不同类型污染土壤中赤子爱胜蚓对伴矿景天重金属吸收的影响初报

伴矿景天Sedum plumbizincicola是我国发现和报道的镉/锌(Cd/Zn)超积累植物,在土壤Cd污染修复方面已开展实际应用。由于超积累植物伴矿景天在不同类型土壤下的生长能力以及对镉锌的去除效果存在较大差异,因此需引入强化修复技术为植物修复提供辅助作用。作为大型土壤动物,蚯蚓对植物生长的促进作用已有较多研究,但其对伴矿景天生长和重金属吸取效率的影响则鲜有报道,为探究赤子爱胜蚓对不同类型土壤种植下的伴矿景天是否具有强化修复效应,以及不同类型土壤下的强化修复效应差异,设计以下盆栽试验。通过在常湿淋溶土(Perudic Luvisols)、水耕人为土(Stagnic Anthrosols)、湿润雏形土(Udic Cambisols)3种土壤上种植伴矿景天、引入赤子爱胜蚓Eisenia foetida,探究赤子爱胜蚓对伴矿景天生长及Cd/Zn吸收性的影响。选取Cd有效性较高、修复潜力较大的水耕人为土(Stagnic Anthrosols)进行第二季盆栽修复试验。第一季修复结果显示,在酸性的常湿淋溶土中,添加赤子爱胜蚓使伴矿景天地上部生物量较对照处理增加了106%,Cd和Zn吸收量分别提高了72.0%和36.0%,且蚯蚓结合伴矿景天的处理修复后土壤Cd有效性进一步降低,其余两种土壤仅添加蚯蚓无强化修复效应;第二季结果显示,同时添加秸秆和蚯蚓,可强化中性的水耕人为土上种植的伴矿景天生长,增大植物地上部生物量和Cd/Zn吸收量。结果表明,添加蚯蚓可增强伴矿景天在常湿淋溶土中的养分吸收,提高生物量,以此强化其修复效应。在水耕人为土中,外加秸秆可作为蚯蚓强化伴矿景天修复的配套技术。     

伴矿景天-水稻轮作及磷修复剂对水稻锌镐吸收的影响

采用盆栽试验,将锌镉超积累植物伴矿景天与镉低积累水稻中香1号轮作种植于重金属污染土壤,并向土壤添加钙镁磷肥和磷矿粉,研究两种磷修复剂对伴矿景天和锡低积累水稻生长及地上部重金属积累性的影响.盆栽试验结果表明,在轻污染土壤上施用50g"kg-'磷矿粉时伴矿景天地上部的Zn,Cd吸收量分别达到每盆11.5和0.79 mg,效果好于施用4g·kg(-1)钙镁磷肥处理.在重金属污染土壤上种植伴矿景天使后茬水稻地上部Zn、Cd浓度上升,但钙镁磷肥的施用显著降低了水稻体内的Zn,Cd积累量.种植伴矿景天后添加钙镁磷肥稳定调控剂对土壤中水溶态及NH4 OAc提取态Zn、Cd的稳定效果明显优于磷矿粉,且在高污染土壤上效果更佳.田间试验结果显示,施用钙镁磷肥不仅可增加水稻产量,且可一定程度上降低水稻地上部的Zn、Cd吸收量.     

伴矿景天-水稻轮作及磷修复剂对水稻锌镉吸收的影响

采用盆栽试验,将锌镉超积累植物伴矿景天与镉低积累水稻中香1号轮作种植于重金属污染土壤,并向土壤添加钙镁磷肥和磷矿粉,研究两种磷修复剂对伴矿景天和镉低积累水稻生长及地上部重金属积累性的影响.盆栽试验结果表明,在轻污染土壤上施用50 g·kg^-1磷矿粉时伴矿景天地上部的Zn、Cd吸收量分别达到每盆11.5 和0.79 mg,效果好于施用4 g·kg^-1钙镁磷肥处理.在重金属污染土壤上种植伴矿景天使后茬水稻地上部Zn、Cd浓度上升,但钙镁磷肥的施用显著降低了水稻体内的Zn、Cd积累量.种植伴矿景天后添加钙镁磷肥稳定调控剂对土壤中水溶态及NH₄OAc提取态Zn、Cd的稳定效果明显优于磷矿粉,且在高污染土壤上效果更佳.田间试验结果显示,施用钙镁磷肥不仅可增加水稻产量,且可一定程度上降低水稻地上部的Zn、Cd吸收量.     

巨大芽孢杆菌对伴矿景天修复镉污染农田土壤的强化作用

伴矿景天(Sedum plumbizincicola)是一种Cd/Zn超积累植物,常用于Cd污染土壤的植物修复。巨大芽孢杆菌(Bacillus megaterium)是一种溶磷型细菌,既可以促进植物生长,也可以提高土壤重金属生物有效性,对重金属污染土壤植物修复具有强化作用。本研究采用盆栽试验方法,分析了巨大芽孢杆菌不同接种量(10～60 mL)对伴矿景天修复Cd污染农田土壤效率的影响。结果表明: 在Cd污染农田土壤中接种巨大芽孢杆菌可以提高土壤中Cd的活性,土壤有效态Cd含量较对照(CK)增加15.0%～45.0%。与CK相比,巨大芽孢杆菌提高了伴矿景天地上和地下部的生物量,增幅分别为8.7%～66.7%和13.6%～81.8%,并显著增加了伴矿景天地上部的Cd含量,增幅在29.2%～60.4%。在种植伴矿景天并接种巨大芽孢杆菌条件下,土壤Cd去除率在26.7%～42.9%。这说明接种巨大芽孢杆菌可以促进伴矿景天的生长,增加其Cd含量,从而提高Cd污染农田土壤的修复效率。     

麦季间作伴矿景天对不同土壤小麦-水稻生长及锌镉吸收性的影响

采用黑龙江黑土、河南潮土和浙江水稻土等我国粮食主产区典型土壤开展盆栽试验,研究小麦/伴矿景天间作、水稻轮作模式下Zn、Cd超积累植物伴矿景天对当季小麦和后茬水稻生长及重金属吸收性的影响,探索粮食作物主产区污染土壤边生产边修复技术的可行性.结果表明:麦季间作伴矿景天,土壤硝酸钠提取态Zn、Cd浓度较小麦单作处理显著提高,间作处理下水稻土、潮土与黑土的提取态Zn较单作处理分别提高55％、32％和110％,水稻土与黑土提取态Cd较单作分别提高38％和110％,潮土的提取态Cd与对照处理没有差异.间作处理水稻土、潮土和黑土上小麦地上部重金属浓度是单作处理的1.1～1.9倍.麦季间作伴矿景天对后茬水稻生长及其地上部重金属吸收性无显著影响,虽然后茬水稻糙米中Cd含量仍高于0.2 mg·kg-1的“食品中污染物限量”标准,但种植过伴矿景天处理的水稻糙米重金属与前季单作小麦处理相比呈下降趋势.表明通过伴矿景天/小麦-水稻的间作和轮作种植模式,可吸取修复污染土壤中有害重金属,降低后茬水稻的食物链风险.     

土壤pH对东南景天修复镉和锌污染土壤的影响

采用盆栽方法研究重金属(Zn、Cd)2种污染水平(T1处理:Zn 1200 mg·kg-1+Cd 20 mg·kg-1;T2处理:Zn 300 mg·kg-1+Cd 2.0 mg·kg-1)、4个p H水平(4.0、5.5、7.0和8.5)下,土壤Zn、Cd有效态的变化、东南景天吸收和积累特征以及植物对土壤中Zn、Cd的去除效果。结果表明,随着p H的降低,土壤Zn、Cd的有效态含量显著增大,东南景天吸收和积累土壤Zn、Cd的效率显著提高。T1处理时东南景天生物量在p H 5.5时最大,但与其他p H处理的差异并不显著;Zn、Cd在植物地上与地下部分的含量均在p H 4.0时最大。T2处理时东南景天在p H 4.0时体内重金属含量最高,但由于植物生长受到Al和Mn等元素的毒害,此时生物量最小。东南景天对土壤重金属去除率均在p H 5.5时最高,其中T1处理时Cd、Zn去除率分别为16%和1.33%,T2处理时分别为27%和1.09%;2种污染水平土壤重金属的去除率均在p H 8.5时最小。因此,适当降低土壤p H,可有效提高植物积累和去除土壤Zn、Cd的效率。本研究为进一步利用东南景天修复重金属污染土壤、提高植物修复效率提供了科学依据。     

重金属污染土壤的伴矿景天/小麦-茄子间作和轮作修复

在重金属污染土壤上开展田间微区试验,研究伴矿景天/小麦间作、茄子轮作种植模式下锌镉超积累植物伴矿景天对当季小麦和后茬茄子生长及重金属吸收的影响,探索边生产边修复的可行性。结果表明:间作处理下小麦籽粒、茄子植物体和伴矿景天地上部生物量均无明显影响;麦季间作伴矿景天能显著降低小麦籽粒中重金属浓度,间作小麦籽粒与单作相比降低了52.4%;麦季间作伴矿景天也有效降低了后茬茄子对重金属的吸收,茄子果实中镉浓度显著低于单作;作物在与伴矿景天间作的情况下也能显著减少土壤中重金属浓度,其中间作处理全量镉比对照降低了24.3%,达到了较好的修复效果。因此,麦季间作伴矿景天既能有效减少污染土壤中重金属浓度,又能降低小麦及后茬茄子的重金属污染风险,为土壤修复与生产兼顾的修复模式提供理论支持。     

芹菜与伴矿景天间作对污泥农用锌镉污染土壤化学与微生物性质的影响

采集长期施用污泥导致的锌镉污染菜地土壤,通过盆栽试验研究芹菜与伴矿景天单作和两者间作模式下连续种植的修复效果.结果表明:随着修复次数的增加,单作处理中的植物生长不良,而间作处理下伴矿景天生长旺盛;与芹菜单作和伴矿景天单作相比,间作处理土壤有机质、速效氮、全氮、全磷显著降低,而速效钾浓度显著上升,土壤细菌数量提高7.9和18.4倍、真菌数量提高3.7和4.3倍,但脲酶和过氧化氢酶活性没有明显变化;BIOLOG结果也显示,间作处理下土壤微生物碳源利用能力和微生物群落功能多样性指数均显著高于单作处理;间作处理下土壤中Zn和Cd全量分别降低5.8％和50.0％,显著高于单作处理.表明土壤微生物效应可能是影响植物生长的重要原因之一.     

不同类型土壤小麦-水稻轮作体系施用含重金属污泥的环境效应

采用贵州黄壤、石灰土和浙江水稻土,通过盆栽试验探讨了在3种土壤上施用含不同浓度重金属的污泥对小麦、水稻生长及锌(Zn)镉(Cd)吸收性的影响.结果表明： 不同土壤施用同种污泥所产生的重金属污染风险不同,在黄壤和水稻土上施用高浓度重金属污泥对作物的污染风险较高.一次施用Zn、Cd浓度分别为1789、8.47 mg·kg-1的污泥1.6%,使黄壤小麦籽粒中Zn、Cd浓度分别达109、0.08 mg·kg-1;第二次施用后种植水稻,糙米中Zn、Cd浓度达52.0、0.54 mg·kg-1.而施用污泥后石灰性土壤的两种作物其可食部分均无重金属污染风险.土壤醋酸铵提取态Zn是影响麦粒和糙米中Zn浓度的主要因素,而土壤醋酸铵提取态Cd对麦粒和糙米中Cd浓度无明显影响.施用高浓度重金属污泥使3种土壤Zn、Cd全量显著提高,且两次施用后土壤全量Zn均超过国家土壤环境质量二级标准.     

锌肥对不同基因型大麦吸收积累镉的影响

对土壤添加不同Zn、Cd条件下两种基因型(Sahara和Clipper)大麦对Zn、Cd的吸收积累研究表明,在本实验条件下土壤添加Zn、Cd对植物地上部生物量没有显著影响,但土壤添加Zn抑制植物根系生长,在土壤不缺Zn情况下添加Zn<20mg·kg^-1时并没有对大麦体内Cd浓度产生显著影响;当土壤Zn添加量达到40mg·kg^-1时,植物体内Cd浓度明显降低,植物吸收Cd的总量随着土壤添加Zn的增加而显著下降,这主要是由于根系生物量的下降所致,两个基因型大麦品种Zn效率存在显著差异,但这一差异对植物吸收Cd的总量没有影响,Zn高效品种Sahara根部Cd浓度显著低于Clipper。     

Effects of organic amendments on Cd, Zn and Cu bioavailability in soil with repeated phytoremediation by Sedum plumbizincicola

Organic materials with different functional groups can be used to enhance metal bioavailability. Traditional organic materials (rice straw and clover) and ethylenediamine disuccinic acid (EDDS) were applied to enhance metal uptake from polluted soil by Sedum plumbizincicola after repeated phytoextraction. Changes in pH, dissolved organic carbon (DOC) and metal concentrations were determined in the soil solution after EDDS application. Amendment of the soil with ground rice straw or ground clove resulted in higher concentrations of Cd only (by factors of 1.92 and 1.71 respectively) in S. plumbizincicola compared to control soil. Treatment with 3 mmol kg(-1) EDDS increased all the metals studied by factors of 60.4, 1.67, and 0.27 for Cu, Cd, and Zn, respectively. EDDS significantly increased soil solution DOC and pH and increased soil plant-available metals above the amounts that the plants could take up, resulting in high soil concentrations of soluble metals and high risk of ground water contamination. After repeated phytoremediation of metal contaminated soils the efficiency of metal removal declines as the concentrations of bioavailable metal fractions decline. Traditional organic materials can therefore be much more effective and environmentally friendly amendments than EDDS in enhancing phytoremediation efficiency of Cd contaminated soil     

Soil pH Effects on Uptake of Cd and Zn by Thlaspi caerulescens

For phytoextraction to be successful and viable in environmental remediation, strategies that can optimize plant uptake must be identified. Thlaspi caerulescens is an important hyperaccumulator of Cd and Zn, whether adjusting soil pH is an efficient way to enhance metal uptake by T. caerulescens must by clarified. This study used two soils differing in levels of Cd and Zn, which were adjusted to six different pH levels. Thlaspi caerulescens tissue metal concentrations and 0.1 M Sr(NO₃)₂ extractable soil metal concentrations were measured. The soluble metal form of both Cd and Zn was greatly increased with decreasing pH. Lowering pH significantly influenced plant metal uptake. For the high metal soil, highest plant biomass was at the lowest soil pH (4.74). The highest shoot metal concentration was at the second lowest pH (5.27). For low metal soil, due to low pH induced Al and Mn toxicity, both plant growth and metal uptake was greatest at intermediate pH levels. The extraordinary Cd phytoextraction ability of T. caerulescens was further demonstrated in this experiment. In the optimum pH treatments, Thlaspi caerulescens extracted 40% and 36% of total Cd in the low and high metal soils, respectively, with just one planting. Overall, decreasing pH is an effective strategy to enhance phytoextraction. But different soils had various responses to acidification treatment and a different optimum pH may exist. This pH should be identified to avoid unnecessarily extreme acidification of soils.     

Response of Thlaspi caerulescens to nitrogen, phosphorus and sulfur fertilisation

The main limiting factor for cleaning-up contaminated soils with hyperaccumulator plants is the low production of aerial biomass and the number of successive crops needed to reach the objective of remediation. The aim of this study was to contribute to the determination of a fertilisation strategy to optimise soil metal phytoextraction by Thlaspi caerulescens. A pot experiment was conducted on an agricultural soil and on a contaminated soil from the vicinity of a former Pb/Zn smelter. The nitrogen (N) treatment consisted of 4 levels (0, 11, 21.5 and 31 mg N kg(-1) dry soil (DS)) added as NH4NO3. The highest N treatment was combined with 4 levels of phosphorus (P) (0, 20, 40 and 80 mg P kg(-1) DS as KH2PO4) and sulfur (S) additions (0, 10, 20 and 30 mg S kg(-1) DS as MgSO4). The highest N fertilisation contributed significantly to enhance biomass production of T. caerulescens and to decrease the concentration of Cd and Zn in the biomass. At constant N addition, P supply did not affect metal extraction by T. caerulescens but negatively affected plant health. Sulfur supply slightly increased phytoextraction of Cd. Our results show that N and S fertilisation might interact but further investigations on the effect of such interaction on Cd extraction efficiency are needed.     

Enhanced phytoextraction: I. Effect of EDTA and citric acid on heavy metal mobility in a calcareous soil

Phytoextraction, the use of plants to extract heavy metals from contaminated soils, could be an interesting alternative to conventional remediation technologies. However, calcareous soils with relatively high total metal contents are difficult to phytoremediate due to low soluble metal concentrations. Soil amendments such as ethylene diaminetetraacetate (EDTA) have been suggested to increase heavy metal bioavailability and uptake in aboveground plant parts. Strong persistence of EDTA and risks of leaching of potentially toxic metals and essential nutrients have led to research on easily biodegradable soil amendments such as citric acid. In our research, EDTA is regarded as a scientific benchmark with which degradable alternatives are compared for enhanced phytoextraction purposes. The effects of increasing doses of EDTA (0.1,1,10 mmol kg(-1) dry soil) and citric acid (0.01, 0.05, 0.25, 0.442, 0.5 mol kg(-1) dry soil) on bioavailable fractions of Cu, Zn, Cd, and Pb were assessed in one part of our study and results are presented in this article. The evolution of labile soil fractions of heavy metals over time was evaluated using water paste saturation extraction (approximately soluble fraction), extraction with 1 M NH4OAc at pH 7 (approximately exchangeable fraction), and extraction with 0.5 M NH4OAc + 05 M HOAc + 0.02 M EDTA at pH 4.65 (approximately potentially bioavailable fraction). Both citric acid and EDTA produced a rapid initial increase in labile heavy metal fractions. Metal mobilization remained constant in time for soils treated with EDTA, but a strong exponential decrease of labile metal fractions was noted for soils treated with citric acid. The half life of heavy metal mobilization by citric acid varied between 1.5 and 5.7 d. In the following article, the effect of heavy metal mobilization on uptake by Helianthus annuus will be presented.     

Phytoextraction of cadmium and zinc by Salix from soil historically amended with sewage sludge

Short rotation coppice (SRC) such as Salix spp. can be grown as an energy crop and offers some potential for economic and practical phytoextraction of marginally contaminated arable soil. This study tested various soil amendments intended to increase soil metal availability to Salix, investigated the distribution of metal between different tree fractions and assessed the viability of phytoextraction using SRC on arable soils. Several Salix genotypes were grown in field trials over 4 years. Cd and Zn concentrations were generally ranked in the order leaves > bark > wood. Metal concentrations in wood increased towards the top of the willow stems, whereas concentrations in leaves showed the opposite trend. None of the amendments significantly increased uptake of Zn by willow. However, in response to a range of soil HCl treatments, mean Cd concentrations in stems and leaves were 112% and 130% of control values. Data from the current experiment, and previous studies, were combined to develop a predictive model of Cd and Zn stem uptake by Salix. The minimum biological concentration factor (BCF) required to achieve a prescribed soil metal target was also calculated based on typical proportions of bioavailable Cd in sludge-amended soils for a 25-year Salix rotation. The best Salix genotypes investigated achieved less than 20% of the uptake rate required to remove one third of the soil Cd content (equivalent to the average isotopically exchangeable Cd fraction in soils at the study site).     

Long-term field phytoextraction of zinc/cadmium contaminated soil by Sedum plumbizincicola under different agronomic strategies

In two long-term field experiments the zinc (Zn)/cadmium (Cd) hyperaccumulator Sedum plumbizincicola (S. plumbizincicola) was examined to optimize the phytoextraction of metal contaminated soil by two agronomic strategies of intercropping with maize (Zea mays) and plant densities. Soil total Zn and Cd concentrations decreased markedly after long-term phytoextraction. But shoot biomass and Cd and Zn concentrations showed no significant difference with increasing remediation time. In the intercropping experiment the phytoremediation efficiency in the treatment “S. plumbizincicola intercropped with maize” was higher than in S. plumbizincicola monocropping, and Cd concentrations of corn were below the maximum national limit. In the plant density experiment the phytoremediation efficiency increased with increasing plant density and 440,000 plants ha^?1 gave the maximum rate. These results indicated that S. plumbizincicola at an appropriate planting density and intercropped with maize can achieve high remediation efficiency to contaminated soil without affecting the cereal crop productivity. This cropping system combines adequate agricultural production with soil heavy metal phytoextraction.     

Predictability of the Zn and Cd phytoextraction efficiency of a Salix smithiana clone by DGT and conventional bioavailability assays

Aims

Phytomanagement of metal-polluted soils requires information on plant responses to metal availability in soil, but the predictability of metal accumulation in plant shoots and/or roots may be limited by metal toxicity and inherent shortfalls of the bioavailability assays.

Methods

We measured the uptake of Cd and Zn in a Salix smithiana clone grown in a pot experiment on soils with different characteristics and metal availabilities, determined by conventional soil single extractions (0.05 M Na₂-EDTA and 1 M NH₄NO₃), soil solution obtained by centrifugation, and diffusive gradients in thin films (DGT). The Cd and Zn phytoavailability after a 2-year phytoextraction by willow was assessed by metal accumulation in the straw of the following barley culture.

Results

The phytoextraction efficiency was largest on a moderately polluted acid soil. Biomass and shoot Zn concentrations of S. smithiana were better predicted by DGT-measured Zn concentrations in soil solution (C _DGT) than by Zn concentrations in the soil solution and extractable soil fractions. The weaker correlation for Cd in shoots may be related to relative Cd enrichment in the plant tissues. The metal accumulation in barley straw was unaffected or increased after a 2-year phytoextraction.

Conclusions

The shoot Zn and Cd removal of the tested Salix clone can be predicted by C _DGT concentrations and is highest on either calcareous or moderately polluted acid soils. Single extraction with NH₄NO₃ and the C _DGT value of Cd were not able to predict shoot Cd removal on the tested soils. Only shoot removal of Zn was predicted fairly well by the C _DGT value.     

Rhizosphere concentrations of zinc and cadmium in a metal contaminated soil after repeated phytoextraction by Sedum plumbizincicola

A growth chamber pot experiment and a field plot experiment were conducted with the installation of rhizobags to study the effects of repeated phytoextraction by Sedum plumbizincicola on the bioavailability of Cd and Zn in the rhizosphere and bulk soil Repeated phytoextraction gave significantly lower Cd and Zn concentrations in both rhizosphere and bulk soil solutions compared with soil without repeated phytoextraction. The depletion rates of NH40Ac-extractable Zn in rhizosphere soil in each treatment (L-PS, L-NPS, H-PS, and H-NPS) were 59.7, 18.0, 16.3, and 18.6%, respectively. For NH40Ac-extractable Cd, the depletion rates in treatments L-PS, L-NPS, H-PS, and H-NPS were 6.67, 29.4, 40.3, and 41.4%, respectively. Plant shoot biomass decreased in the order H-PS > H-NPS > L-PS > L-NPS, with dry weights of 0.56, 0.42, 1.43, and 1.21 g pot(-1), respectively. Plant Cd uptake increased with increasing aqua-regia extractable metal concentrations. The NH4OAc extraction procedure was satisfactory to predict the bioavailability of Cd and Zn in rhizosphere soil in terms of shoot uptake by S. plumbizincicola with positive correlation coefficients of 0.545 (p < 0.05) and 0.452 (p < 0.05), respectively. The field study results show a slight decrease in water soluble and NH4OAc-extractable metals, a trend similar to that found in the pot experiment.     

Phytoremediation of soil contaminated with cadmium, copper and polychlorinated biphenyls

A pot experiment and afield trial were conducted to study the remediation of an aged field soil contaminated with cadmium, copper and polychlorinated biphenyls (PCBs) (7.67 +/- 0.51 mg kg(-1) Cd, 369 +/- 1 mg kg(-1) Cu in pot experiment; 8.46 +/- 0.31 mg kg(-1) Cd, 468 +/- 7 mg kg(-1) Cu, 323 +/- 12 microg kg(-1) PCBs for field experiment) under different cropping patterns. In the pot experiment Sedum plumbizincicola showed pronounced Cd phytoextraction. After two periods (14 months) of cropping the Cd removal rates in these two treatments were 52.2 +/- 12.0 and 56.1 +/- 9.1%, respectively. Total soil PCBs in unplanted control pots decreased from 323 +/- 11 to 49.3 +/- 6.6 microg kg(-1), but with no significant difference between treatments. The field microcosm experiment intercropping of three plant species reduced the yield of S. plumbizincicola, with a consequent decrease in soil Cd removal. S. plumbizincicola intercropped with E. splendens had the highest shoot Cd uptake (18.5 +/- 1.8 mg pot(-1)) after 6 months planting followed by intercropping with M. sativa (15.9 +/- 1.9 mg pot(-1)). Liming with S. plumbizincicola intercropped with M. sativa significantly promoted soil PCB degradation by 25.2%. Thus, adjustment of soil pH to 5.56 combined with intercropping with S. plumbizincicola and M. sativagave high removal rates of Cd, Cu, and PCBs.