Remediation of arsenic-contaminated paddy soil by intercropping aquatic vegetables and rice

被引:14
作者
Huang, S. Y. [1 ,2 ,3 ]
Zhuo, C. [1 ,2 ,3 ]
Du, X. Y. [1 ,2 ,3 ]
Li, H. S. [1 ,2 ,3 ]
机构
[1] South China Agr Univ, Minist Agr, Key Lab Trop Agroenvironm, Guangzhou, Peoples R China
[2] South China Agr Univ, Coll Nat Resources & Environm, Guangdong Higher Educ Inst, Key Lab Soil Environm & Waste Reuse Agr, Guangzhou, Peoples R China
[3] South China Agr Univ, Inst Trop & Subtrop Ecol, Guangzhou, Peoples R China
基金
中国国家自然科学基金;
关键词
Paddy field; phytoremediation; soil remediation;
D O I
10.1080/15226514.2021.1872485
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Soil contamination by arsenic (As) is an important environmental issue globally. Intercropping of hyperaccumulators with main crop is typically applied for remediation of As-contaminated soil. Most hyperaccumulators are wild plants with small biomass and slow growth rates. Thus, remediation is slow. Here, we propose an effective intercropping system for remediation of As-contaminated paddy soil. Four treatments-intercropping with water spinach (Ipomoea aquatica Forsk) (T1), water celery (Oenanthe javanica (Blume) DC.) (T2), or Guangdong white arrowhead (Sagittaria sagittifolia L. var) (T3), with rice (Oryza sativa L.) monoculture (control, CK)-were used. Compared with the CK, grain yield per plant of rice under T1 and T2 increased by 58.13% and 10.48%, respectively, but decreased by 46.90% in T3. As concentration, bioaccumulation factor, and translocation factor in brown rice were significantly lower in the intercropping treatments than in CK. As removal by water spinach was 7.04 and 1.47 times that by water celery and arrowhead, respectively. The pH of paddy soil was significantly higher in all treatments than in CK, and iron plaque on rice roots under T1 and T2 decreased significantly but increased significantly under T3 compared with that of CK. Rice intercropped with water spinach had the best remediation effect. Novelty Statement: We believe that the following highlights of this manuscript will make it interesting to general readers of this journal. First, in recent years, many articles about intercropping system for the remediation of soil heavy metal pollution focus on dry land, and few studies have focused on paddy soil. The present study was on arsenic-contaminated paddy soil remediation. Second, water spinach, water celery, and arrowhead have great potential for phytoremediation. Studies have shown that these three aquatic vegetables play a role in the removal of certain pollutants, such as heavy metals. Moreover, when intercropped with rice, they can effectively increase rice yield and reduce rice diseases and insect pests. However, studies on remediation of arsenic-contaminated soil by intercropping aquatic vegetables and rice have not been reported. We propose here a rice-aquatic vegetables (water spinach, water celery and arrowhead) intercropping pattern for remediation of arsenic in soil. Third, according to the arsenic concentration and removal rate, we used a bioaccumulation factor, translocation factor, and arsenic removal per unit area of plants for the quantitative evaluation of the remediation effects of the intercropping systems. We found that the intercropping of rice and water spinach could be used to remediate arsenic-contaminated soil. Moreover, the extraction contents of arsenic using intercropping with water spinach was higher than that achieved in a previous study that applied intercropping with the arsenic hyperaccumulator Pteris vittata over the same growth time. This study provides a reference for realizing both remediation and increased production in arsenic-contaminated soil and for promoting sustainable development of agriculture.
引用
收藏
页码:1021 / 1029
页数:9
相关论文
共 46 条
[1]   Uptake of Aromatic Arsenicals from Soil Contaminated with Diphenylarsinic Acid by Rice [J].
Arao, Tomohito ;
Maejima, Yuji ;
Baba, Koji .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2009, 43 (04) :1097-1101
[2]  
Chang Xuexiu, 2000, Yingyong Shengtai Xuebao, V11, P315
[3]   Anthropogenic arsenic cycles: A research framework and features [J].
Chen, Wei-Qiang ;
Shi, Ya-Lan ;
Wu, Shi-Liang ;
Zhu, Yong-Guan .
JOURNAL OF CLEANER PRODUCTION, 2016, 139 :328-336
[4]  
Chen YX., 2000, ACTA SCI CIRCUMSTANT, V20, P467, DOI DOI 10.13671/J.HJKXXB.2000.04.017
[5]   Reducing arsenic in rice grains by leonardite and arsenic-resistant endophytic bacteria [J].
Dolphen, Rujira ;
Thiravetyan, Paitip .
CHEMOSPHERE, 2019, 223 :448-454
[6]  
Du JB, 2018, J INTEGR AGR, V17, P747, DOI [10.1016/S2095-3119(17)61789-1, 10.1016/s2095-3119(17)61789-1]
[7]   Arsenic hyperaccumulating fern: Implications for remediation of arsenic contaminated soils [J].
Fayiga, Abioye O. ;
Saha, Uttam K. .
GEODERMA, 2016, 284 :132-143
[8]   Arsenic species in an arsenic hyperaccumulating fern, Pityrogramma calomelanos:: a potential phytoremediator of arsenic-contaminated soils [J].
Francesconi, K ;
Visoottiviseth, P ;
Sridokchan, W ;
Goessler, W .
SCIENCE OF THE TOTAL ENVIRONMENT, 2002, 284 (1-3) :27-35
[9]   Root iron plaque alleviates cadmium toxicity to rice (Oryza sativa) seedlings [J].
Fu, Youqiang ;
Yang, Xujian ;
Shen, Hong .
ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY, 2018, 161 :534-541
[10]  
[高帅强 Gao Shuaiqiang], 2019, [环境科学学报, Acta Scientiae Circumstantiae], V39, P2182