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长江入东海的化学物质输送特点 总被引:5,自引:0,他引:5
本文基于1984~1987年间对长江下游及河口地区的4个航次的观测和分析结果,讨论了常量与重金属元素的浓度及输送模式.与世界上其他大河流相比长江重金属元素的浓度较低,相反常量元素含量较高,这与中国大陆强烈的化学剥蚀和相对较低的人类活动水平有关.在淡水-咸水混合过程中大多数颗粒态元素呈稳定态分布,特别是当元素的绝对浓度用A1或Sc校正后尤为明显.溶解常量元素呈保守性,因此它们的输送通常可根据河流末端浓度与流量或含沙量之积来估算.大多数溶解态痕量元素是非保守的,在估算它们的外输通量时应根据元素在河口的分布曲线乘以相应的增高或减小因子. 相似文献
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用KCl、肾上腺素(EPI)、去甲肾上腺素(NE)、L—DOPA和GABA(γ-氨基丁酸)进行了不同浓度不同处理时间对硬壳蛤(Mercenaria mercenaria L )幼虫变态诱导实验。结果表明,KCl、肾上腺素、去甲肾上腺素和DDOPA对硬壳蛤幼虫的变态均有诱导作用,而GABA的诱导作用不显著。KCl的最佳诱导浓度随处理时间不同而有所不同。处理时间为1~24,48,72h时KCl的最佳诱导浓度分别为33.56,20.13~26.85,13.42mmol/L。肾上腺素和去甲肾上腺素的诱导作用与浓度和处理时间均有关。肾上腺素的最佳处理浓度为100μmol/L,最佳处理时间均为8h,此时幼虫变态率提高最大,为36.97个百分点。当去甲肾上腺素的诱导浓度为100μmol/L,处理时间为8~16h时,幼虫变态率提高也较大,均大于18个百分点,死亡率增加,但均低于30个百分点,当去甲肾上腺素诱导浓度为500μmol/L时,虽然在8~16h的处理时间范围内,幼虫变态提高率也较大,均大于18个百分点,但当处理时间超过8h,在16~48h范围内,幼虫死亡率提高明显增大,均大于50个百分点。L-DOPA的适宜诱导浓度为10~50μmol/L,适宜处理时间为8~24h,此时幼虫变态率均提高30个百分点以上,最高可提高79.43个百分点。GABA的诱导作用较弱,最佳诱导浓度随处理时间的不同而有所不同,处理时间为24h和48h时,最佳诱导浓度为0.1μmol/L;处理时间为0.5~16h时,最佳诱导浓度为100μmol/L。 相似文献
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Oleg Chudaev Valentina Chudaeva Kenji Sugimori Akihito Kuno Motoyuki Matsuo 《中国地球化学学报》2006,25(B08):211-211
On the Kuril Islands there are 85 volcanoes, 39 of which are active. Hot springs and mud pots are wide spread in this area and have significant inputs on the chemical composition of the surrounding surface waters and environment. We present results of trace elements as well as data on H, O, S, and He isotope ratios for hydrothermal systems of the Mendeleev Volcano (Kunashir Island) and surrounding surface waters. Water and gas samples were taken from springs and holes as well as creeks and the Lesnaya River. Among the thermal water types, three main groups can be distinguished. The first group includes the waters, in which SO4^- ion predominant. The water temperature on the surface reaches 97℃, and TDS varies from a few g/L to 7 g/L. These waters are acid to superacid with pH values ranging 0.6 to 2.3. The second group is sodium-chloride waters. A maximum TDS is 14.2 g/L. The waters are neutral or alkaline; pH varies from 6.9 to 8.2. The third group is the sodium-chloride-sulfate-bicarbonate water. The Stolbovskie springs, located in the periphery of the Mendeleev Volcano are representative of this type. The pH of these waters is close to neutral. TDS is 1.9 g/L. They are rather the derivatives of sodium-chloride waters arisen from dilution of them by subsurface waters. The Kuslyi Creek and Lesnaya River are located near the Mendeleev Volcano. The most acid springs discharge into the Kislyi Creek as a result pH of this creek being 2.5, and contents of most elements rather high. For example, the contents of dissolved solids of Si, Fe, Al, Mn, Zn, in waters of the Kislaya Creek are 22.1, 8.1, 6.2, 1.29, and 0.28 mg/L, and correspondently. The water of the Lesnaya River, (Before the Kislyi Creek, pH is about 8 with TDS 102 mg/L, but after the Kuslyi Creek, pH decreases and the concentrations of chemical elements increase. Debit of the Kislayi Creek in summer season is about 370 L/sec. It means that every day only this small creek inputs in the Lesnay River about 706 kg of Si; 相似文献
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引言 数十年来,海洋科学界一直关注着对进入海洋的源于大自然及人类的物质的估算和过程的了解.在这一领域早期的工作集中于由河流和江川带入海洋的明显的物质输入,随后的研究考查了下水道排放、倾倒等直接输入途径.然而近十至二十年来,已经搞清楚大气层不仅是将自然物质和污染物质从陆地输往海岸和海洋的一个重要途径,在有些情况下甚至是主要途径.这些物质包括矿物粉尘、厂矿残渣;燃烧过程释放的含氮物质、化肥;杀虫剂及来源于各种工业及民用生产过程的其它有机化合物. 相似文献
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生长激素/胰岛素样生长因子-I轴(Growth hormone/insulin-like growth factor-I axis,GH/IGF-I轴)是调控鱼类生长的主要内分泌轴线,许多外源化学物质能够影响鱼类的生长,并且能够干扰GH/IGF-I轴。本文介绍了鱼类GH/IGF-I轴的组成、功能及其对鱼类生长的调控模式,并从GH/IGF-I轴角度探究外源化学物质影响鱼类生长的内分泌作用机制,展望了该领域的发展方向。 相似文献
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Mohammad Rasul Jan Mahmood A Khawaja Jasmin Sha Kashif Gul 《中国地球化学学报》2006,25(B08):182-182
Due to the persistent nature of DDT, a persistent organic pollutant and its adverse environmental and health impacts, the present study was undertaken to examine the residual DDT in and around DDT manufacturing factory in Amman Gharh, Nowshera, NWFP. The factory was established in 1963 and remained in operation till 1994. Composite samples of soil, sediments and water were collected in and around the factory area, nearby DDT stores, main factory drain leading to river and nearby villages. Standard procedures were used for the collection, transportation and storage of samples for analysis. Physical parameters for the collected water samples measured were temperature, pH and conductance. Extraction of each sample for DDT analyses was carried out in triplicates using soxhlet extraction apparatus. The extract was transferred to well washed, clean; dry glass vial, sealed and put in the refrigerator. Gas Chromatograph with electron capture detector and capillary column was used for analysis. DDT in the samples was identified on the basis of their retention time and quantified on the basis of peak areas. It is evident from the analytical data obtained in the present study that both water and soil in and around the factory area are still contaminated with DDT, despite the closure of the factory since the past few years. 相似文献