上新世——早更新世青藏高原北缘隆升的磁性地层学证据

对新疆叶城剖面西域砾岩及下伏第三纪地层的磁性地层学研究表明 ,西域砾岩的沉积时代为晚上新世至早更新世 ,磁性地层年龄为 3.5至 <1.8Ma。阿图什组沉积于早上新世 ,古地磁年龄为 4 .6～ 3.5 Ma。阿图什组以砂岩和粉砂岩为主夹薄层砾岩 ,为河流相及冲积扇前缘相。西域砾岩以厚层砾岩为主夹风成粉砂岩 ,为典型洪积—冲积扇堆积。西域砾岩的沉积反映了青藏高原北缘晚上新世至早更新世强烈的隆起和剥蚀     

基于遥感的江苏省大陆岸线岸滩时空演变

基于江苏省1984-2016年61景多源遥感影像数据和部分实测潮位、坡度数据,利用遥感技术结合改进的水边线方法提取了多时相的海岸线和平均大潮低潮线,研究了江苏省绣针河口至连兴河口大陆岸线岸滩的时空演变特征。结果表明：1984-2016年,由于海岸带开发,江苏省的海岸线整体以向海推进为主,自然岸线由458.24 km逐渐减少至166.74 km,人工岸线由163.66 km快速增加至598.74 km,大陆岸线长度由621.90 km增加至765.48 km。发生位置和长度变化的岸段中,淤长岸段长127.62 km,年均向海推进83.03 m;围垦岸段长401.21 km,年均向海推进87.63 m;冲刷岸段长71.17 km,年均离海后退10.81 m;围垦被侵蚀岸段长25.95 km,年均离海后退8.64 m。海岸线的空间变化导致江苏省沿海陆地面积净增加104332 hm²,其中由于围垦增加的陆地面积98520 hm²,围垦是陆地面积增加的主要原因。海岸线的离海后退主要发生在废黄河三角洲岸段,但是到2008-2016年,岸线的侵蚀范围已向南扩大至新洋河口至斗龙港岸段。受围垦活动及岸线侵蚀影响,江苏省潮间带坡度不断变陡,统计断面的平均坡度由1.4‰增加至1.9‰,其中废黄河三角洲岸段的中山河口至扁担河口岸段坡度最陡,基本在3~14‰之间;辐射沙洲陆岸岸段坡度最为平缓,但坡度也在逐渐陡化,由0.9‰增加至1.5‰。潮间带面积由271747 hm²减少至168645 hm²,减幅38%;潮间带平均宽度由5064 m减少至3096 m,减幅39%。     

应用改进的相干算法提高三维地震资料解释精度

作者在文中详细探讨了C1、C2和C3三种相干算法及其。根据三维地震数据体的特点提出了实用的相干算法，并编制了相应的软件。我们对三种相干算法对应相干数据体的解释结果进行了细致的分析，C2相干算法基本能够平衡提高横向分辨率和信噪比之间的矛盾，而C3相干算法则取得了更精确的效果。     

真江蓠杭州湾海域栽培试验及生态因子对藻体生长的影响

在杭州湾上海金山海域进行了真江蓠(Gracilaria verrucosa)栽培试验并在实验室内研究了温度、盐度和光照强度对真江蓠生长的影响。结果表明,温度、盐度和光照强度对真江蓠的生长影响极显著(P0.01)。真江蓠生长适宜温度为20~30℃;适宜盐度为15~25;适宜光照强度在90μmol/(m2.s)左右。温度、盐度和光照强度对真江蓠生长存在显著的交互效应(P0.05),三者的最佳组合为温度25℃、盐度20和光照强度90μmol/(m2.s)。海区栽培实验表明真江蓠可在杭州湾海域正常生长,全年平均特定生长率(RSG)为9.42%/d。     

氨氮胁迫对刺参几种免疫酶活性的影响

以养殖刺参(Apostichopus japonicus)为研究对象,对不同浓度的氨氮处理及病菌感染条件下刺参体腔液免疫酶的变化进行了测定.结果表明:随着氨氮处理强度的增加,刺参体腔液中超氧化物歧化酶(SOD)、碱性磷酸酶(ALP)、谷胱甘肽过氧化物酶(GPx)及溶菌酶(LSZ)活性呈现先升高后降低的趋势,而同时感染病菌的情况下,较低质量浓度的氨氮胁迫可使SOD、GPx、ALP及LSZ活性上升,但在较高浓度氨氮处理时,酶活性的诱导则受到抑制.说明适宜浓度的氨氮处理可增强刺参的免疫力,从而减轻病菌感染对刺参造成的免疫功能损伤和提高刺参抗病力.刺参在感染病原菌假交替单胞菌(Pseudoalte-romonas sp)的条件下,3 mg/L、4 mg/L和6 mg/L浓度的氨氮处理第6天,刺参的累积发病死亡率分别为44.4％、55.6％和72.2％,高于对照组,表明较高浓度的氨氮胁迫能够显著降低刺参的免疫力,增加对病原菌的易感性.因此,在刺参养殖过程中,氨氮浓度的调控具有重要的意义.     

电感耦合等离子体质谱法测定地质样品中稀散元素铬镓铟碲铊

采用电感耦合等离子体质谱技术,研究了地质样品中稀散元素铬、镓、铟、碲、铊含量的质谱分析方法。研究确定了最佳测定酸度、干扰元素的校正方法,结果令人满意。方法检出限为0.001 3~0.063μg/g,精密度(RSD,n=11)为2.00%~4.87%,优于其他方法,具有较好的灵敏度。方法快速、简便,结果准确,可用于地质样品中稀散元素铬、镓、铟、碲、铊含量的分析,适用于批量样品的快速测定。     

海岸资源质量管理与海岸综合整治修复对策探讨

文章讨论海岸资源质量管理的计量手段,根据海岸的类型、资源功能以及自然演变和开发利用过程中出现的问题,探讨海岸资源质量管理的内涵和海岸综合整治修复的对策。建议制定《海岸线修测技术规范》,明确海岸线修测技术方法和海岸线长度计量方法,为海岸资源质量管理奠定计量基础;针对不同的海岸类型和开发利用方式,制定《海岸资源质量评价技术标准》,适应差别化的海岸管控政策;加强海岸资源综合统筹规划管理,强化海岸综合整治修复,保护自然海岸和人工海岸生态环境,修复恢复严重影响海岸生态环境和废弃的人工海岸,最大限度地保育自然海岸。     

Carbon pools and fluxes in the China Seas and adjacent oceans

The China Seas include the South China Sea, East China Sea, Yellow Sea, and Bohai Sea. Located off the Northwestern Pacific margin, covering 4700000 km~2 from tropical to northern temperate zones, and including a variety of continental margins/basins and depths, the China Seas provide typical cases for carbon budget studies. The South China Sea being a deep basin and part of the Western Pacific Warm Pool is characterized by oceanic features; the East China Sea with a wide continental shelf, enormous terrestrial discharges and open margins to the West Pacific, is featured by strong cross-shelf materials transport; the Yellow Sea is featured by the confluence of cold and warm waters; and the Bohai Sea is a shallow semiclosed gulf with strong impacts of human activities. Three large rivers, the Yangtze River, Yellow River, and Pearl River, flow into the East China Sea, the Bohai Sea, and the South China Sea, respectively. The Kuroshio Current at the outer margin of the Chinese continental shelf is one of the two major western boundary currents of the world oceans and its strength and position directly affect the regional climate of China. These characteristics make the China Seas a typical case of marginal seas to study carbon storage and fluxes. This paper systematically analyzes the literature data on the carbon pools and fluxes of the Bohai Sea,Yellow Sea, East China Sea, and South China Sea, including different interfaces(land-sea, sea-air, sediment-water, and marginal sea-open ocean) and different ecosystems(mangroves, wetland, seagrass beds, macroalgae mariculture, coral reefs, euphotic zones, and water column). Among the four seas, the Bohai Sea and South China Sea are acting as CO_2 sources, releasing about0.22 and 13.86–33.60 Tg C yr~(-1) into the atmosphere, respectively, whereas the Yellow Sea and East China Sea are acting as carbon sinks, absorbing about 1.15 and 6.92–23.30 Tg C yr~(-1) of atmospheric CO_2, respectively. Overall, if only the CO_2 exchange at the sea-air interface is considered, the Chinese marginal seas appear to be a source of atmospheric CO_2, with a net release of 6.01–9.33 Tg C yr~(-1), mainly from the inputs of rivers and adjacent oceans. The riverine dissolved inorganic carbon (DIC) input into the Bohai Sea and Yellow Sea, East China Sea, and South China Sea are 5.04, 14.60, and 40.14 Tg C yr~(-1),respectively. The DIC input from adjacent oceans is as high as 144.81 Tg C yr~(-1), significantly exceeding the carbon released from the seas to the atmosphere. In terms of output, the depositional fluxes of organic carbon in the Bohai Sea, Yellow Sea, East China Sea, and South China Sea are 2.00, 3.60, 7.40, and 5.92 Tg C yr~(-1), respectively. The fluxes of organic carbon from the East China Sea and South China Sea to the adjacent oceans are 15.25–36.70 and 43.93 Tg C yr~(-1), respectively. The annual carbon storage of mangroves, wetlands, and seagrass in Chinese coastal waters is 0.36–1.75 Tg C yr~(-1), with a dissolved organic carbon(DOC) output from seagrass beds of up to 0.59 Tg C yr~(-1). Removable organic carbon flux by Chinese macroalgae mariculture account for 0.68 Tg C yr~(-1) and the associated POC depositional and DOC releasing fluxes are 0.14 and 0.82 Tg C yr~(-1), respectively. Thus, in total, the annual output of organic carbon, which is mainly DOC, in the China Seas is 81.72–104.56 Tg C yr~(-1). The DOC efflux from the East China Sea to the adjacent oceans is 15.00–35.00 Tg C yr~(-1). The DOC efflux from the South China Sea is 31.39 Tg C yr~(-1). Although the marginal China Seas seem to be a source of atmospheric CO_2 based on the CO_2 flux at the sea-air interface, the combined effects of the riverine input in the area, oceanic input, depositional export,and microbial carbon pump(DOC conversion and output) indicate that the China Seas represent an important carbon storage area.     

混合吸附剂分离富集-电感耦合等离子体质谱法测定地质样品中铂钯金

贵金属分析应用火试金法分离富集时,试金配料复杂、耗时较长,分析成本相对较高,空白较难控制.本文建立了采用过氧化氢-盐酸湿法分解样品,电感耦合等离子体质谱同时测定地质样品中Pt、Pd、Au的分析方法.在10％的盐酸介质中,以LSC-400巯基树脂和活性炭为混合吸附剂,采用动态吸附方式对样品中的Pt、Pd、Au分离富集,用Lu作内标元素,195 Pt、197 Au、108 Pd为待测同位素消除了非谱线干扰和谱线干扰,三元素的回收率均大于96.4％.方法检出限(3σ):Pt为0.06 ng/g,Pd为0.08 ng/g,Au为0.12 ng/g,优于火试金等其他分离富集方法的检出限.应用于测定国家标准物质,Pt、Pd、Au的测定结果与标准值相符,12次测定的相对标准偏差均小于16.1％,满足区域地球化学调查样品的分析要求.该方法操作简便、成本低廉,提高了分析速度,有效地降低了测试过程的空白值.     

海南岛“0810”特大暴雨物理量诊断及多普勒特征分析

应用常规观测、海口多普勒回波及NCEP1×1°再分析等资料,对2008年10月12～15日海南特大暴雨成因进行诊断分析,并揭示了暴雨过程中的多普勒回波特征。结果表明：导致海南岛产生强降水的主要原因是热带低压移动缓慢和弱冷空气的低层入侵;当冷暖空气交绥,大气温湿结构发生突变,θse面陡立造成对流系统斜压发展,激发位势不稳定能量释放。正差动假相当位温平流意味着低层暖湿空气的平流大于高层,加强了层结对流不稳定发展;在斜压扰动作用下,对流层中层正差动涡度平流和低压东侧的暖平流破坏了海南岛的准地转平衡,动力强迫和热力强迫共同作用激发了次级环流,导致暴雨区上空的垂直运动的发展,促使暴雨增强。充沛的水汽输送及水汽的强烈辐合,为暴雨发生的有利水汽条件。多普勒径向速度揭示了暴雨区低层冷平流高层暖平流、风向风速的垂直切变大的垂直结构以及持续性的强烈辐合等等特征,回波停滞和＂列车效应＂使降水增幅,降水回波的性质差异,可造成强降水区域分布的不同。