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

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D.S. Rothman / Ecological Economics 25 (1998) 177–194 181<br />

Fig. 2. GDP by Sect<strong>or</strong> 1993 (W<strong>or</strong>ld Resources Institute, 1996).<br />

1994; Grossman, 1995; Suri and Chapman, 1996).<br />

Most of <strong>the</strong>se have concluded that <strong>the</strong>re has been<br />

a decline in environmental degradation over time,<br />

as expected. On <strong>the</strong> o<strong>the</strong>r hand, Grossman and<br />

Krueger (1994) find an increasing trend f<strong>or</strong> urban<br />

particulate matter and a number of water pollutants,<br />

Shafik and Bandyopadhyay (1992) see one<br />

f<strong>or</strong> fecal colif<strong>or</strong>m concentrations in water, and<br />

Cropper and Griffiths (1994) get mixed results<br />

looking at def<strong>or</strong>estation rates. Grossman and<br />

Krueger (1992) do discuss changing composition,<br />

but look at this principally in a separate discussion<br />

of international trade, arguing that <strong>the</strong> data<br />

do not supp<strong>or</strong>t <strong>the</strong> hypo<strong>the</strong>sis that differences in<br />

environmental regulation are an imp<strong>or</strong>tant determinant<br />

of trade patterns. (A broader review of <strong>the</strong><br />

trade literature suggests that this conclusion is not<br />

accepted as a rule, however (Low, 1992; Folke et<br />

al., 1994; OECD, 1994). Due to its imp<strong>or</strong>tance,<br />

this issue is returned to in m<strong>or</strong>e depth later in this<br />

paper.)<br />

Selden et al. (1996) and (de Bruyn, 1997)<br />

provide notable exceptions in <strong>the</strong>ir decomposition<br />

of observed changes in aggregate and per capita<br />

emissions. Using data f<strong>or</strong> a number of air pollutants<br />

in <strong>the</strong> US, and going beyond Grossman and<br />

Krueger, Selden et al. (1996) fur<strong>the</strong>r decompose<br />

<strong>the</strong> technique effect into energy efficiency, energy<br />

mix and o<strong>the</strong>r technique effects, i.e. changes in<br />

emissions per unit output. They conclude that <strong>the</strong><br />

greatest effects have come from <strong>the</strong> technique<br />

effect, particularly <strong>the</strong> o<strong>the</strong>r technique effect.<br />

Changes in sect<strong>or</strong>al composition have also had a<br />

noticeable effect, however, especially f<strong>or</strong> particulate<br />

matter and sulfur oxides. de Bruyn (1997)<br />

examines sulfur dioxide emissions in The Ne<strong>the</strong>rlands<br />

and Western Germany. He also concludes<br />

that shifts in technology have been dominant in<br />

explaining changes in <strong>the</strong>se emissions.<br />

3.2. The consumption-based approach<br />

Ehrlich and Holdren (1971), Holdren and<br />

Ehrlich (1974) introduced <strong>the</strong> I=PAT identity<br />

(commonly referred to as <strong>the</strong> Ehrlich equation),<br />

m<strong>or</strong>e than a quarter of a century ago. This iden-

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