东湖沉积物中微生物磷脂的垂向分布

以武汉东湖柱状沉积物为研究对象,利用磷脂法测定了3个采样点各层的微生物量,同时测定了沉积物中各层的pH,简要分析了沉积物中磷脂含量的垂向分布与pH垂向分布的相关性。结果表明:各样点沉积物中磷脂平均含量分别为:1号点59.40nmol/g.dw,2号点为20.56nmol/g.dw,3号点为31.57nmol/g.dw。在沉积物的垂向分布上,微生物量与pH均随着沉积物深度的增加而降低,并且存在很高的相关系数。     

中国长足摇蚊幼虫和霍普水丝蚓扰动下沉积物氧气特征分析

为研究中国长足摇蚊幼虫(Tanypus chinensis)和霍普水丝蚓(Limnodrilus hoffmeisteri)扰动对表层沉积物氧气渗透及空间分布的影响,采集梅梁湾表层沉积物,借助高精度溶氧微电极,研究两种生物扰动作用下,太湖梅梁湾表层沉积物氧气渗透深度和空间分布的变化,并根据氧气在流动培养体系中浓度的变化和在扩散边界层中的扩散过程这两种方法计算界面氧气交换速率。结果表明,中国长足摇蚊幼虫和霍普水丝蚓两种底栖生物扰动均能提高沉积物界面氧气交换速率,且微电极法的计算值要低于流动培养法。通过溶氧微电极剖面能够准确的获得氧气渗透深度的信息。结果发现:长足摇蚊幼虫的扰动能提高沉积物氧气渗透深度并造成氧气在沉积物内空间分布的差异,长足摇蚊幼虫扰动后沉积物氧气渗透深度由无扰动的6 mm增至10 mm。与长足摇蚊幼虫相比,霍普水丝蚓扰动没有增加沉积物氧气渗透深度及造成空间分布差异。对比两种计算方法发现,在生物扰动作用下,由于生物作用的影响,根据氧气在扩散边界层的扩散得到的值可能会低估氧气的界面交换速率。       

太湖春季沉积物间隙水中磷的分布特征及界面释放的影响

通过对太湖春季不同湖区水体和沉积物间隙水中磷的分布特征研究,探讨了间隙水中磷的释放对上覆水环境的影响。结果表明,颗粒态磷(PP)和溶解态有机磷(DOP)是太湖水体中主要的磷形态,占总磷的58%～95%。不同湖区沉积物间隙水磷的剖面变化可能与生态特征及水动力引起的沉积物-水界面的扰动强度密切相关。湖心和西部沿岸沉积物扰动强烈,致使间隙水中磷含量向上逐渐降底,而梅梁湾和贡湖间隙水磷的垂向变化不大。东太湖和竺山湖沉积物界面间隙水中磷含量偏高,可能是由于表层沉积物的有氧环境使Fe2+被氧化固定下来,并促进了总磷(TP)和溶解态活性磷(DRP)的扩散释放。总体而言,间隙水中各形态磷具有向上覆水体释放的趋势,其中DRP的扩散潜力最大,竺山湖沉积物-水界面DRP扩散通量高达11.42mg.m-2.d-1,表明春季浮游植物的复苏生长对DRP的迫切需求。     

生物扰动对沉积物中污染物环境行为的影响研究进展

生物扰动由于显著改变沉积物结构和性质,进而影响沉积物中污染物的环境行为。综述生物扰动对沉积物中氮、磷、重金属和疏水性有机污染物环境行为的影响。生物扰动促进这些污染物从沉积物向水体释放。生物扰动还对不同的污染物产生其它不同的影响。对于氮,生物扰动还影响其硝化与反硝化作用;对于磷,生物扰动不仅改变其化学形态,还提高有机磷降解。对于重金属,生物扰动还能改变其在沉积物中的分布及化学形态。对于疏水性有机污染物,生物扰动主要增强生物富集和代谢,以及提高生物降解。     

连续提取和液体磷核磁共振表征太湖梅梁湾沉积物中磷的剖面分布

应用连续提取法(SMT)和液体磷核磁共振(³¹PNMR)技术研究了太湖北部梅梁湾沉积物中磷形态和组成的剖面变化。结果表明,铁/铝磷是沉积物中磷的主要形态,约占总磷含量的44.0-54.6%。总磷、无机磷、有机磷和铁/铝磷含量均随沉积深度增加呈降低趋势,至18cm以下略有增加,而钙磷却在柱样下部随沉积深度增加呈累积趋势。³¹PNMR显示,沉积物磷主要由正磷酸盐(72.0-99.2%)和磷酸单酯(0.8-25.9%)构成,磷酸二酯、膦酸盐和焦磷酸盐的相对含量非常低,分别为1.0%、0.4-1.0%和 0.1%。正磷酸盐含量在沉积物表层9cm内减少了65%,9cm以下波动变化,但总体呈降低趋势。这些特征表明沉积物中磷对梅梁湾上覆水体具有强烈的释放潜力,是太湖富营养化发生的重要因素。     

泉州湾洛阳江河口沉积物中磷的形态分布

分析了泉州湾洛阳江河口沉积物中总磷及5种形态磷(可交换态磷(DP)、铁铝结合态磷(Fe/Al-P)、钙结合态磷(Ca-P)、有机磷(OP)和闭蓄态磷(Re-P))的含量,探讨了它们的垂向分布特征、相互关系及环境指示意义。结果表明:沉积物中的总磷(TP)以无机磷为主,占TP比例76%~89%;除可交换态磷外,沉积物中形态磷的垂向分布规律具有相似性,大体随深度增加而减小,且在表层有富集现象,反映了沉积物中总磷和各形态磷的分布受人类活动影响较明显;通过相关性分析,钙结合态磷是总磷和无机磷的主要控制因素,而总磷和其他形态磷(除了可交换态磷外)相互间均具有显著相关性,且有机质对各形态磷的分布均有一定影响;TP和各形态磷含量,以及(Fe/Al-P)/TP、Ca-P/TP、OP/TP都在同一层出现了显著变化,反映了水利设施和围垦工程对沉积环境和各形态磷迁移转化有较大影响。     

福建漳江口红树林湿地沉积物中四种重金属的空间分布特征

对漳江口红树林湿地沉积物中4种重金属(Pb、Cd、Ni、Fe)含量空间分布的研究表明,漳江口红树林湿地沉积物中Pb、Fe含量较高,Cd、Ni含量相对较低;林内沉积物的Pb、Cd含量显著高于林外沉积物;在垂岸方向上,表层沉积物中除Ni外其它三种元素含量均表现出从林外到林内增加的趋势;在垂直梯度上,四种元素含量均随着沉积物深度增加而逐渐降低。     

杭州湾滨海湿地不同植被类型沉积物磷形态变化特征

研究了杭州湾滨海湿地不同植被类型下0-5 cm和10-20 cm沉积物总磷(TP)、无机磷(IP)、有机磷(OP)及其形态变化特征,揭示湿地植被演替对沉积物磷形态的影响.结果表明,沉积物TP,互花米草(MC)显著高于其他植被类型.在IP中,可溶性松散态磷(Soluble and loosely bound P,SL-Pi)含量光滩(CK)最小、MC最大;还原态可溶性磷(Reductant soluble P,RS-Pi)含量芦苇(LW)和MC显著高于CK和海三棱藤草(BC);钙磷(Ca-Pi)含量CK和BC显著大于LW和MC.在OP中,活性有机磷( Labile Po,L-Po)含量最低、中等活性有机磷(Moderately labile Po,ML-Po)含量最高、非活性有机磷(Nonlabile Po,NL-Po)处于中间水平.IP是磷素的主要形态、占TP的74％ -89％,而Ca-Pi又是IP的主要形态、于湿地沉积物淤积初期通过吸附沉淀作用存留.杭州湾湿地植被自然演替过程中不同植物生物量积累和营养物质循环过程的变化导致沉积物中磷形态的差异.植被演替初期,BC显著改变0-5 cm沉积物磷形态,对10-20 cm沉积物无显著影响;植物演替后期的LW和MC促使0-5 cm沉积物有机磷快速积累、10-20 cm沉积物有机磷小幅增加,同时促进Ca-Pi向可溶性、活性态磷转变.     

水动力扰动方式对富营养化湖泊藻毒素的影响

太湖是一个典型的大型浅水湖泊,在季风影响下,常年受风浪扰动影响。为了解风浪扰动对太湖水体中微囊藻释放藻毒素(MC)的影响,于2018年7月采集含有微囊藻水华的太湖原水,在中国科学院太湖湖泊生态系统研究站设置了对照、间歇扰动和持续扰动3种处理方式来进行模拟实验,研究水体中藻毒素的变化,实验共持续19 d。结果表明:3种处理方式下,MC浓度的变化趋势一致,1~13 d呈升高趋势,其后均有不同幅度的下降;对照组MC浓度最低,平均值为1.69μg·L-1,显著低于间歇扰动组和持续扰动组(P<0.05);间歇扰动组和持续扰动组MC均值分别为1.81和1.86μg·L-1,两者差异不显著;3种处理方式下,单位藻细胞MC含量1~7 d持续减小,且各组间差异不显著(P>0.05);10~19 d各组均有一个先增加后减小的过程,且组间差异均显著(P<0.05),对照组、间歇扰动组和持续扰动组单位藻细胞MC含量均值分别为0.55、1.20和1.98μg·108cells-1;本实验条件下MC与氮磷等因子显著负相关,与水温、SS、Chla等之间显著正相关。本研究表明,扰动可促进水体中藻毒素浓度及单位藻细胞藻毒素含量的升高。     

环境因素对黑水滩河上游河段潜流层大型无脊椎动物群落的影响

在黑水滩河上游河段选取5个断面调查了潜流层大型无脊椎动物及其生境特征,研究微观尺度环境因素对潜流层大型无脊椎动物群落组成及分布的影响。结果表明:调查河段共发现大型无脊椎动物29种,其中水生昆虫种类最多;各断面大型无脊椎动物的密度、生物量和丰富度均随着潜流层深度的增加而降低;潜流层沉积物的中值粒径、垂向水力梯度和垂向渗透系数是影响大型无脊椎动物组成和分布的主要因素,其中最重要的是中值粒径。潜流层无脊椎动物群落变化也可能受到食物源和生物之间相互作用等因素的影响,所有这些因素共同形成了一个复杂的自然过滤系统,控制着潜流层无脊椎动物的群落结构和空间分布。     

Relative influence of bioturbation and predation on organic matter processing in river sediments: a microcosm experiment

1. Our objective was to measure the effects of bioturbation and predation on the physical characteristics and biogeochemical processes in river sediments. 2. We investigated the impacts of tubificid worms tested separately and together with an omnivore (Gammarus pulex), which does feed on tubificids, on sediment distribution, water flux, sediment organic carbon, biofilm biomass and microbial activities, and the concentrations of dissolved oxygen, dissolved organic carbon, PO, NO, NO and NH in slow filtration sand–gravel columns. We hypothesised that gammarids, which exploit the top 2–3 cm of the sediment, would modify the impact of worms at the sediment surface. 3. In experiments both with and without gammarids, bioturbation by the tubificids modified both the distribution of surface particles in the sediment column and water flux. In addition, microbial aerobic (oxygen consumption) and anaerobic (denitrification and fermentative decomposition of organic matter) processes in the sediment were stimulated in the presence of tubificid worms. However, G. pulex did not affect either the density or bioturbation activity of the tubificid worms. 4. Bioturbation by the benthos can be a major process in river habitats, contributing to the retention of organic matter in sediment dynamics. The presence of at least one predator had no effect on bioturbation in sediments. In such systems, physical heterogeneity may be sufficient for tubificids to escape from generalist predators, though more specialised ones might have more effect.     

Invertebrate bioturbation can reduce the clogging of sediment: an experimental study using infiltration sediment columns

1. Invertebrate bioturbation can strongly affect water‐sediment exchanges in aquatic ecosystems. The objective of this study was to quantify the influence of invertebrates on the physical characteristics of an infiltration system clogged with fine sediment. 2. Two taxa (chironomids and tubificids) with different bioturbation activities were studied in experimental slow infiltration columns filled with sand and gravel and clogged with a 2 cm layer of fine sediment at the surface. We measured the effects of each taxon separately and combined on hydraulic head, water mobility and sediment reworking. 3. The results showed that invertebrates could reduce sediment clogging and this effect was linked to the functional mode of bioturbation of each group. Tubificid worms dug networks of galleries in the fine sediment, creating pathways for water flow, which reduced the clogging of sediment. In contrast, the U‐shaped tubes of chironomids were restricted to the superficial layer of fine sediments and did not modify the hydraulic conductivity of experimental columns. The combination of invertebrates did not show any interactive effects between tubificids and chironomids. The occurrence of 80 tubificids in the combination was enough to maintain the same hydraulic conductivity that 160 worms did in monospecific treatment. 4. The invertebrates like tubificid worms can have a great benefit on functioning of clogged interfaces by maintaining high hydraulic conductivity, which contributes to increased water‐sediment exchanges and stimulates biogeochemical and microbial processes occurring in river sediments.     

Ecosystem engineering at the sediment–water interface: bioturbation and consumer-substrate interaction

In soft-bottom sediments, consumers may influence ecosystem function more via engineering that alters abiotic resources than through trophic influences. Understanding the influence of bioturbation on physical, chemical, and biological processes of the water–sediment interface requires investigating top-down (consumer) and bottom-up (resource) forces. The objective of the present study was to determine how consumer bioturbation mode and sediment properties interact to dictate the hydrologic function of experimental filtration systems clogged by the deposition of fine sediments. Three fine-grained sediments characterized by different organic matter (OM) and pollutant content were used to assess the influence of resource type: sediment of urban origin highly loaded with OM and pollutants, river sediments rich in OM, and river sediments poor in OM content. The effects of consumer bioturbation (chironomid larvae vs. tubificid worms) on sediment reworking, changes in hydraulic head and hydraulic conductivity, and water fluxes through the water–sediment interface were measured. Invertebrate influences in reducing the clogging process depended not only on the mode of bioturbation (construction of biogenic structures, burrowing and feeding activities, etc.) but also on the interaction between the bioturbation process and the sediments of the clogging layer. We present a conceptual model that highlights the importance of sediment influences on bioturbation and argues for the integration of bottom-up influence on consumer engineering activities. Electronic supplementary material  The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

铜锈环棱螺生物扰动对"蓝藻水华"水体底泥及其间隙水中碳、氮、磷含量的影响

实验室内建立小型模拟生态系统,根据铜锈环棱螺(Bellamya aeruginosa)的密度设置了3个处理组和1个对照组.结果显示:铜锈环棱螺对底泥0～0.5 cm及0.5～2 cm有机质影响较明显,显著降低了底泥中的C:P.处理组3和处理组2间隙水NH4+-N含量分别在底泥0～0.5cm及0.5～2 cm深度和对照组之间存在显著差异(p＜0.05).间隙水中NO2--N+NO3--N的变化较复杂,处理组NO2--N+NO3--N含量在0～0.5 cm,0.5～2cm及2～4cm与对照组相比差异显著(p＜0.05).间隙水中DIP含量随底泥深度先增后减,在2～4 cm处含量达最大,DIP含量在0.5～2 cm深度处理组与对照组之间有显著差异(p＜0.05).铜锈环棱螺生物干扰增加了底泥表层有机质的含量,同时降低了其稳定性.     

The effect of tubificid oligochaetes on the uptake of zinc by Lake Erie sediments

A laboratory experiment was conducted to determine the effect of tubificid worms on the flux of zinc into lake sediments. Forty-six cores of Lake Erie sediment, with and without (control) tubificid worm populations, were exposed to aquarium water with a zinc concentration of about 5 mg 1^–1 for 139 days. Pore water and exchangeable particulate zinc concentrations in the top 12 cm of sediment were periodically determined in pairs of cores — one with worms and one without worms — at 1 cm depth increments. After 139 days, pore water zinc concentrations in sediments with and without worms were nearly identical in the 0–1 cm interval (4.1 and 4.3 mg 1^–1 respectively), but were significantly greater in the sediments with worms in the 1–2 cm (4.4 vs. 0.3 mg^1–1) and the 2–3 cm (1.3 vs. 0.3 mg 1^–1) intervals. Exchangeable particulate zinc concentrations in the 0–1, 1–2, and 2–3 cm intervals in sediments with worms were 612.3, 750.7, and 191.5 µg g^–1 dry sediment respectively, whereas in sediments without worms, concentrations were 375.4, 5.9, and 3.2 µg g^–1 dry sediment. The increased flux of zinc into tubificid-inhabited sediments was caused by the conveyor belt feeding activity of the worms, which continuously exposed sedimentary particles to the overlying water. Movement of zinc into sediments with worms was dominated by adsorption and by particle movement, whereas movement of zinc into control sediments was by adsorption at the sediment-water interface and diffusion. The increased concentration of zinc in tubificid-inhabited sediments has important implications with respect to the trophic transfer of zinc through the aquatic food chain.     

High resolution vertical profiles of pH in recent sediments

High resolution (0.1 cm sampling interval) profiles of pH were obtained from some recent estuarine (Long Island Sound, Chesapeake Bay) and freshwater (Lake Erie) sediments and from laboratory microcosms containing homogenized Lake Erie sediment (both with and without tubificid oligochaetes) by incrementally precessing a micro-pH electrode downward through the sediment. These profiles revealed that hydrogen ion undergoes chemical reactions on a scale smaller than can be resolved using classic 1 cm sampling intervals, and that the vertical distribution of hydrogen ion is affected by bioturbation. In all sediments examined, a local pH minimum occurred immediately below the oxidized zone. In estuarine sediments, a second deeper pH minimum was observed. The presence of tubificids prevented profound pH changes from developing in microcosm sediments treated with a layer of activated sewage sludge and resulted in more modest alterations of pH profile in microcosm sediments lacking such a layer. The technique used in this study is by no means limited to pH. In principal, any chemical species that can be directly determined by electrodes (e.g. O₂, S^-2) may be studied. Microelectrode techniques could be especially useful in the study of chemical gradients around animal burrows and in time series studies of whole core diagenesis.     

The effect of tubificids and chironomids on particle redistribution of lake sediment

The effects of chironomid larvae,Chironomus plumosus, and tubificid worms,Limnodrilus spp., on particle redistribution in lake sediment were investigated experimentally using pots containing sediments obtained from Lake Suwa, Japan. The chironomids and tubificids increased the water content of surface sediment. The chironomid larvae had no effect on particle size distribution, while tubificids continuously accumulated small particles on the surface sediment through their selective feeding activity. Particles larger than 0.125 mm were buried at a sediment depth of 6 cm. In Lake Suwa, long diatom frustules, large plant debris and blue-green algal flocs were found to accumulate in the deeper layer of the lake sediment inhabited by tubificids at high density.     

Stratification of alkaline phosphatase in sediments of two urban lakes and its effect on phosphorus cycle

Phosphorus loadings in sediments play an important role in lake eutrophication and the progress of its recovery. The phosphorus release is controlled by physical, chemical and biological mechanisms. Alkaline phosphatase catalyzes remineralization of organic phosphorus and then it may be an important factor accelerating phosphorus cycling in sediments. In this paper, distributions, properties and function of alkaline phosphatase with depths in sediments of two urban lakes were discussed. Alkaline phosphatase activity (APA) in the sediments of Lake Yuehu decreased with the sediment depth. APA in sediments of Lake Yuehu was, mostly, inhibited by Phe and L-Cys; and inhibiting ability of Phe could be stronger than L-Cys. APA in deeper layer (20–30 cm) of sediments was more sensitive to the inhibitors than other layers, but range of variation in APA was most wide in the subsurface layer (10–20 cm). All the facts implied that alkaline phosphatase occurred in various forms (isoenzymes). APA in the sediments with different depths of Lake Donghu responded Phe differently. Reacted with Phe and incubated for 1 day, the amounts of SRP released by these sediments varied correspondingly. SRP on the overlying water in deeper layers (5–10 cm and 15–20 cm) of Site T1 was higher than that in surface layer (0–5 cm) of the same site, 1 day after incubation. Hence, the SRP release resulted, at least partially, from the hydrolysis of some liable organic phosphorus mediated by APA. Alkaline phosphatase in lake sediments plays an important role in the release of internal phosphorus loadings and eutrophication. A possible explanation for the sensitivity at deeper layers could be another active region of hydrolysis by alkaline phosphatase from organic phosphorus, which added a new dimension in phosphorus cycling mediated by some biochemical mechanisms.     

Ecological Significance of Nitrogen Cycling by Tubificid Communities in Shallow Eutrophic Lakes of the Danube Delta

Importance of tubificid populations on nitrogen cycle in two categories of shallow eutrophic lakes in the Danube Delta was quantitatively assessed for the 1992-1993 period. The structure of the primary producers in the studied lakes was used to discriminate between the two categories:(i) lakes dominated by macrophytes (A₁) and (ii) lakes dominated by phytoplankton (A₂). In both categories tubificid worms represented important fraction of the entire benthic community (35 and 32%, respectively, as number of individuals). They influence the sediment-water exchange of nutrients. The main processes involved are excretion of nutrients and their continuous release from sediments by molecular diffusion or through channels created by bioturbation. Inorganic nitrogen released from bottom sediments may regulate nitrogen load in the water body and thus, phytoplankton production. In 1992-1993, nitrogen stocks in tubificid biomass accounted for 5.3% in A₁ lakes and 15.6% in A₂ lakes of the amount stocked in phytoplankton, and only for 1.2 and 2.9% respectively, of the nitrogen load in water body. Nitrogen excretion rates ranged between 60.52 and 153.74 mg N m^–2 year^–1, and release rates from sediments between 378.26 and 960.87 mg N m^–2 year^–1, the lowest values being recorded for A₂ category. Differences are related to tubificid biomass, structure and abundance of primary producers and to nutrient load in different ecosystems. Ratios between release rate of inorganic nitrogen by tubificid worms and sedimentation rate of organic nitrogen in the two categories of lakes were 8.3 and 6.4% respectively. Contribution of nitrogen released daily from sediments to the dissolved inorganic nitrogen load in the water column was less than 0.5%. However, in A₁ and A₂ lakes, the released nitrogen had a potential to sustain 24.74 and 8.01%, respectively, of the annual phytoplankton production. These values suggest the significance of tubificids in keeping the eutrophication process at a high level, especially during the periods when nitrogen is the main limiting factor for phytoplankton production.     

Binding of phosphate in sediment accumulation areas of the eastern Gulf of Finland,Baltic Sea

The relationships between P and components binding P were studied by analysing the concentrations of N, P, Fe, Mn, Ca and Al in sediments and pore water along the estuarine transect of the River Neva in August 1995. The high sediment organic matter concentration resulted in low surface redox potential and high pore-water o-P concentration, whereas the abundance of amphipods resulted in high surface redox potentials and low pore-water o-P concentration. However, despite the variation in sediment organic matter and the abundance of amphipods, very reduced conditions and slightly variable concentrations of Tot-P (0.7–1.1 mg g^–1 DW) were observed in the 10–15 cm sediment depth along the estuarine gradient, indicating that the pools of mobile P were largely depleted within the depth of 0–15 cm. Multiple regression analysis demonstrated that organic matter and Tot-Fe concentration of the sediment were closely related to the variation in Tot-P concentration of the sediments (r ² = 0.817, n=32). In addition, the high total Fe:P ratio suggested that there is enough Fe to bind P in sediments along the estuarine gradient. However, low Fe_diss concentrations in the pore water of reduced sediment (redox-potential <–50 mV) indicated efficient precipitation of FeS (FeS and FeS₂), incapable to efficiently bind P. Consequently, the low Fe_diss:o-P ratio (< 1) recorded in pore water in late summer implied that Fe³⁺ oxides formed by diffusing Fe_diss in the oxic zone of the sediments were insufficient to bind the diffusing o-P completely. The measured high o-P concentrations in the near-bottom water are consistent with this conclusion. However, there was enough Fe_diss in pore water to form Fe³⁺ oxides to bind upwards diffusing P in the oxic sediment layer of the innermost Neva estuary and the areas bioturbated by abundant amphipods.