环境因子及沉水植物对底泥磷释放的影响研究

通过环境因子（温度、pH、扰动、溶解氧等）及沉水植物对底泥磷释放影响的研究，分析了环境因子影响底泥磷释放的因素，及不同环境条件下沉水植物影响底泥磷释放的因素，得出了如下结论：溶解氧、pH、温度及扰动等对底泥磷向上覆水体释放都有一定影响，其中溶解氧和pH值影响较大；湖泊特别浅水型湖泊中，磷对水体富营养化起重要作用；沉水植物在控制湖泊底泥营养向水体扩散、风等外界因素扰动底泥起关键作用；浅水型湖泊中，湖泊底泥受扰动较大适合种植象狐尾藻类多分枝的沉水植物，这样有利于抑制底泥磷向水体的释放．     

影响富营养化湖泊底泥氮、磷释放的因素

[目的]分析水体酸碱度、温度以及上覆水营养盐浓度,为合理评估环境因素对湖泊底泥氮、磷释放的影响提供科学依据。[方法]选择富营氧化比较严重的云南省昆明市城市景观湖泊翠湖为研究区域,通过控制不同pH值、温度和上覆水营养盐浓度来模拟影响底泥氮磷释放的因素。[结果](1)放置时间相同条件下底泥氮、磷释放量受到水体酸碱性的影响,中性环境下(pH=7.5)释放量高于酸性和碱性水体条件。底泥释放5,10h条件下,pH值为7.5时底泥磷释放量分别达到5.88,8.28mg/kg;pH值为7.5时底泥氮释放量分别达到22.8,38.4mg/kg;(2)底泥氮、磷释放量随着温度升高而增加。温度为20℃时底泥氮、磷的释放量分别达到28.62,3.75mg/kg;(3)底泥氮、磷的释放量均随着上覆水浓度增加而减少,随着放置时间延长而增加。放置时间5h上覆水氨氮浓度0.31mg/L底泥氮的释放量最大,达到21.63mg/kg。放置10h在氨氮为2.37mg/L时底泥氮的释放量达到最大值(39.22mg/kg);底泥磷释放量在上覆水磷浓度0.14mg/L时底泥总磷的释放量最大;放置时间为5,10h时分别达到4.25,4.91mg/kg。[结论]底泥中营养盐释放是一相当复杂的动态过程,水体酸碱度、温度或上覆水营养盐浓度是影响释放量的主要因素。     

刚毛藻分解对荣成天鹅湖沉积物磷释放的影响

在荣成天鹅湖刚毛藻暴发和非暴发区域分别采集沉积物进行室内加藻模拟试验,定期监测上覆水的溶解氧（DO）、pH、化学需氧量（COD）和可溶性磷（SRP）等指标的变化,并分析了刚毛藻分解对沉积物磷释放的影响。结果表明,避光培养过程中,刚毛藻分解使上覆水体的DO含量大幅降低,形成厌氧环境（0~0.14 mg.L-1）;COD含量则明显增加,各处理最大值变化在0.59~6.93 mg.L-1之间。刚毛藻分解可明显促进沉积物中磷的释放,培养期间上覆水SRP的含量大幅上升,变幅为0.01~1.51 mg.L-1;暴发区沉积物＋10 g藻和沉积物＋30 g藻处理的最大释磷量分别为沉积物处理的2.06倍和1.91倍。不同湖区沉积物磷的释放能力存在较大差异,暴发区沉积物的释磷量明显高于非暴发区,沉积物释放是前者上覆水磷含量增加的主要来源,而在非暴发区藻类分解释放的磷高于沉积物中释放的磷。     

哈素海表层沉积物中内源磷的释放研究

以浅水湖泊哈素海为研究对象,开展了上覆水质、温度、pH、溶解氧、扰动和光照等环境要素对湖泊沉积物内源磷释放的影响试验研究。结果表明,温度升高、碱性条件、厌氧和强烈的扰动作用等均有利于内源磷的释放,而照度则间接地限制了沉积物释磷对上覆水中磷浓度的影响。HSH-2、HSH-5和HSH-6等3个站位TP的最大释放量在自然光照条件下分别为1.53、1.39和1.27 mg·kg^-1,避光条件下分别为1.77、1.52和1.52 mg·kg^-1;静置条件下分别为1.42、1.38和1.68 mg·kg^-1,R=60 r·min^-1时分别为1.75、1.50和2.00 mg·kg^-1,R=120 r·min^-1时分别为2.52、2.64和4.02 mg·kg^-1;在pH=11时释放量最大,分别为10.82、6.83和16.68 mg·kg^-1。各环境因子中,以pH和扰动对哈素海沉积物内源磷的释放影响最大。哈素海为浅水湖泊,在湖水咸化程度逐渐增高的条件下,将会导致湖泊沉积物内源磷的大量释放,从而将进一步加剧水体的富营养化。     

达里诺尔湖磷赋存特征及底泥释放影响因素

[目的]揭示封闭性内陆湖磷组成特点及底泥释放影响因素,为控制达里湖磷元素污染提供理论支持。[方法]对达里诺尔湖水体总磷(TP)、溶解性总磷(DTP)、溶解性无机磷(DIP),沉积物形态磷进行监测,并利用因子分析的方法对影响沉积物底泥释放的因素分类讨论。[结果]达里湖上覆水总磷(TP)均值2.00±0.02mg/L,间隙水TP均值2.50±0.02mg/L,沉积物TP在206.09~940.49mg/kg之间。沉积物中无机磷(IP)占TP的47.9%,是沉积物主要的磷形态之一。钙磷(Ca-P)是IP中含量最多的形态磷(217.76±47.01mg/kg),其次为铁铝结合态磷(Fe/Al-P,62.73±28.34mg/kg)和交换态磷(Ex-P,36.50±19.13mg/kg),有机磷(OP,200.28±135.13mg/kg)含量占TP的41.8%;通过因子分析法将影响底泥释放的因素分为三类:沉积物TP,Ca-P,Fe/Al-P和生物有效性磷含量归为沉积物磷因子;水体pH,DO,Eh值以及间隙水磷含量归为界面影响因子;湖水水深归为湖泊自身特征因子。[结论]达里湖存在沉积物磷底泥释放的风险,根据因子分析的结果可知,影响沉积物底泥释放的因素分为沉积物磷、水—沉积物界面理化指标和湖水水深3大类。     

不同时间尺度下湖泊氮素内源释放强度影响因素的研究

在外源污染得到控制后,氮、磷内源释放成为湖泊持续富营养化的主因。从氮素内源释放机理入手,甄别了影响湖泊氮素释放强度的主要因子,构建了铵态氮和硝态氮释放强度对pH、温度、溶氧量、水动力条件4个因子的对数模型,通过底泥释氮正交模拟实验,对模型进行了回归,结果表明,铵态氮是氮素内源释放的主要形态,其释放强度与pH负相关,与温度正相关,与溶氧量负相关。对于小型浅水型城市湖泊,氮素内源释放强度的影响因素取决于时间尺度：短期水动力条件对释放强度影响较大,但在长期并不显著。溶氧量对氮素内源释放强度的影响长期比短期更明显。本研究可为湖泊氮素内源释放的预测和治理富营养化湖泊工程手段的完善提供参考。     

种植沉水植物对富营养化水体沉积物中磷形态的影响

研究太湖常见6种沉水植物在五里湖未扰动底泥上生长情况及其对沉积物磷化学形态的影响。通过综合分析沉积物中磷的化学形态,释放规律及其影响因素,结果表明,由于沉水植物生长过程使水体的pH、Eh以及藻类含量的变化,使铁磷、有机磷等主要化学形态磷的释放得到明显的控制,同时沉水植物的生长使沉积物中总磷水平也有明显的降低。所以恢复沉水植物是控制湖泊内源磷负荷的有效方式。     

疏浚深度和光照对海河表层沉积物氮磷释放的实验研究

采用混合均匀的海河表层底泥并以自来水为上覆水进行室内沉积物氮、磷静态释放模拟实验,研究了疏浚深度和光照对沉积物总磷和氨氮释放的影响。结果表明,实验期间（2007年7月20日至2008年1月8日）,无论光照与否,与未疏浚相比,完全疏浚能使上覆水总磷平均浓度从0．27～0．41mg·L^-1显著降低至0．02～0．03mg·L^-1（P〈0．05）,但疏浚深度对上覆水氨氮浓度无显著性影响（乃0．05）。与避光组相比,光照可使部分疏浚组和未疏浚组上覆水总磷平均浓度分别降低0．05和0．26mg·L^-1,但对沉积物氨氮释放的影响不明显（光照组氨氮浓度略高于避光组）。其余水质指标监测结果表明,光照组的水温、电导率均值比避光组分别高约0-3℃和20μs,光照组和避光组的pH值无显著差别。此外无论光照与否,电导率均随疏浚深度的增加逐渐降低,pH值变化与疏浚深度关系不大。     

岱海表层沉积物中影响氨氮释放的模拟研究

以北方半干旱地区典型内陆封闭湖泊岱海为研究对象,采用室内模拟实验方法,开展了温度、pH、溶解氧及水生植物对湖泊沉积物中NH4^＋—N释放的影响研究。结果表明,温度升高,中性条件,厌氧条件均有利于NF4^＋-N的释放。狐尾藻对上覆水NH4^＋-N含量的有效控制作用是其抑制底泥释放、同化吸收作用和增强上覆水氧化条件等综合作用的结果,植物修复是控制湖泊富营养化水平的有效措施。     

不同沉水植物在太湖污染底泥上适应性生长过程及水体氮磷的响应

利用太湖五里湖污染底泥,在不破坏表层沉积物层理结构的情况下,研究太湖常见沉水植物在此底泥上适应性生长情况及其对富营养化水体的净化能力。结果表明:实验沉水植物都能在污染底泥中生长良好,同时不同沉水植物均可使上覆水体中氮和磷水平明显降低,叶绿素a的含量也大幅度的减少,水体透明度增大,水质改善。间隙水中氮磷含量在实验时间内也有一定的降低。因此,恢复太湖沉水植被,是重建富营养化湖泊生态系统的重要措施。     

滇池沉积物的功能: 磷源还是磷库?

Dianchi Lake is a highly eutrophic lake in southwestern China where phosphorus (P) is the limiting element for eutrophication and where lake sediments play an important role in the P cycle. One hundred and eighteen sites were sampled throughout Dianchi Lake in 2002 to investigate the P loading of the lake sediments, while fresh surface sediments were studied in the laboratory to clarify its role for phosphorus. The results showed that concentrations of total phosphorus (TP) in sediments were very high, with a maximum value of 6.66 g kg^-1, and decreased with sediment depth. P adsorption on surface sediments was rapid with adsorption amounts higher in acidic than in alkaline conditions. The release experiments showed that P release increased as pH rose from 7.0 to 10.5. Additionally, compared with aerobic conditions, P release was much higher under anaerobic: conditions, especially with low P content in the lake water. At present, the sediments in Dianchi Lake still function as a sink for phosphorus at high P levels in lake water. However, if the external P load was reduced and P content in lake water became low, the sediment would have a large potential for P release under anaerobic conditions.     

Lake Sediments from Dianchi Lake： A Phosphorus Sink or Source？

Dianchi Lake is a highly eutrophic lake in southwestern China where phosphorus (P) is the limiting element for eutrophication and where lake sediments play an important role in the P cycle. One hundred and eighteen sites were sampled throughout Dianchi Lake in 2002 to investigate the P loading of the lake sediments, while fresh surface sediments were studied in the laboratory to clarify its role for phosphorus. The results showed that concentrations of total phosphorus(TP) in sediments were very high, with a maximum value of 6.66 g kg^-1, and decreased with sediment depth. P adsorption on surface sediments was rapid with adsorption amounts higher in acidic than in alkaline conditions. The release experiments showed that P release increased as pH rose from 7.0 to 10.5. Additionally, compared with aerobic conditions, P release was much higher under anaerobic conditions, especially with low P content in the lake water. At present, the sediments in Dianchi Lake still function as a sink for phosphorus at high P levels in lake water. However, if the external P load was reduced and P content in lake water became low, the sediment would have a large potential for P release under anaerobic conditions.     

太湖、巢湖、龙感湖沉积物中磷的地球化学形态

A sequential extraction method for the fractionation of phosphorus （P） in lake sediments was used to analyze phos- phorus fractions of sediments taken from three large, shallow. eutrophic freshwater lakes of China-Talhu Lake. Chaohu Lake, and Long.an Lake. All three lakes are located in the lower reaches of the Changjiang River （Yangtze River）. In Taihu Lake and Chaohu Lake, algae blooms occurred every year, while Longgan Lake was a macrophyte-dominated lake. Results showed that exchangeable phosphorus fractions were much higher in the eutrophic lake sediments than in the macrophyte-flourishing lake sediment. Also, the ratio of Fe：P in the sediments of the algae-predomlnant lakes was generally much lower than that in the macrophyte-predominant lakes. Thus, the geochemical fractions of phosphorus in sediments had a closer relationship with the type of aquatic vegetation.     

Mobilization Potential of Heavy Metals: A Comparison Between River and Lake Sediments

Toxic metals introduced into aquatic environments by human activities accumulation in sediments. A common notion is that the association of metals with acid volatile sulfides (AVS) affords a mechanism for partitioning metals from water to solid phase, thereby reducing biological availability. However, variation in environmental conditions can mobilize the sediment-bound metal and result in adverse environmental impacts. The AVS levels and the effect of AVS on the fate of Cu, Cd, Zn, Ni in sediments in the the Changjiang River, a suboxic river with sandy bottom sediment and the Donghu Lake, a anoxic lake with muddy sediment in China, were compared through aeration, static adsorption and release experiments in laboratory. Sips isotherm equation, kinetic equation and grade ion exchange theory were used to describe the heavy metal adsorb and release process. The results showed that AVS level in the lake sediment are higher than that of the river. Heavy metals in the overlying water can transfer to sediments incessantly as long as the sediment remains undisturbed. The metal release process is mainly related to AVS oxidation in lake sediment while also related to Org-C and Fe–Mn oxyhydroxide oxidation in river sediment. The effect of sulfides on Zn and Ni is high, followed by Cd, and Cu is easy bound to Org-C. AVS plays a major role in controlling metals activity in lake sediment and its presence increase the adsorption capacity both of the lake and river sediments.     

Phosphorus Fractionation and Short-term Mobility in the Surface Sediment of a Polymictic Shallow Lake Treated with a Low Dose of Alum (Courtille Lake,France)

Lake Courtille was a polymictic eutrophic lake prone to large pH variations and sediment resuspension. Short term P release (96 hr) under laboratory resuspension conditions for two sedimentsample types, surface sediments which represent sediment accumulated over several years and trap sediments which representcurrent year sediment, was studied. The experiments were carriedout in oxic conditions at different pH values. According to phosphorus fractionation, Fe-bound-P, Al-bound-P and Organic-bound-P comprised the largest phosphorus pool (80% of Total Phosphorus). Phosphorus release was from the Fe-P, Al-P and organic fractions. These represent 35% of the total phosphorus content at pH 10. At circumneutral pH, in oxic conditions, a lower quantity of P was released (roughly 4% of total P sediment content) than at pH 10. The organic matter mineralization occurring at the end of summer can also influenceP release as illustrated by the difference in total phosphoruscontent between sediment samples of 2000 and of the last five years. This type of P release was observed in Lake Courtille. High soluble reactive phosphorus content was measured in the water column at the end of summer. Aluminium treatment was thus not efficient in preventing P release. Moreover, a higher alum dose was needed to reduce P content in the water column in order to decrease primary productivity and subsequent organic matter sedimentation.     

Phosphorus Retention and Release Characteristics of Sewage-Impacted Wetland Sediments

Sediment deposited in traps positioned along a sewage-impacted wetland receiving phosphorus (P)-retaining reactants from natural wetland water was fractionated into different particle sizes, and the amount of P retained in these particle sizes was investigated. Subsamples of the sediments collected from different sites along the wetland system were also equilibrated with water at different water:sediment ratios and equilibration periods to investigate the extent of P released from these sediments under aerobic and anaerobic conditions. Results obtained showed that most of P deposited in sediments is in fine fractions (<16 µm), particularly in sediments collected from confluence sites where water inflow from the natural wetland provides P-retaining reactants and from sites immediately below these confluence sites (postconfluence sites). The extent of P release from sediments depended on the aerobic-anaerobic conditions of the sediments, equilibration period, water:sediment ratio and the position of sites within the wetland. The rate of P released from sediments associated with an increase in equilibration period tended to be higher under aerobic than anaerobic conditions. Water:sediment ratio was found to be a more important factor in controlling the release of P from sediments under anaerobic than aerobic conditions. The amount of P released from the confluence and postconfluence sites was higher than that from other sites over a range of equilibration periods and water:sediment ratios under aerobic and anaerobic conditions.     

湖泊沉积物中磷释放的研究进展

沉积物是湖泊营养物质的重要蓄积库,也是湖泊内源性P的主要来源。沉积物中部分固定的P可通过分解或溶解作用而释放磷酸盐到沉积物间隙水中,然后通过扩散作用或表层沉积物的再悬浮作用而释放到上覆水体中。本文就目前对沉积物P释放的影响因素及释放机制的研究进展作一简要概述。