Fending off waste from the west: The impact of China's Operation Green Fence on the international waste trade

Date01 October 2020
Published date01 October 2020
DOIhttp://doi.org/10.1111/twec.12949
AuthorMark Sanctuary,Adomas Balkevicius,Sigita Zvirblyte
2742
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wileyonlinelibrary.com/journal/twec World Econ. 2020;43:2742–2761.
© 2020 John Wiley & Sons Ltd
Received: 21 November 2019
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Revised: 21 February 2020
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Accepted: 4 March 2020
DOI: 10.1111/twec.12949
ORIGINAL ARTICLE
Fending off waste from the west: The impact of
China's Operation Green Fence on the international
waste trade
AdomasBalkevicius
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MarkSanctuary
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SigitaZvirblyte
Department of Economics, Stockholm School of Economics, Stockholm, Sweden
KEYWORDS
China, environmental policy, international waste trade, recycling
1
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INTRODUCTION
The global trade of waste and scrap is becoming increasingly a flow of waste from developed to de-
veloping countries, growing 500% over the two decades since 1992 (Kellenberg, 2015). Proponents
of the waste trade maintain that importers can benefit by gaining access to cheap, recycled input ma-
terials. Opponents claim that waste importers lack the capacity to effectively manage waste imports.
By exporting to these countries, the costs of proper disposal are avoided resulting in "waste havens",
which are a special case of the pollution haven.
China is by far the world's largest importer of non-hazardous waste, accounting for 22% of the
global waste imports in 2014 (UN Comtrade, 2016). This type of waste import is slated for recycling
and/or recovery and thereby serves as an input to production. Hence, this type of trade should be in
principle no different from trade in intermediate inputs. However, poor quality (e.g., contaminated)
waste shipments and waste smuggling were a problem. A concern was the cost of sorting imposed on
domestic manufacturing, and the associated environmental impact of the unwanted wastes (Flower,
2016).
In response to the problem of poor quality wastes and smuggling, China adopted policies that
target the flow of unwanted, poor quality wastes that are costly to recover or dispose. As part of the
response, China launched Operation Green Fence (OGF) from 1 February to 31 November 2013. The
main objective of the 10-month-long policy intervention was to enforce waste trade policies already
adopted by China and thereby restrict illegal hazardous waste imports. In practice, this entailed a
marked increase in inspection efforts and policing activity at the border.
This paper assesses the impact of OGF on the global, non-hazardous waste trade.1 We study the
non-hazardous waste trade because China has a ban on all hazardous waste imports. We focus on two
1The international trade of hazardous waste is of course also an important and related issue; see Baggs (2009) and Kellenberg
(2015) for a description of this type of waste trade.
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BALKEVICIUS Et AL.
empirical issues. First, we examine the extent to which waste exports from developed countries to
China were affected by the intervention.2 We are particularly interested in identifying the types of
waste that were affected by OGF.
Second, we seek to identify the extent to which OGF resulted in an increase in waste exports from
developed countries to developing countries excluding China.3 As part of this second line of inquiry,
we test the waste haven hypothesis: OGF resulted in an increase in wastes imported by developing
countries (excluding China) with weak environmental regulation.
To assess the impact of OGF, we make use of the international trade panel data available from UN
Comtrade and US Census Bureau, which yields annual observations of the net weight (kg) and value
(US$) of non-hazardous wastes shipped at the 6-digit level Harmonised System (HS) code between
developing countries and developed countries over the 6-year period of 2010-15.
If OGF had an impact on the international waste trade, it would be on those waste shipments clas-
sified as ‘illegal’. Non-hazardous waste imports by China are classified as illegal if contamination
levels surpass a threshold, or if other criteria are not met such as faulty declarations of waste type, or
if the waste is too damp or wet. We focus our analysis on 54 product categories described as waste at
the HS6 level—following the method deployed by Kellenberg and Levinson (2014) who studied the
impact of the Basel Convention on the international waste trade.
We posit that low-quality waste is more likely to be contaminated, and rejected under OGF.
However, we do not directly observe the quality of the waste export. To address this, we use the aver-
age unit value of the waste as a proxy for waste quality. Low-quality waste exports are defined as waste
exports with the lowest unit value within a given HS 6-digit category across all countries exporting
that waste category. The effects of OGF should be most pronounced for low-quality waste shipments.
Identification of the impact of OGF is achieved using the within-HS6×country-pair deviation in net
weight from the 5-year trend. We estimate the effect using a gravity model of trade with exporter–im-
porter–HS6 waste type fixed effects.
We find that OGF reduced the flow of low-quality waste from developed countries to China by 26%,
equivalent to 3.93 metric megatons over the period OGF was in effect. We do not find evidence that OGF
resulted in significant spillover effects to other developing countries: we do not find that OGF resulted in a
statistically significant increase in low-quality waste exports from developed countries to developing coun-
tries (excluding China). Moreover, we do not find any evidence of a waste haven effect: OGF did not have
a significant impact on waste exports to developing countries with the weakest environmental regulation.
To the best of our knowledge, this is the first econometric analysis of the impact of OGF on the
international waste trade. More generally, there are few studies that examine the international waste
trade specifically; Kellenberg (2015) reviews the literature. Kellenberg and Levinson (2014) study
the impact on countries ratifying a multilateral agreement seeking to regulate the international waste
trade, ‘The Basel Convention on the Control of Transboundary Movements of Hazardous Waste and
their Disposal’. Our study is similar in terms of methodology and data sources. They find no evidence
that the Convention affected exports of waste from developed countries, although they did find some
evidence that developing countries restricted waste imports. A distinction is that our study considers
the impact of enforcing policy, whereas Kellenberg and Levinson (2014) study policy ratification.
Kellenberg (2012) tests the waste haven hypothesis, which states that the differences in domestic
environmental laws might result in the exports of waste streaming to less regulated countries. The author
found the effects to be statistically significant and substantial, concluding that more stringent domestic
2EU and/or OECD countries are referred to as developed. China includes mainland China and Hong Kong, but not Macao.
3Developing countries are identified as countries that are not part of EU or OECD.

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