SII型海洋重力仪稳定平台颤动故障与排除方法

S型海洋重力仪是目前海洋重力测量中较为常用的一种仪器，其产品性能也逐步得到提高。介绍了进行全自动化控制升级后，最新引进的SⅡ型海洋重力仪使用中出现的稳定平台颤动故障现象及排除办法。     

南沙群岛西南陆架区条尾鲱鲤资源状况研究

根据2003年南沙群岛西南陆架区春秋两季调查资料,分析南沙群岛西南陆架区条尾鲱鲤的资源现状.结果表明,渔获率有明显的季节变动,秋季（1.76kg/h）高于春季（0.08kg/h）,春季密集分布于91～100m水深,秋季密集分布于71～80m水深.其群体组成也有季节差异,春季的平均体长、平均体重大于秋季,春季优势体长组为101～110mm,秋季优势体长组为91～100mm,渔获中不足1龄鱼占多数,其资源密度及现存资源量分别为12.02kg/km^2 和880.82t,现存资源量只有原始资源量的54.92%,该鱼种资源已接近衰退状态.文中并讨论合理利用该资源的措施.     

鲈鱼胆汁中芘及代谢产物含量与水体中芘含量的关系

运用GC—MS的方法和荧光分光光度法，研究鲈鱼分别暴露于0．1、1．0和10．0μg／dm^3质量浓度芘溶液中7d，水体中芘及其鲈鱼胆汁中芘和1-羟基芘含量的变化,实验结果显示：(1)鲈鱼对水体中的芘具有非常显著的去除作用。(2)随着芘暴露浓度的增大，鲈鱼对芘的代谢去除作用增强。(3)随着暴露时间的延长和芘暴露浓度的增大，胆汁的1-羟基芘浓度递增。(4)鲈鱼胆汁具有较高的芘浓度，对海水中的芘具有较强的富集作用。(5)鲈鱼胆汁的1-羟基芘及芘的浓度与水体芘浓度均具有很好的相关性，对于指示水体的芘污染程度具有一致性；可作为指示水体芘污染程度的生物标志物。     

海洋木栖真菌抗菌活性的初步研究

从福建厦门海沧、集美及漳州浮宫等地采集到的红树林等海洋潮间带的各种腐木样品中分离得到176株海洋木栖真菌,对其进行抗菌活性检测.其结果表明共有96株海洋木栖真菌对大肠杆菌、枯草杆菌及白色假丝酵母中的一种或多种拮抗指示菌具有抑制作用,占供测菌株总数的54.5%.在这些活性菌株中,红树源菌株拮抗比例为30.2%,非红树源菌株拮抗比例为69.8%.具有抗菌活性的菌株主要分布于15个属中,包括木霉Trichoderma、青霉Penicillium、拟青霉Paecilomyces和一些不产孢的分类群.某些稀有真菌如盘多毛孢Pestalotia、茎点霉Phoma也具有一定的抗菌活性.     

GPS数据采集技术及其在海洋调查中的应用

本文应用VB6．0开发了智能化的GPS数据采集软件．对该软件的功能进行了简单的介绍，同时对一些关键技术作了较详细的描述。利用该软件、GPS接收机及PC机的组合，可对走航式测量仪器(或移动设备)进行实时定位并保存定位记录，且大大减少一些不必要的数据，使得软件更为实用。     

海洋细菌抑菌活性菌株的筛选

从不同海区的海洋底质，生物样，水样中分离到480株海洋细菌，其中包括150株芽孢细菌和108株粪大肠杆菌，利用纸片法对其抑菌活性进行检测，结果表明：117株海洋细菌具有抑菌活性，占总分离菌株的24.4%；一般细菌，芽孢细菌，粪大肠杆菌的抑菌活性菌株分别占各供测菌株的17.1%,27.3%,35.2%；抑菌活性菌株的比例与样品来源密切相关，且各类海洋细菌的抗菌谱有很大的不同。     

台湾南湾秋末冬初水螅水母类的组成与分布

本文分析了2001年11月2～3日和12月8～10日在台湾南湾12个测站采集的表层和底层92份浮游动物样品,共鉴定水螅水母18种,其中8种是台湾周围海域的新记录.半口壮丽水母(Aglaura hemistoma)和四叶小舌水母(Liriope tetraphylla)为优势种,它们在11月和12月分别占水螅水母类总量的77％和94％以上.南湾水螅水母类的种类数和个体丰度均以12月(17种,3102×10~(-3)个/m~3)明显多于11月(6种,72×10~(-3)个/m~3).在冬季,外海高盐水团是影响水螅水母类分布的主要因素,盐度与水螅水母类多样性指数的相关关系显著,文章还比较了南湾与邻近海区水螅水母类的季节变化.     

Retention of arsenic and phosphorus in iron-rich concretions of Tagus salt marshes

Iron-rich concretions are frequently found around plant roots in Tagus estuary (Portugal) where radial delivery of O₂ takes place. Salt marsh sediments exhibit cracks that are an additional feature to introduce O₂ and other solutes in the upper sediments. Metal concentrations in salt marsh sediments are clearly above the background levels reflecting the anthropogenic sources from a large city with 2.5 million inhabitants, and several industrial centres. In order to evaluate how both oxidised structures influences the redistribution of redox sensitive elements in salt marsh sediments, concretions were collected from roots of Halimione portucaloides below the oxygenated zone. These tubular cylindrical structures were analysed for Fe, Al, Mn, As, and P along 1-cm radial transect in a millimetre scale from the inner part to the adjacent anoxic sediment. In addition, oxidised cracks were analysed for the same spatial resolution, from the sediment–water interface to anoxic layers (2-cm transept). The parallelism between Fe, As, and P concentrations at this microscale is the most noticeable aspect. Iron and As presented very high concentrations in the 4-mm concretions (3.4 mmol g⁻¹ and 3.1 μmol g⁻¹, respectively) and decreased sharply to the host sediment. Oxygen released from roots oxidise the solid sulphides, and the reduced Fe and As are transported towards the root by both diffusion and pore water flow associated with the root water uptake. Subsequently, Fe(III) precipitates and As is retained by sorption and/or coprecipitation. These elements are also enriched in the first 2-mm of oxidised cracks, but in lower concentrations (50% and 30%, respectively). Manganese concentrations in concretions were low (11.8 μmol g⁻¹), indicating that Fe dominates the sediment chemistry. Phosphorus and iron concentrations in the ascorbate fraction were higher in the oxidising surfaces of concretions (10.7 μmol g⁻¹ and 1.6 mmol g⁻¹, respectively) and of cracks (5.1 μmol g⁻¹ and 0.47 mmol g⁻¹). The parallelism of Fe and As distributions includes not only their similar redox chemistries, but also that to phosphate, including control by coprecipitation of the host iron phases. The mechanisms involved in the mobilisation of As and P are however different, whereas As comes from the oxidation of iron sulphides; dissolved P derives from reduction of ferri-hydroxide phases.