligned}$$

    and differentiating W w.r.t. \(\widehat{P}\), we get

    $$\begin{aligned} \frac{\partial W}{\partial c}=-\frac{\partial \widehat{P}}{\partial c} =(\alpha \rho -r)K>0\ \mathrm {for}\ \alpha \rho >r. \end{aligned}$$
  2. 2.

    \(P=\overline{P}\), then the welfare maximization problem is

    $$\begin{aligned} \max _{c}W&=\max _{c}\left\{ P^{\max }-\overline{P}-d\left[ L_{0} -2iK+\frac{(iK)^{2}}{L_{0}}\right] +(1+\lambda )s(c,K)\varPi \left( \overline{P},K\right) \right\} \\ \mathrm {s.t.}&\overline{P}=\beta \left( 1+L_{0}-2\underline{i} K+\frac{(\underline{i}K)^{2}}{L_{0}}\right) +(1+\rho )K+\rho S^{\circ }\\&\varPi (\overline{P})=\beta (i-\underline{i})K\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right] +(\rho -cr)K+\rho S^{\circ }\\&s(c,K)=\frac{S^{\circ }}{S^{\circ }+(1-c)K}. \end{aligned}$$

    By differentiating w.r.t. to c, we get

    $$\begin{aligned} \frac{\partial W}{\partial c}&=\frac{\partial s}{\partial c}(1+\lambda )\varPi (\overline{P},K)+s(c,K)(1+\lambda )\frac{\partial \varPi (\overline{P} ,K)}{\partial c}=\\&=\frac{Ks(c,K)}{S^{\circ }+(1-c)K}(1+\lambda )\varPi (\overline{P} ,K)-s(c,K)(1+\lambda )rK. \end{aligned}$$

    By giving prominence to \((1+\lambda )Ks(c,K)\) and by substitution of \(\varPi (\overline{P},K)\), we get

    $$\begin{aligned} \frac{\partial W}{\partial c}=\frac{\beta K(i-\underline{i})}{S^{\circ }+(1-c)K}\left[ 2-\frac{(i+\underline{i})K}{L_{0}}\right] +\frac{(\rho -cr)K+\rho S^{\circ }}{S^{\circ }+(1-c)K}-r \end{aligned}$$

Notice that

$$\begin{aligned} \frac{(\rho -cr)K+\rho S^{\circ }}{S^{\circ }+(1-c)K}-r>0\Longrightarrow \frac{\partial W}{\partial c}>0\Longrightarrow c=\overline{c}. \end{aligned}$$

By solving we obtain

$$\begin{aligned} \frac{(\rho -cr)K+\rho S^{\circ }}{S^{\circ }+(1-c)K}-r=\frac{(\rho -r)(S^{\circ }+K)}{S^{\circ }+(1-c)K}>0. \end{aligned}$$

Appendix 3: Calibration exercise and simulations

Given the expression of optimal investment chosen by the social planner and those arising in equilibrium with partial privatization, it is difficult to consider the issue of investment distortions only in theoretical terms. We expect, however, that in most real situations, with credible parameter values, this distortion can be well defined. For this reason, in this section we calibrate the model to a plausible real case. Due to the difficulty to retrieve real data, we use a couple of studies to find the parameter values and to cross-check the consistence of some common parameter estimates. Calibration data are obtained from South-West France (Garcia and Thomas 2003) and Norway (Venkatesh 2012). Total demand is normalized to 1, so every water quantity is rescaled accordingly; we assume that, without any investment, water leaks would amount to 40 % of the total demand, i.e., \(L_{0}=0.4\). Monetary values in millions of Euros, M€.

  • France Table 1 presents the main figures from the French case. We use the average values for calibration. The variable cost is equal to \(\beta (1+L)\), therefore \(\beta \simeq 0.18\).

  • Norway The study presents many data from which we can infer technical and economic values. We use the extrapolated data concerning: total demand, leak volumes, rehabilitation cost, avoided leaks, cost savings. Monetary values are converted to Euros and considered in current terms. We obtain the following values: \(i\simeq 0.15\), variable costs can be estimated 0.568 M€/Mm3, therefore, in our normalized example, \(\beta \simeq 0.227\).

Table 1 Extrapolated data from Garcia and Thomas (2003), approximated figures

Summing up, we obtain reasonably close values for \(\beta \). Moreover, we can set \(i\simeq 0.15\) and \(d\simeq 0.04\),Footnote 18 corresponding to 0.1 €/m3. Therefore, we consider a “current” setting with parameters values

Starting from these reference settings, we explore a wide set of scenarios, for i ranging from 0.075 to 1.8 and \(\beta \) from 0.016 to 3.178. All cases are evaluated for \(\lambda \) from 0.01 to 0.3 (Snow and Warren 1996). This means that, for robustness check, we extend the parameter values well beyond a reasonably realistic range. For the sake of brevity, we present what we consider to be the most interesting and illustrative results. The full results are available upon request. Figure 2 shows the optimal investment chosen by a social planner, Fig. 3 shows the optimal investment with mixed firms, and Fig. 4 includes both types of investments to show when overinvestment or underinvestment is likely to arise. The values of optimal investments are plotted with respect to the efficiency parameter i in the cases of low/current/high variable cost and low/regular/high marginal cost of public funds.

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Cavaliere, A., Maggi, M. & Stroffolini, F. Investment-driven mixed firms: partial privatization by local governments. Int Tax Public Finance 24, 459–483 (2017). https://doi.org/10.1007/s10797-016-9426-z

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