共查询到17条相似文献，搜索用时 218 毫秒
1.
磷在"沉积物-自然生物膜-上覆水"三相体系中的迁移转化 总被引：1，自引：0，他引：1
地表水体中沉积物表面通常会附着一层自然生物膜,对上覆水-沉积物界面化学物质的迁移转化有着重要的影响.以往研究往往会忽略这一生物层面,因而,开展磷在"沉积物-自然生物膜-上覆水"三相界面之间的迁移转化研究具有重要的实际意义.以软性填料表面形成的自然生物膜模拟沉积物表层以及悬浮颗粒物表层的自然生物膜,开展磷在沉积物-自然生物膜-上覆水之间的迁移转化过程研究.结果表明:有无曝气情况下,自然生物膜界面的存在均能够显著降低上覆水中总磷、溶解态总磷、溶解态无机磷的含量,明显抑制沉积物中可交换态磷向上覆水释放.研究证明自然生物膜在水体磷的迁移转化中起着不可忽视的作用,在研究沉积物-上覆水界面之间磷的迁移转化行为时,要充分考虑自然生物膜界面的存在. 相似文献
2.
运河(杭州段)沉积物磷释放的模拟试验 总被引：18，自引：1，他引：18
采用室内模拟的方法研究了扰动情况下运河（杭州段）表层沉积物磷的释放对上覆水的影响以及投加石灰、投加三气氛发化铁、连续曝气、换水清洗等措施对沉积物磷释放的控制效果，研究表明，在扰动、开放体系条件下，运河（杭州段）沉积物磷释放导致的上覆水总磷浓度在释放初期最高，随时间逐渐下降，表现出净吸附，采集于有机污染较重河段的沉积物磷释放能力显著高于总磷含量较高但以重金属污染为主的河段的沉积物，上覆水投加石灰最终导致沉积物磷释放量的增加，投加三氯化铁显著降低了上覆水总磷浓度，上覆水连续曝气降低了上覆水的平衡磷浓度、换水清洗对上覆水磷浓度的降低效果是有限的，然而上述措施均未能将上覆水总磷浓度控制在V类水的浓度限定值以下，因此，就上覆水TP的浓度指标而言，运河（杭州段）沉积物的内源释放对其影响很大。 相似文献
3.
过氧化钙在处理厌氧底泥中的应用初探 总被引：1，自引：0，他引：1
为改善河道厌氧底质及内源氮、磷等营养盐释放问题,考察对沉水植被恢复的影响,研发可同步解决沉积物供氧和削减内源氮、磷释放的氧缓释材料.实验通过向沉积物-水界面处散点注射不同剂量的过氧化钙(Ca O2),研究界面处溶解氧的动态变化特征及表层沉积物与底层水体之间溶解态氮、磷的交换过程.结果表明:添加Ca O2显著提高了界面处底层上覆水溶解氧浓度,随着Ca O2浓度的增加溶解氧浓度增加,不同处理组之间具有显著差异;Ca O2对沉积物中PO3-4-P释放具有明显的抑制作用,且随Ca O2浓度的增加抑制效果愈加明显,上覆水中可溶性活性磷浓度最大可削减98%.实验开始时,磷释放速率可降至-241.916±22.501 mg/(m2·d),降幅最高可达到144%;Ca O2对沉积物NH+4-N释放的抑制效果不佳,上覆水中NH+4-N浓度随着时间的变化波动性较大,且有逐渐增大的趋势.另外,添加Ca O2会显著提高底层上覆水p H值,不同处理组之间差异显著,但当Ca O2投加量小于0.529 kg/m2时,不会对苦草种子的萌发生长有显著影响,p H值波动在可接受范围内(7.62~10.87).因此,结合污染沉积物的状况,适当地投加Ca O2有望同步解决底质厌氧、内源磷释放及后期沉水植被定植底质生境改善的问题,可推荐为一种黑臭污染底泥治理技术在实际的河道生态工程中应用,其适宜浓度为0.176 kg/m2左右. 相似文献
4.
为进一步了解人类活动及环境因子对太湖磷污染的贡献，揭示磷在太湖不同介质中的迁移转化规律，本文以太湖主要入湖湖区竺山湖、西部沿岸区、南部沿岸区和主要出湖湖区东太湖为对象，调查了表层水、上覆水、间隙水和沉积物中总磷(TP)分布的概况，分析了不同介质中磷的交换特征及其影响因素. 结果表明，表层水和上覆水TP浓度基本相当，平均值均为0.10 mg/L，上覆水和间隙水TP差异较大，间隙水平均浓度约为上覆水的7倍，表层沉积物TP含量为474~2160 mg/kg. 在本研究水域中，TP具有较强的沉积物吸附特性，沉积物作为“汇”的特征明显强于其“源”的特征，且磷的留存能力高度依赖于铁浓度. 空间分布上，入湖湖区磷污染程度明显高于出湖湖区，竺山湖和西部沿岸区存在较大的底泥污染释放风险，但竺山湖外源污染影响较内源污染更加突出，应列为当前太湖磷治理重点关注的区域，建议以控源截污作为竺山湖周边区域的治理重点. 西部沿岸区需注重外源和内源污染同步控制. 南部沿岸区周边区域需妥善处理好未来经济发展与废水排放负荷的关系. 相似文献
5.
以淮南后湖非稳沉采煤沉陷区沉积物-水体界面为研究对象,分析该湖未开发区(A区)、水产养殖区(B区)和水生蔬菜种植区(C区)3个功能区上覆水-间隙水-沉积物体系中氮、磷分布及其迁移特征.结果表明,氮、磷在不同水体界面的分布差异较大.其中上覆水中氮、磷浓度表现为A区B区C区;间隙水中氮、磷分布差异不显著,然而各功能区间隙水的氮、磷浓度明显高于上覆水,氮、磷主要由间隙水向上覆水中移动;沉积物中氮、磷含量以C区最高.后湖采煤沉陷区水体表现出氮污染、磷限制的现象. 相似文献
6.
为探究太湖梅梁湾水体及沉积物中微囊藻毒素（MC-LR、MC-RR、MC-YR）含量的垂向分布特征，于2018年5月采集梅梁湾6个点位表层水、上覆水、混合水、间隙水以及柱状沉积物样品，并采用超高效液相色谱-串联质谱法分析样品中微囊藻毒素的含量.分析结果表明：水体中（表层水、上覆水、混合水以及间隙水）MC-LR、MC-RR、MC-YR的浓度范围分别为11.80~1297.14、2.50~818.40、1.80~176.00 ng/L，表层水、上覆水以及混合水中MC-LR的浓度高于MC-RR和MC-YR，MC-RR和MC-YR之间差别较小，而间隙水中MCs三种异构体浓度大小顺序为：MC-LR > MC-RR > MC-YR；垂向分布上，间隙水中MCs异构体（MC-LR、MC-RR、MC-YR）浓度均远高于表层水、上覆水以及混合水，表层水MCs异构体浓度略高于上覆水，混合水MCs异构体浓度介于表层水和上覆水之间.对沉积物的研究发现，1~10 cm表层沉积物中MC-LR、MC-RR、MC-YR含量范围分别为0.60~26.95、0~0.90、0~8.10 ng/g，且1~10 cm层中MCs三种异构体平均含量大小顺序为：MC-LR > MC-YR > MC-RR，其中MC-LR、MC-RR、MC-YR的检出率分别为100%、70%、92%；垂向分布上，MC-RR含量较低且变化不大，而MC-YR和MC-LR含量均随沉积物深度的增加先升高后降低.相关性分析结果表明，表层水和混合水中MCs与总磷浓度呈显著正相关，而与总氮浓度无显著相关性；上覆水、间隙水以及沉积物中MCs与总氮、总磷浓度均呈显著正相关. 相似文献
7.
水丝蚓(Tubificid worms)扰动对磷在湖泊沉积物-水界面迁移的影响 总被引：20，自引：6，他引：14
为探讨水丝蚓(Tubificid worms)扰动对磷在湖泊沉积物-水界面间迁移的影响,选取太湖梅梁湾与大浦口两富营养化湖区为研究对象,通过室内培养实验,利用Rhizon间隙水采样器等技术,研究了水丝蚓扰动对太湖沉积物-水界面理化性质及溶解活性磷(SRP)在界面通量的影响.结果表明水丝蚓扰动能够增大表层沉积物含水率、氧化还原电位,减小间隙水中Fe2+浓度.水丝蚓没有显著改变梅梁湾间隙水中SRP浓度,同时促进了梅梁湾沉积物中SRP向上覆水的释放;但水丝蚓显著减小了大浦口间隙水中SRP浓度,并抑制了大浦口沉积物中SRP向上覆水的释放.水丝蚓扰动对磷在沉积物-水界面间迁移的不同影响可能是由沉积物中Fe2+含量差异较大造成的. 相似文献
8.
滇池水-沉积物界面磷形态分布及潜在释放特征 总被引：14，自引：3，他引：11
通过现场调查和室内模拟实验,对滇池35个上覆水-沉积物磷的分布特征以及沉积物中磷释放动力学特征进行研究,结果表明:滇池表层沉积物中不同形态磷含量表现为:有机磷(OP)(1482.49±1156.82 mg/kg)钙结合态磷(Ca-P)(865.54±558.40 mg/kg)金属氧化物结合态磷(Al-P)(463.77±662.18 mg/kg)残渣态磷(Res-P)(218.52±83.11 mg/kg)可还原态磷(Fe-P)(128.13±101.56 mg/kg)弱吸附态磷(NH4Cl-P)(2.26±3.05 mg/kg);滇池上覆水草海总磷浓度处于劣Ⅳ类水平,外海不同湖区总磷浓度介于Ⅳ~Ⅴ类之间;滇池水体中的磷以颗粒态磷含量最高;滇池表层沉积物中磷的释放是由快反应和慢反应两部分组成.释放过程主要发生在前8 h内;不同区域沉积物磷的最大释放速率、最大释放量、磷的释放潜力平均值均表现为:草海外海北部外海南部湖心区;滇池表层沉积物中磷的释放主要由NH4Cl-P、Fe-P、Al-P和OP进行,其中,NH4Cl-P和Fe-P所占比重较大;磷的释放与上覆水中溶解性总磷、溶解态无机磷和溶解态有机磷呈显著正相关,预示着上覆水中磷的迁移转化更多地受到水-沉积物界面浓度梯度的控制,进一步说明不能以总磷含量来评价湖泊磷素释放的状况,需与磷形态及分布特征相结合进行分析. 相似文献
9.
为了解东平湖菹草(Potamogeton crispus)腐烂分解对水体温室气体溶存浓度和界面扩散通量的影响,于2016年5-7月在东平湖菹草腐烂期采集上覆水和沉积物柱样,测定上覆水和孔隙水中温室气体(N_2O、CH_4和CO_2)的溶存浓度,采用Fick第一定律和双层模型计算沉积物-水-气界面扩散通量,同时分析上覆水和沉积物的理化性质,并采用网袋分解法于现场进行菹草腐烂分解试验,以探究东平湖菹草腐烂过程中温室气体溶存和扩散的主要影响因子及其主要来源.结果表明,菹草腐烂符合二次指数模型,分为快速衰减和慢速分解两个阶段;菹草腐烂过程中上覆水pH和亚硝态氮浓度表现为先降低后升高,而溶解氧、氨氮、硝态氮和可溶性正磷酸盐浓度则为先升高后下降,沉积物中铵态氮含量表现为先升高后降低,硝态氮为先降低后显著升高,有机质和p H呈降低-升高-降低的波动变化;上覆水中各温室气体浓度和水气界面扩散通量均表现为CO_2 CH_4 N_2O,其扩散通量分别为5862.9±5441.4、31.15±41.3和0.15±0.57μmol/(m~2·h),整体表现为大气温室气体的"源",并以碳排放为主;上覆水中N_2O浓度和水-气界面扩散通量均先降低后升高,孔隙水中N_2O浓度在快速和慢速分解阶段分别出现极大值(22.7和55.6 nmol/L),而其沉积物-水界面通量前期持续增加至腐烂结束后迅速降低;上覆水和孔隙水中CH_4浓度及其各界面通量均表现为前期略有降低后持续升高;上覆水中CO_2浓度和水-气界面通量表现为持续升高后降低并趋于稳定,而孔隙水中CO_2呈波动变化,在菹草腐烂初期向孔隙水扩散,后期向上覆水扩散.水温是影响上覆水中温室气体浓度和水-气界面通量的主要因素;沉积物是水体N_2O和CH_4的主要来源,孔隙水中浓度是控制其沉积物-水界面扩散的重要因素;而上覆水中CO_2呈现多源性,但以上覆水中有机物质的矿化为主. 相似文献
10.
湖泊水底Fe~(2+)和ΣS~(2-)浓度的快速增加是湖泛暴发最早发生于沉积物-水界面的主要前提,缺氧环境下水底扩散层附近Fe~(2+)和ΣS~(2-)的迁移是其在沉积物-水界面处稳定积累的重要原因.以蓝藻聚积水体沉积物-水界面为研究对象,应用湖泊过程模拟装置及间隙水被动采样等技术,重点研究了间隙水和底层上覆水中Fe~(2+)和ΣS~(2-)的垂向分布特征,并定量估算了二者的扩散通量及迁移方向.结果表明:湖泛样品水体沉积物-水界面处于典型的还原性环境,表层沉积物间隙水中Fe~(2+)和ΣS~(2-)浓度显著高于对照样品,二者在表层沉积物中积累趋势明显.湖泛水体沉积物-水界面处Fe~(2+)释放通量较高,表现出较强烈的自沉积物向上覆水方向的释放能力;而湖泛样品ΣS~(2-)在沉积物-水界面处释放通量为负,迁移方向为自上覆水向沉积物扩散.Fe~(2+)和ΣS~(2-)在湖泛水体沉积物-水界面处不同的迁移特征证明:缺氧/厌氧条件下,湖泊水体表层沉积物间隙水中高浓度Fe~(2+)向上覆水的扩散为湖泛致黑物质的形成提供了重要的物质基础;底层上覆水及界面水中SO~(2-)4在表层沉积物中被还原,为终端还原产物ΣS~(2-)为湖泛致黑物质的形成提供了另一重要物质来源. 相似文献
11.
Experimental study on phosphorus release from sediments of shallow lake in wave flume 总被引：2，自引：2，他引：2
Influence of wave on sediment resuspension and nutrients release from sediments, collected from Lake Taihu and Lake Chaohu, was studied in flume experiments. Under strong-wave conditions, concentrations of suspended solids (SS), total phosphorus (TP) and dissolved total phosphorus (DTP) in overlying water were increased significantly following the sediments re-suspension. During the experiments on sediments of Lake Taihu and Lake Chaohu, TP concentrations increased 6 times and 3 times, and DTP concentration increased 100% and 70% more than it in presuspension, respectively. Concentration of soluble reactive phosphorus (SRP) of experiment on sediment of Lake Taihu increased 25%. During the massive sediment suspension, the dissolved phosphorus in pore water and much of the phosphorus adsorbed by the sediment particles were released into overlying water. The phenomena in this wave flume experiment are quite similar to the situation observed in situ of Lake Taihu. The critical wave stresses of sediment re-suspension are nearly equal. The change of concentrations of SS, TP, and SRP was the same as that in situ situation. This study showed that concentrations of TP and SRP in lake water could be increased significantly by wave disturbance. Phosphorus release was significantly enhanced by wave disturbance at the beginning of massive sediment re-suspension, but decreased later. 相似文献
12.
Influence of wave on sediment resuspension and nutrients release from sediments, collected from Lake Taihu and Lake Chaohu, was studied in flume experiments. Under strong-wave conditions, concentrations of suspended solids (SS), total phosphorus (TP) and dissolved total phosphorus (DTP) in overlying water were increased significantly following the sediments re-suspension. During the experiments on sediments of Lake Taihu and Lake Chaohu, TP concentrations increased 6 times and 3 times, and DTP concentration increased 100% and 70% more than it in presuspension, respectively. Concentration of soluble reactive phosphorus (SRP) of experiment on sediment of Lake Taihu increased 25%. During the massive sediment suspension, the dissolved phosphorus in pore water and much of the phosphorus adsorbed by the sediment particles were released into overlying water. The phenomena in this wave flume experiment are quite similar to the situation observed in situ of Lake Taihu. The critical wave stresses of sediment re-suspension are nearly equal. The change of concentrations of SS, TP, and SRP was the same as that in situ situation. This study showed that concentrations of TP and SRP in lake water could be increased significantly by wave disturbance. Phosphorus release was significantly enhanced by wave disturbance at the beginning of massive sediment re-suspension, but decreased later. 相似文献
13.
波浪水槽中研究了小波掀沙(波高8.77cm,波周期0.8s)和大波掀沙(波高12.31cm和13.29cm,波周期1.0s)对太湖沉积物悬浮及N、P营养盐释放的作用规律.结果显示:小波掀沙时,底泥并未发生大量悬浮,SS浓度最高时仅13.6mg/L;大波掀沙时,底泥大规模悬浮,SS浓度最高达达245.2mg/L水体悬浮物、营养盐浓度变化滞后波高变化1h以上.当波高改变1h后,水体悬浮物、N、P营养盐浓度才改变到相应的平衡浓度.除总磷浓度显著提高外,小波掀沙对水体N、P浓度的影响很小,大波掀沙则显著提高了水体总氮、总溶解氮、总磷、总溶解磷、氨氮(NH4 -N)、溶解性活性磷(SRP),其中NH4 -N、SRP最大增幅达30％和20％.小波和大波掀沙过程中,水体溶解氧浓度均持续增加,掀沙2h后增高2mg/L,溶解性有机碳持续下降,2h后下降33％-51％.试验结果表明,掀沙过程中水体充氧及颗粒物的絮凝、吸附作用可能是限制NH4 -N、SRP浓度增高的重要因素之一. 相似文献
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15.
Investigation on the Pollution Potential of Waterworks Sludges Several contaminated sludges from water treatment plants with known or estimated concentrations of trace elements were investigated for their leaching characteristics and long-term stability using standard and advanced test procedures. Potentially hazardous elements in the sludge are zinc, nickel, and arsenic with concentrations of up to 1.2 g/kg dry matter (mass). Preliminary sorption tests with synthetic sludge components like iron hydroxide, manganese oxide, silicate clay minerals, and chitine powder as a model organic component showed that Cu is associated with the organic phase wheras arsenic is predominantly bound to the iron oxide minerals. The recently suggested pHstat test procedure was used to assess the leaching characteristics of metals at typical pH values. This procedure was compared with the DEV-S4 test, the current standard test in Germany, consisting of a simple lixiviation of the solids with water, without pH control. The pHstat test yields results which are much better to interprete than those obtained by the DEV-S4 procedure. The iron and manganese sludges are well buffered against changes in pH and redox potential so that low pH values and/or reducing conditions can hardly occur. Thus, in deposited material a sudden leaching of heavy metals is unlikely and due to the presence of iron and manganese oxides the pentavalent arsenic is protected against conversion into the highly mobile trivalent form at neutral to low pH. Co-deposition with reducing organic matter and alkaline stabilisation material or waste (like fly ash) could influence the binding properties and should be strictly avoided. 相似文献
16.
水源水库季节性分层及悬浮物行为对铁锰迁移的影响——以辽宁省碧流河水库为例 总被引：2，自引：0，他引：2
铁和锰是氧化还原敏感的元素，水源水库热分层引起的底层水体缺氧造成了沉积物中铁和锰的释放，对城市供水造成了极大的影响.以往鲜有悬浮物行为对铁和锰在水库水-沉积物界面迁移影响的研究，于2014年2月-2015年2月对碧流河水库深水区的水、悬浮物以及沉积物铁和锰的垂向分布特征进行综合调查分析，并进一步分析铁和锰的季节性变化规律及悬浮物行为对其的影响.Spearman相关分析结果表明铁浓度与总悬浮固体、总氮和总磷的相关性较大；锰浓度与总悬浮固体、溶解氧、pH和总氮的相关性较大.进一步讨论分析表明碧流河水库的热分层、底层缺氧以及沉积物再悬浮是影响铁和锰浓度的重要因素，水库铁和锰的季节变化规律存在差异.分层期溶解态的锰在底层累积，平均浓度达到0.18 mg/L，而沉积物中溶解态的铁释放很少.混合期水库的中上层锰浓度升高，达到了0.07 mg/L.沉积物的再悬浮是水库底层水体中铁的主要来源，底层颗粒态铁的平均浓度约为0.3 mg/L.絮凝的颗粒物以及其吸附的锰在水库长期悬浮，难以沉积到水库底部，使得悬浮物中Mn的含量显著高于表层沉积物，约为沉积物的7倍.建议应在碧流河水库采用分层取水、水库曝气以及联合供水等措施，以减少铁和锰的浓度升高对供水产生的影响，保障大连市城市供水安全. 相似文献
17.
A study was conducted to evaluate monitored natural attenuation (MNA) as a remedy for arsenic in groundwater at a former phosphate mining and manufacturing facility. The mineralogy, speciation, and lability of arsenic in phosphatic wastes present in soils were characterized using sequential extraction procedures, leaching experiments, batch adsorption tests, and microchemical speciation analysis. A PHREEQC-based reactive transport model was also parameterized using these laboratory results, and it was used to evaluate the importance of identified attenuation mechanisms on arsenic concentrations along a vertical flow path from a shallow, alluvial aquifer to the underlying Floridan aquifer. Arsenic was found to occur in several chemical forms in phosphatic wastes, including unstable sulfide minerals, adsorbed surface complexes, and relatively insoluble phosphate and oxide minerals. Most arsenic was associated with stable minerals. The reactive transport model predicted that historical leaching of solid-phase waste materials in soils would not have generated enough arsenic to explain the concentrations observed in downgradient groundwater; instead, the source of arsenic to groundwater was likely acidic and saline process water that infiltrated though unlined ponds and ditches during historical manufacturing operations. A key factor affecting the long-term effectiveness of natural attenuation of arsenic in groundwater is the occurrence and stability of iron oxyhydroxides in aquifer sediments. According to laboratory and reactive transport model results, sufficient levels were found to be present at the site to effectively limit arsenic migration at concentrations exceeding drinking water standards in the future in the Floridan aquifer. This study presents the geochemical evaluations that are needed to satisfy EPA guidelines on determining whether or not MNA is an acceptable remedy for a site. It specifically details the characterization and modeling that were used to demonstrate effectiveness at a site where MNA was ultimately selected as the remedy for arsenic in groundwater. 相似文献