表面波对于混合层中湍流强化作用的实验研究

文中介绍了一项二层流体内密度界面处湍流挟卷的实验室研究。实验结果表明,有表面波存在时,混合层下密度界面处的挟卷速度较之无表面波时有明显的增大。这个实验事实的可能的海洋学含义为:不破碎的表面势波对于混合层内湍流有强化的作用,因而成为在考查密跃层变迁问题中应考虑在内的动力因素。     

第23章 DNS模式:一种为大洋波浪预报而改进的谱模式

23.1 介绍 模拟与频率和方向相关的大洋波谱F（f,θ）的工作是极其困难的。唯一有点统一的理论（Hasselmann,1967）也还没有简化成一种实用形式。这篇研究中所探讨的是结合零散的,现有的理论,以达到这样一种目的:即发展一种与我们目前对风浪成长谱的了解相一致 ·95.的波谱模式。本章中我们将讨论一种离散的谱模式,这种模式采用了一种改进的能量传播的特征方法。数值方法最早是由Barnett等（1969）提出的。     

大西洋扇贝贝壳生长年轮的氧同位素研究

两只活的大洋扇贝Placopecten magellanicus分别于1983和1985年采自加拿大诺瓦·斯科舍省布朗斯浅滩,其氧同位素记录展示出一种年度性的循环,并与由环境海水的实测温度和同位素组成所预计的贝壳同位素组成十分接近。外生长线的位置与这些循环中δ~(18)O的最大值吻合,这说明外生长线于底层海水温度最低时(春季)形成。据测定的δ~(18)O的结果证明,外生长线是年度性形成的,这与生物学证据一致。     

由偏顶蛤贝壳中稳定同位素剖面追溯海水温度记录

本文用在加拿大诺瓦·斯科舍省芬克湾采集到的两只活体偏顶蛤(Modiolus)贝壳上的氧同位素组成重建了过去十年间的底层海水温度记录,它也可作为一种独立的方法来确定贝壳上外生长线的沉积时间。由于对贝壳进行了密集采样(可多至每个贝壳沉积年份取15个样品),贝壳上的δ~(16)O变化反映了芬克湾底层海水的季节性变化。两只贝壳所得的温度剖面符合得很好,说明它们基本上是与真实的环境温度相对应的。本研究证明在海胆疾病爆发时底层海水的温度并没有异常升高,这说明疾病传播的关键因素是带病的生物体,而不是温度。同位素技术也说明了在贝壳外表面上可见的外生长线是年轮性的,它们是在每年冬季最低水温时沉积出来的。     

五种植物提取液的抗鱼病菌和抗鱼病毒效应(英文)

本文旨在探索用廉价的野生植物防治鱼病。所用的植物有牛繁缕(Stellaria aqu-atica),双花凤仙(Impatiens biflora),夜来香(Oenothera biennis),艾草(Artem-isia vulgaris)和忍冬(Lonicera japonica)。用作试验的鱼病菌共13种(18个菌株),分属于气单孢菌属、假单孢菌属、爱德华氏菌属、耶尔森氏菌属、弧菌属。所用的鱼病毒为传染性胰脏坏死病毒IPNV,传染性造血组织坏死病毒IHNV。上述病原微生物均获自美国马里兰大学微生物系。实验结果表明,五种植物提取液均有不同程度的抗鱼病菌作用,其中以牛繁缕的抗菌谱最广,作用力最强。忍冬、艾草、牛繁缕有抗鱼病毒作用。其中以忍冬的效果最好,它能抑制IPNV和IHNV。而艾草和牛繁缕只能抑制IHNV。     

Using benthic macrofauna to assess environmental quality of four intertidal mudflats in Hong Kong and Shenzhen Coast

Abstract-Intertidal zone is a significant wetland between land and ocean. It plays an important rolein maintaining local ecological balance. Both Mai Po and Futian intertidal mudflats are located in Shen-zhen Bay and are important "refueling" point along the East Asian/Australian flyway of migratory birds.The environmental quality of Mai Po and Futian mudflats have aroused great concern due to rapid eco-nomic developments in Hong Kong and Shenzhen in recent decades. Microinfauna of Mai Po and Futianmudflats was investigated in December 2000 and the faunal data were used to assess their environmentalquality. Two other mudflats, namely Ma Wan Typhoon Shelter (a more disturbed area) and Luk Kengintertidal mudflat (a place with relatively less human disturbance), were also sampled for macroinfaunaand used as reference mudflats. Shannon-Weaver species diversity index (I_(sd)), biotic coefficient (C_b)and macrofaunal pollution index (I_(mp)) of the macrofauna community on four intertidal mudflats wereused to     

重金属对海洋围隔生态系中初级生产力的影响

1985年4月,中国和加拿大科学家首次在厦门合作进行添加重金属(Cu,Hg,Zn,Pb,Cd)的围隔生态系实验,实验是在海边大水池内的塑料袋中进行,实验结果说明低水平(ppb)混合重金属对浮游植物的影响首先表现在对光合作用速率的抑制作用,以及在浓度较低的情况下可能引起的种群演替现象,本文还阐述了颗粒有机碳(POC)和颗粒有机氮(PON)与初级生产力的相关性.     

Environmental consequence analyses of fish farm emissions related to different scales and exemplified by data from the Baltic--a review

The aim of this work is to review studies to evaluate how emissions from fish cage farms cause eutrophication effects in marine environments. The focus is on four different scales: (i) the conditions at the site of the farm, (ii) the local scale related to the coastal area where the farm is situated, (iii) the regional scale encompassing many coastal areas and (iv) the international scale including several regional coastal areas. The aim is to evaluate the role of nutrient emissions from fish farms in a general way, but all selected examples come from the Baltic Sea. An important part of this evaluation concerns the method to define the boundaries of a given coastal area. If this is done arbitrarily, one would obtain arbitrary results in the environmental consequence analysis. In this work, the boundary lines between the coast and the sea are drawn using GIS methods (geographical information systems) according to the topographical bottleneck method, which opens a way to determine many fundamental characteristics in the context of mass balance calculations. In mass balance modelling, the fluxes from the fish farm should be compared to other fluxes to, within and from coastal areas. Results collected in this study show that: (1) at the smallest scale (<1 ha), the "footprint" expressing the impact areas of fish cage farm often corresponds to the size of a "football field" (50-100 m) if the annual fish production is about 50 ton, (2) at the local scale (1 ha to 100 km2), there exists a simple load diagram (effect-load-sensitivity) to relate the environmental response and effects from a specific load from a fish cage farm. This makes it possible to obtain a first estimate of the maximum allowable fish production in a specific coastal area, (3) at the regional scale (100-10,000 km2), it is possible to create negative nutrient fluxes, i.e., use fish farming as a method to reduce the nutrient loading to the sea. The breaking point is to use more than about 1.1 g wet weight regionally caught wild fish per gram feed for the cultivated fish, and (4) at the international scale (>10,000 km2) related to the Baltic Proper, the contribution from fish farms to the overall nutrient fluxes are very small. We have also given two case-studies at the local scale where the impact of the fish farm emissions are greatest and the idea is to identify coastal areas unsuitable and suitable for fish cage farms and the reasons why. It should also be stressed that the results presented here are exemplified using emissions from fish farms, but that the underlying principles to evaluate the ecosystem effects of nutrient discharges from point source emissions are valid in a wider and more general perspective.     

Correlative changes in metabolism and DNA damage in turbot (Scophthalmus maximus) exposed to benzo[a]pyrene

Juvenile turbot (Scophthalmus maximus) were injected intraperitoneally with either corn oil or 5 mg/kg benzo[a]pyrene (BaP) dissolved in corn oil and sampled I and 3 days after injection. After 1 day, no elevation of 7-ethoxyresorufin O-deethylase (EROD) activity was observed, however bile metabolites (BaP-7,8 dihydrodiol representing 70% of the total metabolites) and a single hepatic DNA adduct spot (0.47 adducts/10(8) nucleotides) identified by 32P-postlabelling were formed. No BaP metabolites or DNA adducts were observed in either control or carrier control fish. Fish sampled after 3 days reported 5-fold higher (P < 0.05) levels of EROD activity, a shift in the bile metabolite profile towards BaP phenol formation (1OH and 30H BaP comprising up to 60% of total metabolites detected) and the formation of two adduct spots (0.86 and 0.71 adducts/10(8) nucleotides). These results show that BaP can be metabolised and form hydrophobic DNA adducts in turbot without EROD elevation. Following EROD elevation, a shift in the profile of both BaP metabolites and BaP metabolite-DNA interactions occurs indicative of other oxidative processes.