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Coaseian Biodiversity Conservation and Market Power

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Abstract

We apply a land-use approach to biodiversity conservation (BC) by assuming that the global public good ‘biodiversity’ is positively correlated with the share of land protected by land-use restrictions against the deterioration of habitats, ecosystems, and biodiversity. The willingness to pay for BC is positive in developed countries (North), but very low in developing countries (South). Taking the no-policy regime as our point of departure, we analyze two concepts of BC: the northern countries’ financial support of BC in the South, and the coordination of northern countries’ BC efforts. In each regime, governments may either take prices as given or may act strategically by seeking to manipulate the terms of trade in their favor. Our numerical analysis yields results with unexpected policy implications. If northern countries support BC financially in the South without coordinating their actions, the protected land, biodiversity and welfare increase so slightly that this BC policy is almost ineffective. The BC concept with a Coaseian flavor—in which northern countries support BC financially in the South and coordinate their action—is efficient if governments act non-strategically. Otherwise, the concept is an ineffective BC policy instrument, because the incentives for expanding the protected land the BC policy creates are so strong that biodiversity actually becomes excessive.

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Notes

  1. In its recent Fifth Report to the Convention on Biological Diversity (European Commission 2014), the European Union states that extensive areas of agriculture, grasslands and wetlands continue to decline across Europe, while artificial surfaces continue to expand.

  2. Ferraro and Simpson (2002) have investigated the cost-effectiveness of payments for ecosystem conservation.

  3. In ecology, a large literature applies the “species area curve”, which describes the relationship between the area of a habitat and the number of species found within that area. A reduction in the size of a habitat reduces biodiversity in terms of the species area relationship (e.g. Kinzig and Harte 2000; May et al. 1995), which is also used in economic papers on land use and biodiversity conservation (e.g. Barbier and Schulz 1997; Polasky et al. 2004).

  4. For a more realistic land-use approach based on the new economic geography with centrifugal-centripetal forces in economic and ecological systems, see Rauscher and Barbier (2010).

  5. Since the North is willing to pay more for biodiversity than the South, it is in the North’s interest to compensate the South for expanding its protected area. Panayotou (1994) describes a similar market concept without providing a formal analysis.

  6. In the Coaseian spirit, we refrain from providing an institutional structure for the North–North coordination such as a North–North BC market or a self-enforcing North–North agreement (as e.g. Barrett 1994) to focus on the North–South issue without unnecessary analytical complexity.

  7. We disregard the fourth regime characterized by ‘North–North coordination’ without ‘North–South compensation’, because we find it less relevant than the three regimes listed in Table 1.

  8. We know that the aggregate welfare rises, if we move from Regime 1 with or without strategic action to Regime 3 without strategic action, because Regime 1 is inefficient and Regime 3 without strategic action is efficient.

  9. The Convention on Biological Diversity combined with the Global Environment Facility does not fit precisely into any of the three regimes, but may come close to Regime 2.

  10. It is obvious that the real world exhibits all kinds of intermediate forms of land use. Nonetheless, the partition of land into protected and non-protected areas captures the essence of the allocation problem for the purpose of our conceptual analysis and secures tractability at the same time.

  11. The subscript i [j] denotes an element of the set \(\mathcal{N}\)\([\mathcal{S}]\), and the subscript h represents an element of the set \(\Omega \).

  12. To simplify, inputs other than land are sector-specific and constant in (2) and (3). While all economic activities have some spatial dimension, it is also true that their space requirements differ and in some cases are small.

  13. We denote by \(g_h, x_i, y_j\) the supply of goods and by \(g_h^d, x_h^d, y_h^d\) their demand.

  14. For details on ‘degenerate’ profit maximization and land market equilibrium, see “Appendix A”.

  15. Note that (7) defines equilibrium in the markets of protected and unprotected land, and implies clearance of the market for green goods via Walras’ Law.

  16. Observe that all prices are related to the price of the green good, which has been chosen as a numeraire. Hence, \(\frac{\partial P^x}{\partial b_i}\) captures the strategic action of manipulating the terms of trade \(\frac{p_x}{p_g}\).

  17. See Coase (1960) for the basic idea. Pearce (2004) discusses the Coaseian concept and its potential for BC without formal modeling.

  18. The information in (12) about the size of the protected area in the fallback Regime 1 is important, in order to rule out the offer of protected areas in the BC market that would already be protected areas in Regime 1.

  19. The first-order conditions of Regimes 1–3 for the parametric model are given in “Appendix C”. The closed-form solutions for non-strategic action are presented in “Appendix D”.

  20. In Table 3, is the value of the variable \(v_h= b_h, w_h\) etc. of country h in Regime \(k = 1, 2, 3\). In addition, we use the superscripts s and \(*\) to indicate the allocation and prices of regimes with and without strategic action, respectively.

  21. See Table 3. Price exceeds price by an amount that is too small to be captured in Table 3. It must be higher, since otherwise, the protected land in North could not be larger with than without strategic action.

  22. As a consequence, strategic manipulation of the price of green goods is impossible.

  23. For details, see Tables 89 and 10 in the “Appendix D”.

  24. In the following tables, we use the notation for the variable \(v=b, w, p_x, p_y\) with \(k= 2, 3 \) and \(h= \mathcal{N}, \mathcal{S}\).

  25. Note, however, that the changes in the first row of Table 4 are due to the introduction of the BC market (without North–North coordination), while in Table 3, the differences between the first and second rows are due exclusively to the move from non-strategic to strategic action.

  26. The absolute aggregate-welfare gap between Regimes 2 and 3 is small, but almost as large as between Regimes \(1^*\) and \(3^*\).

  27. For the interested reader, we provide in “Appendix C” the relevant results of Example 2, along with those of the Examples 1 and 3, to allow for a row-by-row comparison.

  28. Recall that we denote Regime \(k = 1, 2, 3\) as Regime \(k^*\), if governments act non-strategically, as Regime \(k^s\), if they act strategically, and as Regime k (without superscript) if both types of that regime are addressed.

  29. Items (A)–(C) imply that moving from price-taking to strategic action increases total protected land in all regimes. This feature is reminiscent of the famous observation Hotelling made in a different context, that “the monopolist is the conservationist’s best friend.”

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Correspondence to Thomas Eichner.

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Helpful comments from Charles Perrings and two anonymous reviewers are gratefully acknowledged. Remaining errors are the authors’ sole responsibility.

Appendix

Appendix

1.1 Appendix A: Protected and Unprotected Land Markets

For simplicity, we treat the protected area \(b_h\) as the governments’ policy parameter assuming that the land zones are imposed in a command and control fashion. It is straightforward to introduce competitive domestic markets, one for protected and one for unprotected land, to allocate the land to domestic firms. We determine the equilibrium on these markets as follows. After the government of country \(h \in \Omega \) has divided total land into protected and unprotected land, the equilibrium prices for the goods X and Y are determined by (8). Denote by \(p_{e}^i\) and \(p_{e}^j\) the price of unprotected land use in the production of good X, \(i \in \mathcal{N}\) and good Y, \(j \in \mathcal{S}\), respectively. Consider the first-order conditions of profit maximization \(p_x X_i'(e_i) =p_{e}^i\) and \(p_y Y_i'(e_i) =p_{e}^j\), respectively. The first-order conditions clearly define the land prices, \(p_{e}^i= p_x X_i'(e_i) \) and \(p_{e}^j= p_y Y_i'(e_i) \).

Next, consider the market for ecosystem services in country h and define the prices \(p_g=1\), \(p_b^h\) and the profit of the firm in country h that produces green goods, \(G_h(b_h) - p_b^h b_h\). The first-order condition of profit maximization determines the equilibrium price of protected land in country h: \(p_b^h{:=} G_h'(b_h)\).

Finally, observe that the income of country \(i\in \mathcal{N}\) and \(j \in \mathcal{S}\), respectively, is given by

$$\begin{aligned} I_i:= & {} p_e^i e_i + p^i_b b_i +(g_i -p_b^i b_i)+\,(p_x x_i-p_e^i e_i)\nonumber \\= & {} g_i + p_x x_i= G_i(b_i) + p_x X_i (\ell _i -b_i), \end{aligned}$$
(A1)
$$\begin{aligned} I_j:= & {} p_e^j e_j + p^j_b b_j +(g_j -p_b^j b_j)+\,(p_y y_j - p_e^j e_j)\nonumber \\= & {} g_j + p_y y_j= G_j(b_j) + p_y Y_j (\ell _j -b_j). \end{aligned}$$
(A2)

1.2 Appendix B: Social Optimum

Maximizing the Lagrangian (24) yields the first-order conditions

$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial x^d_h}= & {} V'_h - \lambda _x = 0, \quad \, h \in \Omega , \end{aligned}$$
(B1)
$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial y^d_h}= & {} U'_h - \lambda _y = 0, \quad \, h \in \Omega , \end{aligned}$$
(B2)
$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial g^d_h}= & {} 1- \lambda _g = 0, \quad \, h \in \Omega , \end{aligned}$$
(B3)
$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial z_{i}}= & {} - \lambda _x X'_{i} + \lambda _z = 0, \quad \, i \in \mathcal{N}, \end{aligned}$$
(B4)
$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial z_{j}}= & {} - \lambda _y Y'_{j} + \lambda _z = 0, \quad \, j \in \mathcal{S}, \end{aligned}$$
(B5)
$$\begin{aligned} \frac{\partial \mathcal{L}}{\partial z^d_{h}}= & {} \lambda _g G'_h + \sum _{\mathcal{N}} B_i' - \lambda _z = 0, \quad \, h \in \Omega . \end{aligned}$$
(B6)

The standard procedure of equating shadow prices with prices on perfectly competitive markets yields \(\lambda _x = p_x\), \(\lambda _y = p_y\), \(\lambda _g =p_g\) and \(\lambda _z = p_z\), and proves that the allocation in Regime \(3^*\) is efficient.

1.3 Appendix C: Parametric Functions and Numerical Examples

Regime 1 The consumer’s demand for good X and Y is given by

$$\begin{aligned}&V'(x_h^d) = p_x \quad \iff \quad x_h^d = \frac{a_x -p_x}{\beta _x} \equiv x^d \quad \text{ for } \,\, h = \mathcal{N}, \mathcal{S}, \end{aligned}$$
(C1)
$$\begin{aligned}&U'(x_h^d) = p_y \quad \iff \quad y_h^d = \frac{a_y -p_y}{\beta _y} \equiv y^d \quad \text{ for } \,\, h = \mathcal{N}, \mathcal{S}. \end{aligned}$$
(C2)

Inserting the demands (C1), (C2) and the supplies \(x_h =2 \alpha _{x} \sqrt{\ell - b_{\mathcal{N}}}\) and \(y_h =2 \alpha _{y} \sqrt{\ell - b_{\mathcal{S}}}\) into the equilibrium conditions \((n+s) x^d = n x_{\mathcal{N}} \) and \((n+s) y^d = sx_{\mathcal{S}}\) we obtain

$$\begin{aligned} p_x = P^x(b_{\mathcal{N}}) = a_x - \frac{2 n \alpha _{x } \beta _x}{n+s} \sqrt{\ell - b_{\mathcal{N}}}, \quad p_y = P^y (b_{\mathcal{S}}) = a_y - \frac{2 s \alpha _{y} \beta _y}{n+s} \sqrt{\ell - b_{\mathcal{S}}}.\nonumber \\ \end{aligned}$$
(C3)

Inserting the parametric functions (25) into (10) and (11) we get

$$\begin{aligned} \alpha _{g} - \frac{p_x \alpha _{x}}{ \sqrt{\ell - b_{\mathcal{N}}}} + \gamma = 0, \quad \alpha _{g} - \frac{p_y \alpha _{y}}{ \sqrt{\ell - b_{\mathcal{S}}}} = 0 \end{aligned}$$
(C4)

for non-strategic action and

$$\begin{aligned}&\alpha _{g} - \frac{p_x \alpha _{x}}{ \sqrt{\ell - b_{\mathcal{N}}}} + \frac{\partial P^x}{\partial b_{\mathcal{N}}} \cdot \left( 2 \alpha _{x} \sqrt{\ell - b_{\mathcal{N}}} - \frac{a_x-p_x}{\beta _x} \right) + \gamma = 0, \end{aligned}$$
(C5)
$$\begin{aligned}&\alpha _{g} - \frac{p_y \alpha _{y}}{ \sqrt{\ell - b_{\mathcal{S}}}} + \frac{\partial P^y}{\partial b_{\mathcal{S}}} \cdot \left( 2 \alpha _{y} \sqrt{\ell - b_{\mathcal{S}}} - \frac{a_y-p_y}{\beta _y} \right) = 0 \end{aligned}$$
(C6)

for strategic action.

Regime 2 In Regime 2 the consumer’s demands are given by \(x^d = \frac{a_x - p_x}{\beta _x}\), \(y^d = \frac{a_y - p_y}{\beta _y}\) and the price functions by

(C7)
(C8)

For the parametric functions (25) the first-order conditions (18)–(20) turn into

(C9)

for non-strategic action and

(C10)
(C11)

for strategic action.

Regime 3 In Regime 3 the first-order conditions (18), (22) and (23) turn into

(C12)

for non-strategic action and

figure a

for strategic action.

1.4 Appendix D: Closed-Form Solution for Non-strategic Action

For non-strategic action we get the following closed-form solutions.

Regime 1 Solving (C4) we get

figure b

where and . The welfare levels of northern and southern countries are given by

figure c

Regime 2 Solving (C9) one gets

figure d

where and . Inserting (D1) and (D2) into (D8) and (D9) and solving for and yields

figure e

The welfare levels are

figure f

where and .

Regime 3 Solving (C12) and (C13), we obtain

figure g

where and . Inserting (D2) and (D3) into (D18) and (D19) and solving for and yields

figure h

The welfare levels are given by

figure i

where and .

Table 8 Equilibrium values in Example 1 (\(\beta _x = 0.1\))
Table 9 Equilibrium values in Example 2 (\(\alpha _y = 0.9\))
Table 10 Equilibrium values in Example 3 \((\beta _x=0.5)\)

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Eichner, T., Pethig, R. Coaseian Biodiversity Conservation and Market Power. Environ Resource Econ 72, 849–873 (2019). https://doi.org/10.1007/s10640-018-0225-0

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