Review on remediation technologies for arsenic-contaminated soil

doi:10.1007/s11783-019-1203-7

Front. Environ. Sci. Eng.

2020, Vol. 14

Issue (2) : 24 https://doi.org/10.1007/s11783-019-1203-7

REVIEW ARTICLE

Review on remediation technologies for arsenic-contaminated soil

Xiaoming Wan^1,², Mei Lei^1,²(

), Tongbin Chen^1,²

¹. Institute of Geographic Sciences and Natural Resources Research Chinese Academy of Sciences, Beijing 100101, China
². University of Chinese Academy of Sciences, Beijing 100049, China

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Abstract

• Recent progress of As-contaminated soil remediation technologies is presented.

• Phytoextraction and chemical immobilization are the most widely used methods.

• Novel remediation technologies for As-contaminated soil are still urgently needed.

• Methods for evaluating soil remediation efficiency are lacking.

• Future research directions for As-contaminated soil remediation are proposed.

Arsenic (As) is a top human carcinogen widely distributed in the environment. As-contaminated soil exists worldwide and poses a threat on human health through water/food consumption, inhalation, or skin contact. More than 200 million people are exposed to excessive As concentration through direct or indirect exposure to contaminated soil. Therefore, affordable and efficient technologies that control risks caused by excess As in soil must be developed. The presently available methods can be classified as chemical, physical, and biological. Combined utilization of multiple technologies is also common to improve remediation efficiency. This review presents the research progress on different remediation technologies for As-contaminated soil. For chemical methods, common soil washing or immobilization agents were summarized. Physical technologies were mainly discussed from the field scale. Phytoextraction, the most widely used technology for As-contaminated soil in China, was the main focus for bioremediation. Method development for evaluating soil remediation efficiency was also summarized. Further research directions were proposed based on literature analysis.

Keywords Arsenic, field-scale Immobilization Phytoextraction Soil washing

Corresponding Author(s): Mei Lei

Issue Date: 30 December 2019

Cite this article:

Xiaoming Wan,Mei Lei,Tongbin Chen. Review on remediation technologies for arsenic-contaminated soil[J]. Front. Environ. Sci. Eng., 2020, 14(2): 24.

URL:

https://academic.hep.com.cn/fese/EN/10.1007/s11783-019-1203-7
https://academic.hep.com.cn/fese/EN/Y2020/V14/I2/24

Tab.1 Reagents used in As-contaminated soil washing

Immobilization agent	Soil utilization	Total As concentration (mg/kg)	Soil pH	Reagent	Concentration	Immobilization efficiency (%)	Period	Reference
Laboratory-scale
(hydro) oxides	Agricultural field	3500	7.4	Schwertmannite	5% weight	63	35 days	^{Yang et al. (2017)}
	Mining site	2548	6.3	Maghemite nanoparticles	5% weight	99	10 days	Arenas-Lago et al. (2019)
	Mining site	479	4.6	Aluminum oxide	5% weight	31	2 days	^{Doherty et al. (2017)}
	Mining site	479	4.6	Manganese (IV) oxide	3% weight	40	2 days	^{Doherty et al. (2017)}
	Mining site	479	4.6	Kaolinite	10% weight	26	2 days	^{Doherty et al. (2017)}
	Mining site	479	4.6	Ferric chloride+ lime	1%:1% weight	71	2 days	^{Doherty et al. (2017)}
	Mining site	479	4.6	Zero valent iron powder	1% weight	90	2 days	^{Doherty et al. (2017)}
	Mining site	479	4.6	Ferrihydrite (synthesized)	3% weight	84	2 days	^{Doherty et al.(2017)}
	Mining-metallurgy site	70200	6.4	Zero-valent iron nanoparticles	10% weight	92	72 hours	Gil–Díaz et al.(2017)
	Mining-metallurgy site	25900	6.4	Zero-valent iron nanoparticles	10% weight	91-95	72 hours	Gil–Díaz et al.(2017)
	Agricultural field	2047	4.2	Al₂O₃·2SiO₂·CaO	6% weight	96.2	28 day	Wang et al. (2019)
biochar	Mining site	15,076.80	3.7	Biochar	2% weight	22	2 hours	^{Chen et al. (2018b)}
	Landfill site	1202	4.6	Biochar	10% weight	25	7 days	^{Alozie et al. (2018)}
	Paddy field	47	6.9	Biochar	1% weight	16	35 day	^{Zhu et al. (2019)}
Solid waste	Paddy field	131.5	6.0	Acid mine drainage sludge	3% weight	93	25 days	^{Ko et al. (2015)}
	Farmland	118	6.8	Coal mine drainage sludge	7% weight	98	28 days	^{Cui et al. (2018)}
	Farmland	118	6.8	Waste cow bones	3% weight	74	28 days	^{Cui et al. (2018)}
	Farmland	118	6.8	Steel making slag	7% weight	98	28 days	^{Cui et al. (2018)}
	Agricultural areas	54	7.4	Municipal solid waste compost	3% weight	45	2 months	Abou Jaoude et al. (2019)
Combined	Paddy field	47	6.9	Bismuth-impregnated biochar	2%	69	35 day	^{Zhu et al. (2019)}
Combined	Paddy field	59	4.7	Fe:biochar	5%:1% weight	41	120 day	^{Qiao et al. (2018)}
Bio-materials	Paddy soil	140	5.9	Soil microbial fuel cells bioanode	N/A	47	50 days	Gustave et al. (2018)
Field-scale
(hydro) oxides	Brownfield	43300	7.0	Nanoscale zero-valent iron	2.5% weight	57	32 month	Gil-Díaz et al. (2019)
	Brownfield	7280	7.2	Nanoscale zero-valent iron	2.5% weight	74	32 month	Gil-Díaz et al. (2019)
	Agricultural field	600	8	Zero-valent iron	1% weight	95	15 years	^{Tiberg et al. (2016)}
	industrial site	8280	7.4	Fe-Mn binary oxide	10% weight	7.8	10 months	^{Tiberg et al. (2016)}
	Abandoned smelter	142	4.6	Fe-based sorbent (46.1% Fe₂O₃, 15.4% MgO, 14.3% CaO, 12.9% SO₃, 8.3% SiO₂, and 1.7% Al₂O₃)	1% weight	18.8	1 week	An et al. (2019)
Solid waste	Paddy field	131.5	6.0	Acid mine drainage sludge	3% weight	45	2 years	^{Ko et al. (2015)}

Tab.2 Reagents used in As-contaminated soil immobilization

Tab.3 Several representative phytoextraction projects of As-contaminated soil in China

Tab.4 Examples of microorganisms used in bioremediation of As-contaminated soil

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