根系分泌物与重金属的化学行为研究

通过毛细管电泳测定根系分泌物的组成发现,根系在受到重金属铅、镉或铅-镉共同作用下分泌物种类与对照都有不同程度的变化;透析袋平衡透析方法则证实了根系分泌物与重金属之间存在着络合反应,络合能力的大小与重金属本身的性质有关,小麦根系分泌物对铅的络合能力大于镉。溶解试验表明,小麦分泌物对红壤中铅、镉的溶出没有显著的影响。小麦无菌根系分泌物、非无菌分泌物、非无菌过0.45m分泌物均促进红壤对铅、镉的吸附。其中铅吸附量较对照分别增加了12%,16%,21%;镉吸附量较对照分别增加了66%,102%,72%。     

废弃混凝土对水中重金属铜和铅的吸附特性

工业废水的直接或间接排放导致中国自然水体受重金属污染程度较高,对重金属污水处理刻不容缓,但现有重金属去除方法普遍存在工艺过于复杂或投资高等缺点。由于废弃混凝土颗粒含有水泥水化产物和未水化的水泥颗粒,具有一定的活性和较高的比表面积,因此该研究拟尝试采用废弃混凝土颗粒作为重金属污染水的吸附材料。通过重金属浸出试验发现,重金属浸出量与废弃混凝土粒径相关,粒径越大,重金属析出量越小。基于试验数据以及《国家污水综合排放标准》的排放阈值要求,最终确定了废弃混凝土颗粒材料的最佳选取粒径。随后,通过静态吸附试验,重点考察了吸附时间、吸附剂用量、重金属初始质量浓度对废弃混凝土吸附重金属铜和铅的影响。结果表明：铜和铅在废弃混凝土上的吸附是一个先快速而后缓慢的过程,在100min基本达到吸附平衡,且废弃混凝土对铜和铅的吸附量随铜和铅初始质量浓度的升高而提高,去除率则随着铜和铅初始质量浓度的升高而降低,随着废弃混凝土用量的升高而提高。废弃混凝土对铜和铅的吸附符合Langmiur等温吸附模型,拟合得到的最大吸附量分别为40.75和86.73mg/g;准二阶动力学模型更适合描述废弃混凝土对铜和铅的吸附过程,说明控...     

Adsorption of heavy metals by a porous bioadsorbent from lignocellulosic biomass reconstructed in an ionic liquid

A novel porous bioadsorbent for metal ion binding (Pd(2+) and Cd(2+)) was successfully prepared from lignocellulosic biomass in ionic liquid by homogeneous succinoylation and sequent chemical cross-linking. The morphology of the bioadsorbent and the interaction between bioadsorbent and metal ions was revealed by scanning electron microscopy and Fourier transform infrared spectroscopy. Results showed that the adsorption mechanism of the bioadsorbent was an ion exchange. A lower dose of cross-linker or higher carboxyl content increased the adsorption capacities of Pd(2+) and Cd(2+). The adsorption capacities of Pd(2+) and Cd(2+) remarkably increased as the pH of metal ion solutions increased. The pores in the bioadsorbent greatly favored the diffusion and adsorption of metal ions, and the adsorption equilibrium time was about 50 min. The adsorption of metal ions could be well explained by the Langmuir model, and the maximum adsorption capacities of Pd(2+) and Cd(2+) were 381.7 and 278.6 mg/g.     

Model experimental study on the migration behavior of heavy metals in electrokinetic remediation process for contaminated soil

Recently in Japan, like in other industrialized countries, treatment of contaminated soil or ground has become an important issue in redeveloping such areas as old factories, mining sites, and other polluted sites. In these cases, measures such as a construction of cut-off walls and disposal to controlled waste disposal sites have been so far taken. But, the treatment of contaminated soils has become more difficult nowadays. Therefore, remediation of contaminated soil by removal or extraction of contaminants is necessary and various methods have been developed and applied in many countries. Authors have tried to develop an electrokinetic remediation method for soil contaminated with heavy metals and some basic and pilot scale experiments have been carried out. In this paper, the results of a model experiment using an artificial soil contaminated with Cu or Ph or Cr are presented as follows. i) In the electrokinetic process, migration of water to the cathode by electroosmosis, migration of ions to the cathode or anode by electrophoresis and electrolysis of water occur spontaneously. ii) Upon DC loading, Cu and Pb migrate to the cathode and accumulate as oxides or hydroxides near the cathode but are not removed from contaminated soil. However, in the case of Cr contaminated soil, Cr in the form of Cr(VI) migrates to the anode and is removed from soil through the drainage water. iii) After DC loading for 2 weeks, the concentration of exchangeable cations and composition of soil changed drastically while the CEC and clay mineralogy did not change appreciably.     

基于双层神经网络与GIS可视化的土壤重金属污染评价

针对土壤重金属污染进行评价,以四川省川芎主产区为例,对川芎主产区—都江堰、崇州、新都等15地土壤的重金属元素取样检测分析,采用双层组合神经网络和GIS空间分析技术综合评价川芎主产区土壤重金属污染。结果表明：研究区大部分区域处于轻度重金属污染状态,处于中度污染状态的区域为崇州、都江堰和彭州。基于双层组合BP神经网络和GIS的研究方法,可以在只具有少量数据的情况下对数据进行比较精确的空间分析,能够在满足一定精度分析的原则下适当的降低采样分析成本,得到比单因子指数评价准确度更高的空间分布图。     

煤矸石山重金属元素研究进展

对煤矸石及其周围土壤、水体、大气,以及煤矸石山上植物体中重金属元素的有关研究分析表明1)我国大多数矿区煤矸石属于普通固体废弃物,重金属元素超标倍数不大;2)煤矸石山对周围土壤、水体、大气影响较小,但其本身不宜生产具有食用价值的植物产品;3)煤矸石植被恢复后,大多数植物体内重金属元素含量超过蔬菜限量物质指标.     

复合污染土壤中土霉素的吸附行为及其对土壤重金属解吸影响的研究

参考经济合作与发展组织(OECD)化学品试验导则No.106,采用批量平衡试验的方法,探讨了土霉素(Oxytetracycline,OTC)在3种土壤中的吸附解吸特性,并考察了土霉素外加量对土壤中4种代表性重金属元素(铜、锌、铅、镉)解吸量的影响。试验设置的土霉素初始浓度为0.01、0.1、1.0、5.0、10.0、25.0、50.0、100、200和400 mg L-1。结果表明:(1)存在一个土霉素特征浓度,高于或低于该浓度值时土霉素的吸附性质有所差异,且高低两个浓度范围内的数据均能用Freundlich模型与Langmuir模型较好地拟合;(2)当土霉素浓度在0~25 mg L-1之间时,能在土壤表面与重金属发生竞争吸附,且重金属解吸量随土霉素浓度的增加而增加;当土霉素浓度在25~100 mg L-1之间时,部分游离态重金属以与土霉素的络合物形式重新固定于土壤表面,土壤重金属的解吸量随土霉素浓度增加而减少;土霉素浓度高于100 mg L-1时,体系p H相对于对照有明显下降,土壤重金属的解吸量与土霉素浓度又呈正相关。     

Adsorption isotherms of some heavy metals under conditions of their competitive adsorption onto highly calcareous soils of southern Iran

Recently, application of sewage sludge or effluents resulted in raising the concentrations of some heavy metals in some agricultural soils of Iran. Experiments were conducted to evaluate the competitive adsorption of lead (Pb), copper (Cu), zinc (Zn), and cadmium (Cd) on six calcareous soils. Adsorption characteristics were evaluated by equilibration of 1 g of each soil sample with 20 ml of 0, 10, 20, 30, 40, 50, 100, or 200 mg L^?1 of their nitrate solutions and 0.01 M NaNO₃ as background electrolyte. Furthermore, solid/liquid distribution coefficients (K_d) of studied metals, as an index of soil capacity to resist a change of the soil solution concentration, were calculated. Results indicated that amounts of adsorbed Pb, Cu, Zn, and Cd increased with increase in their concentrations in the contact solutions, but this trend was more pronounced for Pb and Cu than the others. For all studied soils and metals, Langmuir equation described the adsorption behavior fairly well. Furthermore, Langmuir and Freundlich equation parameters were positively correlated to cation exchange capacity (CEC) and smectite contents; whereas, they were negatively correlated to sand content. Considering K_d values, the selectivity sequence of the metal adsorption was Pb > Cu > Zn > Cd. Therefore, the risk of leaching and also plant uptake of Zn and Cd will be higher as compared to those of the other elements.     

扬州市土壤重金属含量的调查

对全市385个土样分析结果表明,扬州市耕地土壤总体是清洁的,全市89 35%的土壤属于清洁地范围(综合污染指数≤0 7),7 53%的土壤属尚清洁范围(综合污染指数0 7～1 0之间),3 12%的土壤属轻度污染(综合污染指数1 0～2 0之间)。全市土壤重金属污染的顺序是Hg>Cr>As>Cu>Pb>Cd,各地区中,以邗江区土壤重金属含量相对较高。     

不同内源重金属生物炭对Cu和Cd吸附及其对老化作用的响应

为明确老化作用对不同内源污染物生物炭吸附重金属稳定性的影响,该研究以不同污染程度（清洁、中度和重度污染）土壤种植的巨菌草秸秆制备3种不同内源Cu和Cd含量的生物炭RB、SB和JB,分析3种生物炭对Cu2+和Cd2+的吸附能力以及干湿和冻融老化对饱和吸附后生物炭中Cu和Cd的生物有效性的影响。结果表明：3种生物炭表面均分布丰富的孔隙结构,RB含有最高的pH值和灰分含量;生物炭对Cu2+和Cd2+的吸附符合Langmuir模型（R2=0.951～0.998）,且RB对Cu2+和Cd2+的吸附量最大,分别为54.3和37.3 mg/g;与此相同,饱和吸附后RB对Cu2+和Cd2+的固持量最大,分别为21.4和4.78 mg/g。与老化前相比,干湿老化较冻融老化更显著地降低了饱和吸附后生物炭中Cu的TCLP（Toxicity Characteristic Leaching Procedure）浸出含量,促进了Cu从酸溶态和残渣态向还原态和氧化态转化,降低了Cu的环境风险;但是干湿和冻融老化作用增加了饱和吸附后生物炭中Cd的TCLP浸出含量,促进了Cd从残渣态向酸溶态、还原态和氧化态转化,增加了Cd的环境风险。这可能是由于3种生物炭对Cu2+的吸附主要以表面络合为主,对Cd2+的吸附以化学沉淀机制为主。总体上,RB生物炭固持最高的Cu2+和Cd2+,但是干湿和冻融老化增加了饱和吸附后生物炭Cd环境风险,研究结果对于评估生物炭长期钝化修复稳定性具有一定的指导意义。     

天然沸石对重金属离子的竞争性吸附研究

通过室内分析的方法研究了天然沸石对4种重金属离子Cd2 、Zn2 、Cu2 、Pb2 的竞争性吸附特性。研究结果表明,与单一离子体系比较,沸石在竞争体系中对Cd2 、Zn2 、Cu2 、Pb2 4种重金属离子的吸附量均呈下降的趋势。竞争体系下,其它重金属离子的存在显著地抑制了沸石对Cd2 的吸附,而对Pb2 的吸附几乎没有影响。天然沸石对4种重金属离子的富集系数,其大小顺序依次为Pb2 >Cu2 >Zn2 >Cd2 。该选择性吸附顺序可能与重金属离子的水合能、离子半径、有效水合离子半径等因素密切相关。     

Combination effects of heavy metals and fluoranthene on soil bacteria

The effects of (1) Cd, Cu, Zn, and fluoranthene (FLA), separately applied, and (2) combinations of one of these heavy metals with FLA on the growth of bacteria were studied in agar plate experiments. The bacteria were extracted from A horizons of a Eutric Regosol and a Calcic Chernozem. Significant reductions of bacterial counts were observed for both soils at concentrations > 1.0 mg Cd l^–1, 0.5 mg Cu l^–1, and 0.5 mg Zn l^–1, respectively. Additions of FLA up to 100 mg l^–1 did not result in increasing reductions of bacterial growth in the Regosol. Only 0.5, 2, and 100 mg FLA l^–1 caused significant reductions of 22–27%. Bacterial counts were not affected by 0.2 mg FLA l^–1. Low concentrations of heavy metals which were not affective when added separately were found to reduce bacterial growth when applied in combination with 0.2 mg FLA l^–1. At higher levels of heavy metals up to 2.5 mg l^–1, addition of FLA also increased the toxicity of the metals. It is assumed that the enhancement of toxicity by FLA is due to an alteration of the permeability of bacterial cell membranes. Received: 19 July 1996     

Effects and relative toxicity of heavy metals on Cuscuta reflexa

The effects of four concentrations (0.5, 1, 5 and 10 μg mL^?1) of the heavy metals Hg, As, Pb, Cu, Cd, and Cr on some senescence variables of Cuscuta reflexa Roxb. were studied. All of the treatments, except 0.5 μg mL^?1, decreased Hill reaction activity, chlorophyll and protein contents and dry matter percentage in biomass and increased tissue permeability over control data. The harmful effects of the metals were best visible at 10 μg mL^?1. The general order of sensitivity was As > Cd > Pb > Hg > Cu > Cr (absolute metal concentration). The data suggest that Cuscuta reflexa shows tolerance to the heavy metals tested up to 0.5 μg mL^?1.     

Behavior of heavy metals in forest microcosms

Transport and distribution of heavy metals were determined in soil and vegetation (Acer Rubrum) of intact forest microcosms. Litter from a contaminated forest and baghouse dust from a primary Pb smelter were applied to three of the microcosms, while three uncontaminated microcosms served as controls. Total dosages for Ph, Cd, Zn, and Cu on the treated microcosms were 11.0, 0.128, 0,748, and 0.161 mg cm^?2, respectively. All metals were mobilized in soil and were enriched in at least one tissue component of Acer rubrum. Enrichment of Pb, Cd, and Zn occurred in all Acer tissues; Cu enrichment was found only in leaves. Uptake of metals by Acer rubrum was similar to a contaminated forest in southeastern Missouri and decreased in order: Zn, Cu, Cd, and Pb. Results of this experiment indicate that intact microcosms may be useful in assessing uptake and mobility of toxic chemicals which may be applied to forest ecosystems.     

土壤中重金属离子竞争吸附的研究进展

本文主要对土壤中重金属离子竞争吸附的研究现状进行了综述。讨论了影响重金属离子竞争吸附能力的一些主要因子、吸附平衡模型及吸附反应的动力学过程。重金属离子的一级水解常数、离子半径、电负性等性质及其外界环境条件,如pH值、离子强度、有机质含量等因素影响着离子选择性吸附的强弱。竞争的Langmuir方程和扩展的Freundlich方程被用来对竞争吸附过程进行描述,同时指出竞争吸附过程中存在着一个"过饱和点"。最后,对竞争吸附的发展方向进行了展望,指出应加强理论模型和多因子综合作用影响的研究。     

重金属的土水分配行为研究——根际土壤溶液采样器的应用

采用根际土壤溶液采样器(Rhizon-SMS)原位采集河南平原耕地土壤溶液.用土壤溶液中重金属浓度对数作为因变量、土壤溶液理化性质作为自变量,进行多元线性逐步回归,结果表明:只有有机碳进入Cu的相关方程,pH进入Cd的相关方程.土壤溶液pH和土壤中的Zn都作为自变量进入Zn的相关方程.土壤溶液中的Cu与pH没有线性关系,而Cd和Zn与土壤溶液pH有显著的线性关系(p＜0.01).计算了土壤中Cu、Cd、Zn在土壤与土壤溶液中的分配系数Kd.本研究中,3种重金属的Kd大小顺序为:Cu＞Zn＞Cd.根据Freeze 和Cherry模型,联合log(Kd-Cd)、log(Kd-Zn)与pH的线性关系,估计了Cd和Zn在土壤中的迁移速度.     

Influence of carbonate on the reaction of heavy metals in soils

The reaction of Cu, Zn and Cd with soils with carbonate contents ranging from 0 to 75 mg g⁻¹ was studied before and after removal of soil carbonates with acetate buffer at pH 5. Treatment with acetate buffer caused a strong decrease in metal retention by those soils containing carbonates, although if no carbonate was originally present, the treatment caused little effect or even an increase in the amounts sorbed. Before the treatment, adsorption of increasing amounts of Cu and Zn was accompanied by a continuous increase in Ca + Mg released, and those soils containing carbonate released Ca + Mg in excess of their exchangeable amounts, due to dissolution of carbonates and/or penetration of the heavy metal into the carbonate structure. It is suggested that Cu was preferentially retained by the treated soils through precipitation of Cu oxide, and by adsorption on the soil carbonates in the case of the original samples. Zn was removed from the solution by the original carbonate soils through formation of ZnCO₃. Treated soils were likely to retain Zn by cation exchange and/or adsorption. Adsorption was probably the main process involved in retention of Cd. In all cases pH was the master variable in controlling the extent and probably the nature of the reaction.     

Accumulation of heavy metals in oil-contaminated peat soils

X-ray fluorescence and X-ray radiometry represent easy and simple methods to determine concentrations of heavy metals in the ash of peat soils contaminated with oil and can be applied for soil monitoring purposes. Oil spills on peat bogs produce two contamination zones differing in the composition of heavy metals. In the zone of primary contamination, the peat surface is covered by a bitumen crust with V, Ni, Sr, Ba, Ce, and La accumulating there. This zone adjoins the zone of secondary peat contamination, where heavy alkaline-earth metals (Sr, Ba) and lanthanides (Ce and La) are accumulated to a lesser extent. Biological preparations recommended for remediation of oil-contaminated peat soils should be tolerant to high concentrations of heavy metals, particularly, V, Ni, and Ba that are present in the oil contaminated soils in relatively high amounts.     

Cadmium and other heavy metals in sea-skaters

Exceptionally high concentrations of Cd (100 to 200 ppm dry weight) were found in samples of Halobates collected off Baja California. In contrast, no detectable Cd was found in Rheumatobates collected from mangrove lagoons in the Gulf of California. Concentrations of five other heavy metals in the two marine insects are also presented.