Environmental Kuznets curves—real progress or passing the buck ...

Environmental Kuznets curves—real progress or passing the buck ... Environmental Kuznets curves—real progress or passing the buck ...

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186 D.S. Rothman / Ecological Economics 25 (1998) 177–194 countries is often referred to as the ‘pollution haven hypothesis’. Before discussing the logic behind this hypothesis, the author wants to be careful to point out that, for this argument, only a weak version of this argument has to hold. To the extent that differences in the environmental impact of production processes between domestic and imported commodities can be accounted for, what is important is the changing ratio between domestic consumption and domestic production. Even if domestic production stays the same or increases, if domestic consumption rises faster, then some of the increase in consumption must be met by importing goods (ignoring changes in inventories). This will be missed in a productionbased measure of environmental degradation, resulting in a bias toward acceptance of the EKC hypothesis. If production processes are dirtier in exporting countries, this further increases the bias. Of course, this bias can also work the other way under different circumstances, e.g. cleaner production processes in exporting countries or faster growth in production than consumption. The reasoning behind the pollution haven hypothesis follows from the same logic that is proposed to explain, in part, the existence of an EKC. In this case, however, the demand for environmental quality, which is assumed to rise with increased income levels, does not lead to a shift to a cleaner production process in the country where the demand is generated, but rather to a movement of the production process to a location outside of the country. Because there is a strong incentive to carry out processing stages as near as possible to the source of the raw material, as the best-quality resources are exhausted in the industrialized countries, there is a further tendency for many traditionally energy- and pollution-intensive activities to migrate to poorer countries (Ayres, 1996). It is also often assumed that poorer countries have cleaner environments because of less previous development and, therefore, will suffer less damage from any given reduction in environmental quality. Finally, the argument has been made that poorer people suffer fewer economic costs from the health effects of poorer environmental quality. This relies on the fact that economic losses due to health problems are often calculated as being directly related to income levels. This is a practice that has been commonly used by economists, leading at times to severe criticism, as in the reaction to the leaked memo written by World Bank economist Lawrence Summers (The Economist, 1992) and the recent estimates of the economic costs of global warming summarized by the IPCC (Pearce et al., 1996). At the same time, it should be noted that several authors have hypothesized that, due to their comparative advantage in labor vis-à-vis man-made capital, the latter of which is usually associated with dirtier industries, these industries should actually migrate away from poorer countries to wealthier ones. Because the latter tend to have stricter environmental standards, trade should lead to lower overall levels of pollution and resource degradation (Birdsall and Wheeler, 1992; López, 1992). Little empirical work has been done on this hypothesis and there is very little evidence supporting it. To the extent that the pollution haven hypothesis is true, a city, region, or nation, via trade, can create an illusion of sustainability (Rees, 1993). From a thermodynamic perspective, a locale acts as a dissipative structure, i.e. increasing the order in the local system at the expense of greater disorder in the larger system in which it is embedded (Hornburg, 1992). In order to describe this expropriation of resources elsewhere in space, terms such as ‘shadow ecologies’ (MacNeil, 1992) and ‘appropriated carrying capacity’ (Wackernagel and Rees, 1995) have begun to be seen in the literature. Several studies have explored the existence of pollution havens, including Birdsall and Wheeler (1992), Dean (1992), Low and Yeats (1992), Lucas et al. (1992), Radetzki (1992), Copeland and Taylor (1994, 1995), Benarroch et al. (1995). The results of these studies are mixed, but most do point to some validity in the general hypothesis. Low and Yeats (1992) point to an expansion in the share of polluting industries in the exports of developing countries for the period 1965–88, as well as a greater overall dispersion of points of origin for polluting industries than for cleaner ones (no results were presented for an analysis using country of destination rather than origin).

D.S. Rothman / Ecological Economics 25 (1998) 177–194 187 Thus, it appears that the developed countries are less likely to ‘farm out’ cleaner industries. Birdsall and Wheeler (1992), in examining the toxic intensity in industry for Latin American countries from 1960–88, report a migration of industries with higher toxic intensities. They are careful to point out that this is mostly to countries with relatively closed economies, as countries with more open economies are more susceptible to external influences and, therefore, pay more attention to environmental regulations. Also of note, their results indicate that the overall toxic intensity of the economy rises with income in all countries. Lucas et al. (1992), in examining scale and composition effects on toxic intensity using data over the same period also find support for the displacement hypothesis. They note also that more open economies tend to be cleaner. They do find a weak indication of an EKC for pollution emission intensity with rising income, but this is principally a reflection of the decreased importance of the manufacturing sector as a whole in the economy. Also, as Ramón López points out in his comments, the absolute levels of pollution continue to rise (Lucas et al., 1992). Adriaanse et al. (1997) present data that the US, Germany, Japan and The Netherlands rely on imports to meet 5, 35, over 50 and more than 70% of their total material requirements, respectively. Again, these may be somewhat misleading as the materials required to meet export demands are not currently deducted. Two recent empirical studies begin to give more insight into the net balance of trade in environmental pollution and resource use. Antweiler (1996) uses sectoral pollution intensities (tons per unit output) derived from US data (United States Environmental Protection Agency, 1995) and sectoral trade data derived from Statistics Canada (1994) to estimate the net embodied levels of six air pollutants—sulfur dioxide, carbon monoxide, nitrogen dioxide, lead, particulate matter under 10 m and volatile organic compounds—for 164 countries in 1987. The data only consider the composition of trade, as the same sectoral intensities are applied to each country. Although understandable due to a lack of data, this results in a bias ‘favoring’ countries with dirtier technologies than the US and ‘penalizing’ countries with cleaner technologies. Secondly, since the pollution coefficient data are developed from plant-specific data, the analysis discounts primary resource sectors, which do not generally have ‘plants’ but make up a relatively larger share of exports for developing countries. A plot of per capita data against GDP per capita, shown in Fig. 5, reveals a pattern of a few major exporters of embodied pollution, particularly Ireland, Singapore, West Germany and Japan, with no clear relationship between net exports and income 10 . Atkinson and Hamilton (1996), alternatively, examine net dollar flows for 95 countries in 1985 related to trade in commercial natural resources—crude oil, timber, zinc, iron ore, phosphate rock, bauxite, copper, tin, lead and nickel. Fig. 6 shows a strong tendency among non major oil exporters for an increase in net resource imports per capita as countries become wealthier. Oil exporting countries show a different pattern, but this can be explained by the fact that oil exports significantly determine average income in these nations. It is somewhat surprising that little or no empirical work has been done looking at trade in the context of the EKC hypothesis. The original analysis by Grossman and Krueger (1992) was an exercise to consider the potential impacts of the NAFTA, but even in their analysis their treatment of trade was separate from their EKC analysis. Suri and Chapman (1998) include the shares of manufactured goods in imports and exports, as well as an interactive term between manufacturing imports and income. These are intended to compensate, in part, for differences between the structure and production within a country, where the second term is included to capture the changing nature of imports as incomes rise. Kaufmann et al. (1998) includes exports per unit GDP of iron and steel in their estimation for the same reasons. Notably, both studies conclude that trade makes a significant contribution to the shape of curves relating resource use and environmental quality 10 Data from countries with under 1 million persons were dropped, as they were considered unrepresentative and resulted in large outliers. The figures for the other pollutants are similar, but not shown.

186<br />

D.S. Rothman / Ecological Economics 25 (1998) 177–194<br />

countries is often referred to as <strong>the</strong> ‘pollution<br />

haven hypo<strong>the</strong>sis’. Bef<strong>or</strong>e discussing <strong>the</strong> logic behind<br />

this hypo<strong>the</strong>sis, <strong>the</strong> auth<strong>or</strong> wants to be careful<br />

to point out that, f<strong>or</strong> this argument, only a<br />

weak version of this argument has to hold. To <strong>the</strong><br />

extent that differences in <strong>the</strong> environmental impact<br />

of production processes between domestic<br />

and imp<strong>or</strong>ted commodities can be accounted f<strong>or</strong>,<br />

what is imp<strong>or</strong>tant is <strong>the</strong> changing ratio between<br />

domestic consumption and domestic production.<br />

Even if domestic production stays <strong>the</strong> same <strong>or</strong><br />

increases, if domestic consumption rises faster,<br />

<strong>the</strong>n some of <strong>the</strong> increase in consumption must be<br />

met by imp<strong>or</strong>ting goods (ign<strong>or</strong>ing changes in invent<strong>or</strong>ies).<br />

This will be missed in a productionbased<br />

measure of environmental degradation,<br />

resulting in a bias toward acceptance of <strong>the</strong> EKC<br />

hypo<strong>the</strong>sis. If production processes are dirtier in<br />

exp<strong>or</strong>ting countries, this fur<strong>the</strong>r increases <strong>the</strong> bias.<br />

Of course, this bias can also w<strong>or</strong>k <strong>the</strong> o<strong>the</strong>r way<br />

under different circumstances, e.g. cleaner production<br />

processes in exp<strong>or</strong>ting countries <strong>or</strong> faster<br />

growth in production than consumption.<br />

The reasoning behind <strong>the</strong> pollution haven hypo<strong>the</strong>sis<br />

follows from <strong>the</strong> same logic that is proposed<br />

to explain, in part, <strong>the</strong> existence of an<br />

EKC. In this case, however, <strong>the</strong> demand f<strong>or</strong> environmental<br />

quality, which is assumed to rise with<br />

increased income levels, does not lead to a shift to<br />

a cleaner production process in <strong>the</strong> country where<br />

<strong>the</strong> demand is generated, but ra<strong>the</strong>r to a movement<br />

of <strong>the</strong> production process to a location<br />

outside of <strong>the</strong> country. Because <strong>the</strong>re is a strong<br />

incentive to carry out processing stages as near as<br />

possible to <strong>the</strong> source of <strong>the</strong> raw material, as <strong>the</strong><br />

best-quality resources are exhausted in <strong>the</strong> industrialized<br />

countries, <strong>the</strong>re is a fur<strong>the</strong>r tendency f<strong>or</strong><br />

many traditionally energy- and pollution-intensive<br />

activities to migrate to po<strong>or</strong>er countries (Ayres,<br />

1996). It is also often assumed that po<strong>or</strong>er countries<br />

have cleaner environments because of less<br />

previous development and, <strong>the</strong>ref<strong>or</strong>e, will suffer<br />

less damage from any given reduction in environmental<br />

quality. Finally, <strong>the</strong> argument has been<br />

made that po<strong>or</strong>er people suffer fewer economic<br />

costs from <strong>the</strong> health effects of po<strong>or</strong>er environmental<br />

quality. This relies on <strong>the</strong> fact that economic<br />

losses due to health problems are often<br />

calculated as being directly related to income levels.<br />

This is a practice that has been commonly<br />

used by economists, leading at times to severe<br />

criticism, as in <strong>the</strong> reaction to <strong>the</strong> leaked memo<br />

written by W<strong>or</strong>ld Bank economist Lawrence Summers<br />

(The Economist, 1992) and <strong>the</strong> recent estimates<br />

of <strong>the</strong> economic costs of global warming<br />

summarized by <strong>the</strong> IPCC (Pearce et al., 1996).<br />

At <strong>the</strong> same time, it should be noted that<br />

several auth<strong>or</strong>s have hypo<strong>the</strong>sized that, due to<br />

<strong>the</strong>ir comparative advantage in lab<strong>or</strong> vis-à-vis<br />

man-made capital, <strong>the</strong> latter of which is usually<br />

associated with dirtier industries, <strong>the</strong>se industries<br />

should actually migrate away from po<strong>or</strong>er countries<br />

to wealthier ones. Because <strong>the</strong> latter tend to<br />

have stricter environmental standards, trade<br />

should lead to lower overall levels of pollution<br />

and resource degradation (Birdsall and Wheeler,<br />

1992; López, 1992). Little empirical w<strong>or</strong>k has<br />

been done on this hypo<strong>the</strong>sis and <strong>the</strong>re is very<br />

little evidence supp<strong>or</strong>ting it.<br />

To <strong>the</strong> extent that <strong>the</strong> pollution haven hypo<strong>the</strong>sis<br />

is true, a city, region, <strong>or</strong> nation, via trade, can<br />

create an illusion of sustainability (Rees, 1993).<br />

From a <strong>the</strong>rmodynamic perspective, a locale acts<br />

as a dissipative structure, i.e. increasing <strong>the</strong> <strong>or</strong>der<br />

in <strong>the</strong> local system at <strong>the</strong> expense of greater<br />

dis<strong>or</strong>der in <strong>the</strong> larger system in which it is embedded<br />

(H<strong>or</strong>nburg, 1992). In <strong>or</strong>der to describe this<br />

expropriation of resources elsewhere in space,<br />

terms such as ‘shadow ecologies’ (MacNeil, 1992)<br />

and ‘appropriated carrying capacity’ (Wackernagel<br />

and Rees, 1995) have begun to be seen in<br />

<strong>the</strong> literature.<br />

Several studies have expl<strong>or</strong>ed <strong>the</strong> existence of<br />

pollution havens, including Birdsall and Wheeler<br />

(1992), Dean (1992), Low and Yeats (1992), Lucas<br />

et al. (1992), Radetzki (1992), Copeland and<br />

Tayl<strong>or</strong> (1994, 1995), Benarroch et al. (1995). The<br />

results of <strong>the</strong>se studies are mixed, but most do<br />

point to some validity in <strong>the</strong> general hypo<strong>the</strong>sis.<br />

Low and Yeats (1992) point to an expansion in<br />

<strong>the</strong> share of polluting industries in <strong>the</strong> exp<strong>or</strong>ts of<br />

developing countries f<strong>or</strong> <strong>the</strong> period 1965–88, as<br />

well as a greater overall dispersion of points of<br />

<strong>or</strong>igin f<strong>or</strong> polluting industries than f<strong>or</strong> cleaner<br />

ones (no results were presented f<strong>or</strong> an analysis<br />

using country of destination ra<strong>the</strong>r than <strong>or</strong>igin).

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