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1.
Dissolved organic matter (DOM) plays an important role in the process of mercury release from water body. In this study, the influence of DOM from different sources (DOMR, DOMS and DOMH, extracted from rice straw, compost and humic soil respectively) on mercury reduction was investigated. The molecular weight distribution and chemical composition of DOM from each source were determined using ultrafiltration membrane technique and elemental analysis respectively. The result showed that mercury release from DOM-added samples was much lower than the control; the lowest mercury release flux was observed in the treatment of DOMH, 25.02% of the control, followed by DOMS and DOMR, 62.46% and 64.95% of the control, respectively. The higher saturation degree and lower molecular weight of DOMH was responsible for the highest inhibition degree on the mercury release. The link between DOMH, concentration and mercury flux was also estimated and the result showed that mercury flux was increased with DOMH at lower concentration, while decreased with DOMH at higher concentration. Different mechanism dominated the influence of DOM on mercury release with variation of DOM concentration.  相似文献   

2.
Effects of dissolved organic matter (DOM) on adsorption and desorption of Hg were investigated in two kinds of soils, Xanthi-Udic Ferralosols (XUF) and Typic Purpli-Udic Cambosols (TPUC). The DOM was obtained from humus soil (DOMH), rice straw (DOMR), and pig manure (DOMP). The presence of DOM obviously reduced Hg maximum adsorption capacity with up to 40% decreases over the control, being an order of DOMH (250.00 mg/kg)< DOMR (303.03 mg/kg) < DOMP (322.58 mg/kg) < CK (control 416.67 mg/kg) for the XUF and ...  相似文献   

3.
水溶性有机质对土壤及底泥中汞吸附行为的影响   总被引:5,自引:0,他引:5  
以重庆市2种耕作土(黄壤和中性紫色土)及鱼塘底泥为试验材料,分别添加提取自腐殖土的DOM(DOMh),提取自稻草的DOM(DOM)和提取自污泥堆肥的DOM(DOMa),研究DOM对土壤及底泥中Hg的吸附行为的影响.结果表明.DOM对土壤及底泥中汞的吸附行为均有一定的抑制作用,这种抑制作用与DOM种类和试验材料的性质有关.添加不同来源的DOM,对Hg的抑制作用具体表现为:DOMh>DOMr>DOMa;添加同一种DOM时,对Hg吸附的抑制作用表现为鱼塘底泥>紫色土>黄壤.  相似文献   

4.
Norfloxacin (Nor) sorption and the factors (soil organic matter (SOM), pH, and exogenous copper (Cu) influencing the sorption were investigated in a black soil (soil B), a fluvo-aquic soil (soil F), and a red soil (soil R). With increasing of Nor concentrations, sorption amount of norfloxacin increased in both the bulk soils and their SOM-removed soils, but the sorption capacity in SOM-removed soils was higher than that of their corresponding bulk soils, indicating that the process of norfloxacin sorption in soil was influenced by the soil properties including SOM. The sorption data in all bulk soils and SOM-removed soils were fitted to Freundlich and Langmuir models. The correlation coefficients suggested that the experimental data fitted better to Freundlich equation than to Langmuir equation. Furthermore, the data from soil F and SOM-removed F could not be described by Langmuir equation. The norfloxacin sorption amount decreased in soil B and soil F, whereas it increased in soil R as solution pH increased. The maximum KD and KOC were achieved in soil R when the equilibrium solution pH was 6. And the norfloxacin sorption was also influenced by the exogenous Cu2+ ions, which depended on the soil types and Cu2+ concentrations. With increasing of Cu2+ concentrations in solution, generally, sorption amount, KD and KOC for norfloxacin in soils increased and were up to a peak at 100 mg/L Cu2+, and then the sorption amount decreased regardless of norfloxacin levels.  相似文献   

5.
刘纪阳  薛爽  张营  刘强 《环境科学学报》2021,41(5):1930-1939
以Suwannee River NOM (SRNOM)和Upper Mississippi River NOM (UMRNOM)两种水源溶解性有机质(DOM)为代表,利用500W高压氙灯作为光源模拟太阳光,进行室内光解实验.考察了冻融前后两种DOM在不同pH条件下的光谱特性参数及其与苊的结合常数(KDOC),同时通过苊...  相似文献   

6.
溶解性有机质(DOM)对水生环境中汞的赋存形态及转化过程具有极其重要的影响.但从更加微观的角度,如DOM的组成部分及其官能团特征等,却缺乏相关研究以阐明DOM影响汞形态转化的机制.为探究渔业养殖区来源于不同有机物(如残饵、鱼粪和底泥)的DOM各亚组分对水体中汞甲基化的影响,应用多级树脂联用技术,将渔业养殖区不同来源的DOM分离出6种亚组分,利用室内培养方式进行Hg2+的甲基化试验.傅里叶红外光谱分析结果表明,DOM中含有各种不同的官能团.亲水性组分主要包含羟基、羧基等极性较强的官能团;疏水性组分则包含一些无极性或者弱极性官能团如甲基、亚甲基和酚羟基等.疏水性亚组分是DOM的主要组成成分,其中又以疏水性碱性物质(HOB)为最,在有机物腐解过程中一直占有最大的比重.总体而言,疏水性有机组分对汞甲基化的促进作用显著高于亲水性有机组分;这主要是因为亲水性有机组分含有大量的羧基、羟基等官能团,可以更好地与活性Hg2+结合,降低甲基化反应的底物浓度,从而抑制甲基化发生.而疏水性组分对汞亲和性较弱,而且所含酚羟基以及还原性含硫基团等都可作为电子供体,从而促进汞甲基化的发生.从总体来说,在有机质腐解过程中,各种非同源有机质所形成的HOB对汞甲基化的促进作用不断增强.  相似文献   

7.
Sorption of tetrabromobisphenol A (TBBPA) by soil influences its fate and transport in the environment. The presence of dissolved organic matter (DOM) may complicate the sorption process in soil. The effects of DOM from sewage sludge on TBBPA sorption by three soils were investigated using batch equilibration experiments in the study. DOM was observed to be sorbed on the soils and the isotherms could be fitted by the Langmuir model. The effects of DOM on TBBPA sorption were dependent on the characteristics ...  相似文献   

8.
祝惠  阎百兴  张丰松  路永正  王莉霞 《环境科学》2010,31(10):2315-2320
为进一步揭示汞在松花江沉积物表面的环境行为,通过模拟实验,研究粒级、pH和溶解性有机质(DOM)对汞在松花江沉积物表面吸附-解吸量的影响.结果表明,不同粒级沉积物的吸附能力差别较大,本实验条件下,沉积物粒级越小,其吸附能力越强.在各种浓度的实验设计组中均有:pH由3.5升高至4.5时,吸附量增加,当pH4.5时,随pH的继续升高吸附量开始降低;沉积物中汞的解吸量随pH的增加呈先下降后上升的趋势变化,各体系的最小值均出现在pH5.柠檬酸对沉积物吸附汞的影响以抑制作用为主,其抑制作用强度与吸附体系中汞浓度有关;柠檬酸对解吸量的影响也比较明显,随着柠檬酸浓度的增加,对沉积物中汞解吸作用的影响表现为促进-抑制-稳定的变化趋势.因此,以上因素对汞在沉积物表面吸附-解吸的影响较大,在进行河流汞污染控制及突发污染事件处理时,有必要充分考虑以上因素的影响.  相似文献   

9.
以污水处理厂化学除磷工艺产生的常见化学磷(AlPO4和FePO4)沉淀为研究对象,考察了两种化学磷分别与剩余活性污泥(即生物污泥)混合厌氧发酵过程中化学磷和生物磷的释放情况.结果表明:在纯水中,AlPO4在强酸强碱条件下均能释出部分磷,FePO4只在强碱条件下才能溶解释磷.在(35±1)℃,不同pH值下将含AlPO4的混合污泥厌氧发酵时,强酸性厌氧发酵能释出较多的化学磷,但微生物活性被抑制,不利于发酵产酸;碱性发酵(pH=10~11)能释出28%~55%的化学磷,43%~49%的生物磷,总释磷量比中性条件下高17.5%~62.7%,同时利于发酵产酸,维持pH 10和11时产酸量分别比中性条件高233%和117%;对于含FePO4的混合污泥厌氧发酵,中性条件下即能释放FePO4中40%的磷和生物污泥中50%的磷,释磷量高于pH=11的碱性厌氧发酵释磷量.  相似文献   

10.
土壤有机质对土霉素在土壤中吸附-解吸的影响   总被引:12,自引:2,他引:12       下载免费PDF全文
采用批量平衡方法,研究了土霉素在原土及去除有机质土壤中的吸附和解吸.结果表明,土霉素在原土和去除有机质土壤中的吸附和解吸等温线均不同程度地偏离线性模型,其中Freundlich模型可以对吸附和解吸数据进行良好的非线性拟合,在不同土壤以及不同土壤处理中的拟合相关系数(r)均达到极显著水平.去除有机质能够降低土霉素在土壤中的吸附容量(lgKf),但增加了吸附强度(1/n).土霉素在土壤上的解吸过程存在明显的滞后现象,在所设土霉素浓度范围内,土霉素在褐土和红壤中的平均滞后系数(HIa)分别为0.039和0.015;去除有机质后的褐土和红壤对土霉素的解吸滞后现象显著增强(P<0.01),其HIa分别增加到0.068和0.028.  相似文献   

11.
农田灰钙土中有机质和碳酸钙对Zn吸附-解吸行为的影响   总被引:3,自引:0,他引:3  
采用序批平衡法,研究了Zn在去除有机质及去除碳酸钙前后灰钙土的吸附-解吸行为.结果表明,在试验土壤中吸附量均随着加入Zn浓度的增加而增加,且去碳酸钙土对Zn吸附固定能力明显低于灰钙土,即有机质对灰钙土Zn的吸附影响小于碳酸钙;去有机质及去碳酸钙前后灰钙土对Zn的吸附过程不适合用 Langmuir方程描述,而 Freundlich方程能够很好地拟合,调整后的决定系数R2¢均大于0.90,达到极显著水平(P<0.01);去除有机质和碳酸钙后灰钙土对Zn的解吸率都升高,且灰钙土去碳酸钙后解吸率略高于去有机质;去除有机质及碳酸钙前后灰钙土的解吸量均随吸附量的升高而升高,且去碳酸钙土解吸量最大,去有机质土次之,灰钙土最小;土壤有机质和碳酸钙对Zn均有较强的络合吸附效应,能有效降低Zn的迁移活性,从而促进吸附,抑制解吸.  相似文献   

12.
Effects of free iron oxyhydrates (Fed) and soil organic matter (SOM) on copper (Cu2+) sorption-desorption behavior by size fractions of aggregates from two typical paddy soils (Ferric-Accumulic Stagnic Anthrosol (Soil H) and Gleyic Stagnic Anthrosol (Soil W)) were investigated with and without treatment of dithionite-citrate-bicarbonate and of H2O2. The size fractions of aggregates were obtained from the undisturbed bulk topsoil using a low energy ultrasonic dispersion procedure. Experiments of equilibrium sorption and subsequent desorption were conducted at soil water ratio of 1:20, 25℃. For Soil H, Cu2+ sorption capacity of the DCB-treated size fractions was decreased by 5.9% for fine sand fraction, by 40.4% for coarse sand fraction, in comparison to 2.9% for the bulk sample. However, Cu2+ sorption capacities of the H2O2-treated fractions were decreased by over 80% for the coarse sand fraction and by 15% for the clay-sized fraction in comparison to 88% for bulk soil. For Soil W, Cu2+ sorption capacity of the DCB-treated size fraction was decreased by 30% for the coarse sand fraction and by over 75% for silt sand fraction in comparison to 44.5% for the bulk sample. Cu2+ sorption capacities of the H2O2-treated fractions were decreased by only 2.0% for the coarse sand fraction and by 15% for the fine sand fraction in comparison to by 3.4% for bulk soil. However, Cu2+ desorption rates were increased much in H2O2-treated samples by over 80% except the clay-sized fraction (only 9.5%) for Soil H. While removal of SOM with H2O2 tendend to increase desorption rate, DCB- and H2O2-treatments caused decrease in Cu2+ retention capacity of size fractions. Particularly, there hardly remained Cu2+ retention capacity by size fractions from Soil H after H2O2 treatment except for clay-sized fraction. These findings supported again the dominance of the coarse sand fraction in sorption of metals and the preference of absorbed metals bound to SOM in differently stabilized status among the size fractions. Thus, enrichment and turnover of SOM in paddy soils may have great effects on metal retention and chemical mobility in paddy soils.  相似文献   

13.
太湖沉积物磷形态及pH值对磷释放的影响   总被引:64,自引:3,他引:64  
对太湖不同营养水平和不同特征的 4 种沉积物的总磷、磷形态、粒径组成、化学组成进行了分析,模拟研究了不同 pH 值对上覆水体中总溶解性磷和溶解性活性磷含量的影响.结果表明,太湖沉积物样品总磷含量在 336.1~3408.01mg/kg,属于中富营养化到极富营养化水平.pH 值是影响磷释放的重要因素,碱性条件下,促进NaOH-P 的释放;酸性条件下,促进 HCl-P的释放.严重富营养化湖区沉积物的磷主要由无机磷组成,其中主要是 NaOH-P,该区中 pH值增加会导致磷释放量的大幅度增加,而 pH值下降对磷释放量的影响较小.中富营养化湖区沉积物的无机磷组成中,部分湖区 NaOH-P 含量高,部分湖区 HCl-P 含量高,所以该区中 pH 值变化对沉积物磷释放的影响,由于 NaOH-P 和HCl-P 含量不同而存在差异,NaOH-P含量较高,pH值增加会导致磷释放量的大幅度增加;HCl-P 含量较高,pH值下降会导致磷释放量的大幅度增加.  相似文献   

14.
以铜绿微囊藻为对象,研究了预氯化过程中藻胞内代谢物释放及铝盐混凝除藻过程中残留铝的变化规律.结果表明,氯投量对胞内物质释放量和释放有机物特征有重要影响.与未投加氯的对照体系相比,在较低氯投量时(1~2 mg·L-1),水中有机物浓度升高26%~31%,UV254值升高46%~49%,且有机物主要为中等分子量(2191、2830和3168 Da)和高芳香度的有机物.增大氯投量至3~4 mg·L-1,水中有机物浓度和UV254值有所下降;就不同分子量有机物而言,大分子量有机物(16304 Da)浓度升高而中等分子量有机物(2830、3168和6163 Da)浓度下降,且出现少量小分子量有机物(180 Da).分子量较大或芳香度较高的溶解性有机物在铝盐混凝中可被优先去除.释放到水中的蛋白质能与铝盐形成可溶性蛋白质-混凝剂复合物,从而导致出水铝浓度升高,但增大铝投量可在一定程度上降低残留铝浓度.  相似文献   

15.
采用密闭培养实验装置于室温(25℃左右)及pH为7.5条件下,对西湖底泥中有机质完全降解及转化为CO  相似文献   

16.
通过选择性去除土壤组分的方法,探讨了三峡库区消落带落干期3种典型土壤中有机质、铁氧化物组分对磷形态和磷吸附-解吸的影响.结果发现,三峡库区消落带落干期3种典型土壤去除的有机质以易氧化组分为主,去除有机质后,土壤中各种磷形态的含量变化较小.然而,去除游离铁氧化物后,土壤中各种磷形态的含量均发生明显降低.同时,去除有机质、游离铁氧化物组分后并未改变土壤中各种磷形态的相对大小顺序,均为:钙结合磷(Ca-P) > 有机磷(OP) > 铁/铝结合磷(Fe/Al-P).此外,黄壤(FJ)、紫色潮土(KX)和灰棕紫泥(FL)去除有机质后对磷的吸附能力较原始土壤仅分别降低0.5%、2.3%、6.5%(P=0.017<0.05,显著性差异),表明3种土壤中有机质组分对磷吸附的影响较小;而去除游离铁氧化物后对磷的吸附能力分别降低45.6%、51.7%、43.9%(P=0.004<0.05,显著性差异),表明土壤中游离铁氧化物组分是决定磷吸附大小的重要因素.另外,3种土壤去除游离铁氧化物后较原始土壤吸附磷的解吸能力明显增加,表明游离铁氧化物组分是控制3种土壤吸附磷的解吸的重要因素.FL土壤去除有机质组分后较原始土壤吸附磷的解吸能力略有降低,而KX和FJ土壤去除有机质组分后较原始土壤吸附磷的解吸能力无明显差异,表明有机质组分对土壤吸附磷的解吸的影响与土壤类型有关.  相似文献   

17.
采用密闭培养实验装置于室温(25℃左右)及pH为75条件下,对西湖底泥中有机质完全降解及转化为CO2和CH4的速率进行了模拟研究.结果表明,在西湖湖水现有供氧水平(50—86mg(O2)/L)条件下,底泥中有机质完全降解的速率最为缓慢,培养期间(42天)平均只有072mg(C)/(kg·d).当湖水供氧水平进一步上升(86→120→160mg(O2)/L),CO2释放速率增加,最大值可达到87mg(C)/(kg·周);当湖水供氧水平下降(86→0mg(O2)/L),CH4释放速率加快,最大值可达到46mg(C)/(kg·周).  相似文献   

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