有潜在性的大孔吸附树脂模拟植物根系分泌有机酸吸附的方法

为探索一种根系分泌物富集的方法,用静态吸附法,通过研究HPD-400型大孔吸附树脂对水溶液中柠檬酸、苹果酸和酒石酸的吸附行为,模拟大孔吸附树脂对根系分泌物收集液中主要有机酸吸附的结果表明,相同条件下,HPD-400型大孔吸附树脂对3种有机酸的吸附强度依次为柠檬酸>苹果酸>酒石酸;它对各有机酸的吸附能力随各有机酸浓度的升高而增加,随温度的降低而增加;对各有机酸的吸附均符合Freundlich等温吸附方程,且表现为优惠吸附。试验表明,用HPD-400型大孔吸附树脂可作为根系分泌物的富集材料。     

天鹅湖沉积物对磷的吸附动力学及等温吸附特征

以荣成天鹅湖这一天然泻湖为研究对象,研究了6个样点沉积物对磷的吸附动力学曲线和等温吸附方程,并分析了沉积物理化性质与磷吸附参数间的关系.结果表明,天鹅湖不同区域沉积物对磷的吸附动力学均符合二级动力学方程,吸附反应主要在前10h内完成,且0～2h内反应迅速.根据Langmuir模型,6个样点沉积物对磷的理论吸附容量(Qmax)的范围为294.12～1 111.11 mg/kg,其中湖区北部和中部沉积物的吸附能力高于南部.沉积物对水体中磷的吸附解吸平衡浓度(EPC0)的变幅为0.002 ～ 0.033 mg/L,其与沉积物本底吸附态磷(NAP)呈较弱的正相关关系.本研究条件下,大部分样点的EPC0小于上覆水中磷的浓度,其中湖区西北部和东南部沉积物中磷具有向上覆水体释放的趋势.沉积物的NAP与总氮、有机质、活性铝和黏粒间均呈显著正相关,Qmax与铁铝结合态磷、有机质、活性铝和粉粒间呈显著的正相关关系.活性铝、有机质和粒度是影响沉积物磷吸附的主要因素.     

苄嘧磺隆在几种氧化物表面的吸附及氯离子对吸附的影响

 利用平衡吸附法研究了苄嘧磺隆在高岭土、针铁矿、水铁矿、非晶型氢氧化铝及水钠锰矿表面的吸附以及氯离子对吸附的影响。结果表明 ,供试粘土矿物及氧化物对苄嘧磺隆的吸附均符合Langmuir方程 ,最大吸附量大小顺序为 :非晶型氢氧化铝 >针铁矿 >水铁矿 >水钠锰矿 >高岭石 ,且吸附量随氯离子浓度的增加而降低。其中在非晶型氢氧化铝和针铁矿表面的降幅较大     

Cd/Cu/Pb对磺胺嘧啶在土壤中吸附迁移的影响

通过室内批平衡实验和土柱出流实验,探讨了不同浓度镉(Cd)及相同浓度的Cd、铜(Cu)、铅(Pb)对磺胺嘧啶在土壤中吸附、迁移的影响,并分别用Freundlich、Langmuir、Linear方程及Hydrus-1D中的单点和两点吸附模型模拟其在土壤中的吸附、运移过程。结果表明:当Cd浓度为10.0mg·kg~(-1)时促进磺胺嘧啶的吸附;Cd浓度为1.0、300.0mg·kg~(-1)时抑制磺胺嘧啶吸附;Cd浓度为100.0 mg·kg~(-1)时对磺胺嘧啶的吸附无影响;300 mg·kg~(-1)的Cd、Cu、Pb存在时,磺胺嘧啶吸附量大小顺序为:CdCuPb。土柱出流实验中,当Cd浓度为10.0mg·kg~(-1)时,磺胺嘧啶在土柱中的迁移速度最慢,其他浓度对迁移影响不明显;Cd、Cu、Pb相比较而言,Cu存在时磺胺嘧啶的迁移最快,Cd存在时迁移最慢。在对静态吸附特征的拟合过程中,Linear方程拟合效果最好,决定系数R~2均在0.98以上;Hydrus-1D模拟时,两点模型可更好地拟合磺胺嘧啶的运移特征,R~20.907,均方根误差RMSE0.051,瞬时吸附f所占分数较高,说明磺胺嘧啶在迁移过程中存在较大程度的瞬时吸附。     

广东省香蕉主产区蕉园土壤养分的吸附特性研究

为了探明广东省香蕉主产区蕉园土壤对各主要营养元素的吸附特点,本论文应用土壤养分状况系统研究法对广东省番禺南沙点、东涌点和灵山点、高州沙田点、博罗长宁点、四会大沙点及中山横档点七个有代表性的蕉园土壤进行了系统研究。结果表明:(1)蕉园土壤对磷的吸附能力大小顺序为:博罗长宁>番禺灵山>番禺南沙>四会大沙>中山横档>番禺东涌>高州沙田。(2)蕉园土壤对钾的吸附能力大小顺序为:中山横档>番禺南沙>番禺灵山>番禺东涌>博罗长宁>四会大沙>高州沙田。(3)蕉园土壤对硫的吸附能力大小顺序为:高州沙田>番禺灵山>番禺东涌>中山横档>博罗长宁>番禺南沙>四会大沙。(4)蕉园土壤对硼的吸附能力大小顺序为:博罗长宁>番禺灵山>四会大沙>番禺南沙>中山横档>高州沙田>番禺东涌。(5)番禺南沙和东涌点蕉园土壤对锰的吸附固定能力很强;番禺灵山点蕉园土壤对铜的吸附强于番禺南沙点,但两者都非常弱;番禺南沙和灵山点蕉园土壤对锌的吸附较强,番禺东涌点蕉园土壤则较弱。     

活性炭吸附痕量银的研究

在静态、动态吸附条件下，分别选用果壳类净水用活性炭和煤质净水用活性炭对胶片工业废水中的痕量银的吸附行为进行了研究．结果表明，废水中的银浓度可降至＜５０ｐｐｂ，活性炭对银的吸附量达到３～５ｍｇ／ｇ．微孔发达的活性炭更适于吸附废水中的痕量银．随着银液浓度的升高，银液量增大，活性炭吸附能力增加．银液的最佳吸附ｐＨ值是５．     

Removal of trichloroethylene from aqueous solution by pyrolyzed Japanese cedar bark

The bark of Japanese cedar (Cryptomeria japonica D. Don) was heated in an N₂ atmosphere at 300–900C for 3h to investigate the surface properties of the pyrolyzed residuces and their ability to remove trichloroethylene (TCE) from aqueous solutions. The specific surface areas (S _N) and total pore volumes (V _N) of the pyrolyzed barks steadily increased with rising pyrolysis temperature; no significant differences in the average pore diameters (D _N) were observed at higher temperatures (600–900C). The adsorption capacities of the pyrolyzed residues for TCE were determined under batch mode conditions using an aqueous solution containing 500g TCE dm^–3. The adsorption data were well fitted to the Freundlich equation. The adsorption capacity of the bark pyrolyzed at 900C was about five times larger than that of commercial activated carbon.This study was presented at the 10th International Symposium on Wood and Pulping Chemistry, Yokohama, June 1999     

Transport and adsorption of antibiotics by marine sediments in a dynamic environment

Background, aim, and scope  Bed sediments are the major sink for many contaminants in aquatic environments. With increasing knowledge of and research on the environmental occurrence of antibiotics, there has been growing interest in their behaviour and fate in aquatic environments. However, there is little information about the behaviour of antibiotics in a dynamic water/sediment environment, such as river and coastal marine water. Therefore, the aims of the present study were: (1) to study the transport and distribution of four common antibiotics between water and sediment in both dynamic and quiescent water/sediment systems and (2) to understand the persistence and possible degradation of the four antibiotics in the two different systems. Materials and methods  A lid-driven elongated annular flume, designed to reduce the centrifugal effect, was used to simulate a dynamic water environment. In addition, a quiescent water/sediment experiment was conducted for comparison with the dynamic water system. The seawater and sediment, used in both experiments of flowing and quiescent water/sediment systems, were collected from Victoria Harbour, a dynamic coastal environment in an urban setting. The four antibiotics selected in this study were ofloxacin (OFL), roxithromycin (RTM), erythromycin (ETM), and sulfamethoxazole (SMZ), the most commonly used antibiotics in South China. Results and discussion  Antibiotics in an overlying solution decreased very quickly in the flume system due to the sorption to suspended particles and surface sediment. There were significant differences in the adsorption of the four antibiotics in sediment. OFL showed a high tendency to be adsorbed by sediment with a high K _d value (2980 L/Kg), while the low K _d values of SMZ indicated that there was a large quantity in water. The four antibiotics reached a depth of 20–30 mm in the sediment over a period of 60 days in the flume system. However, the compounds were only found in surface sediment (above 10 mm) in the quiescent system, indicating the influence of the dynamic flume system on the distribution of antibiotics in sediment. OFL showed a moderate persistence in the dynamic flume system, while other three antibiotics had less persistence in sediment. However, all of the four compounds showed moderate persistence in the quiescent system. Recommendations and perspectives  The study showed the rapid diffusive transfer of antibiotics from water to sediment in the dynamic flume system. The four antibiotics exhibited larger differences in their adsorption to sediment in both dynamic and quiescent systems due to their different K _d values. The high sorption of antibiotics to marine sediment may reduce their availability to benthic invertebrates.     

Interactive effects of organic acids in the rhizosphere

Organic acids released into the rhizosphere may perform many beneficial functions to the plant including metal detoxification and enhancement of nutrient acquisition. Typically, these organic acids are studied in isolation; however, roots simultaneously exude a cocktail of organic acids and other substances, and their combined impact on rhizosphere processes may be quite different. It has been hypothesized that some exudates may play secondary roles (e.g. inhibitors of microbial activity, blockage of sorption sites), which might enhance the longevity and nutrient-mobilization capacity of others. Here we investigated how the decomposition, sorption and P-solubilizing effects of citrate, malate and oxalate are affected by the presence of malonate and shikimate. We found that in a range of agricultural soils the decomposition of citrate, malate and oxalate was rapid, but not influenced by the presence of large quantities of shikimate or malonate. This suggests that the individual organic acids are taken up by different transport mechanisms or components of the microbial community. At large concentrations, malonate decreased sorption of citrate, malate and oxalate on the soil, whilst shikimate had little effect. The capacity of citrate, malate and oxalate to desorb P was significantly greater in cocktails containing malonate compared with the single organic acid; no effect was seen with shikimate. We conclude that neither malonate nor shikimate at realistic concentrations will significantly affect the biodegradation of citrate, malate or oxalate in the rhizosphere, and while malonate did enhance P desorption, this effect is additive rather than synergistic. Overall, we found little evidence that malonate and shikimate act as secondary regulators of citrate, malate and oxalate behavior in soil.     

Effect of Soil Properties on Boron Adsorption and Release in Arid and Semi-Arid Benchmark Soils

The adsorption isotherms indicated that the adsorption of boron (B) increased with its increasing concentration in the equilibrium solution. The Langmuir adsorption isotherm was curvilinear and it was significant when the curves were resolved into two linear parts. The maximum value of adsorption maxima (b1) was observed to be 7.968 mg B kg^?1 in Garhi baghi soil and the bonding energy (k) constant was maximum at 0.509 L mg^?1 in Jodhpur ramana soil. The Langmuir isotherm best explains the adsorption phenomenon at low concentrations of the adsorbent, which of course was different for different soils. There was significant correlation between b1 and clay (r = 0.905**), organic matter contents (r = 0.734*), and cation exchange capacity (CEC; r = 0.995**) of soils. A linear relationship was observed in all the soils at all concentration ranges between 0 and 100 mg B L^?1, indicating that boron adsorption data conform to the Freundlich equation. Soils that have a higher affinity for boron adsorption, like Garhi baghi, tended to desorb less amount of boron, that is, 43.54%, whereas Ballowal saunkhari desorbed 48.00%, Jodhpur ramana 48.42%, and Naura soil 58.88% of the adsorbed boron. Boron desorption by these soils is positively and significantly correlated with the sand content (r = 0.714**) and negatively with clay content (r = ?0.502*) and CEC (r = ?0.623**). The maximum value of 37.59 mg kg^?1 for desorption maxima (Dm) was observed in Garhi baghi soil and also a constant related to B mobility (Kd) was found to be maximum in Garhi baghi (0.222 L kg^?1) soil Note: *P<0.05; ^**P<0.01.