铬在土壤中的吸附解吸研究进展

对铬在土壤中的吸附解吸研究进行了综述,土壤中铬的吸附解吸机理包括非专性吸附(离子交换吸附)、专性吸附以及物理表面吸附,分别对pH、氧化还原电位、土壤组分(土壤矿物和有机质)、竞争离子以及离子强度等因素对铬吸附解吸的影响作了论述。文章进一步描述了土壤中铬吸附解吸的数学模型Freundlich方程、Langmuir方程、一级动力学模型、金属-腐殖酸模型(one-sitemodel)和表面络合模型-扩散层模型(DLM)等的研究情况,并对今后的研究方向进行了探讨。     

1,1,2,2-四氯乙烷在土壤中的吸附解吸研究及解吸滞后的新型模型模拟

采用室内实验方法,研究了1,1,2,2-四氯乙烷（1,1,2,2-tetrachloroethane,1,1,2,2-TeCA）在4种土壤上的吸附和解吸行为,并用一种新型解吸模型——＂双元平衡解吸（Dual-EquilibriumDesorption,DED）模型＂对其解吸行为进行了预测。结果表明,1,1,2,2-TeCA在4种土壤上的吸附符合传统的线性吸附模型,lgKoc的平均值为1.86;解吸行为则表现出明显的滞后现象,解吸后的lgKo（c平均值约为4.88）显著大于初始值,且与吸附相污染物的初始浓度、土壤性质无相关性。DED模型比传统线性模型能更好地拟合TeCA在土壤中的解吸滞后现象。     

四氯乙烯和萘在氧化前后的含水层土壤上的吸附 与加标解吸研究

采用批量平衡实验法研究了四氯乙烯和萘在过氧化氢氧化前后含水层土壤上的吸附。原土经过氧化氢处理后有机质含量明显降低,但是处理前后的土样对四氯乙烯和萘的吸附差别极小。过氧化氢对原土中极性官能团的破坏使原土中的大分子有机质变为小分子的可溶性有机质离开体系,造成土壤有机质含量降低。这些具有极性官能团的大分子有机质对研究的两种化合物的吸附贡献很小。在调节液固比使各种单一体系中的液相浓度差异达到一至两个数量级的情况下,加标解吸体系下的等温线仍表现为非常规的近似水平线,说明液相浓度的降低不足以使土壤中吸附的化合物发生解吸。这一结果从另一侧面说明两种目标物在研究土壤上的吸附是以在致密有机相上的吸附为主,而这部分有机质不会被过氧化氢所氧化。因此,在评估污染土壤对地下水的危害时,需慎重使用通过吸附实验得到并基于有机质总量的分配系数。     

菜园土对铅的吸持解吸特性研究

研究结果表明,湖南几种常见的菜园土壤对铅的吸持量大小顺序为：红灰菜园土〉紫泥菜园土〉黄沙菜园土〉红菜园土。后３种土壤对铅的吸持过程均可用Ｌａｎｇｍｕｉｒ、Ｆｒｅｕｎｄｌｉｓｈ和Ｔｅｍｋｉｎ方程来描述;红菜园土和黄沙菜园土的最大吸持量是５５８８．８８ｍｇ／ｋｇ和８５１６．４６ｍｇ／ｋｇ;除红灰菜园土以外,另外３种土壤的解吸量及解吸率都随吸持铅量的增大而大。     

农田土壤中生物质炭的老化及其对有机污染物吸附-解吸影响的研究进展

生物质炭独特的表面性质、形貌结构及丰富而离散的孔隙系统使其对有机污染物具有良好的持留与吸附作用,可望用于土壤污染控制与修复。在田间条件下,进入土壤的生物质炭自身不稳定组分会发生转化、淋溶,并与土壤发生相互作用出现老化现象,导致生物质炭的化学与物理性质发生显著变化。生物质炭在土壤中的老化过程具有复杂性和多样性,主要包括:生物质炭化学性质的变化,如无机元素的流失、表面官能团组成的变化以及部分矿化反应;生物质炭物理性质的改变,主要是土壤有机质和矿物质对生物质炭的包覆作用造成生物质炭的孔隙特征发生改变。生物质炭在土壤中的老化可能会导致有机污染物的吸附-解吸行为发生改变,且受土壤、生物质炭以及污染物性质的影响较大。本文综述了生物质炭在农田土壤中的老化机理及主要影响因素研究方面的进展,总结了生物质炭在土壤中的老化对有机污染物吸附-解吸行为的影响,提出了尚待解决的相关前沿科学问题。     

Comparison of Four Equations to Describe the Kinetics of Lead Desorption from Soils

The rate of Pb desorption was investigated from clay (Silty clay, Torrifluvent), CaCO₃-rich (Sandy clay, Calciorthid), and sandy (Sandy loam, Quartzipsamment) soils at two different temperatures. Lead has not been released from CaCO₃-rich soils which suggests irreversible Pb sorption by the soil. The desorption was quite hysteretic from sand and clay soils. The total amount of Pb released from the clay soil exceeded that released from the sandy soil. The lower Pb desorption associated with the sandy soil is probably due to its higher calcium carbonate content relative to the clay soil. The kinetics of Pb desorption were evaluated using the Elovich, modified Freundlich, parabolic diffusion, and first order equations. The first order and parabolic diffusion equations adequately described the kinetics of Pb desorption from clay and sandy soils under isothermal conditions. The choice of first order and parabolic equations among others investigated was based on the goodness of fit and the more scientific theoretical assumptions of the equations. The apparent Pb diffusion rate coefficient (D_d) and desorption rate coefficient (k_d) values from the clay and sandy soils increased with increasing temperature.     

Zinc Sorption in Selected Soils

Abstract

The adsorption of nutrient elements is one of the most important solid‐ and liquid‐phase interactions determining the retention and release of applied plant nutrients and the efficiency of fertilization. The study showed that the soils with high cation exchange capacity (CEC), CaCO₃, organic matter contents, and heavy texture adsorbed more zinc (Zn). The alkaline soils from Pakistan adsorbed more Zn than English acidic soils. Langmuir and Freundlich isotherm fit was excellent, and r² values for the Langmuir isotherm were highly significant (r²=0.84 to 0.99). The Langmuir b values, representing the adsorptive capacity of a soil, increased as the texture fineness increased in the soil, with increases in the concentration of adsorptive material (such as organic matter and CaCO₃) and with increases in CEC and pH. The alkaline soils from Pakistan had higher bonding energy constant and higher log Kf values than the acidic English soils. Sequential extraction of Zn in these soils showed that most of the Zn was held in CaCO₃ pool in the alkaline soils, whereas in acidic soils adsorbed Zn was in exchangeable form.     

Adsorption and Desorption of Copper in Pasture Soils

Abstract

Copper (Cu) is bound strongly to organic matter, oxides of iron (Fe) and manganese (Mn), and clay minerals in soils. To investigate the relative contribution of different soil components in the sorption of Cu, sorption was measured after the removal of various other soil components; organic matter and aluminum (Al) and Fe oxides are important in Cu adsorption. Both adsorption and desorption of Cu at various pH values were also measured by using diverse pasture soils. The differences in the sorption of Cu between the soils are attributed to the differences in the chemical characteristics of the soils. Copper sorption, as measured by the Freundlich equation sorption constants [potassium (K) and nitrogen (N)], was strongly correlated with soil properties, such as silt content, organic carbon, and soil pH. The relative importance of organic matter and oxides on Cu adsorption decreased and increased, respectively, with increasing solution Cu concentrations. In all soils, Cu sorption increased with increasing pH, but the solution Cu concentration decreased with increasing soil pH. The cumulative amounts of native and added soil Cu desorbed from two contrasting soils (Manawatu and Ngamoka) during desorption periods showed that the differences in the desorbability of Cu were a result of differences in the physico‐chemical properties of the soil matrix. This finding suggests that soil organic matter complexes of Cu added through fertilizer, resulted in decreased desorption. The proportions of added Cu desorbed during 10 desorption periods were low, ranging from 2.5% in the 24‐h to 6% in the 2‐h desorption periods. The desorption of Cu decreased with increasing soil pH. The irreversible retention of Cu might be the result of complex formation with Cu at high pH.     

湿地沉积物磷的吸附与解吸研究

采用恒温培养法研究美国纽约Pelham Bay Park 6种典型淡水湿地沉积物中磷的吸附与解吸行为及其动力学过程。结果表明:湿地沉积物具有强烈吸附溶液中磷的功能,随着溶液中磷浓度的增加,吸附量增大;但是湿地沉积物也有释放磷到溶液中去的功能,释放量为0~41.19 mg/kg,与沉积物吸附磷量的关系不大,沉积物释放磷与沉积物的特性有关。衡量一种淡水湿地沉积物的除磷能力,可根据沉积物最大吸附磷量和吸附解吸附平衡浓度(EPC0)来衡量,6种沉积物中,磷的最大吸附能力强弱依次是:S1>S2>S3>S6>S5>S4;S1沉积物吸附磷的最大量为500 mg/kg。各沉积物的平衡浓度相差很大,S4的吸附与解吸附平衡浓度最高,其值为166.00μg/L,而S2的吸附与解吸附平衡浓度最低,其值为0.36μg/L。低的EPC0值表明,沉积物有很强的吸附磷的能力,故S2湿地生态系统有非常强的除磷能力。     

The Role of Soil Properties in Pyrene Sorption and Desorption

Soil type will greatly affect the sorption and subsequent desorptionof hydrophobic contaminants. To gain a better understanding of theimpact of soil type on sorptive behavior, the sorption-desorption of pyrene (PYR) with three different soils was studied. The first soil originated from Colombia and is classified as silty sand with3.54% soil organic matter (SOM) and 18% clay materials (<2 microns). The New Mexico soil is a sandy lean clay comprisedof 8.4% SOM and 10% clay. The last soil originated fromOhio and is a silty sand with 1.84% SOM and 9.6% clay. Based on soil mineralogy and sorption-desorption isotherms,the Colombia soil had the greatest binding potential followedby the New Mexico and Ohio soils. The Freundlich model couldfit both the Colombia and New Mexico soils. For the Ohiosoil, a two-stage Freundlich model was required. For allthree soils, PYR desorption was slow and resistant, anddepicted an apparent hysteresis. The extent of sorption-desorption for each soil was attributed to its individual classification.For instance, the SOM present in the New Mexico soil (8.4%) enabled a relatively easy desorption in comparison to the other two soils. For the Ohio and Colombia soils, the interaction with the clay fractions rendered a stronger sorptive bond.     

Differential Sorption Behavior of Cadmium,Lead, Zinc,and Copper in Some Tropical Soils and Their Environmental Implications

This study evaluated cadmium (Cd), lead (Pb), zinc (Zn), and copper (Cu) sorption characteristics of three tropical soils. Data obtained conformed to Freundlich sorption model and the S-shaped isotherm curve. Sorption efficiency of Zn and Pb were highest in alkaline soil while slightly acid soil had the highest Cd and Cu sorption efficiency for monometal sorption. In competitive sorption, metals were more sorbed in slightly acid soil while the least efficiency was recorded in acid soil. Distribution coefficient; K_d (average across soil types) in monometal sorption followed the order: Pb > Zn > Cd > Cu. For competitive sorption, the order was Zn > Pb > Cu > Cd. When in competition, Cd was preferentially sorbed in slightly acid and alkaline soils and Zn for acid soil. Conclusively, lead is more in equilibrium solution when in competition with Cd, Zn and Cu making it potential agent of soil and groundwater pollution.     

Sorption and Desorption Behavior of FTuoroquinolone Antibiotics in an Agricultural Soil

<正>Dear Editor,Fluoroquinolones(e.g.,ciprofloxacin(CIP),enrofloxacin(ENR),and levofloxacin(LEV))are an extensively used family of antibiotics prescribed for various infections;however,they are also increasingly used     

熟污泥改性黄土对镉的吸附解吸特征

使用序批实验方法,研究熟污泥改性黄土对镉(Cd)的吸附解吸特征。结果表明:Cd初始添加浓度大于20 mg/L,供试改性黄土对Cd的吸附等温线发生显著变化;Freundlich型吸附等温式是描述供试改性黄土对Cd吸附过程的最佳模型。各土样对Cd的解吸量与吸附量的关系可以用幂函数很好地描述。随着土样中熟污泥含量的增加,Cd的吸附固定作用增强。有机质成分是影响供试土样Cd固定能力最大的因素。     

Multi-Step Competitive Sorption and Desorption of Chlorophenols in Surfactant Modified Montmorillonite

Single- and bi-solute sorption and desorption of 2,4-dichlorophenol (2,4-DCP) and 2,4,5-trichlorophenol (2,4,5-TCP) in montmorillonite modified with hexadecyltrimethylammonium (HDTMA) were investigated using multi-step sorption and desorption procedure. Effect of pH on the multi-step sorption and desorption was investigated. As expected by the magnitude of octanol-water partition coefficient, K _ow , both sorption and desorption affinity of 2,4,5-TCP was higher than that of 2,4-DCP at pH 4.85 and 9.15. For both chlorophenols, the protonated speciation (at pH 4.85) exhibited a higher affinity in both sorption and desorption than the predominant deprotonated speciation (about 95% and 99% of 2,4-dichlorophenolate and 2,4,5-trichlophenolate anions at pH 9.15, respectively). Desorption of chlorinated phenols was strongly dependent on the current pH regardless of their speciation in the previous sorption stage. Freundlich model was used to analyze the single-solute sorption and desorption data. No appreciable desorption-resistant (or non-desorbing) fraction was observed in organoclays after several multi-step desorptions. This indicates that sorption of phenols in organoclay mainly occurs via partitioning into the core of the pseudo-organic medium, thereby causing desorption nearly reversible. In bisolute competitive systems, sorption (or desorption) affinity of both chlorophenols was reduced compared to that in its single-solute system due to the competition between the solutes. The ideal adsorbed solution theory (IAST) coupled to the single-solute Freundlich model successfully predicted bisolute multi-step competitive sorption and desorption equilibria.     

三种水稻土对磷的吸附解吸特性

实验研究了三种不同水稻土磷等温吸附及解吸的情况,并对影响等温吸附特性的因素做了相关探讨。结果表明:三种水稻土磷吸附曲线与简单的Langmuir等温吸附方程极为吻合,磷的解吸曲线与Langmuir等温方程也具备较好的吻合性。供试样品的相关系数均达到显著水平。土壤物理性粘粒含量显著影响土壤最大吸磷量,但对土壤磷的解吸量没有显著影响。     

磺胺嘧啶在土壤及土壤组分中的吸附/解吸动力学

抗生素在土壤中的吸附/解吸及迁移过程受其理化性质的强烈影响,其中土壤中的矿物成分,如高岭石、蒙脱石及腐殖酸等是重要控制因素。本文主要研究了磺胺嘧啶在土壤、高岭石、蒙脱石和腐殖酸中的吸附/解吸动力学过程,并对反应前后的高岭石、蒙脱石和腐殖酸进行傅里叶红外光谱(Fourier transform infrared, FTIR)表征,探讨其可能的吸附机理。结果表明:磺胺嘧啶的吸附(解吸)动力学过程,可以分为快速吸附(解吸)、吸附解吸动态平衡和吸附(解吸)平衡3个阶段;磺胺嘧啶在土壤及其3种组分中的吸附(解吸)均可在24 h内达到平衡,其浓度高低会导致土壤及其组分的吸附差异,不同土壤组分中的官能团含量、带电性质及氢键是造成吸附差异的主要原因;分别用伪一级动力学模型、伪二级动力学模型和Elovich模型对其吸附过程进行拟合,其动力学吸附过程更符合伪二级动力学模型,R20.99,主要受控于物理化学吸附;FTIR图谱表明磺胺嘧啶与高岭石以物理吸附为主,并有少量氢键作用,与蒙脱石之间主要以氢键作用完成吸附,而在腐殖酸中存在表面络合和π–π共轭作用。     

诺氟沙星在胡敏酸上的吸附热力学与动力学特征研究

根据OECD Guideline106批平衡实验,研究了诺氟沙星在胡敏酸上的吸附热力学和动力学,并探讨了其可能吸附机理。结果表明,诺氟沙星在经过约12h的快速吸附阶段后,进入缓慢吸附阶段,其吸附平衡时间为48h。伪二级动力学方程能够较好地描述不同pH条件下诺氟沙星在胡敏酸上的吸附动力学特性。诺氟沙星在胡敏酸上的吸附等温线符合Freundlich方程,该方程的拟合系数1/n〈0.5,表明诺氟沙星在胡敏酸上为非线性吸附。ΔH0=-48.85kJ·mol-1和ΔG0〈0,表明诺氟沙星在胡敏酸上的吸附是自发进行的放热过程,且离子交换是其主要吸附机理,同时也可能存在着偶极间作用力、氢键力和电荷转移等吸附机理;ΔS0〈0表明吸附过程中熵在减小。吸附位点的能量随着吸附量的增大而降低,也表明胡敏酸的异质性和吸附的非线性。     

土壤不同粒径组分对菲的吸附解吸行为的研究

有机污染物在土壤环境中的行为主要取决于它们与土壤不同组分之间的相互作用,土壤不同粒径组分中有机质的含量和结构特征以及矿物组成不同,它们对有机污染物的环境行为影响也不同。本研究用物理方法将两种不同类型土壤水稻土(SEBC-07)和红壤(SEBC-13)分成粒径大小不同的土壤组分(<2μm、2~20μm、20~54μm、54~105μm、105~280μm、>280μm),研究了它们对菲的吸附解吸行为。SEBC-07土样不同粒径组分对菲的吸附容量(Kf)从大到小顺序为:2~20μm、20~54μm、54~105μm、<2μm、>105μm;SEBC-13土样不同粒径组分的Kf值从大到小顺序为:20~54μm、<2μm、2~20μm、54~105μm、105~280μm、>280μm。除<2μm和20~54μm的粒径组分外,有机质含量较高的水稻土不同粒径组分对菲的吸附容量都明显高于有机质含量较低的红壤。两种土壤20~54μm组分的Koc值都最大,然后向粒径增大和减小的方向都逐渐降低。不同粒径组分的Kf和Koc值与它们的理化性质(有机碳含量、比表面积)都没有显著的相关性。两种土壤的不同粒径组分对菲的解吸都有不同程度的滞后现象。