Abstract:In the study, soybean (Glycine max (L.) Merr.), rape (Brassica napus L.) and wheat (Triticum aestivum L.) were used as the subjects, intercropped with Cd hyperaccumulators, i.e. Sedum plumbizincicola, Sedum alfredii, Amaranthus tricolor L. and Solanum nigrum L., to investigate the remediation effects of various intercropping patterns on Cd polluted farmland soil in southern Jiangsu Province. The findings revealed that intercropping with rape, the Cd concentrations in the hyperaccumulator plants were enhanced, among which Sedum alfredii increased the most, and the Cd concentrations in aboveground parts increased by 24.4% compared with monoculture. After intercropping with wheat, Cd concentration in Sedum alfredii was increased, the Cd concentrations in aboveground parts increased by 2.75% compared with monoculture, but the Cd concentrations of Solanum nigrum and Amaranthus tricolor did not change significantly, indicating that intercropping with rape or wheat could promote the absorption of Cd by Sedum alfredii. Intercropping with Sedum alfredii decreased the Cd concentration in soybean roots, and intercropping with Amaranthus tricolor and Solanum nigrum significantly decreased the Cd concentration in soybean stems and leaves. Under the intercropping mode, the Cd concentration of rape roots and stems decreased significantly, and the Cd concentration of leaves was not significantly affected by intercropping. Intercropping significantly reduced the Cd concentration of wheat, suggesting that intercropping could inhibit the absorption of Cd by crops. The total accumulation of Cd and the removal rate of Cd in soil under Sedum alfredii-rape model were the highest, which were 1343μg/pot and 16.4%. Sedum alfredii-wheat was the second, with 1053μg/pot and 9.8%. In summary, the intercropping pattern of Sedum alfredii-Brassica napus/Triticum aestivum were the suitable model. This study screens out a plant intercropping remediation model suitable for Cd-contaminated farmland soil in southern Jiangsu province area and provide technical support for both safe production and remediation of Cd-contaminated farmland soil in the region.
徐双圆, 朱家辉, 王栋茹, 占新华. 植物套作系统修复镉污染农田土壤的效应——以苏南地区为例[J]. 中国环境科学, 2024, 44(6): 3289-3300.
XU Shuang-yuan, ZHU Jia-hui, WANG Dong-ru, ZHAN Xin-hua. Effect of plant intercropping system on remediation of cadmium contaminated farmland soil—A case study on the southern Jiangsu province area. CHINA ENVIRONMENTAL SCIENCECE, 2024, 44(6): 3289-3300.
[1] Ren S, Song C, Ye S, et al. The spatiotemporal variation in heavy metals in China's farmland soil over the past 20 years:A meta-analysis[J]. Science of The Total Environment, 2022,806:150322. [2] 林云青,章钢娅.粘土矿物修复重金属污染土壤的研究进展[J].中国农学通报, 2009,25:422-427. Lin Y Q, Zhang G Y. Research advances on remediation of heavy metal contaminated soils using clay minerals[J]. Chinese Agricultural Science Bulletin, 2009,25:422-427. [3] 陈能场,郑煜基,何晓峰,等.《全国土壤污染状况调查公报》探析[J].农业环境科学学报, 2017,36(9):1689-1692. Chen N C, Zheng Y J, He X F, et al. Analysis of the report on the national general survey of soil contamination[J]. Journal of Agro-Environment Science, 2017,36(9):1689-1692. [4] 刘孝严,樊亚男,刘鹏,等.基于文献计量分析的长江经济带农田土壤重金属污染特征[J].环境科学, 2022,43:5169-5179. Liu X Y, Fan Y N, Liu P, et al. Characteristics of heavy metal pollution in farmland soil of the yangtze river economic belt based on bibliometric analysis[J]. Environmental Science, 2022,43(11):5169-5179. [5] Zhou Q, Chen J, Xing Y, et al. Influence of intercropping Chinese milk vetch on the soil microbial community in rhizosphere of rape[J]. Plant and Soil, 2019,440:85-96. [6] 李侃麒,吴佳玲,陈喆,等.天然有机酸对伴矿景天吸取土壤镉的影响[J].中国环境科学, 2023,43(5):2413-2422. Li K Q, Wu J L, Chen Z, et al. Effects of natural organic acids on cadmium uptake by Sedum plumbizincicola from the soil[J]. China Environmental Science, 2023,43(5):2413-2422. [7] Odoh C K, Zabbey N, Sam K, et al. Status, progress and challenges of phytoremediation-An African scenario[J]. Journal of Environmental Management, 2019,237:365-378. [8] Yang Y, Ge Y, Tu P, et al. Phytoextraction of Cd from a contaminated soil by tobacco and safe use of its metal-enriched biomass[J]. Journal of Hazardous Materials, 2019,363:385-393. [9] Tang Y T, Deng T H B, Wu Q H, et al. Designing cropping systems for metal-contaminated sites:A Review[J]. Pedosphere, 2012,22:470-488. [10] Ma L, Wu Y, Wang Q, et al. The endophytic bacterium relieved healthy risk of pakchoi intercropped with hyperaccumulator in the cadmium polluted greenhouse vegetable field[J]. Environmental Pollution, 2020,264:114796. [11] Brooker R W, Bennett A E, Cong W F, et al. Improving intercropping:A synthesis of research in agronomy, plant physiology and ecology[J]. New Phytologist, 2015,206:107-117. [12] Liu Z F, Ge H G, Li C, et al. Enhanced phytoextraction of heavy metals from contaminated soil by plant co-cropping associated with PGPR[J]. Water Air and Soil Pollution, 2015,226:1-10. [13] 孟楠,王萌,陈莉,等.不同草本植物间作对Cd污染土壤的修复效果[J].中国环境科学, 2018,38(7):2618-2624. Meng N, Wang M, Chen L, et al. Remediation efficiency of Cd polluted soil by intercropping with herbaceous plants[J]. China Environmental Science, 2018,38(7):2618-2624. [14] Tang Y, He J, Yu X, et al. Intercropping with Solanum nigrum and Solanum photeinocarpum from two ecoclimatic regions promotes growth and reduces cadmium uptake of eggplant seedlings[J]. Pedosphere, 2017,27:638-644. [15] Wang L, Zou R, Li Y C, et al. Effect of Wheat-Solanum nigrum L. intercropping on Cd accumulation by plants and soil bacterial community under Cd contaminated soil[J]. Ecotoxicology and Environmental Safety, 2020,206:111383. [16] 吴龙华,周守标,毕德,等.中国景天科植物一新种--伴矿景天[J].土壤, 2006,(5):632-633. Wu L H, Zhou S B, Bi D, et al. Sedum plumbizincicola, A new species of the crassulaceae from Zhejiang, China[J]. Soil, 2006,(5):632-633. [17] Wu L, Li Z, Akahane I, et al. Effects of organic amendments on Cd Zn and Cu bioavailability in soil with repeated phytoremediation by Sedum plumbizincicola[J]. International Journal of Phytoremediation, 2012,14:1024-1038. [18] Yang X E, Long X X, Ni W Z, et al. Sedum alfredii H.:A new Zn hyperaccumulating plant first found in China[J]. Chinese Science Bulletin, 2002,47:1634-1637. [19] Yang X E, Long X X, Ye H B, et al. Cadmium tolerance and hyperaccumulation in a new Zn-hyperaccumulating plant species (Sedum-alfredii Hance.)[J]. Plant and Soil, 2004,259:181-189. [20] Watanabe T, Murata Y, Osaki M. Amaranthus tricolor has the potential for phytoremediation of cadmium-contaminated soils[J]. Communications in Soil Science and Plant Analysis, 2009,40:3158-3169. [21] Wei S H, Zhou Q X, Wang X, et al. A newly-discovered Cd-hyperaccumulator Solanum nigrum L.[J]. Chinese Science Bulletin, 2005,50:33-38. [22] Han R, Dai H, Twardowska I, et al. Aqueous extracts from the selected hyperaccumulators used as soil additives significantly improve accumulation capacity of Solanum nigrum L. for Cd and Pb[J]. Journal of Hazardous Materials, 2020,394:122553. [23] Liang X, Li N, He L, et al. Inhibition of Cd accumulation in winter wheat (Triticum aestivum L.) grown in alkaline soil using mercapto-modified attapulgite[J]. Science of The Total Environment, 2019, 688:818-826. [24] 鲍士旦.土壤农化分析(第三版)[M].北京:中国农业出版社, 2000:42-106. Bao S D. Soil and agricultural chemistry analysis (3rd Edition)[M]. Beijing:China Agriculture Press, 2000:42-106. [25] Wang Q, Liang X, Dong Y, et al. Effects of exogenous nitric oxide on cadmium toxicity, element contents and antioxidative system in perennial ryegrass[J]. Plant Growth Regulation, 2013,69:11-20. [26] Wang Q, Liang X, Dong Y, et al. Effects of exogenous salicylic acid and nitric oxide on physiological characteristics of perennial ryegrass under cadmium stress[J]. Journal of Plant Growth Regulation, 2013, 32:721-731. [27] 蒋成爱,吴启堂,吴顺辉,等.东南景天与不同植物混作对土壤重金属吸收的影响[J].中国环境科学, 2009,29(9):985-990. Jiang C A, Wu Q T, Wu S H, et al. Effect of co-cropping Sedum alfredii with different plants on metal uptake[J]. China Environmental Science, 2009,29(9):985-990. [28] Liu X M, Wu Q T, Banks M K. Effect of simultaneous establishment of Sedum alfredii and Zea mays on heavy metal accumulation in plants[J]. International Journal of Phytoremediation, 2005,7:43-53. [29] Lin L, Liao M, Mei L, et al. Two ecotypes of hyperaccumulators and accumulators affect cadmium accumulation in cherry seedlings by intercropping[J]. Environmental Progress&Sustainable Energy, 2014,33:1251-1257. [30] 关元静,刘鸿雁,孙曦,等.间作对伴矿景天与红背桂花生长及镉锌吸收的影响[J].农业环境科学学报, 2021,40:347-354. Guan Y J, Liu H Y, Sun X, et al. Effects of intercropping on growth and Cd/Zn uptake by Sedum plumbizincicola and Excoecaria cochinchinensis[J]. Journal of Agro-Environment Science, 2021,40:347-354. [31] Ma L, Liu Y, Wu Y, et al. The effects and health risk assessment of cauliflower co-cropping with Sedum alfredii in cadmium contaminated vegetable field[J]. Environmental Pollution, 2021,268:115869. [32] Li C, Dong Y, Li H, et al. Shift from complementarity to facilitation on P uptake by intercropped wheat neighboring with faba bean when available soil P is depleted[J]. Scientific Reports, 2016,6:18663. [33] Lin L, Chen F, Wang J, et al. Effects of living hyperaccumulator plants and their straws on the growth and cadmium accumulation of Cyphomandra betacea seedlings[J]. Ecotoxicology and Environmental Safety, 2018,155:109-116. [34] Coleman Derr D, Desgarennes D, Fonseca Garcia C, et al. Plant compartment and biogeography affect microbiome composition in cultivated and native Agave species[J]. New Phytologist, 2016,209:798-811. [35] Silva Gonzaga M I, Ma L Q, Gonzaga Santos J A, et al. Rhizosphere characteristics of two arsenic hyperaccumulating Pteris ferns[J]. Science of The Total Environment, 2009,407:4711-4716. [36] Garbeva P, van Veen J A, van Elsas J D. Microbial diversity in soil:Selection of microbial populations by plant and soil type and implications for disease suppressiveness[J]. Annual Review of Phytopathology, 2004,42:243-270. [37] 张子杨,郭瞻宇,管伟豆,等.硫磺和放线菌强化植物修复土壤镉污染[J].中国环境科学, 2019,39(5):2106-2114. Zhang Z Y, Guo Z Y, Guan W D, et al. Combination of sulphur and actinomycete to enhance the efficiency of phytoremediation in cadmium contamination soil[J]. China Environmental Science, 2019, 39(5):2106-2114. [38] Cao X, Luo J, Wang X, et al. Responses of soil bacterial community and Cd phytoextraction to a Sedum alfredii-oilseed rape (Brassica napus L. and Brassica juncea L.) intercropping system[J]. Science of The Total Environment, 2020,723:138152. [39] Rajkumar M, Ae N, Prasad M N V, et al. Potential of siderophore-producing bacteria for improving heavy metal phytoextraction[J]. Trends in Biotechnology, 2010,28:142-149. [40] Betencourt E, Duputel M, Colomb B, et al. Intercropping promotes the ability of durum wheat and chickpea to increase rhizosphere phosphorus availability in a low P soil[J]. Soil Biology&Biochemistry, 2012,46:181-190. [41] Tao Q, Hou D, Yang X, et al. Oxalate secretion from the root apex of Sedum alfredii contributes to hyperaccumulation of Cd[J]. Plant and Soil, 2016,398:139-152. [42] Grzebis W, Szczepaniak W, Barlog P, et al. Phosphorus sources for winter oilseed rape (Brassica napes L.) during reproductive growth-magnesium sulfate management impact on P use efficiency[J]. Archives of Agronomy and Soil Science, 2018,64:1646-1662. [43] Bian F, Zhong Z, Zhang X, et al. Phytoremediation potential of moso bamboo (Phyllostachys pubescens) intercropped with Sedum plumbizincicola in metal-contaminated soil[J]. Environmental Science and Pollution Research, 2017,24:27244-27253. [44] Vergara Cid C, Pignata M L, Rodriguez J H. Effects of co-cropping on soybean growth and stress response in lead-polluted soils[J]. Chemosphere, 2020,246:125833. [45] Chen B, Ma X, Liu G, et al. An endophytic bacterium Acinetobacter calcoaceticus Sasm3-enhanced phytoremediation of nitrate-cadmium compound polluted soil by intercropping Sedum alfredii with oilseed rape[J]. Environmental Science and Pollution Research, 2015,22:17625-17635. [46] Zeng P, Guo Z, Xiao X, et al. Phytoextraction potential of Pteris vittata L. co-planted with woody species for As, Cd, Pb and Zn in contaminated soil[J]. Science of The Total Environment, 2019,650:594-603. [47] 黑亮,吴启堂,龙新宪,等.东南景天和玉米套种对Zn污染污泥的处理效应[J].环境科学, 2007,(4):4852-4858. Hei L, Wu Q T, Long X X, et al. Effect of co-planting of Sedum alfredii and Zea mays on Zn-contaminated sewage sludge[J]. Environmental Science, 2007,(4):4852-4858. [48] Wang S, Wei S, Ji D, et al. Co-planting Cd contaminated field using hyperaccumulator Solanum Nigrum L. through interplant with low accumulation welsh onion[J]. International Journal of Phytoremediation, 2015,17:879-884. [49] Hinsinger P, Plassard C, Tang C X, et al. Origins of root-mediated pH changes in the rhizosphere and their responses to environmental constraints:A review[J]. Plant and Soil, 2003,248:43-59. [50] Tao S, Chen Y J, Xu F L, et al. Changes of copper speciation in maize rhizosphere soil[J]. Environmental Pollution, 2003,122:447-454. [51] 郭可欣,李天元,宋繁永,等.土壤-作物中重金属生物有效性和可给性研究进展[J].中国环境科学, 2023,43(8):4164-4174. Guo K X, Li T Y, Song F Y, et al. Review on heavy metal bioavailability and bioaccessibility in soil-crop system[J]. China Environmental Science, 2023,43(8):4164-4174. [52] Yang X, Li T, Yang J, et al. Zinc compartmentation in root, transport into xylem, and absorption into leaf cells in the hyperaccumulating species of Sedum alfredii Hance.[J]. Planta, 2006,224:185-195. [53] Tao Q, Zhao J, Li J, et al. Unique root exudate tartaric acid enhanced cadmium mobilization and uptake in Cd-hyperaccumulator Sedum alfredii[J]. Journal of Hazardous Materials, 2020,383:121177. [54] Sauve S, Hendershot W, Allen H E. Solid-solution partitioning of metals in contaminated soils:Dependence on pH, total metal burden, and organic matter[J]. Environmental Science&Technology, 2000,34:1125-1131. [55] de Kreij C, van der Burg A M M, Runia W T. Drip irrigation emitter clogging in Dutch greenhouses as affected by methane and organic acids[J]. Agricultural Water Management, 2003,60:73-85. [56] Hou D, Lin Z, Wang R, et al. Cadmium exposure-Sedum alfredii planting interactions shape the bacterial community in the hyperaccumulator plant rhizosphere[J]. Applied and Environmental Microbiology, 2018,84(12):e02797-17. [57] Zhu H, Chen C, Xu C, et al. Effects of soil acidification and liming on the phytoavailability of cadmium in paddy soils of central subtropical China[J]. Environmental Pollution, 2016,219:99-106. [58] Khaokaew S, Chaney R L, Landrot G, et al. Speciation and release kinetics of cadmium in an alkaline paddy soil under various flooding periods and draining conditions[J]. Environmental Science&Technology, 2011,45:4249-4255. [59] Bolan N S, Adriano D C, Mani P A, et al. Immobilization and phytoavailability of cadmium in variable charge soils. II. Effect of lime addition[J]. Plant and Soil, 2003,251:187-198. [60] Wang D Z, Jiang X, Rao W, et al. Kinetics of soil cadmium desorption under simulated acid rain[J]. Ecological Complexity, 2009,6:432-437. [61] Blake L, Goulding K W T. Effects of atmospheric deposition, soil pH and acidification on heavy metal contents in soils and vegetation of semi-natural ecosystems at Rothamsted Experimental Station, UK[J]. Plant and Soil, 2002,240:235-251. [62] Lu L, Tian S, Zhang J, et al. Efficient xylem transport and phloem remobilization of Zn in the hyperaccumulator plant species Sedum alfredii[J]. New Phytologist, 2013,198:721-731. [63] Liu S, Ali S, Yang R, et al. A newly discovered Cd-hyperaccumulator Lantana camara L.[J]. Journal of Hazardous Materials, 2019,371:233-242. [64] Fan S K, Zhu J, Tian W H, et al. Effects of split applications of nitrogen fertilizers on the Cd level and nutritional quality of Chinese cabbage[J]. Journal of Zhejiang University-Science B, 2017,18:897-905. [65] 朱凰榕,周良华,阳峰,等.两种景天修复Cd/Zn污染土壤效果的比较[J].生态环境学报, 2019,28(2):403-410. Zhu H R, Zhou L H, Yang F, et al. Phytoremediation effects and contrast of Sedum alfredii and Sedum plumbizincicola on Cd/Zn contaminated soil[J]. Ecology and Environment Sciences, 2019,28:403-410. [66] 王艳红,龙新宪,吴启堂.两种生态型东南景天根系分泌物的差异性[J].生态环境学报, 2008,(2):751-757. Wang Y H, Long X X, Wu Q T. Differences of root exudates between two ecotypes of Sedum alfredii Hance.[J]. Ecology and Environmental Sciences, 2008,(2):751-757. [67] Tao Q, Liu Y, Li M, et al. Cd-induced difference in root characteristics along root apex contributes to variation in Cd uptake and accumulation between two contrasting ecotypes of Sedum alfredii[J]. Chemosphere, 2020,243:125290. [68] Wang J, Lu X, Zhang J, et al. Rice intercropping with alligator flag (Thalia dealbata):A novel model to produce safe cereal grains while remediating cadmium contaminated paddy soil[J]. Journal of Hazardous Materials, 2020,394:122505. [69] Zhan F D, Qin L, Guo X H, et al. Cadmium and lead accumulation and low-molecular-weight organic acids secreted by roots in an intercropping of a cadmium accumulator Sonchus asper L. with Vicia faba L.[J]. Rsc Advances, 2016,6:33240-33248. [70] 霍文敏,赵中秋,王丽,等.不同超富集、富集植物-玉米间作模式对玉米中镉吸收、转运的影响研究[J].地学前缘, 2019,26:118-127. Huo W M, Zhao Z Q, Wang L, et al. Study of the effects of intercropping different hyperaccumulator and accumulator plants on Cd uptake and transportation by maize[J]. Earth Science Frontiers, 2019,26:118-127. [71] 万家悦,贺希格都楞,彭位华,等.玉米与番茄间作对土壤镉吸收的影响[J].生物工程学, 2020,36:518-528. Wan J Y, Bao H X G D L, Peng W H, et al. Effects of intercropping on cadmium uptake by maize and tomato[J]. Chinese Journal of Biotechnology, 2020,36:518-528.