PASSIVATION OF LEAD IN SOIL BY FULVIC ACID-NANO-ZERO-VALENT IRON COMPLEX
-
摘要: 为了降低土壤中重金属铅的生物活性,将从富硒土壤中提取的富里酸(FA)和传统方法制得的纳米零价铁(NZVI)复合,制得不同FA质量比的复合物,探讨其对土壤铅污染的钝化效应。以SEM、FTIR以及XRD对复合物进行表征;通过土壤培养试验,研究各复合物在不同投加量及反应时间下对土壤中铅的DTPA有效态的影响,并以Tessier五步连续提取法比较形态变化规律,探讨其钝化效果。结果表明:FA与NZVI合成了不同质量比的复合物;在相同投加量下,土壤中铅的二乙基三胺五乙酸(DTPA)有效态随着复合物中FA质量分数提高而减小;以FA质量分数10%的复合物投加土壤质量的2%(20.0 g/kg)进行土壤培育,第10天时土壤中铅的DTPA有效态降低83.01%;加入复合物后,土壤中铅明显从可交换态和碳酸盐结合态向铁锰氧化物结合态和残留态转化,有机结合态含量基本不变,这种变化在添加FA质量占1%的复合物时尤为显著,使得可交换态和碳酸盐结合态分别降低了50.61%和66.90%。基于不同的形态表征方法,土壤铅活性形态均呈下降趋势,表明所制备的复合物对土壤铅具有一定的钝化效应,但其机制有别,表现出的钝化规律具有差异性。
-
关键词:
- 铅 /
- 富里酸-纳米零价铁复合物 /
- 赋存形态 /
- 钝化
Abstract: In order to reduce the biological activity of heavy metals in soil, composites were made using fulvic acid (FA) extracted from selenium-enriched soil and nano-zero-valent iron (NZVI) prepared by conventional methods with different FA mass ratios. The composites were characterized by SEM, FTIR and XRD. Trough soil cultivation experiments, the effect of each compound on the occurrence of DTPA with lead added externally in soil under different dosages and reaction times were studied, and analyzed the morphological changes with Tessier method to discuss its passivation consequent. The results showed that FA and NZVI formed composites successfully with different FA mass ratios; under the same dosage, the effective state of DTPA of lead in the soil decreased with the increase of the FA mass ratio in the composites; when the composites with 10% FA mass was added to the soil in 2% (20.0 g/kg), the DTPA effective state of lead in the soil was reduced by 83.01% on the 10th day; after adding the composites, the lead in the soil transformed significantly from the exchangeable state and the carbonate combined state to Fe-Mn oxide combined state and the residual state, and the organic bound state was unchanged basically. These changes were especially significant when the compound with 1% FA mass was added, making the exchangeable state and the carbonate bound state reduced respectively by 50.61% and 66.90%. Therefore, based on different morphological characterization methods, the active forms of soil lead showed a downward trend, indicating that the prepared composite had a certain passivation effect on soil lead, but the mechanism was different, and the passivation laws shown were different. -
[1] 袁峰,唐先进,吴骥子,等.两种铁基材料对污染农田土壤砷、铅、镉的钝化修复[J].环境科学,2021,42(7):3535-3548. [2] 佚名.全国土壤污染状况调查公报[J].中国环保产业,2014(5):10-11. [3] 张金碧,柯耀义.微波消解-石墨炉原子吸收光谱法测定土壤中铅、镉的探究[J].广东化工,2021,48(5):191-192,190. [4] 冯艳红,郑丽萍,应蓉蓉,等.黔西北炼锌矿区土壤重金属形态分析及风险评价[J].生态与农村环境学报,2017,33(2):142-149. [5] ZHU R,WU M,YANG J. Mobilities and leachabilities of heavy metals in sludge with humus soil[J]. Journal of Environmental Sciences, 2011, 23(2):247-254. [6] ZHANG L W,SHANG Z B,GUO K X,et al. Speciation analysis and speciation transformation of heavy metal ions in passivation process with thiol-functionalized nano-silica[J]. Chemical Engineering Journal, 2019, 369:979-987. [7] LIU Q J,LI X,TANG J P,et al. Characterization of goethite-fulvic acid composites and their impact on the immobility of pb/cd in soil[J]. Chemosphere, 2019, 222:556-563. [8] LIU J F, ZHAO Z S, JIANG G B. Coating Fe3O4 magnetic nanoparticles with humic acid for high efficient removal of heavy metals in water[J]. Environmental Science&Technology, 2008, 42(18):6949-6954. [9] DU Q,LI G X, ZHANG S S,et al. High-dispersion zero-valent iron particles stabilized by artificial humic acid for lead ion removal[J]. J Hazard Mater, 2020, 383:121170. [10] FU R B,ZHANG X,XU Z,et al. Fast and highly efficient removal of chromium (Ⅵ) using humus-supported nanoscale zero-valent iron:influencing factors, kinetics and mechanism[J]. Separation and Purification Technology, 2017, 174:362-371. [11] TANG W W, ZENG G M, GONG J L,et al. Impact of humic/fulvic acid on the removal of heavy metals from aqueous solutions using nanomaterials:a review[J]. Science of the Total Environment, 2014,468/469:1014-1027. [12] 陈林倩.富硒区芥菜土壤腐殖质特征及其对重金属迁移转化的影响[D].海口:海南大学,2018. [13] JIANG D N, ZENG G M, HUANG D L,et al. Remediation of contaminated soils by enhanced nanoscale zero valent iron[J]. Environmental Research, 2018, 163:217-227. [14] LLERME N V, JOSÉ E C, JUNIOR S G P. Influence of soil use on organic carbon and humic substances of an oxisol in tropical systems[J]. Functions of Natural Organic Matter in Changing Environment, 2013, 401-405. [15] LINDSAY W L,NORVELL W A. Development of a dtpa soil test for zinc, iron, manganese, and copper[J]. Soil Science Society of America Journal, 1978, 42(3):421-428. [16] LYDIA L,JEAN-LUC P. A new sequential extraction procedure for the speciation of particulate trace elements in river sediments[J]. International Journal of Environmental Analytical Chemistry, 1999, 73(2):109-128. [17] 王培.纤维素改性纳米零价铁及其对水中染料的脱色降解研究[D].昆明:昆明理工大学,2015. [18] ARANGANATHAN L,RAJASREE R R S,GOVINDARAJU K,et al. Spectral and microscopic analysis of fulvic acids isolated from marine fish waste and sugarcane bagasse co-compost[J]. Biocatalysis and Agricultural Biotechnology, 2020, 29:101762. [19] MOHAMMAD B. Ahmed,JOHN L. zhou,HUU H. Ngo,et al. Nano-Fe0 immobilized onto functionalized biochar gaining excellent stability during sorption and reduction of chloramphenicol via transforming to reusable magnetic composite[J]. Chemical Engineering Journal, 2017, 322(1):571-581. [20] 赵庆圆,李小明,杨麒,等.磷酸盐、腐殖酸与粉煤灰联合钝化处理模拟铅镉污染土壤[J].环境科学,2018,39(1):389-398. [21] BAI H C, LUO M, WEI S Q,et al. The vital function of humic acid with different molecular weight in controlling cd and pb bioavailability and toxicity to earthworm (Eisenia fetida) in soil[J]. Environmental Pollution, 2020, 261. [22] MALANDRINO M,ABOLLINO O,BUOSO S,et al. Accumulation of heavy metals from contaminated soil to plants and evaluation of soil remediation by vermiculite[J]. Chemosphere, 2011, 82(2):169-178. [23] 赵中秋,朱永官,蔡运龙.镉在土壤-植物系统中的迁移转化及其影响因素[J].生态环境,2005,14(2):282-286. [24] 崔妍,丁永生,公维民,等.土壤中重金属化学形态与植物吸收的关系[J].大连海事大学学报,2005,31(2):59-63. [25] 乔庆霞,黄小凤.沘江表层底泥中重金属化学形态的研究[J].昆明理工大学学报,1999(2):3-5. [26] DOU X M,LI R,ZHAO B,et al. Arsenate removal from water by zero-valent iron/activated carbon galvanic couples[J]. Journal of Hazardous Materials, 2010, 182(1):108-114. [27] KlÜPFEL L,KEILUWEIT M,KLEBER M,et al. Redox properties of plant biomass-derived black carbon (biochar)[J]. Environmental Science&Technology, 2014, 48(10):5601-5611. [28] 鲁秀国,武今巾,郑宇佳.核桃壳生物炭对土壤中镉的钝化修复[J].环境工程,2020,38(11):196-202. [29] 王向琴,刘传平,杜衍红,等.零价铁与腐殖质复合调理剂对稻田镉砷污染钝化的效果研究[J].生态环境学报,2018,27(12):2329-2336. [30] 高晓宁.土壤重金属污染现状及修复技术研究进展[J].现代农业科技,2013(9):229-231.
点击查看大图
计量
- 文章访问数: 140
- HTML全文浏览量: 30
- PDF下载量: 1
- 被引次数: 0