共查询到19条相似文献，搜索用时 171 毫秒
1.
对中国南方的3个水稻土样品进行了Cd、Pb单一离子和混合离子吸附特点的研究。结果表明,3个水稻土样品中Cd、Pb的吸附特点都相似,Langmuir等温方程可很好地描述Cd、Pb的吸附等温线。3个土壤样品中,有较高pH值和较低有机物、CEC浓度、粘土含量、高岭石含量的2个土壤样品对Cd、Pb有较大的吸附量,且其等温吸附拟合的最大吸附量（B）也较大。在两组分混合溶液中,尽管共存离子的存在影响了土壤对单一离子的吸附,同时土壤对Cd的吸附在一定程度上受影响的程度大,但3个土壤样品都表现出对Pb有强的吸附能力。在3个土壤样品中,Langmuir等温方程中Pb的健合能常数（K）都大于Cd的健合能常数（K）,混合溶液中的K值高于单一溶液的K值,表明2种金属离子对吸附位点的竞争提高了特定吸附位点的保持力,使金属离子在土壤中特定位点的吸附更加坚固。 相似文献
2.
研究了山西省3种不同质地的土壤对Cd2＋、Pb2＋、Hg2＋的吸附、解吸和3种离子在土壤中的运移特性。结果表明,Cd2＋、Pb2＋和Hg2＋在粘粒土壤中的吸附能力大于在砂粒土壤中的吸附能力,且3种土壤对Pb2＋都有很强的吸附能力,吸附的Pb2＋很难在土壤中解吸下来。3种土壤对3种金属离子的吸附能力为Pb2＋＞Cd2＋＞Hg2＋,解吸能力正好相反,这主要与土壤的不同性质和3种重金属离子的水合离子半径、离子的水合能密切相关。Cd2＋在3种土壤中的等温吸附符合Freundlich和Langmuir方程,Pb2＋在3种土壤中的吸附特征符合Henry方程,而Hg2＋在3种土壤中的吸附符合Langmuir方程。土柱淋滤实验表明,Hg2＋在土壤中的穿透性很强,Cd2＋次之,Pb2＋在土壤中的穿透性最慢,其在长达20天的淋滤过程中仍然没有穿透土柱。3种不同质地的土壤对Cd2＋、Pb2＋和Hg2＋的迁移能力都表现为：大同土壤＞临汾土壤＞太原土壤。 相似文献
3.
土壤中重金属元素Pb、Cd地球化学行为影响因素研究 总被引：12，自引：0，他引：12
通过研究湖南洞庭湖地区水稻土中Pb、Cd与土壤有机质、粘粒和pH值的关系,结果表明,(1)土壤中有机质含量与Cd、Pb有着显著的正相关性,土壤中有机质含量增加可明显降低Cd和Pb的离子态和可交换态含量。(2)随着粘粒含量增加,Pb和Cd离子可交换态占全量的比值略有增加,这说明粘粒表面吸附的Pb和Cd容易进入植物体中,对生态系统安全具有危害的组分。(3)Cd离子交换态与土壤pH值呈显著相关关系,土壤酸化使Cd的离子交换态比例上升,可直接导致农作物中Cd含量增加,防止土壤酸化是控制Cd对生态系统危害的有效途径;Pb的离子交换态与全量的比值与pH值具有显著的相关性,对于Pb污染严重的土壤,保持土壤pH值在弱酸性至弱碱性范围,防止土壤酸化和盐碱化,可以降低Pb危害。土壤有机质含量、pH值等是控制重金属元素地球化学行为的重要因素之一。 相似文献
4.
针铁矿/水界面反应性的实验研究 总被引：1，自引：0，他引：1
选择针铁矿对Pb2+、Cu2+、Cd2+等3种重金属离子的吸附实验,开展矿物/水界面反应性研究.金属离子(M2+)在矿物-水溶液间分配有多种表面反应机制,这些表面反应发生作用的条件主要取决于吸附质水化学性质和矿物表面荷电性,因此,溶液pH值是影响矿物/水界面反应性的关键因素.在不同pH值条件下, 表面羟基可通过发生质子化或去质子化反应而使得矿物表面产生荷电性并发生改变,而金属离子的水解则可显著加快金属羟基配合物的形成,从而进一步增强了矿物/水界面反应.本实验条件下针铁矿表面对重金属离子的吸着量随pH值升高而升高,在一个较窄的pH值范围内吸附率急剧升高,呈S形分布.针铁矿对3种不同的重金属离子的吸附能力的强弱顺序是Cu2+＞Pb2+＞Cd2+.无论是Langmuir方程还是Freundlich方程,都能较好拟合针铁矿对重金属离子的等温吸附过程.Freundlich方程的n值均在0.1～0.5之间,说明重金属离子在针铁矿表面的吸附并不能简单地归结为单配位或双配位模式,可能存在着多种吸附结合形态.表观吸附常数KM值的变化规律,说明重金属离子与针铁矿表面反应模式及其表面吸附形态发生了变化,具体的吸附形态还有待谱学研究进一步证实. 相似文献
5.
土壤样品分别采于山西省大同、太原和临汾3个地区。实验分成吸附解吸、竞争吸附和运移实验3个部分。其中吸附实验又分成砂粒土壤和粘粒土壤2个粒级分别实验。结果表明：在常温常压下,3种土壤对Cd的吸附用Langmuir模式来拟合较合适,土壤粘粒的吸附能力大于土壤砂粒的吸附能力。Zn^2＋与Cd^2＋共存时,Cd的吸附受到抑制,在本实验浓度下,腐殖酸对土壤吸附Cd的抑制作用不明显。解吸过程显示土壤对Cd离子的解吸与有机碳、阳离子代换量成负相关。Cd在土壤中的穿透曲线是Cd在土壤中吸附、解吸、络合、迁移等作用的综合体现．Cd在各种土壤中的运移时间顺序为：大同土壤〉临汾土壤〉太原土壤,从而得出Cd在壤质砂土中运移得最快、在粉土中运移得最慢的结论。 相似文献
6.
7.
随着我国经济社会的快速发展,土壤重金属的超标问题越来越突出,尤其是Cd。土壤Cd活动性受到各种因素的影响,但成土母质对土壤Cd活动性影响的研究成果还鲜有报道。以珠江三角洲为研究区,系统采集了由第四纪沉积物、酸性侵入岩和陆源碎屑岩3种不同成土母质发育形成的水稻土样品235件,查明了土壤理化特征,探讨了Cd全量及其活动态的影响因素。结果表明：不同成土母质发育形成的水稻土理化性质、Cd全量及其活动态的影响因素存在差异。第四纪沉积物发育形成的水稻土CaO、K2O、Na2O、TFe2O3、阳离子交换量(CEC)、pH、有机质、黏粒平均含量显著高于酸性侵入岩和陆源碎屑岩,Cd超标最为严重,不同方法提取的Cd活动态含量也最高;陆源碎屑岩发育形成的水稻土中Cd全量与土壤理化指标的相关性均强于其他两类成土母质;酸性侵入岩发育形成的水稻土中Cd全量与土壤理化指标的相关性较弱。Cd全量对其活动态含量有重要影响,此外,第四纪沉积物发育的水稻土中Cd活动态含量与pH、有机质和TFe2O3 相似文献
8.
在分析研究了约500套水稻籽实-耕层土及约300套小麦籽实-耕层土样品相关元素含量等地球化学调查数据基础上,报道了江苏典型地区水稻与小麦籽实中Cd、Hg、Cu、Pb、Zn、Cr、As、Se、Mo、Mn、Fe、K、Ca、Mg等14个元素的生物富集系数(BCF)分布状况,统计结果显示,各元素的BCF值差异较大,通常Pb、Cr、Fe等元素BCF多小于1%,Hg、As、Mn、Ca等元素BCF多为1%～10%,Mo的平均BCF最大、Fe的平均BCF最小。研究发现,水稻与小麦籽实中Pb与Cd超标率分别超过15%、6%,BCF值差异与稻谷、小麦的元素含量无直接关系,部分元素的BCF与土壤pH、TOC、CEC、B含量等具有统计上的相关性,其中土壤pH与Cd、Ca、Mg元素的BCF呈显著负相关,而土壤的有机碳含量、阳离子交换量及B含量等也对部分元素的BCF值有一定影响。 相似文献
9.
10.
土壤中Pb离子地球化学行为模拟实验
——以山西的典型土壤为例 总被引：2，自引：0，他引：2
土壤样品分别采于山西省大同、太原和临汾3个地区。实验分成吸附解吸、竞争吸附和运移实验3个部分。其中吸附实验分成砂粒土壤和粘粒土壤2个粒级分别进行。结果表明：在常温常压下,Hery模式更适合描述3种土样砂粒部分和粉粘粒部分对Pb^2＋的吸附。吸附实验结果表明,土壤对Pb有很强的吸附作用,吸附过程受CEC的影响很大。在竞争吸附实验中,Pb的存在减少了土壤对Cd的吸收;腐殖酸对土壤吸附Pb^2＋表现出抑制作用。解吸实验结果表明,Pb在土壤中以专性吸附为主,吸附的Pb很难解吸下来。运移实验结果显示,在长达20天的淋滤过程中Pb^2＋仍没有穿透土柱,说明土壤对P^2＋的吸附能力极强,Pb迁移非常缓慢。 相似文献
11.
Competitive sorption and desorption of cadmium and lead in paddy soils of eastern China 总被引：3，自引：0，他引：3
To assess the competitive sorption and desorption of cadmium (Cd) and lead (Pb), batch equilibrium experiments were performed using single- and binary-metal solutions in surface samples of three paddy soils from eastern China. Sorption isotherms were well fitted with one-metal and competitive Langmuir equation for single- and binary-metal system, respectively. The distribution coefficient (K d) values were K d single (Pb) > K d binary (Pb) > K d single (Cd) > K d binary (Cd), indicating that Pb was stronger sorbed by these soils than Cd in binary metal system. Soils with high pH and clay content had the greatest sorption capacity as estimated by the maximum sorption parameter (Q). The co-existence of both metals reduces their tendency of sorption, whereas Cd sorption was affected to a greater extent than that of Pb. The Langmuir binding strength parameter (b) in binary sorption system was greater than that in single sorption system for all soils (b < b 1), indicating that competition for sorption sites promote the retention of both metals into more specific sorption sites. Sorption of Cd and Pb decreased soil pH by 1.61 U for YRS, 1.39 U for PCS, and 0.91 U for SLS. The decreases of pH in binary metal system were greater than in single-metal system for three soils. Cadmium and Pb desorption increased with increasing Cd and Pb sorption saturation for all soils; however, Cd desorption ratio in binary metal system (d Cd*) was much greater than Pb (d Pb*), indicating that under the competitive sorption conditions, the sorbed Cd was more readily desorbed from the soils than the sorbed Pb. 相似文献
12.
不同粒级土壤中镉铅汞的吸附特性 总被引：2，自引：0，他引：2
将3种不同质地的土壤样品分为3种不同的粒级:自然状态、砂粒和粉黏粒,分别研究了这3种不同土壤在3种不同粒级时对镉、铅、汞的吸附特点。结果表明,镉、铅在粉黏粒土壤中的吸附大于在自然土壤和砂粒土壤中的吸附,而汞却表现出相反的结果,其在砂粒土壤中的吸附远远大于在粉黏粒土壤和自然土壤中的吸附。3种不同质地的土壤对镉、铅、汞的吸附与分粒级土壤的吸附表现出了相似的吸附特性。同时,镉在3种不同土壤不同粒级中的吸附符合Langmuir方程,铅在3种不同土壤不同粒级中的吸附符合Henry方程,而汞在3种不同土壤不同粒级中的吸附符合Freundlich方程。 相似文献
13.
Susana Serrano Peggy A. O’Day Maria Teresa García-González 《Geochimica et cosmochimica acta》2009,73(3):543-558
The bioavailability and fate of heavy metals in the environment are often controlled by sorption reactions on the reactive surfaces of soil minerals. We have developed a non-electrostatic equilibrium model (NEM) with both surface complexation and ion exchange reactions to describe the sorption of Pb and Cd in single- and binary-metal systems over a range of pH and metal concentration. Mineralogical and exchange properties of three different acidic soils were used to constrain surface reactions in the model and to estimate surface densities for sorption sites, rather than treating them as adjustable parameters. Soil heterogeneity was modeled with >FeOH and >SOH functional groups, representing Fe- and Al-oxyhydroxide minerals and phyllosilicate clay mineral edge sites, and two ion exchange sites (X− and Y−), representing clay mineral exchange. An optimization process was carried out using the entire experimental sorption data set to determine the binding constants for Pb and Cd surface complexation and ion exchange reactions.Modeling results showed that the adsorption of Pb and Cd was distributed between ion exchange sites at low pH values and specific adsorption sites at higher pH values, mainly associated with >FeOH sites. Modeling results confirmed the greater tendency of Cd to be retained on exchange sites compared to Pb, which had a higher affinity than Cd for specific adsorption on >FeOH sites. Lead retention on >FeOH occurred at lower pH than for Cd, suggesting that Pb sorbs to surface hydroxyl groups at pH values at which Cd interacts only with exchange sites. The results from the binary system (both Pb and Cd present) showed that Cd retained in >FeOH sites decreased significantly in the presence of Pb, while the occupancy of Pb in these sites did not change in the presence of Cd. As a consequence of this competition, Cd was shifted to ion exchange sites, where it competes with Pb and possibly Ca (from the background electrolyte). Sorption on >SOH functional groups increased with increasing pH but was small compared to >FeOH sites, with little difference between single- and binary-metal systems. Model reactions and conditional sorption constants for Pb and Cd sorption were tested on a fourth soil that was not used for model optimization. The same reactions and constants were used successfully without adjustment by estimating surface site concentrations from soil mineralogy. The model formulation developed in this study is applicable to acidic mineral soils with low organic matter content. Extension of the model to soils of different composition may require selection of surface reactions that account for differences in clay and oxide mineral composition and organic matter content. 相似文献
14.
影响向海湿地草根层土壤吸附铅、镉能力的因素 总被引：9，自引：7，他引：2
利用向海湿地采集的草根层土壤进行吸附铅、镉的热力学实验,结果表明草根层土壤吸附铅、镉的过程符合Langmuir和Freundlich等温吸附曲线(n=8,p=0.01).吸附铅、镉存在干扰吸附现象,吸附铅的能力约是吸附镉的能力的3倍.而且草根层土壤吸附铅、镉的最大吸附量与土壤中的有机质和铁、锰氧化物含量存在着正相关性.土壤的理化性质是影响土壤吸附铅、镉能力的内在主要因素;pH等是影响草根层土壤吸附铅、镉能力的外部主要因素. 相似文献
15.
《Applied Geochemistry》2003,18(11):1723-1731
The mobility and bioavailability of heavy metals depends on the metal retention capacity of soil and also on the geochemical phases with which metals are associated. Laboratory batch experiments were carried out to study the sorption and distribution of Cd, Ni and Pb in 3 soils differing in their physicochemical properties from India: Oxyaquic Haplustalf (SL1), Typic Haplustalf (SL2) and Typic Haplustert (SL3). The heavy metal adsorption was studied by isotherms and the distribution coefficient (KD) for each metal was obtained from the linear regressions of the concentration of metal remaining in equilibrium solution and the amount adsorbed. In general, the sorption capacity for all the metals decreased in the order: SL3>SL2>SL1. Among metals, the sorption capacity in all the soils decreased in the order: Pb>>Ni>Cd. Distribution of sorbed metals at various equilibrating concentrations was studied by sequential extraction. Results showed significant differences in the distribution of metals in these soils. At higher additions (such as 200 μM l−1) most of the metals were extracted in their more mobile fractions, exchangeable and/or inorganic in contrast to their original partitioning in soils, where they were preferentially associated with the less mobile residual fraction. Largest percentages of metals extracted in the exchangeable fraction corresponded to those soil–metal systems with smaller KD values, e.g. Cd, Ni and Pb in SL1 and Cd and Ni in SL2. In neutral and alkaline soils (SL2, pH=7.1, and SL3, pH=8.6) Pb was predominantly extracted from the inorganic fractions and this corresponded to higher KD values for Pb in these soils. The predominance of metals associated with the exchangeable fraction together with low KD values indicates higher mobility of metals retained in the acidic soil (SL1, pH=5.2) compared with the others. 相似文献
16.
岩溶区典型土壤对Cd2+的吸附特性 总被引：2，自引：2，他引：0
文章采用有序批试验,就岩溶区两种典型石灰土（棕色、黑色石灰土）对Cd2+的吸附行为进行研究。试验结果表明:石灰土对重金属Cd2+具有较强的吸附能力（平均吸附率范围89.84~98.84）,黑色石灰土的吸附能力高于棕色石灰土,吸附量随平衡浓度的增加而增大;Langmuir和Freundlich方程均能很好地描述两种石灰土对Cd2+的等温吸附过程,Freundlich方程拟合最优;两种石灰土吸附镉的动力学特征相似,吸附过程可分为快速反应、慢速反应和吸附平衡3个阶段,棕色石灰土对Cd2+吸附动力学的最优模型为Elovich方程和双常数方程（R>0.9）,黑色石灰土仅在Cd2+初始浓度为100 mg/L条件下,Elovich方程、双常数方程和W-M方程的模拟达到较显著水平（R>0.8）;有机质、碳酸钙含量及CEC值是影响石灰土对Cd2+吸附能力的主控因素,铁、铝、硅氧化物含量对Cd2+吸附影响不大;综合热力学、动力学及影响因素分析认为石灰土对Cd2+吸附机理包括土壤颗粒表面官能团的专性吸附及不均匀粒内扩散、静电作用等非专性吸附过程。 相似文献
17.
Lotfi Mouni Lazhar Belkhiri Abdelkrim Bouzaza Jean-Claude Bollinger 《Arabian Journal of Geosciences》2017,10(4):77
The chemical associations of Cd, Cu, Pb, and Zn in four mine soil samples from the Amizour-Bejaia Pb/Zn mine (Algeria) have been investigated by a five-step sequential extraction procedure. Although Cd preferentially binds to carbonates, Cu, Pb, and Zn are mainly associated with the organic and reducible fractions. Batch adsorption experiments with either mono- or multi-metallic solutions are described with the Freundlich isotherm model. Whatever the nature of the soil sample, the sorption behavior for each given metal except Pb is very similar, indicating that the binding sites at the soil surface are progressively occupied by the metal from the solution. On each soil sample, the decreasing order of sorption can be established as Pb >> Cu > Cd > Zn. When the four metals are simultaneously applied to each soil sample, their specific behavior is strongly affected by their interactions and/or competition for the available surface sites: we generally observed isotherm curves with a slight maximum before the plateau at higher solution concentration. Although Cu is only slightly affected by the other metals, in the case of Pb, Cd, and Zn, the sorbed amounts strongly decreased. 相似文献
18.
Simultaneous competitive adsorption behavior of Cd, Cu, Pb and Zn onto nine soils with a wide physical–chemical characteristics
from Eastern China was measured in batch experiments to assess the mobility and retention of these metals in soils. In the
competitive adsorption system, adsorption isotherms for these metals on the soils exhibited significant differences in shape
and in the amount adsorbed. As the applied concentration increased, Cu and Pb adsorption increased, while Cd and Zn adsorption
decreased. Competition among heavy metals is very strong in acid soils with lower capacity to adsorb metal cations. Distribution
coefficients (K
dmedium) for each metal and soil were calculated. The highest K
dmedium value was found for Pb and followed by Cu. However, low K
dmedium values were shown for Zn and Cd. On the basis of the K
dmedium values, the selectivity sequence of the metal adsorption is Pb > Cu > Zn > Cd and Pb > Cu > Cd > Zn. The adsorption sequence
of nine soils was deduced from the joint distribution coefficients (K
dΣmedium). This indicated that acid soils with low pH value had lower adsorption capacity for heavy metals, resulting in much higher
risk of heavy metal pollution. The sum of adsorbed heavy metals on the soils could well described using the Langmuir equation.
The maximum adsorption capacity (Q
m) of soils ranged from 32.57 to 90.09 mmol kg−1. Highly significant positive correlations were found between the K
dΣmedium and Q
m of the metals and pH value and cation exchange capacity (CEC) of soil, suggesting that soil pH and CEC were key factors controlling
the solubility and mobility of the metals in soils. 相似文献
19.
《Chemie der Erde / Geochemistry》2015,75(1):29-33
The potential effect of urban particulate matter (PM) accumulation on metal sorption onto two contrasting soils (Chernozem and Fluvisol) was investigated in a batch sorption experiment. While the Freundlich isotherms did not indicate any effect of PM addition to the soils, the Langmuir isotherm allowed us to estimate the potential behaviour of the PM in the soil. The PM added to the Chernozem did not lead to substantial changes in sorption of Cd, Cu, Mn, Ni, Pb, and Zn. On the contrary, the presence of PM in the Fluvisol increased the number of potential sorption sites in the soil. However, the results of the approximation showed a lower affinity of Cd, Mn and Ni for the Fluvisol and a better stability and a lower bioavailability of these elements in the Chernozem. In the case of Pb and Cu, no significant changes were observed in PM-enriched soils regardless of the soil properties. 相似文献