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1.
黄皓  周通  吴龙华  李华  李加迅 《土壤》2020,52(5):927-934
油用牡丹是一种新型的木本食用油料植物,其在重金属污染耕地上的生产安全性鲜有报导。本文对云南西部某矿区周边油用牡丹种植区的土壤和植物镉(Cd)、铅(Pb)污染状况进行调查,并结合田间小区试验探讨中重度污染耕地化学钝化修复的可行性。结果表明,油用牡丹种植区的土壤和植物可食部分存在严重的Cd、Pb污染,土壤全量Cd、Pb较风险筛选值(GB 15618-2018)的超标率分别为100%和82.8%;油用牡丹籽粒中Cd和Pb浓度超标率高达100%和82.1%(GB 2762-2017),中药材牡丹皮中Cd超标率也高达77.1%以上。钝化修复显著提高了中重度污染耕地上油用牡丹根系生物量和根长,但对其成活率和株高无显著影响。生石灰和海泡石复合钝化剂施用显著降低了土壤CaCl2提取态Cd、Pb浓度,降幅在56%和59%以上,且随着钝化剂用量的增加钝化效果显著增强。虽然钝化修复显著降低了重度污染土壤上牡丹皮Cd浓度,但牡丹皮Cd浓度仍存在较高的超标风险。为保证中重度污染耕地的油用牡丹生产安全性,应提高钝化剂施用量以持续降低污染土壤中重金属有效性,并加强土壤和农产品Cd、Pb的协同监测。  相似文献   

2.
基于籽粒Cd消减率与边际效率评价Cd污染稻田的修复效果   总被引:3,自引:1,他引:2  
高效、低成本钝化材料的研发及盆栽与田间试验结果的一致性仍然是目前重金属污染土壤原位钝化修复的技术难点。该文以镉(Cd)污染的湖南红壤与浙江水稻土为对象,以2种不同Cd敏感性水稻(Cd低吸收品种JH212、Cd高富集品种XS09)为试材,通过盆栽与田间对比试验,基于水稻籽粒Cd消减率、修复边际效率及土壤中Cd有效态含量的变化等对不同钝化剂的修复效果进行了测定。结果表明:不同钝化剂对2种不同Cd敏感性水稻籽粒Cd的吸收、转运均有显著(P0.05)降低作用。盆栽试验条件下,与对照相比,不同钝化剂处理后湖南红壤中水稻籽粒Cd浓度最大降低65.3%,浙江水稻土中籽粒Cd浓度最大降低61.4%;在田间试验条件下,不同钝化剂处理的红壤中水稻籽粒Cd浓度最大降低61.8%,水稻土中籽粒Cd浓度最大降低60.1%。就2种不同的Cd敏感性水稻品种而言,不同钝化剂对Cd高富集品种XS09的钝化效果要优于Cd低吸收品种JH212。总体而言,不同钝化剂对2种不同Cd敏感性水稻籽粒Cd消减率为41.6%~65.3%,对XS09的籽粒Cd消减率略高于JH212,在酸性红壤的钝化效果高于水稻土;不同钝化剂对水稻籽粒Cd消减效果依次为黏土矿物钝化剂AT腐殖质钝化剂WG≈岩基钝化剂FS。不同钝化剂对Cd污染红壤与水稻土的修复边际效率为9.10%~15.4%,最高为AT处理,其次为WG与FS处理;综合籽粒Cd消减率与修复边际效率2个指标进行考虑,不同钝化剂对Cd污染土壤的修复效果顺序为ATWGFS。  相似文献   

3.
镉(Cd)和砷(As)是土壤环境中广泛存在的重金属污染物,具有不可降解性和生物累积性的特点,应及时开展Cd和As污染的修复工作。研究以湖南中、轻度Cd和As污染农田土壤为对象,选取当地优势植物。通过田间试验,添加生物炭与纳米零价铁的复合钝化剂,利用不同植物(油菜-蚕豆、玉米-苎麻)配套种植模式,探讨基于复合钝化剂施用植物轮作模式对土壤中Cd和As污染的修复效果。结果表明:(1)间作种植模式(蚕豆-油菜、玉米-苎麻)更有利于土壤中Cd和As的固定,试验土壤中Cd和As的最佳固定效果依次为原供试土壤的45.19%和19.00%。(2)复合钝化剂可显著提升农田土壤中Cd和As的固定效果,当生物炭和纳米零价铁以53∶1的比例混合配施时,Cd和As的钝化效果最为明显。(3)在间作模式下施加复合钝化剂,可以有效促进Cd和As污染土壤的修复。研究认为此类方式更适合中、轻度Cd和As复合污染土壤的修复工程应用。复合钝化剂最佳配比及植物间作模式的使用为Cd和As复合污染土壤的修复与治理工作提供试验依据和理论支撑。  相似文献   

4.
二种钾肥对海泡石钝化修复镉污染土壤效应影响的研究   总被引:2,自引:0,他引:2  
为了揭示钾肥对Cd污染土壤钝化修复效果的影响,为土壤钝化修复过程中合理施钾肥提供理论依据。本文选取不同剂量(含量以K2O计算,分别为0.1 g·kg~(-1)、0.2 g·kg~(-1)和0.3 g·kg~(-1))的KCl和K_2SO_4作为典型钾肥,以海泡石(10 g·kg~(-1))作为钝化材料,通过油菜盆栽试验,研究了两种钾肥在海泡石钝化条件下对Cd污染土壤修复效应的影响。结果表明:K_2SO_4显著增加了油菜的生物量,其增幅为6.06%~10.05%。与单施海泡石钝化相比,在海泡石钝化时施用KCl和K_2SO_4两种钾肥,油菜地上部茎叶Cd含量分别增加16.38%~60.73%和15.62%~25.19%;施用KCl和K_2SO_4对土壤p H未产生显著性影响,却显著地增加了土壤有效态Cd含量,其增幅分别为25.51%~34.65%和18.5%~24.96%。添加海泡石可使土壤的Zeta电位向负值方向移动,提高土壤对Cd的负载能力;但添加海泡石下施用KCl和K_2SO_4均能提高土壤的Zeta电位,降低土壤对Cd的负载能力。等温吸附试验同样表明,添加KCl和K_2SO_4均能降低海泡石对Cd的吸附量,在水溶液中海泡石对Cd的最大吸附量为5.30 mg·kg~(-1),添加KCl和K_2SO_4后吸附量分别降低至2.87 mg·g~(-1)和4.92 mg·g~(-1)。KCl和K_2SO_4显著改善了土壤中K、Mn、Cu和Zn等营养元素的有效态含量。从上述结果可以发现,在海泡石钝化修复Cd污染土壤过程中,施K_2SO_4对钝化效果的影响小于施KCl。  相似文献   

5.
在田间试验条件下,研究施用生物有机肥和生物炭对稻田Cd和Pb污染的钝化修复效果。研究结果表明:施用生物有机肥和生物炭处理可以提高土壤p H值以及土壤养分含量,并显著降低土壤有效态Cd和Pb的含量,且土壤p H值与土壤有效态Cd和Pb的含量呈极显著负相关;生物有机肥和生物炭处理还可以降低水稻体内Cd和Pb的含量,其中水稻糙米Cd降幅达到了22.00%和18.34%,水稻糙米Pb含量的降幅也达到了33.46%和12.31%,且水稻糙米Cd和Pb的含量与土壤有效态Cd和Pb的含量呈显著正相关。综合各处理对土壤p H值、土壤养分含量、土壤有效态Cd和Pb的含量以及水稻Cd和Pb的影响,可以看出生物有机肥和生物炭处理对于Cd和Pb污染稻田土壤有较好的修复效果。  相似文献   

6.
钝化剂对酸性高镉土壤钝化效果及水稻镉吸收的影响   总被引:6,自引:2,他引:4  
以海泡石、磷酸二氢钾、钙镁磷肥、钢渣、生石灰及生物炭为重金属镉钝化材料,研究钝化剂对湖南省酸性高镉(Cd)稻田土壤及水稻中Cd含量的影响。以土壤pH值和有效态镉作为评价指标,筛选出三种效果较优的钝化剂,通过正交试验进行复配,选择最优的钝化剂配方进行田间验证。结果表明,海泡石、钙镁磷肥、钢渣在施用比例为1%时均可显著提高土壤pH,pH的提升效果排序为钢渣钙镁磷肥海泡石;除钢渣外,其余钝化剂在施用比例为1%时均可不同程度降低土壤有效态Cd含量,钝化效果排序为磷酸二氢钾钙镁磷肥生物炭海泡石生石灰。选取海泡石、钙镁磷肥和磷酸二氢钾复配钝化剂,依据正交试验结果并综合考虑钝化效果、成本及材料易得性,确定钝化剂的最优施用量组合为海泡石500 mg kg-1、钙镁磷肥500 mg kg-1、磷酸二氢钾170 mg kg-1。大田试验结果表明,施用钝化剂后,土壤pH值提高0.5个单位,土壤有效Cd含量降低34.00%,糙米中Cd含量降低19.44%,水稻各器官Cd的富集与迁移系数明显降低,水稻产量明显升高。  相似文献   

7.
施肥能显著提高植物产量,改变土壤环境中元素的生物有效性,已成为植物修复过程中必要的强化措施。针对长期自然老化的重金属复合污染土壤,采用盆栽试验研究了KH2PO4、Ca(H2PO4)2、NaH2PO4和NH4H2PO4在P2O5 0~352 mg/kg时,对东南景天(Sedum alfredii H.)地上部锌(Zn)、镉(Cd)积累和养分元素吸收的影响。结果表明,外源施入磷酸二氢盐促进了东南景天生长,P2O5 352 mg/kg显著增加了地上部干物质重;地上部磷(P)含量显著增加,Zn含量随着P浓度的增加而显著升高,而Cd含量显著下降。磷肥降低了植物地上部氮(N)、中量元素钙(Ca)、镁(Mg)、硫(S)和微量元素锰(Mn)、铁(Fe)、铜(Cu)的含量,对钾(K)含量的影响不显著,地上部总碳(C)含量随P浓度增加而升高。一季收获后,东南景天地上部对Zn的提取量在施P2O5 88和352 mg/kg时显著增加,Cd提取量仅在高浓度时显著升高。KH2PO4和NH4H2PO4两种磷肥在施P2O5 352 mg/kg时对东南景天提取土壤Zn、Cd的效果最为明显,可在实际修复应用中使用。因此,合理磷酸盐施用能增加植物对C的生物固定,提高东南景天对Zn/Cd复合污染土壤的修复效率,缩短修复周期。  相似文献   

8.
森美思土壤调理剂对镉污染稻田改良的影响研究   总被引:1,自引:0,他引:1  
为研究稻田镉(Cd)污染的治理与修复技术,于2016年在珠海开展了森美思土壤调理剂对水稻Cd污染修复大田验证试验。结果表明:与S0相比,各森美思处理均能在一定程度上促进水稻增产,且S1、S2和Sc处理均能显著降低水稻稻谷中的总Cd含量,降幅达56.67%~63.33%(P0.05);施用森美思可以对土壤有效态Cd起到一定的钝化作用;各处理对比S0均显著提高了土壤的p H值(P0.05),但对其他理化性质无显著影响。  相似文献   

9.
原位钝化是镉污染稻田土壤修复的主要方法之一,钝化剂的选择对修复效果十分关键。通过3个田间试验和示范区对比调查研究了施用石灰石及主要调理剂对稻田土壤镉的钝化效应,并提出有效的技术措施。结果表明,施用足量石灰石(≥3.75 t/hm~2,试验Ⅰ)、钙镁磷肥(3.75 t/hm~2,试验III)和生物质炭(9.00 t/hm~2,试验II;7.50 t/hm~2,试验III)、石灰(3.00 t/hm~2,试验III)碱性调理剂均能显著提高土壤pH,降低土壤Cd提取率(P0.05);施用硅藻土(8.25 t/hm~2)和羟基磷灰石(3.75 t/hm~2)也能降低土壤Cd提取率。其中施用石灰石11.25 t/hm~2能使Cd提取率降低21个百分点;施用硅藻土8.25 t/hm~2(试验Ⅱ)、生物质炭9.00 t/hm~2(试验Ⅱ)可以显著降低土壤Cd提取率(P0.05),分别降低10,19个百分点。试验Ⅲ中与对照相比,施用石灰3.00 t/hm~2、钙镁磷肥3.75 t/hm~2、生物质炭7.50 t/hm~2处理的土壤pH显著提高(P0.05),石灰、钙镁磷肥、生物质炭、羟基磷灰石3.75 t/hm~2处理的土壤Cd提取率显著降低(P0.05);同时发现,石灰处理土壤pH显著高于钙镁磷肥、生物质炭、羟基磷灰石3个处理,而土壤Cd提取率则显著小于后三者。对比调查的相关性分析结果表明,Cd提取率与土壤pH呈显著负相关,与土壤有效态Cd含量呈显著正相关(P0.05)。聚类分析得出,可将不同调理剂对土壤镉的钝化效应分为5类,钝化效应较大的为石灰6.00,9.00 t/hm~2和GSA-4 6.00,9.00 t/hm~2,可优先用于实际的钝化修复,而钝化效应不显著的有海泡石4.50 t/hm~2、沸石4.50 t/hm~2、腐殖质4.50 t/hm~2和羟基磷灰3.00 t/hm~2,则不予以推荐。  相似文献   

10.
有机-无机型钝化剂对水稻土镉钝化效果研究   总被引:1,自引:0,他引:1  
为了降低水稻土镉(Cd)生物有效性,确保水稻安全生产,采用纯土培和盆栽试验,通过研究不同改性方法、配比条件及施用量下山核桃壳及矾浆对土壤Cd钝化效果的影响,研发了一种有机-无机型Cd钝化剂及其施用方法。结果表明,山核桃壳对Cd的吸附能力显著高于矾浆。山核桃壳和矾浆经0.5 M草酸和1 M NaOH加热改性后,Cd最大吸附量分别提高了30%和233%。淹水条件下,改性后的山核桃壳和矾浆按照85%和15%的比例制备的有机-无机型钝化剂可使水稻土醋酸提取态Cd含量降低49.8%。此外,山核桃壳与矾浆按此比例混合后,山核桃壳的分解速率降低,120 d内固定土壤Cd的效果持续稳定。水稻种植前,将该钝化剂按1.0%的添加量(v/v)与Cd污染土壤(Cd2 mg·kg~(-1))充分混匀,收获的稻米中Cd含量降低了52.1%。本研究结果为山核桃壳、矾浆复配运用于稻田土壤Cd污染的钝化修复提供了一定的理论依据。  相似文献   

11.
原位化学钝化技术是修复重金属污染土壤的重要途径之一,通过施入一些钝化剂以降低土壤中重金属有效态含量,从而减少其迁移及对植物的毒害。选取羟基磷灰石(HA)、磷矿粉(PRX和PRH)、沸石、赤泥、新鲜植物残体、玉米秸秆粉末以及相应的处理共21种钝化剂,在同一培养条件和添加浓度下,比较其对人工Cd污染土壤中可交换态Cd含量的影响,并分析了其在不同培养时间对钝化效果的时间效应,试验的结果对于筛选Cd污染土壤钝化剂有着重要的意义。结果表明,纳米化赤泥、羟基磷灰石和纳米化酸洗赤泥可显著降低土壤中可交换态Cd含量,钝化比例高达35%-55%;赤泥、酸洗赤泥、沸石达15%-25%;富含巯基植物蒜苗、油菜、大葱植物残体也可达20%-25%。磷矿粉、大葱粉末、玉米秸秆和巯基化玉米秸秆的钝化效果相对较差;HA、铵型沸石、纳米赤泥、酸洗纳米赤泥、干油菜粉末、酸洗赤泥对可交换态Cd的钝化效果的时间效应不明显;赤泥、大葱残体、特别是玉米秸秆和巯基玉米秸秆随时间增长钝化效果增加显著,在8周和16周时段钝化效果较好。  相似文献   

12.
生物炭的性质与老化作用是影响生物炭钝化修复Cd污染土壤效果的重要因素。比较研究4种不同原料生物炭(污泥类、秸秆类、动禽粪便类和木本类)对Cd2+吸附作用和Cd污染土壤的钝化修复效果的差异。结果表明:施用生物炭显著提升土壤孔隙水pH(棕榈丝生物炭除外),降低孔隙水DOC和Cd浓度,从而减少水稻根系对孔隙水中Cd的吸收。同时,4种生物炭提高土壤pH,降低土壤有效态Cd、水稻根系和籽粒Cd含量。老化作用减弱稻秆生物炭的钝化效果,显著增强棕榈丝生物炭对土壤Cd的钝化作用,然而,老化作用对富含灰分的猪粪生物炭和污泥生物炭的影响较小。因此,选择生物炭钝化修复Cd污染稻田土壤时,必须考虑生物炭的原料及其老化作用。  相似文献   

13.
张晶  苏德纯 《农业环境保护》2012,(10):1927-1932
通过土壤培养试验和生物盆栽试验,研究不同镉污染土壤上作物秸秆炭化后还田对不同镉污染土壤中镉的赋存形态和生物有效性影响,结果表明:在碱性的镉污染土壤上,秸秆炭化后还田降低了玉米地上部生物量,但对玉米地上部镉含量和镉吸收量无显著影响;在酸性的模拟镉污染土壤上秸秆炭化后还田对玉米生长无影响,但还田含镉的油菜秸秆黑炭显著增加了玉米地上部镉含量和镉吸收量;还田不含镉的玉米秸秆黑炭对镉污染土壤中DTPA提取态镉含量没有明显影响,但还田含镉的油菜秸秆黑炭显著增加了镉污染土壤中DTPA提取态镉含量;施用含镉的油菜秸秆黑炭增加了镉污染土壤中水溶和交换态镉含量;施用玉米和油菜秸秆黑炭均显著降低了模拟镉污染土壤中水溶和交换态镉含量;增加了松有机结合态、碳酸盐结合态和紧有机结合态镉含量;模拟镉污染土壤施用玉米和油菜秸秆黑炭6个月后土壤中水溶和交换态镉仍然是土壤镉的主要赋存形态,水溶和交换态镉占土壤全镉的70%以上。综合以上结果可知,秸秆黑炭不能降低污染土壤中镉的生物有效性和植物对土壤镉的吸收量。  相似文献   

14.
Cadmium (Cd) pollution in agricultural soils has exerted a serious threat due to continuous application of pesticides, fertilizers, and wastewater irrigation. The present study aimed to test the efficiency of KOH-modified and non-modified rice straw-derived biochar (KBC and BC, respectively) for reducing Cd solubility and bioavailability in Cd-contaminated soil. Cadmium-contaminated soil was incubated for 60 d with 15 and 30 g kg-1 BC and KBC. At the end of incubation, Cd mobility was estimated by the European Community Bureau of Reference sequential extraction and toxicity characteristic leaching procedure (TCLP), while bioavailability was determined using 1 mol L-1 NH4NO3 extraction. The bioavailability risk index and bioaccessibility, assessed by a simple bioaccessibility extraction test, of Cd were used to examine the potential effects of Cd on living organisms. The results indicated that application of both KBC and BC significantly increased soil pH, cation exchange capacity, nutrients, and organic carbon. The soluble fraction of Cd was significantly decreased by 30.3% and 27.4%, respectively, with the addition of KBC and BC at 30 g kg-1 compared to the control (without biochar addition). Similarly, the bioaccessible Cd was significantly decreased by 32.4% and 25.2%, respectively, with the addition of KBC and BC at 30 g kg-1 compared to the control. In addition, both KBC and BC significantly reduced Cd leaching in the TCLP and NH4NO3-extractable Cd in the amended soil compared to the control. The reduction in Cd solubility and bioaccessibility by KBC and BC may be due to significant increases in soil pH and surface complexation. Overall, KBC at an application rate of 30 g kg-1 demonstrated positive results as soil amendment for Cd immobilization, and reduced bioaccessible Cd in contaminated soil.  相似文献   

15.
利用土壤改良剂固定污染土壤中铅、镉的研究进展   总被引:21,自引:0,他引:21  
Since the inception of industrial revolution, metal refining plants using pyrometallurgical processes have generated the prodigious emissions of lead (Pb) and cadmium (Cd). As the core target of such pollutants, a large number of soils are nowadays contaminated over widespread areas, posing a great threat to public health worldwide. Unlike organic pollutants, Pb and Cd do not undergo chemical or microbial breakdown and stay likely in site for longer duration after their release. Immobilization is an in-situ remediation technique that uses cost-effective soil amendments to reduce Pb and Cd availability in the contaminated soils. The Pb and Cd contamination in the soil environment is reviewed with focus on source enrichment, speciation and associated health risks, and immobilization options using various soil amendments. Commonly applied and emerging cost-effective soil amendments for Pb and Cd immobilization include phosphate compounds, liming, animal manure, biosolids, metal oxides, and biochar. These immobilizing agents could reduce the transfer of metal pollutants or residues to food web (plant uptake and leaching to subsurface water) and their long-term sustainability in heavy metal fixation needs further assessment.  相似文献   

16.
Reclaimed soils in mining area usually display low fertility and present Cd stress. The amendment of modified biochar effectively fixes Cd in soils, enhances soil fertility, and reduces Cd stress in soil microorganisms. However, the effect of thiourea-modified biochar (TBC) on microbial adaptability to Cd stress in mining reclamation soils is still unclear. The present work studied the Cd immobilization and microbial community changes in a mining reclamation soil displaying extreme Cd contamination under TBC amendment. The results indicated that the amendment of TBC significantly enhanced (P < 0.05) soil pH, the content of available phosphorus (AP), and the activities of urease and polyphenol oxidase by 1.3%, 463.4%, 54.4%, and 84.0%, respectively, compared to the control without amendment. The amount of toxicity characteristic leaching procedure-extracable Cd decreased (P < 0.05) by 68.0% in the TBC-amended soil compared with the unamended soil. The structure of soil microbiota was reorganized and the alpha diversity index was increased in the TBC treatment. The TBC amendment increased the relative abundances of Proteobacteria, Bacteroidota, and Zoopagomycota, which were strongly associated (P < 0.01) with higher soil pH and AP. Structural equation model results demonstrated that Cd immobilization was directly influenced by soil pH, AP, and urease, and indirectly affected by bacterial structure in the TBC treatment. The TBC amendment can effectively improve the structural composition of soil bacteria under Cd stress and enhance the pathways of decreasing soil Cd availability as well. The results might facilitate the development of in-situ remediation programs in Cd-contaminated soils in the future.  相似文献   

17.
Cadmium (Cd) contamination in soils is a serious problem for crop production in the world. Zero-valent iron [Fe (0)] is a reactive material with reducing power capable of stabilizing toxic elements in a solution. In the present study, we examined the effect of zero-valent iron [Fe (0)] application on Cd accumulation in rice plants growing in Cd-contaminated paddy soils. The application of 1.0 and 0.5 mg Fe (0) per 100 g soils significantly reduced the Cd concentration in seeds and leaves by less than 10% and 20% of those without Fe (0) application, respectively. The form of Cd in soil was determined by sequential extraction. The Fe (0) application increased the free-oxides-occluded (less available) Cd content, and decreased the exchangeable and iron-manganese-oxides-bound (more available) Cd content, in Cd-contaminated soils. Thus, this study clearly showed that the application of Fe (0) is a promising approach for remediation of Cd-contaminated paddy soils.  相似文献   

18.
Cadmium (Cd) contamination in soil and its movement into food chain through vegetable dietary poses a risk to human health. A pot experiment was conducted to investigate the effect of humic acid (HA) and two cultivars of Brassica rapa ssp. chinensis L. (pak choi) with differing Cd accumulation abilities on Cd accumulation in different Cd contaminated Ferralsol, Histosol and Luvisol soils. The results showed that HA significantly increased soil pH and cation exchange capacity in Ferralsol (acidic) and Histosol (neutral) soils. HA was more effective in Ferralsol and Histosol soil in reducing bioavailable Cd and its accumulation in both cultivars. Low and high Cd accumulating cultivars combined with HA effectively reduced shoot Cd concentration by 7–34% and 19–35% in Histosol soil, whereas 22–34% and 11–26% in Ferralsol soil, respectively. However, no such reduction was observed for Cd accumulation and bioavailability in Cd-contaminated Luvisol (alkaline) soil. Application of HA enhanced shoot dry biomass in both cultivars grown in Histosol and Ferralsol soils. Therefore, the HA amendment combination with low Cd accumulating cultivars of pak choi could be an effective method for phytostabilization and reduce health risks associated with consuming this vegetable grown in Cd-contaminated acidic and neutral pH soils.  相似文献   

19.
Liu  Yiyun  Xu  Yingming  Qin  Xu  Zhao  Lijie  Huang  Qingqing  Wang  Lin 《Journal of Soils and Sediments》2019,19(2):798-808
Purpose

Natural sepiolite (SP) has proven effective on the in-situ immobilization remediation of Cd-contaminated soils. But the practical remediation effect may largely influenced by water management and the application of organic manure. The effects of chicken manure (CM) on SP-amended soils were investigated under normal and saturated water conditions using a pot experiment with Brassica campestris L.

Materials and methods

Cd-contaminated paddy soils were amended with CM, SP, and CM?+?SP with no amendment as control. The amount of sepiolite was 0.5% (w/w, the same below) either in SP or CM?+?SP amended soils, while the amount of CM was 0.5, 1.0, and 2.0% in CM and CM?+?SP-amended soils. The plant metal contents, fresh weight, and soluble sugar content of plant edible parts were measured on harvest. Soil Cd was extracted by diethylenetriaminepentaacetic acid (DTPA) and HCl to estimate the mobility of heavy metal. Soil pH and dissolved organic matter (DOM) of rhizosphere soil were determined. The electronegative charges of soils were also measured using the zeta potential.

Results and discussion

The application of CM and increasing soil moisture on SP-amended soil increased plant growth to a greater extent than the application of SP alone. The application of CM along with the increase of soil moisture decreased Cd uptake and translocation in plants grown on SP-amended soil compared to the application of SP alone. Cd content of edible plant parts reached a minimum of 0.24 mg kg?1 with the application of 2.0% CM on SP-amended soils under water-saturated conditions, which was approximately 50% lower than the Cd concentration found when applying SP alone.

Conclusions

The results of this study suggest that the application of sepiolite on Cd contaminated soil can effectively reduce Cd uptake by B. campestris L., and the addition of CM combined with effective water management also appears to further reduce Cd absorption and accumulation.

  相似文献   

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