环境因子对长江宜宾段底泥吸附磷的影响

本文主要研究模拟长江底泥对富营养化水体磷的吸附,分析环境因子对底泥吸附磷的影响。结果显示：（1）在25℃时,底泥对磷的吸附在碱性条件时的吸附速率小于酸性和中性条件,中性条件下的吸附速率最大;（2）在控制上覆水温度时,温度越高底泥对磷的吸附量越小,20℃时底泥的吸附量是30℃吸附量的1.5倍;（3）上覆水中溶解氧的浓度越高,吸附速率越高。     

乌伦古湖上覆水水质因子与沉积物理化特性相关性研究

为了解乌伦古湖上覆水水质因子与沉积物理化特性之间的关系,本次对乌伦古湖8个(大湖5个,小湖3个)采样点的上覆水体水和沉积物的相关指标进行了统计性分析和相关性分析,结果表明:乌伦古湖水体中的溶解氧与沉积物有机磷、沉积物总氮、沉积物硝态氮呈一定的负相关,表明高溶解氧的水环境下,有利于抑制沉积物释放氮、磷;水体中的硝态氮与表层沉积物中的水溶性硝态氮、氨氮以及总氮无显著相关关系,表明水体硝态氮的治理应放在外源治理;水体中的总磷与沉积物总磷和沉积物无机磷呈较显著正相关关系,说明底泥中的总磷已经成为水体中总磷的来源之一。     

白洋淀上覆水氮磷浓度对沉积物氮磷释放的影响

采用实验室静态模拟法,研究了白洋淀上覆水氮磷浓度对沉积物中氮磷释放的影响。结果表明,上覆水浓度对沉积物中氮磷释放速率有较大影响,上覆水浓度越低,营养盐释放速率越快,反之越慢。S曲线可以很好地拟合氮磷营养盐累计释放量的变化趋势,指数衰减动力学模型可以很好地描述氮磷释放速率变化趋势。     

文思湖底泥COD释放规律模拟研究

采用室内模拟实验方法，研究环境因子（温度、pH、扰动强度、供气量）对底泥释放COD的影响。结果表明，水温升高能加速底泥中有机质的释放；上覆水在弱酸至中性条件下底泥释放有机质最低；扰动上覆水体会加快有机质的释放。     

复合酶生物促进剂在底泥生物修复中的应用

通过测定河道底泥中微生物的生化呼吸线来表征复合酶生物促进剂对河道自净过程的影响。研究结果表明复合酶生物促进剂对微生物具有激活作用,使微生物的累积耗氧量明显增加,有效地提升了水体的自净能力。复合酶生物促进剂能够有效地修复受萘污染的底泥,修复后底泥中多环芳烃萘的释放量和有机质的含量均明显低于对照样,并可显著降低底泥对上覆水...     

内源磷的释放作用及影响因素研究进展

水体的富营养化已成为目前环境研究中的焦点问题，磷在湖泊中的浓度高低是衡量湖泊富营养化水平的重要指标，是水生态系统基本营养盐之一，并且是淡水湖泊的最主要限制性营养因子。在外源磷得到有效的控制之后，内源磷的污染仍然能够保持湖泊的富营养化状态，此时内源磷的控制就成为了难点和重点。在底泥中的结合态磷，主要是以无机磷和有机磷的形式存在，有机磷与微生物活性密切相关，无机磷则主要与底泥存在的环境联系紧密。湖泊底泥内源磷释放受到一系列物理、化学、生物过程的控制，其影响因素主要包括扰动、氧化还原电位、pH值等，是多种因子综合作用的结果，同时，扰动引起的底泥再悬浮对内源磷有吸附固定作用。故底泥内源磷的释放机理有待进一步探索，在多种影响因素作用下，进一步研究底泥再悬浮对磷的吸附释放作用，从而明确内源磷的主要来源及吸附释放过程，为内源磷的控制提供理论依据，进而控制水体富营养化。     

pH值对黄河兰州段底泥中总磷释放的影响

分析了不同pH值对黄河兰州段底泥总磷（TP）释放特性的影响。结果表明：底泥中的总磷在酸性范围内呈现负释放状态,且pH值越小＂,负释放强度越大＂;在碱性范围内,pH值越大,总磷释放量越大。当pH值为4和6时,水体中的总磷在第1 d都是下降,呈现出负释放的状态;pH值为4时,在第4 d负释放量达到最大值,而pH值为6时到实验结束时负释放量依然在增大。当pH值为10、11、12时,总磷呈现出明显的正释放状态,且在第2 d,总磷的释放量达到最大值。实验数据说明在碱性条件下,底泥中的磷对水质可能产生不良的影响。本次实验对黄河水质的监测以及治理有一定的参考价值。     

沉水植物对富营养化水体的净化效果研究

通过建立小型围隔区,研究了沉水植物对富营养化水体中氮、磷等污染物的净化效果,以及对底泥中磷含量的影响.结果表明:(1)在放养沉水植物的围隔水体中各种营养盐浓度明显低于对照围隔;(2)沉水植物对磷的吸收能够有效地保持底泥中磷的含量,而在对照围隔中的底泥中磷元素含量却不断增加;(3)经50天后,水体中TN、NH4 -N、TP、PO43--P和CODMn平均去除率分别为36.3%、70.5%、54.6%、65.4%和43.1%.     

江苏沿海平原拟建水库咸化趋势分析

为分析江苏沿海拟建平原水库建设后的咸化风险,于2013年4月,在江苏沿海1#、2#、3#、4#拟建水库取0~200cm原装土样,通过对样品氯离子含量和释放速率的测定,建立水质模型,预测不同初始蓄水水质条件下水库咸化风险,模拟结果表明:在模拟运行一年后,1#、2#拟建水库底泥盐分释放量小,来水水质较好,不会发生咸化,可作为生活用水水源地;3#拟建水库底泥盐分释放量较大,一年后各条件下氯离子浓度均高于250mg/L,平均氯离子浓度涨幅为173.20%,咸化风险较高,不适合作为生活用水水源地;4#拟建水库在各条件下氯离子浓度平均上升6.83mg/L,因此当蓄水水源良好时可以作为生活用水水源地。     

海洋沉积物中石油类污染物动态释放的实验研究

以海洋沉积物为研究对象,通过动态模拟实验研究了海洋沉积物中石油类污染物释放的影响因素及各条件下上覆水体中污染物浓度随时间的变化规律。实验结果表明,海洋沉积物中石油类污染物释放强度与沉积物土壤颗粒是否悬起有关,当土壤颗粒大量悬起时污染物释放强度得到显著提高;上覆水体盐度的增加抑制了石油类污染物的释放;海洋沉积物在一定的受污染范围内,随着受污染程度的增加,石油类污染物的释放强度会随之增加;上覆水体中石油类污染物的浓度与反应物的固液比成正相关。     

基于MIKE 21的汾河水库挟沙水流水质数值模拟研究

为了揭示悬浮泥沙(SSC)对水库水质的影响规律,对汾河水库进行样品收集和长期水质监测,采用水动力模型与泥沙转移和富营养化模型相结合的方法,将这三者关联耦合,并通过实测数据对模型进行参数率定和验证,分析含沙水和不含沙水中总氮(TN)、总磷(TP)、叶绿素a(Chla)、溶解氧(DO)四项指标,得出两者对水质造成的影响。结果表明:SSC对TN、TP的去除作用明显,对Chla、DO浓度分布影响较小,并计算了污染物的释放量以及贡献率,得出TP的负荷仅为16.47t,而贡献率高达25.25%。因此在汾河的污染控制方面应侧重削减磷,进而改善汾河地区的污染现状。     

基于MIKE 21的汾河水库挟沙水流水质数值模拟研究

为了揭示悬浮泥沙(SSC)对水库水质的影响规律,对汾河水库进行样品收集和长期水质监测,采用水动力模型与泥沙转移和富营养化模型相结合的方法,将这三者关联耦合,并通过实测数据对模型进行参数率定和验证,分析含沙水和不含沙水中总氮(TN)、总磷(TP)、叶绿素a(Chla)、溶解氧(DO)四项指标,得出两者对水质造成的影响。结果表明:SSC对TN、TP的去除作用明显,对Chla、DO浓度分布影响较小,并计算了污染物的释放量以及贡献率,得出TP的负荷仅为16.47t,而贡献率高达25.25%。因此在汾河的污染控制方面应侧重削减磷,进而改善汾河地区的污染现状。     

LAKE RESTORATION BY SEDIMENT REMOVAL1

ABSTRACT: Fresh water lake sediment removal is usually undertaken to deepen a lake and increase its volume to enhance fish production, to remove nutrient rich sediment, to remove toxic or hazardous material, or to reduce the abundance of rooted aquatic plants. Review of more than 60 projects and five case histories reveals that the first three objectives are usually met through sediment removal. Dredging to control aquatic plants has not been well documented. Disadvantages of dredging include cost, temporary phosphorus release from sediment, increased phytoplankton productivity, noise, lake drawdown, temporary reduction in benthic fish food organisms, the potential for toxic material release to the overlying water and potential for environmental degradation at the dredged material disposal site. The technique is recommended for deepening and for long range reduction of phosphorus release from sediment. Sediment removal to control toxic materials is possible with minimal environmental impact when proper equipment is used, but it may more than double the cost. Lack of definitive information about rooted plant regrowth rates in dredged areas prohibits explicit recommendations on sediment removal to control plant growth.     

静态条件下持续时间对底泥中有机氯农药释放的影响

有机氯农药是广泛存在于环境中一类有机污染物，溶解度低，疏水性强，容易被颗粒物吸附，并随其在沉积物中积累，蓄积在沉积物中的有机氯农药在沉积物的再悬浮过程中会重新释放进入水体，造成二次污染。为了考察悬浮持续时间对沉积物中有机氟农药的释放的影响，采用沉积物释放模拟装置在60天内对微山湖沉积物中有机氯农药释放进行研究。结果表明，随着扰动时间的延长，上覆水中有机氯农药的含量在0—20天内增长很快，在60天左右含量趋于到稳定。不同的有机氟农药在扰动条件下，释放的速率和浓度是不一样的，其中水溶性大的农药更易向水体再次释放。     

ESTIMATING NUTRIENT AND SEDIMENT THRESHOLD CRITERIA FOR BIOLOGICAL IMPAIRMENT IN PENNSYLVANIA WATERSHEDS1

ABSTRACT: This study employs a simple nonlinear statistical approach to establish nitrogen, phosphorus, and sediment concentration and unit area load thresholds to aid in the evaluation of aquatic biological health of watersheds within the state of Pennsylvania. Flow, nitrogen and phosphorus species, sediment, basin area, land cover, and biological assessment data were assembled for 29 Pennsylvania watersheds. For each watershed, rating curves depicting flow versus load relationships were developed using the U.S. Environmental Protection Agency's (USEPA's) storage and retrieval database (STORET) flow and concentration data, then applied to daily flow data obtained from U.S. Geological Survey (USGS) daily flow gauging stations to estimate daily load between 1989 and 1999. The load estimates and concentration data were then sorted into six sets of data: mean annual unit area nitrogen, phosphorus, and sediment loads; and average nitrogen, phosphorus, and sediment concentrations. Results of Mann‐Whitney tests conducted on each of the six datasets indicate that there is a statistically significant difference between the concentrations and unit area loads of nitrogen, phosphorus, and sediment in impaired and unimpaired watersheds. Concentration thresholds, calculated as the midpoint between the impaired and unimpaired watersheds’ 95 percent confidence interval for the median, were estimated to be 2.01 mg/L, 0.07 mg/L, and 197.27 mg/L for nitrogen, phosphorus, and sediment, respectively. Annual unit area load thresholds were estimated to be equal to 8.64 kg/ha, 0.30 kg/ha, and 785.29 kg/ha, respectively, for nitrogen, phosphorus, and sediment species.     

Ecosystem Modeling Applied to Nutrient Criteria Development in Rivers

Threshold concentrations for biological impairment by nutrients are difficult to quantify in lotic systems, yet States and Tribes in the United States are charged with developing water quality criteria to protect these ecosystems from excessive enrichment. The analysis described in this article explores the use of the ecosystem model AQUATOX to investigate impairment thresholds keyed to biological indexes that can be simulated. The indexes selected for this exercise include percentage cyanobacterial biomass of sestonic algae, and benthic chlorophyll a. The calibrated model was used to analyze responses of these indexes to concurrent reductions in phosphorus, nitrogen, and suspended sediment in an enriched upper Midwestern river. Results suggest that the indexes would respond strongly to changes in phosphorus and suspended sediment, and less strongly to changes in nitrogen concentration. Using simulated concurrent reductions in all three water quality constituents, a total phosphorus concentration of 0.1 mg/l was identified as a threshold concentration, and therefore a hypothetical water quality criterion, for prevention of both excessive periphyton growth and sestonic cyanobacterial blooms. This kind of analysis is suggested as a way to evaluate multiple contrasting impacts of hypothetical nutrient and sediment reductions and to define nutrient criteria or target concentrations that balance multiple management objectives concurrently. Any opinions, findings, conclusions, or recommendations expressed in this article are those of the authors alone, and do not necessarily reflect the views of the U.S. Environmental Protection Agency or of the U.S. Government.     

PHOSPHORUS RELEASE AND ASSIMILATORY CAPACITY OF TWO LOWER MISSISSIPPI VALLEY FRESHWATER WETLAND SOILS1

ABSTRACT: Phosphorus fluxes and water quality functions of a bottomland hardwood and freshwater marsh wetland soil were compared. The effect of soil physicochemical conditions, phosphorus loading rate, and diffusive exchange between soils and the overlying food water column on phosphorus release and retention were studied. The predominantly mineral swamp forest soil displayed greater phosphorus sorption potential than the organic freshwater marsh soil. Moreover, due to its low bulk density (0.11 g cm^?3), the freshwater marsh soil surface area required for phosphorus retention is very large compared to the bottomland hardwood wetland soil. For both wetlands, soil redox status affected P release and assimilatory capacity. The more reducing the soils, the smaller their phosphorus retention capacity (greater their release). Phosphorus removal from the overlying water column into the wetland soils followed a first-order kinetic model. Under similar hydrological conditions, phosphorus was found to diffuse 1.2 times faster to the bottom. land hardwood soil than in the freshwater marsh soil. Results indicate that while the bottomland hardwood wetland soil will serve as a sink for phosphorus entering such wetland, phosphorus will be released and exported from the freshwater marsh soil into adjacent ecosystems.     

EFFECTS OF SLUDGE AND CHEMICAL FERTILIZER APPLICATION ON RUNOFF WATER QUALITY1

ABSTRACT: Simulated rainfall was used on experimental field plots to compare the effect of chemical fertilizer and sludge application on sediment, nitrogen, and phosphorus in runoff from no-till and conventional tillage systems. Chemical fertilizer application under the no-till system resulted in the least amount of total N and P in surface runoff. However, sludge application under the no-till system resulted in the least amount of NO₃-N and sediment in surface runoff. The worst water quality scenarios were observed when either sludge or chemical fertilizer were surface-applied under a conventional tillage system. Nitrogen losses from the conventional tillage system were minimized when sludge was incorporated into the soil. However, phosphorus and sediment yield from such a system were significantly higher when compared to phosphorus and sediment yield from the no-till system. The results from this study indicate that the use of sludge on agricultural land under a no-till system can be a viable alternative to chemical fertilizer for nitrogen and phosphorus control in runoff. A more cautious approach is recommended when the sludge is incorporated into the soil in a conventional tillage system because of potential for high sediment and phosphorus yield in surface runoff.