Jaspers & Falkner 2013
Jaspers & Falkner 2013
Track l,hcrnlization has been a key driving force behind glo bal economic grclllth
~111et· rhc Sern11d World War. During this peri od, glo ba l environmental dcgrad.11100
re:Khl'd new heights. Three sets of questions a rise fro m this. Fi rst, is the li hcralrwron
of intern ;1tiona l trade re~ponsible for the global ecologica l cri sis, or do frl'l'r tr.idt.
111Crcased glo ba l competition and greater wea lth help to promote c11vironmenul
protectio n ;ind a mo re efficient use of scarce resources? Second, do the ru b of tht'
111tt·rn.1tiona l trad ing system (mainly the World Trade O rganization - WTO) help
or hinder effort~ to protect the environment, and a re international cnvironmcnul
.1g rccmcnrs consistent with the rules and o bligatio ns of the WTO order? ThirJ.
wi th rl'ga rd to the threat of global warming, does free trade undermine the clinwr
polic1t·~ of mo re am bitious countries because of the threat of industrial reloc,1t1on 111
lagga rd coumrie~. and should trade measures be employed as a tool of intcrnarion.d
clima te policy?
The~e and other questi ons about the trade-environment nex us ha ve hecn inrensdr
de ha ted fo r some time a nd remain critical to the future of the trading system. p:ir11cu-
l;trly with rega rd to climate change (for a general overview of the dchatc, set' Sa111p,on
2005 ). Th is chapter reviews the trade-environment debate and m .:ent scholar~h,p. It
o pens with a brief J i.,cu,;sion of the ge neral relationship between trade, thl' rn\'iron·
lllt'rtt, anJ climate change; rhen focuses on the institutional and jurisdictional n,ntt'xt
. rrJ Jca n d cn v1ronmenta
for . I po 1icy-ma
· k111g;
· · an an,1I),S1.5of the
and concludes with
rr:1dt.· implicJtio m of recent develo pments in climate change policy.
b
•
416 GLOBAL ECONOMY AN D POLI CY
==-====
risk ;1sst·ssmcnt "within a reasonable pcrio<l of time" (J\rriclc S.7). The SPS Agree
ment is the only trade agreement that formally recognizes p~ccllltion a<; a justification
for taking trade measures where there is scientific u'.1eertamty h,_,r so m~ evidence of
potential harm . The question that has repeatedly pitted the Wl O :tga lllst envi ron-
mentalists is whether such uncertainty is only a temporary phenomen on or a more
persistent problem that pervades many areas of environmenta l policy-making, such
as food safety and genetically modified organisms (Post 2006; Isaac and Kerr 2007).
Of the over 500 multilateral environmental agreements (MEAs) that have been
created in the last four decades, a small but growing proportion includes trade
measures among their regulatory instruments. As trade restrictions become more
popular in global environmental policy-making, concern is rising that these measures
will increasingly come into conflict with WTO rules. The definition of trade measures
in MEAs is fairly wide and often imprecise. It most commonly refers to various
forms of restrictions on trade for environmental purposes, such as bans on the
trade of certain polluting substances or embargoes of specific countries that are in
breach of environmental obligations. It may also include other measures that have an
indirect trade impact, such as reporting requirements, labeling systems, prior consent
requirements, or fiscal instruments (e.g. taxes, subsidies) (Brack and Gray 2003: 5-
6). Some MEAs are designed to regulate trade, such as the Convention on Trade
in Endangered Species (CITES), while others use trade restrictions as one of several
instruments to support their main environmental goal (e.g. the Montreal Protocol
on Substances that Deplete the Ozone Layer) .
• Trade measures have become popular instruments in MEAs for a number of
reasons. They broadly serve three purposes (see Brack and Gray 2003: 13-15):
• Target environmental harm. Most trade measures in MEAs seek to tackle envi-
ronmental problems by restricting the international movement of products or
species that are potentially harmful or endangered.
• Promote compliance and regime effectiveness. Some MEAs use trade measures to
e_n sure the ef~ective operatio~ of an environmental regime. For example, restric-
t10ns_~ay be imposed to p_umsh c?untries that do not fully comply with a regime's
prov1s1ons, or t~ ~rev~nt 1_n dustnal flight to non-parties, so-called "leakage."
• Encourage participation m environmental regimes. Trade restrictions are also
seen as a ~orm of pressure on countries that are reluctant to join an environ-
mental regime.
. For example ' the Montreal Protocol' s pro h 1.b mon
. · o f tra d e w1'th
non-parties encouraged some co t · · · h ·
. . un nes to )Om t e agreement to prevent bemg
e~cl~ded from the international trade in regulated substances and products con-
tammg them.
Trade e~perts ?ave raised several concerns about trade measures in MEAs. WTO
ru )es reqmre environmental trad b • · I
-h Id . . . e measures to e non-discriminatory that 1s t 1ey
sb aou ndot d1sc~1mma~e between "like products" from different WTO
members or
etween omest1c and mternatio I d ·
' na pro uct1on. Where environmental treaties target
pro d ucts because of the und I · h
er ymg process and production methods rather than t e
INfER NATION A L lHAD f., rH E ENVIHO NM[ N r , /\ND CLIM/\IL CII/\NC., L
4 1/
_--=.:=== = - = - -=- - - - -
.
cnv1ro1111 1t ,11 1-11
•
l]U;d itv, . ot. .tlit·
.
11rndue1
. .
it st·
·
lt·, •.111 )' 1.t:.~u
. Iting
· trat Ie 1111rrfen·11n
· · co11lcl lw
I
,t'l'il robe in hre;l ~h ot \V O o bligations. A fun he r an:a w here MFAs and th c WT<)
·rnk~ C<H111 ' L •
·hsh 1s• .w here 0 11e !Hrty •
t 0 .•1 ivLlL"Ac uses tratIe sanctions · again st a 11011
p:irry. bur bo~h parties arc mcm l~crs of the WTO. In such cases, the parry rhar suffe r..,
;i rr:1dt: sanction co ul d take action under the WTO a lleging breach of t rade rule~.
,.\s yet, no WTO n~em ber h ~,s ch a llenged an l EA in the WTO's d isp ure-sc rtlc111cnt
mechanism, but wi th grow m g use of MEA-bascd trade measure a future co nflict
over rheir \'VTO compatibil ity ca nnot be ruled ou t . The ne xt section considers w hat
recent WTO ~ispute settl em~nt cases tell u about the evolutio n of WTO jurisdiction
on rrade-en v1ronment co nflict .
l\· e been
les trade
Trends in WTO Jurisprudence
n e more
n eas ures Only a very small fracti o n of the over 500 disputes that have been considered unde r
neasures the GATI/WTO dispute-settlement mecha nism relate to environmenta l issues, even
though environment-related trade disputes have a ttracted a grea t d ea l o f public
attention. A closer examination of the m ost important cases revea ls important d evel-
pmenrs in trade jurisdiction. 2
Tuna-Dolphin
t ...
NOM Y A ND POLICY
GLOBAL ECO
~
418 c-=,-~
country's own jurisdiction, the US-Gasoline case marked the ca utious hcgi .
. . . nn,ngof
less restrictive interpretation of environmental measures. In thi s case, the WTo a
. · · . Pant1
stressed that trade measures must not d1scnmmate among countries but ack
. l . nowJ.
edged that they can be based on grounds o f env1ronmenta protection. The Shri,
Turtle case further strengthened this shift in the WTO's interpretation of environ np-
. rnen-
ta l trade measures · The decision almost reversed the ear 11er. Tuna-Dolphin dee·1s1.on
by arguing that a trade measure based on PPMs can be directed at other countrie
under Article XX, and that animals can qualify as an "exhaustible natural resource!
that may be protected through trade bans. In the EC-Biotech case, the WTO Panel
reinforced the importance of non-discrimination and the proper application of reg-
ulatory procedures, but acknowledged the importance of scientific uncertainty in
justifying trade restrictions, arguing that a moratorium amidst scientific uncertainty
need not necessarily violate international trade law. Thus, WTO jurisdiction ha.s
gradually come to accept that trade-restricting measures under Article XX can be
justified for environmental reasons, but continues to insist that they must not con-
stitute an arbitrary and/or unjustifiable discrimination. Indeed, the primary reason
why environmental measures in Gasoline, Shrimp-Turtle, and Retreaded Tires were
found to be in breach of WTO rules was not the ultimate objective of these measures
but the way in which they had been applied (DeSombre and Barkin 2002).
Climate change has added a new and urgent dimension to the debate on trade and
the environment: whereas previous trade-environment conflicts usually focused on
only a limited number of industries or countries, global warming affects virtually
every country and all aspects of economic life. Addressing climate change creates
fundamental questions of current and inter-generational fairness, equity, and free·
dam, and involves global collective action combined with unprecedented degrees of
market failure and scientific uncertainty (Stern 2007). Rich industrialized countries
are largely responsible for causing global warming in the past, but the majority of
future greenhouse gas emissions will come from rapidly industrializing emerging
economies such as China and India. In 2007, China overtook the USA as the world's
largest emitter, and in 2008, China and India together produced almost twice as
much CO2 as the 27 European Union countries combined.3
If some countries decide to reduce CO 2 em·1ss1on · wit . hout s1m1
. . ar com mi·rments
. . 1
from others, mternat1onal trade allows industr· l . . . h. ft from the
f h I Th 1a act1v1ty to s1mp1y s 1
.orme~ to _t e a tt~r. is ~a-called "carbon leakage" can occur in three ways: energy·
idntens1~e mdustnes physically relocate to countries with less stringent regulations;
omestJC producers lose market 5 h f . due·
tion· or a !owe d d f f . are to oreign competitors that increase pro he
' r eman or ossil fuels 111 . h" h l d ases t
overall price for the f I d h tg -regu ation countries ecre .
se ue s an t us leads tO · d I gu1.ttl011
countries (Frankel 2009 W b increase consumption in ow-re n·
tion costs local mark t ; de_ ~rand Peters 2009). Other factors such as rranspo\iv
' e con ltlons and the f . f n equ,1 .
or more important re b h. ' . cost o capital and labor are ore W t,er
and Peters 2009) H asons e md mdustrial relocation (World Bank 2008; _e 1s
· owever wh · d • [att01 '
such "leakage" und . 'h ere 111 u st nes move to avoid carbon regu' ges
ermmes t e goal f d . d d. our<'
ambitious climate policies. De . o re ucmg global emissions an . isc he111e,
peod mg on the type of emission reducnon sc
INTERN/\TI O N/\l. TRAD E, T H E ENVIHO NM ENT, A ND CLIM /\TE CH A NGE '1 2 1
~
<>i
.
"' nn1ng of 1c:1k:1i.:i.: rares ( i_- c. r1_1c i11cr~a se _i 11 l' l1~i ssio11s i 11 low -regu la rion COll lHrics ;\<; ; \ sh;i IT of
Wl'o a .,ductions 111 high-iegnl.iuon countiies) ha ve hec n estimated at as hig h as o m· fourth
Pant'I
it ai.:k :-~,r rhc iron and _s rec~ sc~tor a:id_~p _to one third for the cement industry (Reinaud
no\vl.
he. SI7 r1n1p_
· JOOS) . When E~11 opeclll coui~ti ies 1 attfied the Kyoto Protocol and introduced rh e El J
11v1r 011 Emissions Trading ?che m e (_ETS ), for instance, th ere was great concern o ve r whethe r
. nie 11•
·111 dee· .
1s100 rhe refusal of the USA t~ ratify the Kyo to Protocol would all o w it robe a " free ride r "
T count. Europe' s climate policy (B_iermann and Brohm 2005), with some arg uing that th e
I ries 011
resource" US rejection of Kyoto can be interpreted as a hidden subsid y for its indu stry and ma y
VfO Panel rhus conflict with trading rules (Stiglitz 2007). 4
·1on of reg. Against this background, some have called for trade measures to be used ro
enainty ·In discourage carbon leakage and free-riding (Stern 2007; Stiglitz 2007). As Barrett
tncenainty (2010: 3) put it bluntly : "If trade measures can enforce trade agreements, why not
liction has use trade measures to enforce climate agreements?" A common line of argument
"<:X can be is that since the WTO has the strongest compliance system of any international
, t not con- regime, it could strengthen international climate policies (Biermann and Brahm 2005;
Frankel 2009). Two specific proposals for climate-related trade measures ha ve been
put forward. A first proposal involves taxing imports from countries that apply less
stringent carbon emission limits. A so-called "border tax adjustment" (BTA) forces
importers to pay a fee that reflects the costs of carbon emissions while exporters may
obtain a tax credit to avoid double taxation (Frankel 2009; Kaufmann and Weber
2011). A second proposal envisions requirements to purchase emission permits in a
cap-and-trade system so that foreign and domestic producers pay the same price for
emitting a ton of CO2. France, the USA, and the EU have already tabled proposals
for how to incorporate trade measures into climate change legislation in the form of
BTAs or the mandatory purchase of emission permits (Biermann and Brahm 2005;
1ge creates Cosbey 2008; Tarasofsky 2008).
, and free- Ideally, since all current economic activity in one way or another produces carbon
degrees of missions, trade measures ought to cover the largest possible range of products. One
countr; ay to do this would be to consider the carbon footprint of each individual product,
iajorii possibly with the help of a standard developed by the International Organization
e for Standardization (ISO 14067; see also Gros et al. 2010). While this would ensure
that a large share of international trade is covered, developing a comprehensive
method to quantify the carbon content of every traded product for tax purposes
is difficult: national authorities may not have the capacity to collect data, produc-
ers have an incentive to underestimate carbon content, and complex international
supply chains make tracing the carbon content of each individual component of a
~roduct cumbersome (Cosbey 2008) . It would certainly be easier to target only a
limited range of internationally traded energy-intensive materials such as aluminum,
cem~nt, steel, paper, glass, iron, and chemicals. This approach, however, may dispro-
Porrionately harm manufacturers in technologically advanced countries who import
lation these materials for further processing without significantly reducing emissions of
·ansporra· energy-intensive manufacturing in heavily polluting countries (Cosbey 2008; Weber
en equallY and Pet ers 2 009). Moreover, the quantity o f em1ss10ns · . . d wit
associate . h b as1c . maten- .
)8; Weber afls ~ery much depends 011 the source of energy with which they were processed (e.g.
ulations, ossil f I
g es Me ue s_versus hydropower) (Cosbey 2008). . .
scourag asunng carbon content poses further d1fficult1es. A system that seeks to
ri scherne, count th e emissions · · of individual firms ma y be too comp 1ICate · d to wor k , given · t I1e
•
GLOBAL ECONOMY AND POLI CY
422
The set"u11d .trl',1 n·l.11t·s Ill die i111t·rpn·1·:1tion of l' Xis1i.11.g leg:il pr()vi1,ic~
/
c\'olvi11g m.111d:1lt' ;111d i11sti1111io11:1I lra111l'Work, tlie WI () ha s h:1d '> ip,ii f'ic•i l:'> pitcan bY ti
. I I , , nt diffll
u11 t'l'rtai11 t·11vin111111t·11tal 111eas11rl'S, as 0111'1 111 et a )ovc. Pa -;t dcci1,ic >n1, hav. _1111 Paq
ch ri rltd p\e3
\\'lut .1 "11ct:t·ssary " c11viro11111l'11tal measure .is; w I,at .is lllt'allt I1y "<· xha u1,1 il)\e ..
. . 11 e n·1t
n·sourt"e" ; whether measures can extend cxtr,itcrntoria y; and l1ow "arhitrar ',,ura\
"u11justitiahle" should be interpreted under t~1e chapeau of Artich: XX . Di~a ,a11 u r,101
mt·nt still cxis·ts however with regard to cnv1ronmcntal measure!> ·1i 111 ,,J
· , , . ' " at Pp~rec. M
especiall y when they are "unincorporated," that ts,_when th~y ca ll not be dctectc<l \
the final product. The definition and use of precaution remams equally contested in
has been illustrated by the EC-Biotech case and the question of "sound" scie 'a\
. . . . . . . nee a\
a cntenon for poltCy-makmg versus a broader 111terpretat1on of the evidence b
as1\
for risk assessment.
The third area relates to the question of inclusiveness and transparency of decision.
making. While the CTE has been tasked with addressing the relationship betwee
MEAs and the WTO, both in institutional and jurisdictional terms, there remain~
considerable debate on how to integrate the two, especially when the former con-
tinue to employ trade-restricting measures that remain vulnerable to challenges
under WTO law (Eckersley 2004; Palmer and Tarasofsky 2007). Another con-
tentious point is the access of external stakeholders, especially civil society and
NGOs, to WTO decision-making processes. While the WTO has promoted dialogue
with interested organizations, NGOs continue to raise concerns about the lack of
transparency in the WTO's deliberations and negotiations, especially with regard to
environmental issues.
The fourth and final area relates to the increasingly important impact of the
climate-change debate on international trade. As states explore different options for
reducing greenhouse gas emissions and global climate governance becomes increas-
ingly fragmented (Falkner et al. 2010), it is becoming clear that trade measures will
be part of the international effort to combat global warming. This could be in the
form of border tax adjustment to address international competitiveness issues, pref-
erential treatment of climate-friendly goods and services, renewable energy subsidies
and product labels indicating carbon content, among others (Brewer 2010). Efforts
to enforce international climate policy through trade measures may test the scope of
Article XX (Frankel 2009), and a push to target carbon content in internationally
traded goods may test the WTO's willingness to accept unilateral trade measures
that are based on PPMs (Hufbauer and Kim 2009). The WTO itself recognizes its
responsibility in the international community to address climate change as part of its
sustainable development agenda, but sees its role primarily as an arbiter of conflicts.
The challenge will be to avoid the trap of green protectionism, where general trade
restrictions are used to seek compliance with quite distinct climate goals. Climate
policy may yet prove to be the biggest challenge for the WTO's ability to manage
the trade-environment relationship.
Acknowledgments
· on but extends Falkner and Jaspers (2012). Research tow·
Th'. 1s chapter bmids 1rd5
,,' he
1
rh1s chapter was supported by a grant from the Kolleg-Forschergruppe (KF_G); ded
Transformative Power of Europe" at Freie Universitat Berlin. The KFG ,s tun
INTERNAl IONI\L lHAnr Tl IL -
- -- ' ENVinONM ENl
-======== - -=- - -=- --=- , /\ND CLIMArF CH/\NGE
'l25
by rhc Gcrm :111 R t'SL':trl·h l-'ound:1ti o n (I : ,
.. . .. I . I ' ) I (,) ·1II I I ·.
llittusI0 11 ot ll L':t s Ill i- lL' 1-.U\ i 11tc n1 ·1I . I . t lt 111g\ toge1hn re\e·1r ·I h
. · ,111( t'X tt' rn · I . ·I· . . , l I c>r1 t ,.
pk:tSl' (011sult www .tr:rn sl o r1neu ropt' .eu . ,t It .111 0 11 s. I-c ir furth er i11forin:1t io11
Notes
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