渤海湾、黄河口和长江口海域海水中颗粒氨基酸含量的分布

海水中除含有大量无机物质外,还含有种类繁多,但含量很低的有机物质,其含量约为C0.5-2.0mg／L。海水有机物质可分为溶解有机物质(DOM)和颗粒有机物质(POM)。前者为主要组分,后者所含比例很小。在大洋中POM的主要来源有:①浮游生物,尤其是浮游植物活体、死骸及其分解碎屑;②海水中进行的DOM POM的动力平衡产物。近岸海水还受河流流入的陆地POM和大气带入的陆源尘埃的影响。POM主要由蛋白质、碳水化合物、脂类等组成。POM是食碎屑动物的良好食物,它构成海洋食物链的一环,与水域生物生产力有直接的联系。POM中蛋白质含量以颗粒氨基酸(PAA)表示。Daumas(1976)曾报道过沿岸海水中PAA含量的季节变异,纪明侯等(1992年)于1980-1981年首次对青岛胶州湾内PAA含量在不同站位和不同季节中的变化特征进行调查研究。作者等继而于1982年7月、1983年10月和1984年5、7、8月乘"金星二号"考察船前后首次研究了渤海湾、黄河口和长江口附近水域中颗粒氨基酸的组成与含量在不同站位中的分布。所得结果如下。     

东海海域海水中颗粒氨基酸(PAA)的组成与含量的分布调查研究

海水中的有机物的含量微少，约为0.5~2.0 C mg/L，但其种类复杂。其中以溶解有机物(DOM)为主，而颗粒有机物(POM)所占比例则更少。大洋海水中的POM主要来源于浮游生物等的死骸及其分解碎屑；另外还有海水中受风浪影响所进行的DOM-POM的动力平衡产物。近岸海水还受河流和大气带入的陆源尘影响。POM主要由颗粒氨基酸(PAA)组成。即由Asp、Glu、Thr、Ser、Ala、Gly、Leu、Ile、Val、Met、Cys、Tyr、Lys、His、Arg、Phe、Pro等17种氨基酸组成。它们是食碎动物的主要食物，构成海洋食物链的一环，与该水域生产力有直接联系。纪明侯等(1992)于1983年和1984年首次对青岛胶州湾海水中的颗粒氨基酸的组成和含量的变化及其季节变化进行了调查研究。并且在1982年和1984年前后对渤海湾、黄河口和长江口附近水域同样调查研究了表层海水中PAA的组成与含量分布。他们还于1981年7、8月和1982年7、8月乘“科学一号”考察船进一步研究了长江口外东中国海，包括福建省外海、济州岛附近海域和黑潮流域26°00′-33°00′N、123°00′-129°00′E范围内海域的20余个站位的表层海水和部分站位上不同水深中的PAA的组成和含量。兹将调查研究结果报道如下。     

东海海域海水中颗粒氨基酸(PAA)的组成与含量的分布调查研究

海水中的有机物的含量微少,约为0.5-2.0C mg／L,但其种类复杂。其中以溶解有机物(DOM)为主,而颗粒有机物(POM)所占比例则更少。大洋海水中的POM主要来源于浮游生物等的死骸及其分解碎屑;另外还有海水中受风浪影响所进行的DOM POM的动力平衡产物。近岸海水还受河流和大气带入的陆源尘影响。POM主要由颗粒氨基酸(PAA)组成。即由Asp、Glu、Thr、Ser、Ala、Gly、Leu、Ile、Val、Met、Cys、Tyr、Lys、His、Arg、Phe、Pro等17种氨基酸组成。它们是食碎动物的     

海水中颗粒有机碳的测定方法

海水中颗粒有机物(POM)主要来自海洋浮游生物和其他动物的分解碎屑和排泄物。另外,还有经过在海水中,进行的溶解有机物(DOM)和POM之间的平衡而形成的POM。POM在海洋生物食物链中起着重要的作用。因此在研究海域生产力时DOM和POM含量的测定都是很重要的参数。通常以测定颗粒有机碳(POC)的含量作为POM的量度。关于海水POC,     

秋季东海溶解态和颗粒态氨基酸的组成与分布

本文对2012年秋季中国东海31个站位的海水样品中溶解态氨基酸(THAA)和颗粒态氨基酸(PAA)的组成与分布进行了研究。结果表明:表层海水中溶解游离氨基酸(DFAA)的平均浓度为(0.12±0.04)μmol/L(0.06—0.19μmol/L),溶解结合氨基酸(DCAA)的平均浓度为(0.61±0.51)μmol/L(0.15—1.79μmol/L),PAA的平均浓度为(0.11±0.06)μmol/L(0.02—0.27μmol/L)。THAA的水平分布特点大致为近岸高、远岸低;PAA的水平分布特点是近岸海域向远海海域分布呈现逐渐减小的趋势。THAA的垂直分布特点是由表层向底层逐渐降低。DCAA、PAA与chl a有很好的相关性,而DFAA与chl a的相关性不明显。东海表层海水中THAA的主要组分是天门冬氨酸、谷氨酸、丝氨酸、甘氨酸、苏氨酸及丙氨酸,PAA的主要组分是天门冬氨酸、谷氨酸、丝氨酸、甘氨酸、丙氨酸及亮氨酸。在表层海水中氨基酸是作为一个整体而对海洋生物地球化学过程产生影响的。     

秋季东海溶解态和颗粒态氨基酸的分布与组成*

本文对2012年秋季中国东海31个站位的海水样品中溶解态氨基酸（THAA）和颗粒态氨基酸（PAA）的分布与组成进行了研究。结果表明：表层海水中溶解游离氨基酸(DFAA)的平均浓度为0.12±0.04 μmol/L (0.06~0.19 μmol/L),溶解结合氨基酸(DCAA)的平均浓度为0.61±0.51 μmol/L (0.15~1.79 μmol/L),PAA的平均浓度为0.11±0.06 μmol/L (0.02~0.27 μmol/L)。THAA的水平分布特点大致为近岸高、远岸低;PAA的水平分布特点是近岸海域向远海海域分布呈现逐渐减小的趋势。THAA的垂直分布特点是由表层向底层逐渐降低。DCAA、PAA与Chl-a有很好的相关性,而DFAA与Chl-a的相关性不明显。东海表层海水中THAA的主要组分是天门冬氨酸、谷氨酸、丝氨酸、甘氨酸、苏氨酸及丙氨酸,PAA的主要组分是天门冬氨酸、谷氨酸、丝氨酸、甘氨酸、丙氨酸及亮氨酸。在表层海水中氨基酸是作为一个整体而对海洋生物地球化学过程产生影响的。     

胶州湾海水中溶解氨基酸的研究

于１９８６年１月－１１月用高效液相色谱法分析胶州湾１０个站位表层和底层海水中溶解游离氨基酸（ＤＦＡＡ）的组成、含量的分布及其季节变化。结果表明，７个站位的表层海水中月平均总溶解游离氨基酸（ＴＤＦＡＡ）含量范围为１．２４－２．２８ｕｍｏｌ／Ｌ。多数站位在２月份处于最低值（０．４ｕｍｏｌ／Ｌ），１１月份达最高值（５．０ｕｍｏｌ／Ｌ）。所测氨基酸中，Ｇｌｕ，Ｇｌｙ、Ａｒｇ、Ｌｅｕ，Ｏｒｎ，Ｓｅｒ等占优势     

利用水色遥感资料估算河口近岸水域叶绿素及悬浮泥沙含量的研究

海水中悬浮物质的组成及其数量分布状况与海水的理化特性、声的传播以及海洋生产力均有密切关系。因此,进行海水中浮游植物叶绿素含量及悬浮泥沙含量的调查研究是十分必要的,不同水域的海水中含有不同数量的浮游植物和悬浮泥沙。     

胶州湾可溶态碳水化合物的分布

海洋中含有大量可溶态和颗粒态有机物质,它们主要来源于海洋生物的分解、分泌产物以及浮游生物的尸骸、碎屑等,近岸海水则又有河流带入陆地的复杂有机物(包括人造有机物质)。大洋表层水的溶解有机碳浓度为0.6—1.0mgC/1,深层水为0.5mg C/1|左右。颗     

环境饵料丰度的季节变化对筼筜湖3种大型底栖动物食性的影响——来自稳定同位素的证据

测定了不同时期筼筜湖3种大型底栖动物(沙筛贝Mytilopsis sallei、日本大螯蜚Grandidierella japonica和腺带刺沙蚕Neanthes japonica)及其潜在食源的稳定同位素组成(δ13C和δ15 N),研究环境饵料丰度的季节变化对筼筜湖3种大型底栖动物食性的影响。结果显示,筼筜湖悬浮颗粒有机物(Particulate organic matter∶POM)的δ13C和δ15 N存在明显的季节变化。3月,受到输入筼筜湖的西海域海水大量陆源有机碎屑以及湖区周围的生活污水以及餐饮业输入的影响,筼筜湖POM的δ13 C和δ15 N明显贫化;而在9月,POM中δ13 C和δ15 N明显富集的内源性浮游植物的贡献增加。沙筛贝是典型的底栖滤食者,主要以POM为食,但它比POM富集的δ13 C值(3月和9月二者之间的Δδ13 C分别为2.9‰和1.6‰)表明它还摄入其他δ13 C相对富集的食物来源:石莼来源的有机碎屑可能是3月份沙筛贝δ13C富集的原因,而9月份则是由于再悬浮的底栖微藻对沙筛贝食源的贡献引起的。食碎屑的腺带刺沙蚕和日本大螯蜚在3月以石莼及其表面的附生生物为食,而9月份底栖微藻和浮游植物来源的POM是它们食源的主要贡献者。本研究的结果显示,筼筜湖3种大型底栖动物的δ15 N都出现明显的季节变化(Δδ15 N介于2.2‰~4.3‰),这是由于它们食源稳定同位素的季节性波动及其食性的季节变化引起的,而消费者食性的季节性变化则受到不同时期环境食物可利用性的影响。     

Sedimentary geology of the Columbia River Estuary

A multiyear study of the sedimentary geology of the Columbia River Estuary has provided valuable data regarding sediment distribution, bedform distribution, and suspended sediment distribution on spatial and temporal scales that permit delineation of sedimentary environments and insight into the sedimentary processes that have shaped the estuary. In comparison to other more-intensively studied estuaries in North America, the Columbia River estuary has relatively larger tidal range (maximum semidiurnal range of 3.6m) and large riverflow (6,700m³s⁻¹). Variations in riverflow, sediment supply, and tidal flow occur over a range of time scales, making the study of modern processes, as they relate to long-term effects, particularly challenging.Analyses of more than 2000 bottom-sediment grab samples indicate that the bed material of the estuary varies in a relatively narrow range between 0 and 8 phi (1.0 and 0.0039mm) with an overall mean size of 2.5 phi (0.177mm). Sediment size decreases generally in the downstream direction. Sediments from the upriver channels are coarse (1.5–2.0phi; 0.25–0.35mm) and moderately sorted; sediments in the central estuary show wider range and variation in grain size and sorting (1.75–6.0phi; 0.016–0.3mm). Sediment from the entrance region has a mean size of 2.75phi (0.149mm) and is well sorted. Seasonal changes in sediment size distributions occur and are best delineated by those samples containing more than 10% mud (silt plus clay). Sediments containing a significant fine fraction generally occur only in the peripheral bays and in channels isolated from strong currents. Thin deposits of fine sediments are occasionally found in main channels, and the ephemeral nature of these sediments suggest that they may erode and produce the silty rip-up clasts that appear intermittently in the same regions.The distribution of bedforms of various size and shape has been mapped with side-scan sonar during three seasons and at various tidal stages. The presence of bedforms with wavelengths of 6–8m and alternating slip faces about 40cm high indicates that the deeper portion of the entrance region is dominated by tidally reversing lower flow regime sediment transport. Bedforms in the upper reaches of the estuary are much larger, with heights of up to 3m and wavelengths of up to 100m. These bedforms, and the smaller, superimposed bedforms, imply downstream transport under fluvial conditions. In the central estuary, bedforms in the deep portion of the main channels are oriented upriver while those on the shallow flanks of the channels are oriented seaward. The landward limit of upriver bedform transport varies seasonally in response to riverflow fluctuations.A complex array of sedimentary environments exists in the Columbia River estuary. Each environment is influenced by the relative importance of waves, fluvial currents, and tidal currents, as modified by the presence or absence of estuarine circulation, vegetation, or human activity. The importance of these enviroments to the ecosystem of the estuary is discussed in subsequent papers in this volume.     

夏季闽江口和椒江口浮游动物群落结构的比较

根据2008年9月在闽江口水域和2010年8月在椒江口水域的调查资料,对两个河口浮游动物的种类组成、生态类群、优势种和生态适应差异进行分析比较,探讨夏季闽江口海域和椒江口海域浮游动物群落结构的区别及其组成受水团变化的影响。研究结果表明:夏季,椒江口受上升流的影响出现13个暖温带种,导致椒江口(44)水域浮游动物种类数要大于闽江口(36);闽江口海域夏季主要受到台湾暖流的影响,6个优势种全部为亚热带种,椒江口有7个优势种,包括4个亚热带种和3个暖温带种;从适温性上看,闽江口和椒江口均主要以亚热带种为主,椒江口由于上升流的原因出现较多数量的暖温带种,从适盐性上看,椒江口主要以近海种为主,闽江口主要以外海种为主,这是闽江口和椒江口浮游动物生态类群的主要差异;闽江口浮游动物群落结构主要受到台湾暖流和沿岸流的影响,而椒江口主要受到浙江近海上升流和沿岸流的影响,通过对两个河口群落结构的比较和生态适应差异的分析,表明水团是各自浮游动物群落结构的形成过程中的一个重要因素。     

Historical changes in the Columbia River Estuary

Historical changes in the hydrology, sedimentology, and physical oceanography of the Columbia River Estuary have been evaluated with a combination of statistical, cartographic, and numerical-modelling techniques. Comparison of data digitized from US Coast and Geodetic Survey bathymetric surveys conducted in the periods 1867–1875, 1926–1937, and 1949–1958 reveals that large changes in the morphology of the estuary have been caused by navigational improvements (jetties, dredged channels, and pile dikes) and by the diking and filling of much of the wetland area. Lesser changes are attributable to natural shoaling and erosion. There has been roughly a 15% decrease in tidal prism and a net accumulation of about 68 × 10⁶m³ of sediment in the estuary. Large volumes of sediment have been eroded from the entrance region and deposited on the continental shelf and in the balance of the estuary, contributing to formation of new land. The bathymetric data indicate that, ignoring erosion at the entrance, 370 to 485 × 10⁶m³ of sediment has been deposited in the estuary since 1868 at an average rate of about 0.5 cm y⁻¹, roughly 5 times the rate at which sea level has fallen locally since the turn of the century.Riverflow data indicate that the seasonal flow cycle of the Columbia River has been significantly altered by regulation and diversion of water for irrigation. The greatest changes have occurred in the last thirty years. Flow variability over periods greater than a month has been significantly damped and the net discharge has been slightly reduced. These changes in riverflow are too recent to be reflected in the available in the available bathymetric data.Results from a laterally averaged, multiple-channel, two-dimensional numerical flow model (described in Hamilton, 1990) suggest that the changes in morphology and riverflow have reduced mixing, increased stratification, altered the response to fortnightly (neap-spring) changes in tidal forcing, and decreased the salinity intrusion length and the transport of salt into the estuary.The overall effects of human intervention in the physical processes of the Columbia River Estuary (i.e. decrease in freshwater inflow, tidal prism, and mixing; increase in flushing time and fine sediment deposition, and net accumulation of sediment) are qualitatively similar to those observed in less energetic and more obviously altered estuarine systems. A concurrent reduction in wetland habitats has resulted in an estimated 82% reduction in emergent plant production and a 15% reduction in benthic macroalgae production, a combined production loss of 51,675 metric tons of organic carbon per year. This has been at least partially compensated by a large increase in the supply of riverine detritus derived from freshwater phytoplankton primary production. Comparison of modern and estimated preregulation organic carbon budgets for the estuary indicates a shift from a food web based on comparatively refractory macrodetritus derived from emergent vegetation to one involving more labile microdetritus derived from allochthonous phytoplankton. The shift has been driven by human-induced changes to the physical environment of the estuary.While this is a relatively comprehensive study of historical physical changes, it is incomplete in that the sediment budget is still uncertain. More precise quantification of the modern estuarine sediment budget will require both a better understanding of the fluvial input and dredging export terms and a sediment tranport model designed to explain historical changes in the sediment budget. Oceanographic studies to better determine the mechanisms leading to the formation of the turbidity maximum are also needed. The combination of cartography and modelling used in this study should be applicable in other systems where large changes in morphology have occurred in historical time.     

珠江河口界面特征与河口管理理念

河口是河流系统与海洋系统之间的界面,它首先是河流与海洋之间的物质界面。河流水体与海洋水体间最大的物质差异是盐分,因此,采用盐度作为河口界面的界定标准,将河口界面界定为盐度为0.5~30的由冲淡水控制的河口中心区域。在此基础上应用界面理论,分析了河口的渗透性和防御性及其动力、沉积、生物与地貌响应。借鉴Gilbert三角洲的动力分类方法,将河口界面按动力结构分为径流优势型、潮汐优势型、波浪优势型及其过渡类型。每一种河口界面又可细分为动力、沉积、地貌及生态等次一级界面。在珠江三角洲地区,磨刀门、蕉门河口等径流优势型河口界面主要承担泄洪任务,而虎门、崖门等潮汐优势型河口界面在纳潮能力上更有优势,其间通过河道支汊相互沟通和联系,形成了珠江河口界面的多层次结构。河口界面动力的复杂性,构成了河口界面形态和功能的复杂性。这些功能包括开发利用功能、生态功能、防洪功能和社会服务功能。河口管理的最高目标是河口的永续健康、结构和功能彼此协调,保持河口界面结构和功能的完整性。河口界面的复杂性对河口管理提出了更高的要求,要注重河口管理内容的综合性、问题的复杂性和管理效应的长周期性。针对珠江河口生境退化、海岸侵蚀、污染严重、咸潮活动加剧和口门淤积造成排水不畅等诸多问题,以及河口无序开发利用、管理体制混乱、公众参与少的管理现状,结合珠江河口界面整体、动态、彼此联系的特点,提出珠江河口管理"科学、和谐、安全和预警"的管理理念,由行政管理转变为服务管理,切实做好珠江河口管理工作。     

珠江河口特征认知的发展

人们对珠江河口的认知发生过几次飞跃。第一次认知飞跃，柯维廉（W.Olivecrona）1915年首次提出了珠江三角洲的概念；第二次认知飞跃，吴尚时1937年证明海水曾深入广州形成珠江河口湾并发育三角洲，1941和1947年先后著文肯定了珠江三角洲的存在，并确定了其主体范围；第三次认知飞跃，曾昭璇1980年提出了冲缺三角洲的概念，1997年提出了串珠状冲缺三角洲发育模式，揭示了珠江三角洲发展的时间与空间位置；第四次认知飞跃，赵焕庭1982年揭示了珠江三角洲叠置晚更新世晚期老三角洲与全新世中期现代三角洲，新资料显示还存在晚更新世中期三角洲；第五次认知飞跃，赵焕庭等于1973-1982年间运用西蒙斯优势流概念和河口盐水楔理论研究了口门和河口湾滩槽地形的发育演变；第六次认知飞跃，吴超羽等于2006年创造性应用自己研发的长周期机理模型和沉积学、地貌动力学等多学科互证，量化再现了珠江三角洲6~2.5 ka BP"镶嵌式"演变过程。     

潍河口水文特征分析

根据1997年和1998年两次潍河河口水文调查资料分析了潍河河口的水文特征及建闸截流的影响。结果说明,潍河是一个M₂潮占主导地位的不规则半日潮弱潮河口。上游建闸截流使得河口5、6月份的水温降低而盐度增高,并减少了口门内重力环流的出现机率。     

鸭绿江口的潮汐特征

对1985年和1996年鸭绿江口6个站位的水位数据进行调和分析,结果显示,鸭绿江口的潮汐以半日潮为主,M2 分潮占优.此外,潮高日不等和涨落潮历时不等的现象较为显著,与实测水位结果一致;由口门向上游方向潮差逐渐减小,落潮历时增大,涨潮历时减小,且落潮历时长于涨潮历时.最下游枢岛验潮站的平均海平面为0.08 m;最上游丹东站为1.14 m(1985);从下游至上游平均海平面呈现增大趋势,主要原因是鸭绿江口为向上游迅速束窄的狭长形喇叭口,大面潮水涌入后水位被束窄抬升所致.利用调和常数计算的潮位与观测数据基本吻合,表明研究区观测期间水位主要受潮汐作用的控制.     

珠江口浮游桡足类摄食研究

根据珠江口2002年7月(夏季)、2003年1月(冬季)和2003年4月(春季)3个航次浮游桡足类现场调查及其肠道色素实验数据,分析了浮游桡足类食性特点、肠道色素含量及其对浮游植物和初级生产力的摄食压力。根据齿缘指数对珠江口浮游桡足类食性分析,发现捕食性桡足类种数高于草食和杂食的滤食性种数,而其丰度低于后两者。珠江口桡足类个体肠道色素平均含量为冬季高于春季和夏季,而对浮游植物现存量和表层初级生产力的摄食压力均为夏季高于春季和冬季。夏、冬季桡足类肠道色素含量与水体叶绿素a浓度呈正相关,春季不相关。     

九龙江口枝角类的分布

本文根据1983年2月至1984年1月在九龙江口采集的浮游动物样品,并参考1979年2月以来所采的样品,分析报道了该海区枝角类的种类组成和数量分布.共鉴定枝角类31种,以淡水类群占优势,种数季节分布为双周期型,总量分布为单周期型,种数和总量在河口上部数量高,在口部数量低。文中还讨论了其分布与环境因素的关系。     

Hydrochemistry of the Tumen River Estuary,Sea of Japan

The hydrological and hydrochemical parameters of the Tumen River estuary were collected at 13 stations in May and October 2015. Vertical temperature, conductivity, dissolved oxygen, chlorophyll fluorescence, and turbidity profiles were obtained. Water was sampled from the surface and bottom layer. The water samples were analyzed for major ions, pH, salinity, concentrations of dissolved oxygen, major nutrients, dissolved organic carbon, humic matter, and δ¹⁸О and δD isotopes. This estuary is attributed to microtidal type with a flushing time of about 10 h. A phytoplakton bloom occurred in the top layer of the estuary. For surface horizons, the hydrochemical parameters show a linear correlation with salinity. In the bottom horizons, all these parameters, except for major ions and δ¹⁸О and δD isotopes, reveal substantial nonconservative behavior. The nonconservative behavior of the hydrochemical parameters in the bottom waters was mainly caused by degradation of the phytoplankton biomass at the water/sediment interface. Hypoxic conditions were established in the bottom waters of the estuary in May.