Abstract
By incorporating the environmental problems caused by consumption into a theoretical model of rural–urban migration, this study analyzes the effect of a reduction in pollution generation rate and factor accumulation. The environment of each rural and urban area is assumed to deteriorate due to pollution from consumption of the respective inhabitants. For institutional reasons, the urban wage rate is fixed at a higher level than the rural wage rate, and unemployment exists in the urban area. Rural–urban migration occurs because of differences in utility, which is affected by both the environment and expected earning in each area. This study shows that, although reduction in the pollution generation rate improves the environment in both areas, whether it mitigates urban unemployment depends on certain conditions. Regarding the effect of factor accumulation, this study shows that an increase in capital endowment decreases the level of unemployment if and only if the environmental effect outweighs the Rybczynski effect.
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Notes
We can interpret \(L_{U}\) as labor that is not used in production.
A specific utility function of this type is adopted owing to the reviewer’s comment.
Note that (12) is derived by assuming that each urban worker is employed in turn and earns \(w_{M}\). Alternatively, if we regard that urban employed labor earns \(\bar{w}\) and unemployed labor has no income, the expected utility of an urban worker is the same as (12): The indirect utility function of urban employed labor is \(v(p,\bar{w}) + G(E^{M} )\), whereas that of unemployed labor is \(G(E^{M} )\). Thus, the expected utility of an urban worker becomes \(\frac{{L_{M} }}{{L_{M} + L_{U} }}\left[ {v(p,\bar{w}) + G(E^{M} )} \right] + \frac{{L_{U} }}{{L_{M} + L_{U} }}G(E^{M} ) = v(p,w_{M} ) + G(E^{M} )\). This equation is derived by the assumption that \(u\) is linearly homogeneous.
In equilibrium, \(E^{M} > ( < )E^{A} \Leftrightarrow w_{M} < ( > )w\) holds. Thus, \(w_{M}\) can either be higher or lower than \(w\), even under the assumption that \(\bar{w} > w\).
Note that this study treats demand and consumption as identical.
Essentially, \(\lambda\) depends on the generation rate of pollution by consumption of each good and \(p\). However, the latter is assumed to be constant. Thus, we refer to \(\lambda\) as the pollution generation rate.
Alternatively, we can refer (21) as the aggregated flow of pollution from urban employed workers.
This study refers to \(L_{U} /L_{M}\) as the unemployment ratio.
This can be seen from (34) and (35) in Appendix A.
This result is derived assuming that each urban worker receives \(w_{M}\). Alternatively, if we regard that an urban employed (unemployed) worker earns \(\bar{w}\) (no income), utilities of both employed and unemployed workers also rise by an improvement in the urban environment (as regards the utility functions of this case, see footnote 4).
If magnitude of \(\lambda\) increases, the environmental effect becomes stronger, at least in terms of direct effect.
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Acknowledgements
The author is indebted to two anonymous referees and Professor Makoto Tawada for insightful comments.
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Appendices
Appendix A: Stability
In the short run, for given \(E^{M}\) and \(E^{A}\), six Eqs. (3), (4), (7), (8), (9), and (16) determine six endogenous variables: \(L_{M}\), \(L_{U}\), \(L_{A}\), \(K_{M}\), \(K_{A}\), and \(w\). Thus, substituting (21) and (25) into (26) and substituting (23) into (28), respectively, the dynamic adjustment process of \(E^{M}\) and \(E^{A}\) can be expressed as
Necessary and sufficient condition for the linear approximation system of (34) and (35) to be globally stable is that the trace of \(S\) (\({\text{tr}} S\)) is negative and the determinant of matrix \(S\) (det \(S\)) is positive, where \(S \equiv \left[ {\begin{array}{*{20}c} {\partial \phi /\partial E^{M} } & {\partial \phi /\partial E^{A} } \\ {\partial \varPsi /\partial E^{M} } & {\partial \varPsi /\partial E^{A} } \\ \end{array} } \right]\).
To investigate the signs of \({\text{tr}} S\) and det \(S\), by differentiating (3), (4), (7), (8), (9), and (16), we obtain
Denoting the determinant of square matrix of (36) as \(J\), we have
Thus, the following relationship holds as regards the sign of \(J\):
We are now in a position to examine the signs of \({\text{tr}} S\) and det \(S\). First, we investigate the sign of \({\text{tr}} S\). From (34) and (35), we have
where \(J^{*} = p(\bar{w}G^{{M^{\prime}}} F_{LK}^{M} F_{KL}^{A} + wG^{{A^{\prime}}} F_{LL}^{M} F_{KK}^{A} ) > 0\). To derive the last expression, we use \(\partial L_{M} /\partial E^{M} = pG^{{M^{\prime}}} F_{LK}^{M} F_{KL}^{A} /J\) and \(\partial L_{A} /\partial E^{A} = pG^{{A^{\prime}}} F_{LL}^{M} F_{KK}^{A} /J\) from (36). Thus, the following relationship holds.
Next, det \(S\) becomes
Therefore, the following relationship holds:
From (37) and (38), if the urban area is more capital abundant than the rural area, that is, \(K_{M} /(L_{M} + L_{U} ) > K_{A} /L_{A}\), then the linear approximation system of (34) and (35) is globally stable.
Appendix B: Environmental effect when capital endowment increases
In the following, we show that \(L_{M}\), \(L_{U}\), and \(K_{M}\) decrease due to the environmental effect of an increase in capital endowment. First, we consider the environmental effect on \(L_{U}\). Because the part in parentheses of the last expression of (33d) becomes \(\begin{aligned} {-}e - G^{{M^{\prime}}} L_{A} d/L_{M} K_{A} & = - G^{{A^{\prime}}} wL_{A} /K_{A} + rG^{{M^{\prime}}} - G^{{M^{\prime}}} L_{A} (\bar{w}L_{M} + rK_{M} )/L_{M} K_{A} \\ & = - G^{{A^{\prime}}} wL_{A} /K_{A} + G^{{M^{\prime}}} \left[ {r(1 - L_{A} K_{M} /L_{M} K_{A} ) - L_{A} \bar{w}/K_{A} } \right] < 0, \\ \end{aligned}\) \(L_{U}\) decreases by the environmental effect.
Next, we investigate the environmental effect on \(K_{M}\). The sum of the environmental effect of \({\text{d}}K_{M} /{\text{d}}K\) and \({\text{d}}K_{A} /{\text{d}}K\) is zero: by adding \(F_{LL}^{M} F_{KK}^{A} ( - J^{*} C + JeK_{A} /L_{A} )\) of (33f) and \(F_{LK}^{M} F_{KL}^{A} \left[ {J^{*} (B + C) + JG^{{M^{\prime}}} d/L_{M} } \right]\) of (33g), it becomes
where to obtain the third expression, we use the definitions for \(B\), \(C\), \(e\), and \(d\), while to obtain the fourth expression, we use the definitions for \(J^{*}\) and \(J\). Thus, remembering that the environmental effect of \({\text{d}}K_{A} /{\text{d}}K\) is positive as expressed in (33g), the environmental effect of \({\text{d}}K_{M} /{\text{d}}K\) becomes negative.
Finally, we consider the environmental effect on \(L_{M}\). From (3), \(L_{M}\) and \(K_{M}\) move in the same direction. Therefore, because \(K_{M}\) decreases due to the environmental effect, \(L_{M}\) also decreases due to the environmental effect.
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Nakamura, A. Pollution from consumption and urban unemployment in a dual economy. Asia-Pac J Reg Sci 2, 211–226 (2018). https://doi.org/10.1007/s41685-018-0071-7
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DOI: https://doi.org/10.1007/s41685-018-0071-7