remediation of polluted soil in china: policy and ...soils.ifas.ufl.edu/lqma/publication/xu...

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Remediation of Polluted Soil in China: Policy and Technology Bottlenecks Congbin Xu, ,Wenjie Yang, § Lusheng Zhu, Albert L. Juhasz, # Lena Q. Ma, Jun Wang,* ,and Aijun Lin* ,College of Chemical Engineering, Beijing University of Chemical Technology, Beijing, 100029, P.R. China College of Resources and Environment, University of Chinese Academy of Sciences, Beijing, 100049, P.R. China § Chinese Academy for Environmental Planning, Beijing, 100012, P.R. China College of Resources and Environment, Shandong Agricultural University, Taian, 271000, P.R. China Soil and Water Science Department, University of Florida, Gainesville, Florida, 32611, United States # Future Industries Institute, University of South Australia, Adelaide, SA 5095, Australia F aced with severe soil pollution, China has promulgated environmental laws, regulations, and standards to control soil pollution. For example, in 2016 the State Council of China issued a Soil Pollution Prevention and Control Action Plan. The plan was aimed at making 90% of polluted farmland soil safe for human use by 2020 and 95% by 2030, as specied in Chinas 13th Five-Year Plan. 1 The Chinese government has made progress by promulgating policies, but the country still lags in its eort to realize these goals in actual practice. China has undertaken 100 soil remediation projects from 2013 to 2015, and the number of projects is 28, 40, and 32, respectively, indicating a decline in 2015 compared to 2014. Farmland restoration accounts for only about 10% of the projects, signicantly below the expectations of the government. 2 A signicant problem facing local governments, companies and the general public is the lack of clarity on the extent of Chinas soil pollution. In 2014, a soil survey report was released by the government. It indicated that 16% of the samples collected from sites across 1500 surveyed areas representing 6.3 million square kilometers exceeded soil standards for a range of organic and inorganic contaminants. 3 However, the survey was limited in its extent and did not fully reect the actual extent of soil pollution across the Chinese landscape. We believe that more comprehensive information is needed to assess the risk to the population and to prioritize remediation of agricultural and urban soils. The Institute of Public & Environmental Aairs published a map (see Figure 1) detailing soil pollution risk, the rst such map made available to the public in China following public outcry regarding soil pollution at a Changzhou school, which caused almost 500 students to suered symptoms such as skin inammation, eczema and bronchitis. 4 The map identied 4500 companies from 13 industries including chemical production, mining and smelting that could have polluted nearby soils. The companies were classied according to whether they were state- owned (89%), nonstate owned (11%) or if they were located in industrial zones. Although geographic regions of potential impact were useful, the map did not provide specic detail regarding the location of polluted sites nor the degree of soil pollution. However, the map may be useful in the soil risk assessment and its remediation prioritization. The pollution risk map and polluted site registry increased public awareness of soil pollution and related issues. To turn awareness into action, we believe that a strategy is required to consolidate soil pollution data and implement Chinas new environmental policies. In addition, it is unclear whether there are enforceable requirements for soil pollution and how these data will be managed and reported. The implementation of long-term soil remediation strategies faces signicant economic challenges. The Soil Action Plan is based on the polluter pays principle, which is the idea underlying the U.S. Superfund. Although this is a pragmatic approach, it may be impractical for China. In China, it is often dicult to identify parties responsible for pollution and to enforce the polluter pays principle. This situation is complicated further by the fact that some soil pollution may have resulted from agricultural inputs by farmers. According to the Ministry of Environmental Protection, 3 the cost of soil remediation could be as high as hundreds of thousands of yuan per ha depending on the contaminant and the extent of contamination. With an annual income from farmland at Received: October 25, 2017 Published: December 8, 2017 Viewpoint pubs.acs.org/est Cite This: Environ. Sci. Technol. 2017, 51, 14027-14029 © 2017 American Chemical Society 14027 DOI: 10.1021/acs.est.7b05471 Environ. Sci. Technol. 2017, 51, 1402714029

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Page 1: Remediation of Polluted Soil in China: Policy and ...soils.ifas.ufl.edu/lqma/Publication/Xu 17.pdfThe pollution risk map and polluted site registry increased ... some countries require

Remediation of Polluted Soil in China: Policy and TechnologyBottlenecksCongbin Xu,†,‡ Wenjie Yang,§ Lusheng Zhu,∥ Albert L. Juhasz,# Lena Q. Ma,⊥ Jun Wang,*,∥

and Aijun Lin*,†

†College of Chemical Engineering, Beijing University of Chemical Technology, Beijing, 100029, P.R. China‡College of Resources and Environment, University of Chinese Academy of Sciences, Beijing, 100049, P.R. China§Chinese Academy for Environmental Planning, Beijing, 100012, P.R. China∥College of Resources and Environment, Shandong Agricultural University, Taian, 271000, P.R. China⊥Soil and Water Science Department, University of Florida, Gainesville, Florida, 32611, United States#Future Industries Institute, University of South Australia, Adelaide, SA 5095, Australia

Faced with severe soil pollution, China has promulgatedenvironmental laws, regulations, and standards to control

soil pollution. For example, in 2016 the State Council of Chinaissued a Soil Pollution Prevention and Control Action Plan.The plan was aimed at making 90% of polluted farmland soilsafe for human use by 2020 and 95% by 2030, as specified inChina’s 13th Five-Year Plan.1 The Chinese government hasmade progress by promulgating policies, but the country stilllags in its effort to realize these goals in actual practice. Chinahas undertaken 100 soil remediation projects from 2013 to2015, and the number of projects is 28, 40, and 32, respectively,indicating a decline in 2015 compared to 2014. Farmlandrestoration accounts for only about 10% of the projects,significantly below the expectations of the government.2

A significant problem facing local governments, companiesand the general public is the lack of clarity on the extent ofChina’s soil pollution. In 2014, a soil survey report was releasedby the government. It indicated that 16% of the samplescollected from sites across 1500 surveyed areas representing 6.3million square kilometers exceeded soil standards for a range oforganic and inorganic contaminants.3 However, the survey was

limited in its extent and did not fully reflect the actual extent ofsoil pollution across the Chinese landscape. We believe thatmore comprehensive information is needed to assess the risk tothe population and to prioritize remediation of agricultural andurban soils.The Institute of Public & Environmental Affairs published a

map (see Figure 1) detailing soil pollution risk, the first suchmap made available to the public in China following publicoutcry regarding soil pollution at a Changzhou school, whichcaused almost 500 students to suffered symptoms such as skininflammation, eczema and bronchitis.4 The map identified 4500companies from 13 industries including chemical production,mining and smelting that could have polluted nearby soils. Thecompanies were classified according to whether they were state-owned (89%), nonstate owned (11%) or if they were located inindustrial zones. Although geographic regions of potentialimpact were useful, the map did not provide specific detailregarding the location of polluted sites nor the degree of soilpollution. However, the map may be useful in the soil riskassessment and its remediation prioritization.The pollution risk map and polluted site registry increased

public awareness of soil pollution and related issues. To turnawareness into action, we believe that a strategy is required toconsolidate soil pollution data and implement China’s newenvironmental policies. In addition, it is unclear whether thereare enforceable requirements for soil pollution and how thesedata will be managed and reported.The implementation of long-term soil remediation strategies

faces significant economic challenges. The Soil Action Plan isbased on the polluter pays principle, which is the ideaunderlying the U.S. Superfund. Although this is a pragmaticapproach, it may be impractical for China. In China, it is oftendifficult to identify parties responsible for pollution and toenforce the polluter pays principle. This situation iscomplicated further by the fact that some soil pollution mayhave resulted from agricultural inputs by farmers. According tothe Ministry of Environmental Protection,3 the cost of soilremediation could be as high as hundreds of thousands of yuanper ha depending on the contaminant and the extent ofcontamination. With an annual income from farmland at

Received: October 25, 2017Published: December 8, 2017

Viewpoint

pubs.acs.org/estCite This: Environ. Sci. Technol. 2017, 51, 14027−14029

© 2017 American Chemical Society 14027 DOI: 10.1021/acs.est.7b05471Environ. Sci. Technol. 2017, 51, 14027−14029

Page 2: Remediation of Polluted Soil in China: Policy and ...soils.ifas.ufl.edu/lqma/Publication/Xu 17.pdfThe pollution risk map and polluted site registry increased ... some countries require

∼¥7500 per ha, it may take over a decade for farmers togenerate the required revenue, which is beyond their means.3

This is particularly challenging for a country with a rapidlydeveloping economy and a large population, where economicgrowth still remains the primary social priority.In contrast, some countries require local governments to bear

the costs of cleanup rather than enforce the polluter paysprinciple. For example, when Japan faced a significant cadmiumpollution event in the 1970s, 856 ha of soil was remediated at acost of $350 million over a 33-year period. Faced with thisburden, the Mitsui mineral company (the polluter), received61% of remediation costs from the government.5 For China,however, this approach is infeasible. China has 124 million haof farmlands to feed over 1.4 billion people, with estimatesindicating that nearly 20% of the country’s farmland is polluted.According to Professor Lan Hong of Renmin University,5

China requires ¥7 trillion to remediate polluted soil usingtechnologies imported from the U.S. and Japan, which isequivalent to a third of its foreign exchange reserves.The prohibitive cost is a main obstacle impeding soil

remediation in China. We believe that the government shouldactively guide companies to participate in soil remediationthrough positive policy measures. We also believe that theyneed to support policies to drive the development of lessexpensive soil remediation technologies. Although there are anumber of companies in China, which offer remediationservices, these companies lack effective technologies for theremediation of soil-borne contaminants. To solve this dilemma,some companies actively import advanced technologies,however, almost all soil remediation technologies are tooexpensive for practical application. In addition, it is unclearwhether or not these technologies will be effective under thediverse soil conditions encountered in China. Therefore, thehighest priority challenge is the development of inexpensiveand effective remediation technologies locally.Policies and technologies must be practical to implement.

Currently, the absence of clear regulations, incompletemonitoring data and a lack of inexpensive technologies arethe main bottlenecks for pollution control and remediation in

China. As a consequence, refined, accountable and standardizedpolicies as well as cost-effective technologies on soilremediation are urgently required to accelerate soil remediationactivities. More importantly, a consolidated effort is needed tointegrate policies, technologies and practice to achieve neededsoil remediation in China.

■ AUTHOR INFORMATIONCorresponding Authors*(J.W.) E-mail: [email protected]*(A.L.) Phone:13520297239; e-mail: [email protected], .ORCIDLusheng Zhu: 0000-0001-6212-1965Lena Q. Ma: 0000-0002-8463-9957Aijun Lin: 0000-0002-8420-2085NotesThe authors declare no competing financial interest.

■ ACKNOWLEDGMENTSThis work was supported by the National Key Research andDevelopment Program of China (2017YFD0801503,2016YFD0800304), National Natural Science Foundation ofChina (41701367) and the National Science and TechnologyMajor Project on Water Pollution Control and Treatment(2018ZX07111003).

■ REFERENCES(1) Cyranoski, D. What China’s latest five-year plan means forscience. Nature 2016, 531, 524.(2) Market situation and development trend of China’s environ-mental protection industry in 2016. China Industrial Information2016, http://www.chyxx.com/industry/201604/406102.html(in Chi-nese).(3) The answer from the responsible person of Ministry ofEnvironmental Protection 2016, http://www.zhb.gov.cn/home/jrtt_1/201605/t20160531_352669.shtml (in Chinese).(4) The frist map of soil pollution risk from the Institute of Public &Environmental Affairs. http://huanbao.bjx.com.cn/news/20160429/729361.shtml (in Chinese).

Figure 1. Nationwide soil pollution sites based on pollution sources (Institute of Public & Environmental Affairs).

Environmental Science & Technology Viewpoint

DOI: 10.1021/acs.est.7b05471Environ. Sci. Technol. 2017, 51, 14027−14029

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(5) Zhang, Y.; Zhou, C., China’s tainted soil initiative lacks pay plan.Chinadialogue 2016, https://www.chinadialogue.net/article/show/single/en/9028-China-s-tainted-soil-initiative-lacks-pay-plan.

Environmental Science & Technology Viewpoint

DOI: 10.1021/acs.est.7b05471Environ. Sci. Technol. 2017, 51, 14027−14029

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