污水颗粒磷在海水中的释放作用

本文模拟研究了污水颗粒物－海水体系中磷的转移过程。污水颗粒物与海水混合之后先是快速吸附磷，之后即以约０．３ｄ＾－１的速率进行释放。总过程仍表现为磷的释放。磷的吸附－释放属于离子交换性质，可用交换平衡动力学模式表示。溶解磷含量的增加速率符合一级动力学方程。     

河口水与污水混合有机物和磷的转移动力学

污水与九龙江河口水混合研究表明，ＣＯＤ的降解符合一级动力学模式，降解速率常数ｋ在０．０４－０．１１ｄ＾－１之间，水体有机物的转移以降解作用为主；两种水体混合时，先产生磷的吸附，后释放，整个过程表现为颗业磷向溶解无机磷的转移。     

纳污海水中CDO生化降解过程的模拟试验研究

１９９５年５￣１１月期间,采取渤海湾海水,控制不同的试验水温和不同的有机物起始浓度,采用试验室模拟方法,测定ＣＯＤ生化降解曲线,依据ＣＣＤ降解动力学理论,得出了不同环境条件下的ＣＯＤ生化降解动力学参数,经过归纳综合,建立了纳污海水中ＣＯＤ的生化降解动力学参数方程式,试验结果显示,渤海湾天津近岸排海污水ＣＯＤ生化降解过程符合一级反应动力学模型,其降解速率系数ｋ值介于０．０２３￣０．０７６ｄ＾－１之间     

海水pH对疏浚物中重金属释放的影响

对厦门员当湖污染疏浚物中的Ｃｄ，Ｃｕ和Ｐｂ在不同ｐＨ的天然海水中溶出的模拟研究结果表明：在ｐＨ为５．０，６．５，８．３条件下，疏浚物中的Ｃｄ，Ｃｕ，Ｐｂ的释放率分别为８０％－９４％，４％－９％和１．０％－２．２％；在相同条件下，Ｃｄ，Ｃｕ，Ｐｂ的释放量（释放量）均随ｐＨ值增大而减少，释放量的顺序为Ｃｄ＞Ｃｕ＞Ｐｂ。讨论了ｐＨ对释放作用的影响及释放过程所遵循的动力学规律。     

长江口竹园排污区磷的转移动力学

模拟研究上海市污水排放长江口竹园排污区时,污水－海水混合过程中磷含量和形态的变化,及基在颗粒物－海水界面的转移动力学,提供动力学模式,测定转移的速率,进行容量校正,为上海市污水排海环境容量估算和水质控制提供动力学资料和理论依据。     

纳污海水中COD生化降解过程的模拟试验研究

1995年5－11月期间,采取渤海湾海水,控制不同的试验水温和不同的有机物起始浓度,采用试验室模拟方法,测定COD生化降解曲线。依据COD降解动力学理论,得出不同环境条件下的COD生化降解动力学参数。经过归纳综合,建立了纳污海水中COD的生化降解动力学参数方程式。试验结果显示,渤海湾天津近岸排海污水COD生化降解过程符合一级反应动力学模型,其降解速率系数足值介于0．023－O．076d-1之间。k值受温度变化的影响较大,温度越高,k值越大。     

海水中砷标准物质的研制

本文介绍了海水中砷标准物质的研制过程，其中包括溶液的配制、均匀性和稳定性检验，标样的分析方法。并对标准物质的定值数据进行统计处理，两种浓度的定值结果分别为：１．００μｇ／ｃｍ３±０．０４μｇ／ｃｍ３和５１．０μｇ／ｄｍ３±２．６μｇ／ｄｍ３。两种浓度砷标准物质的稳定期均为一年     

顺序扫描ICP—AES法测定海水中硼

利用ＩＣＰ—ＡＥＳ方法准确测定海水中元素硼，对射频功率、进样泵速、试样盐度、雾化压力、光谱干扰等多项因素进行考察，选出了最佳工作条件。方法检出限为３μｇ·ｋｇ－１，精度为０．２３％～０．４０％，回收率平均为１００．０４％，相对误差为０．５６％。     

台湾海峡海流结构及海水通量

主要根据台湾海峡的实测海流资料，以夏、冬为代表季节，分析了台湾海峡２—３个纬向断面的海流结构，计算出各断面的海水通量。结果表明：夏季，台湾海峡中、北部海域各层的海流一般偏Ｎ向流动，Ｎ向的海水净通量为３．３２×１０６ｍ３·ｓ－１；冬季，高温高盐的黑潮水和南海水由南向北经南部断面进入台湾海峡，其海水通量分别为１．６９×１０６ｍ３·ｓ－１和０．５９×１０６ｍ３·ｓ－１；而东海水由北向南通过北部断面进入台湾海峡，其海水通量为１．０２×１０６ｍ３·ｓ－１，其中，有０．４０×１０６ｍ３·ｓ－１的海水沿着福建和广东近岸流进南海，其余０．６２×１０６ｍ３·ｓ－１的海水在台湾海峡北部混合后随同黑潮水和南海水流入东海。总之，流经台湾海峡的Ｎ向海水净通量为１．７４×１０６ｍ３·ｓ－１。     

杭州湾海水中的硼和锶的研究

采用作者研究的ＯＰ－ 乳化剂增敏姜黄素分光光度法测定海水中的溶解硼,用ＩＣＰ－ ＡＥＳ法测定海水中的溶解锶。发现在杭州湾海水盐度５ ．５６３ ～２６ ．３９７ ,氯度３．０２２ ～１４ ．５８２ 范围内,硼浓度为０ ．６８ ～３．２４ｍｇ／ｋｇ,锶浓度为１ ．２９～５ ．８８ｍｇ／ｋｇ,Ｂ（ｍｇ／ｋｇ）／Ｃｌ 比值为０ ．２１９～０ ．２４５,平均值为０．２３２±０ ．００７ ,Ｓｒ（ｍｇ／ｋｇ）／Ｃｌ 比值范围为０．３９８ ～０．４４０ ,平均值为０．４１７ ±０．０１１ 。结果表明,湾内海水中的硼和锶浓度与海水盐度或氯度均有很好的线性正相关关系,丰水期与枯水期水样数据关系相同,不因采水时间不同而变化。实验数据统计回归线与理论稀释线比较后表明,湾内海水中锶与硼均具有良好保守性质;湾内海水中的硼和锶主要来自湾外潮汐输入。湾东北沿岸海水高的Ｂ／Ｃｌ比值,暗示着此处有含硼工业废水排入湾内,认为Ｂ／Ｃｌ 比可作为近岸河口海水硼污染的一种指标。杭州湾海水中未检测到硼有机络合物。     

污水与海水混合后海水颗粒物对磷的吸附-释放实验

本文模拟研究了厦门污水与海水混合后,海水颗粒物对磷的吸附-解吸过程,结果表明:颗粒物对磷的吸附只在混合后的1d内进行,之后即产生颗粒磷的释放,并表现为颗粒磷→溶解磷→溶解无机磷的转移过程。溶解无机磷是水体中磷的重要存在形式,其浓度的增加速率基本符合一级动力学模式。颗粒磷的释放过程可用交换吸附动力学模式(t/X)=(t/X_(eq))+B′处理。     

Ecotoxicological evaluation of sewage sludge using bioluminescent marine bacteria and rotifer

Bioassay using the marine bacteria,Vibrio fischeri and rotifer,Brachionus plicatilis, and chemical analyses were conducted to assess the toxicity of the various sewage sludges, one of the major ocean dumped materials in the Yellow Sea of Korea. Sludge elutriates extracted by filtered seawater were used to estimate the ecotoxicity of the sludge. Chemical characterization included the analyses of organic contents, heavy metals, and persistent organic pollutants in sludge. Bacterial bioluminescent inhibition (15 min), rotifer mortality (24 hr) and rotifer population growth inhibition (48 hr) assay were conducted to estimate the sludge toxicity. EC50 15 min (inhibition concentration of bioluminescence after 15 minutes exposed) values by Microtox® bioassay clearly revealed different toxicity levels depending on the sludge sources. Highest toxicity for the bacteria was found with the sludge extract from dyeing waste and followed by industrial waste, livestock waste, and leather processing waste. Clear toxic effects on the bacteria were not found in the sludge extract from filtration bed sludge and rural sewage sludge. Consistent with Microtox® results, rotifer neonate mortality and population growth inhibition test also showed highest toxicity in dyeing waste and low in filtration bed and rural sewage sludge. High concentrations of persistent organic pollutants (POPs) and heavy metals were measured in the samples from the industrial wastes, leather processing plant waste sludge, and urban sewage sludge. However, there was no significant correlation between pollutant concentration levels and the toxicity values of the sludge. This suggests that the ecotoxicity in addition to the chemical analyses of various sludge samples must be estimated before release of potential harmful waste in the natural environment as part of an ecological risk assessment.     

沙滩水体中溶解性石油烃的降解及吸附研究

以海水体系和海水-砂体系作为对比,研究了沙滩水体中溶解性石油烃的降解及吸附作用。实验结果表明,1d内海水中石油浓度的降低主要是由于砂的快速吸附作用,3d以后生物对石油烃的降解作用逐渐占据优势。两种体系中降烃菌数量及石油浓度的变化曲线表明,砂对油的快速吸附显著降低了海水中石油污染物的浓度,使得海水含砂体系中石油降解菌的数量远高于海水体系。海水中石油污染物的降解符合一级动力学模式,当含砂体系中砂的粒径不同时,石油污染物降解的半衰期可由海水体系的31.9d缩短到22.4d和19.5d。系统中砂的存在有利于海水中石油污染物的去除,有约20%的石油污染物被吸附到砂上,然而这种去除是物理去除。     

几种河口生物对天津市污水及其若干组分的回避反应

综合污水包括工业废水、生活污水和农业废水(含化肥、农药等)。据统计，每年排人渤海湾的工业废水达5.28亿吨，生活污水1.4亿吨，它们绝大部分经排污河汇流人海，造成了河口海域的污染。 鱼类等海洋生物具有敏锐的嗅觉和味觉，在体表上亦分布有许多化学感受器，能够感知许多低浓度的化学物质，并发生回避反应，这是海洋生物对水环境污染的一种保护性反应。我们利用梭鱼Mugil so-iuy、鲈鱼Lateolabrax japonicus、罗非鱼Tilapia mossambica和对虾Penaeus orientalis等几种河口生物对天津市南、北排污河综合污水及其主要有机污染物的回避反应进行了试验研究，探讨综合污水及其几种主要有毒组分对海洋生物的毒性效应，为海域环境管理提供科学依据。     

宁波—舟山深水港海域水体有机物分布特征初探

本文根据1987年5月宁波—舟山深水港海域水体中有机物分布,初步讨论了有机物在水体中的行为。海水中溶解态的有机物与有机物总量存在如下关系:[DOM]/[TOM]=0.611[TOM]~(-0.899)。并且在通常状况下,调查海区水体中的有机物随悬浮颗粒物的增加而增高,其关系式为:[TOM]=0.65e~(0.0011〔SS〕)。认为该海区的悬浮物是制约有机物行为的主要因素之一。     

Control of Phosphate Concentration through Adsorption and Desorption Processes in Groundwater and Seawater Mixing at Sandy Beaches in Tokyo Bay, Japan

Field observation was conducted to monitor phosphate concentrations in groundwater and seawater mixing at two sandy beaches in Futtsu and Miura in Tokyo Bay, Japan. Dissolved phosphate concentrations were measured along transects from fresh groundwater aquifer to seawater adjacent the beaches. The concentrations were often high (up to 46 µM) in fresh groundwater samples (Cl^– < 0.2). Coastal seawater, on the other hand, exhibited low phosphate concentrations (1.5 µM or less). Along the transects, phosphate generally displayed non-conservative behavior during mixing of fresh and saline waters in the aquifer; concentrations as high as 100 µM were found around the upper limit of seawater intrusion (Cl^– = 2). Laboratory experiments were executed to identify the processes that control the phosphate behavior in the mixing processes. The results revealed that adsorption-desorption processes by the aquifer sand particles could significantly control the phosphate concentrations in the groundwater. Furthermore, the adsorption and/or desorption was found to be a function of salinity; the equilibrium concentration of dissolved phosphate in slurry of sand and water was the highest in freshwater and decreased considerably in saline water. The extreme concentration of phosphate may be caused by release from sand particles coinciding with the rapid change in salinity with tide.     

Novel technology in pollutant removal at source and bioremediation

Sewage disposal is a major environmental issue in both developed and developing countries and removal of pollutants such as organic matter, nutrients, heavy metals and persistent organic compounds is required to protect the environment. Novel biological systems using constructed mangrove wetland and immobilized microalgal beads have been developed as alternative systems for treating different types of sewage and pollution at source. The feasibility and efficiency of constructed mangrove wetland to remove organic matter and nutrients from primary settled municipal sewage were demonstrated through a series of greenhouse experiments and a pilot-scale field trial. The treatment efficiency of constructed mangrove wetland was comparable to, or higher than, the conventional constructed wetland. An immobilized microalgal system was developed to remove toxic persistent pollutants from industrial wastewater. Pollutant-resistant microalgal species were selected for culture in domestic wastewater. The harvested biomass was immobilized in alginate beads. Bench-scale experiments showed the algal beads were effective in removing industrial pollutants such as heavy metals (e.g. Cu, Zn, Ni, Cr, etc.), organometallic compounds (e.g. tributyltin, TBT), and persistent organic compounds (e.g. polycyclic aromatic hydrocarbons, PAHs) through biosorption and biodegradation. The adsorbed metals could be recovered by desorption process, and the beads could be used repeatedly for many adsorption–desorption cycles.     

Physicochemical modeling of the behavior of microelements (As,V, Cr,Co, and Hg) under the mixing of riverine and marine waters (the Razdol’naya River-Amur Bay System)

By means of physicochemical modeling with the Selector software package, a model for the mixing of riverine water (pH = 7.02) and seawater was compiled and calculated. The Razdol’naya River-Amur Bay (Sea of Japan) system was assessed as an example. By means of the MINTEQA2/PRODEFA2 software package, the role of the sorption processes in riverine and marine waters, as well as in the zone of their mixing, was ascertained. The physicochemical migration forms of microelements (arsenic, vanadium, chromium, cobalt, and mercury) in the waters of the geochemical system considered and their behavior in passing through the geochemical barrier were established.