火焰原子吸收法测定植物样品中微量铜

植物样品在500℃灰化,用硝酸、氢氟酸和高氯酸分解,然后在2％的盐酸介质中,用火焰原子吸收分光光度法测定植物样品中的微量铜。该方法简单、快速、准确。方法的检出限为0.55×10~(-6),回收率97％—102％。对含量为5.14×10~(-6),9.43×10~(-6)和17.63×10~(-6)的三个植物样品进行分析,其相对标准偏差分别是4.62％、4.22％和2.00％。     

氢化物-无色散原子荧光光谱法测定微量碲

氢化物—无色散原子荧光光谱法测定黄铁矿及地球化学样品中微量碲，采用硝酸，盐酸，高氯酸分解样品，用浓盐酸将六价碲还原成四价碲，再用硼氢化钾继续还原使碲形成氢化物ＴｅＨ２，在ＡＦＳ１２０１Ｃ原子荧光光谱仪进行测定碲的检示限为０．１８μｇ／ｇ，精密度ＲＳＤ％为６．８％，该方法操作简便、快速、准确、费用低，可应用于大批量地球化学样品的分析。     

ICP—光量计测定地质样品中的Sc

本方法是用ＩＣＰ—光量计测定地质样品中的Ｓｃ，用氢氟酸—盐酸溶解样品，对几个国家级标样进行测定，结果与推荐值一致。方法检出限为Ｓｃ：０．２２μｇ／ｇ，本方法简单、快速、准确     

植物样品中金的分析方法研究

植物样品中金的分析方法很多。通过大量试验表明,植物样品的灰化温度和分解方式对金的分析结果影响很大。为此,在大量试验的基础上确立了植物样品在650℃灰化,王水溶解,泡沫塑料分离富集,硫脲解脱金,石墨炉原子吸收测定植物样品中金的分析方法。该方法快速、简单、准确、可靠,方法的检出限为0.29×10~(-9)。用3个含量分别为115.4×10~(-9).15.0×10~(-9),18.1×10~(-9)的植物样品做精密度试验。其相对标准偏差分別是5.26％、21.5％、7.37％。     

论激光荧光法测定水系沉积物中的痕量铀

试样经盐酸、硝酸、氢氟酸、高氯酸分解蒸干后,用50g/LNa2CO3溶液浸取分离,用MUB型激光铀分析仪测定上清液的铀的含量。该方法参加了地球化学考核样品的测试,合格率95%以上。适用于大批量的地质样品中痕量铀的测定。     

氢化物原子荧光法测定血、植物样中的硒

硒是一种人体必需的微量元素,但是,如果硒的摄入超过一定量就会对人的肾有所伤害。硒在工业上广泛用于颜料、半导体、电讯器材、特种玻璃制造以及盐酸生产等。工业“三废”的污染均可使农作物含硒量增高,所以,准确测定植物及其它生化样品中硒的含量有重要意义。硒的测定可采用荧光分光光度法,石墨炉原子吸收法和ICP—MS法,但由于血及植物中硒含量普遍低,测定效果不理想。     

大珠母贝术后处理研究

用蚌复康（Ａ组）、鱼蚌康复剂（Ｂ组）和盐酸普鲁卡因（Ｃ组）对人工插核后的大珠母贝进行术后处理，并经室内人工管养度过休养期；结果显示：术后成活率Ｃ组为７０．０％，Ａ组为６０．０％，对照组为３６．４％，留核率Ａ组为６６．７％，Ｃ组为５７．１％，对照组为５０．０％，表明蚌复康与盐酸普鲁卡因可以明显提高植核母贝的术后成活率和留核率；另外，休养期在室内度过也有助于提高留核率。     

巯基棉富集分离—冷原子吸收法测定天然水中痕量汞

用巯基棉富集水中痕量汞,用饱和氯化钠的盐酸溶液解吸,冷原子吸收法测定。当水样取１ Ｌ时,最低检测浓度可达０－００３ μｇ／Ｌ,方法相对标准偏差为３－８ ％ ～６－９ ％ ,巯基棉汞平均回收率为９１－１％ 。该法操作简单、快速、富集倍数大,适用于天然水中痕量汞的分析。     

海洋锰结核中微量铀的测定

样品用王水溶矿，制成１０％ＨＮＯ＿３溶液，通过Ｐ－３５０色谱柱，富集铀分离干扰元素，而后用０．２％ＮａＦ解脱铀，衔接５－Ｂｒ－ＰＡＤＡＰ光度法测定铀。     

无火焰原子吸收法测定天然水中痕量金

在２．０％ＨＣｌ及加入少量饱和溴水的条件下，用泡沫塑料吸附富集金。用１．０％硫脲溶液热浸提取金，然后用涂层石墨管和平台，无火焰原子吸收分光光度计测定天然水中痕量金的含量。该方法简单、可靠。     

GEOCHEMICAL STUDIES OF Fe,Mn,Co,As,Cr,Sb,Zn,Sc AND V IN SURFACE SEDIMENTS FROM JIAOZHOU BAY

The contents of nearly forty-elements in surface sediments in Jiaozhou Bay were determined using a Neutron Activation Analysis Technique(Grancini,et al.,1976;Li Peiquan et al.,1985,1986;Li Xiuxia etal.,1986).This paper's detailed discussion on only nine elements(Fe,Mn,Co,Cr,Sc,As,Sb,Zn andV)includes their distributions,concentrations,correlationships,material sources,background,etc.Based on Zavaristski's classification method,Fe,Mn,Co Cr and V belong to the second group;As and Sb to theeighth groups:Sc and Zn to the third and sixth groups.It was found that their notably good correla-tionship is mainly due to the similarity of their ionic structures and that their variation is controlled by theFe content(except Mn).The source of sediments is mainly terristrial material,and the composition ofsediment is similar to that of shale and shale+clay.The contents for a large number of ele-ments are within the scope of the background level,but there still is pollution of Zn and Cr,at least in a few stations.     

氟、氯、溴、碘等卤族元素与人体健康的关系

卤族元素是人体的必需元素,正常情况下成人摄入量不超过F4 mg/d、C11.7～5.1g/d、I 100～200μg/d;少年不超过F 3 mg/d,儿童I1μg/kg-d,婴儿Cl0.3～1.2 g/d.过量摄入或缺乏卤族元素,都可能导致疾病的发生.而F含量0.5～1.0mg/L、C1＜50mg/L、Br＞100μg/L、I 10～100μg/L的饮用地下水,有利于人体健康.     

Controlling mechanisms for the trace metals, (Cu,Zn, Cd,Fe, Co and Ni) in anoxic sea water in Saanich Inlet,British Columbia,Canada

A study was conducted on Cu, Zn, Cd, Fe, Co and Ni levels in Saanich Inlet anoxic seawater. Data on the concentration of these trace metals and H₂S, and other oceanographic parameters were obtained in four cruises. Equilibrium models are presented together with in situ data. The results strongly support the assumption that the solubilities of Cu, Zn, Cd, Fe, Co and Ni are controlled by bisulfide and/or polysulfide complexes. The species of Cu, Zn, Cd and Ni are shown to be Cu(S₄) ₂ ³⁻ and Cu(Sn₄S₅)³⁻, Zn(HS) ₂ ⁰ and ZnHS ₂ ⁻ , Cd(HS) ₂ ⁰ and Ni(HS) ₂ ⁰ , respectively. The solid species controlling Fe²⁺ and Co²⁺ are respectively the pyrohotites FeS and CoS. The data illustrates that thermodynamic equilibrium has been established in the H₂S-controlled seawater of Saanich Inlet, and that equilibrium has not been established in the H₂S−O₂-coexisted seawater of Saanich Inlet. The lack of equilibrium in the H₂S−O₂-coexisted seawater is a result of the flushing or mixing of oxygenated seawater with anoxic water. The new species of trace metals are still in the processes of reduction and precipitation. Contribution No. 1428 from Institute of Oceanology, Academia Sinica     

Effects of small peptides,probiotics, prebiotics,and synbiotics on growth performance,digestive enzymes,and oxidative stress in orange-spotted grouper,Epinephelus coioides,juveniles reared in artificial seawater

Aquaculture production efficiency may increase by using feed additives. This study investigated the effects of different dietary additives [w/w: 2% small peptides, 0.01% probiotics( Bacillus licheniformis) and 0.2% prebiotics(inulin)] on growth performance, digestive enzyme activities, and oxidative stress in juvenile Epinephelus coioides reared in artificial seawater of two salt concentrations(13.5 vs. 28.5). Weight gain rate was significantly higher in fish fed the diet supplemented with small peptides, B. licheniformis, inulin, or synbiotics than that in fish fed the basal diet; the greatest weight gain rate was found in fish fed the small peptide treatment [56.0% higher than basal diet]. Higher feed efficiency was detected in fish fed the diet supplemented with small peptides than that of fish in the other dietary treatments. Total protease activity in the stomach and intestines was highest in fish fed the small peptide-treated diet, whereas lipase activity was highest in those fed synbiotics(combination of Bacillus licheniformis and inulin) than that in fish fed the other treatments. Antioxidant enzyme(total superoxide dismutase and catalase) activities and hepatic malondialdehyde content were higher in fish receiving the dietary supplements and maintained in artificial seawater containing 13.5 salinity compared with those in the control(28.5). Hepatic catalase activity in grouper fed the diets with small peptides or synbiotics decreased significantly compared with that in control fish. Overall, the three types of additives improved growth rate of juvenile grouper and digestive enzymes activities to varying degrees but did not effectively improve antioxidant capacity under low-salinity stress conditions.     

GROWTH, REPRODUCTION & POPULATION STRUCTURE OF THE FRESHWATER CRAB SINOPOTAMON YANG TSEKIENSE BOTT, 1967, FROM ZHEJIANG, CHINA

Monthly investigatiom were made on the population of Chinese freshwater crab, Sinopotamon yangteskiense Bott, 1967 from April, 1984 to Match, 1985. The data on 4413 specimens show that the growth was affected mainly by temperature. During the April to November growth period, the crabs' major development occured from June through October. One year was required for a fine white oocyte to develop into a mature egg. The reproduction period was June-October. Females bearing eggs were taken from June-August, and crabs with young were found from July-October. The females reproduced once a year but could for more than one year. The number of eggs carried by a female varied greatly according to the size of the crab, ranging from 30 to 100 eggs. New-bom crabs become mature after 1-2 yeats. The sex ratio was approximately 1:1 in the overall population. However, the larger crabs are predominantly male. The age distribution of S. yangtsekinese was estimated from size frequency histograms. There were more adult crabs     

气、水、岩、生、人相互作用及其环境效应

这里所指示的大气圈、水圈、岩石圈、生物圈以及人类的作用千变万化,从而对人类的生存造成巨大影响,构成了一个复杂的生态环境,讨论这些问题,对人类生存至关重要。     

Growth,reproduction & population structure of the freshwater crabSinopotamon yangtsekiense bott, 1967, from Zhejiang,China

Monthly investigations were mae on the population of Chinese freshwater crab,Sinopotamon yangtsekiense Bott, 1967 from April, 1984 to March, 1985. The data on 4413 specimens show that the growth was affected mainly by temperature. During the April to November growth period, the crabs' major development occurred from June through October. One year was required for a fine white oocyte to develop into a mature egg. The reproduction period was June–October. Females bearing eggs were taken from June–August, and crabs with young were found from July–October. The females reproduced once a year but could for more than one year. The number of eggs carried by a female varied greatly according to the size of the crab, ranging from 30 to 100 eggs. New-born crabs become mature after 1–2 years. The sex ratio was approximately 1∶1 in the overall population. However, the larger crabs are predominantly male. The age distribution ofS. yangtsekinese was estimated from size frequency histograms. There were more adult crabs (over 70%) from June to October and more immature crabs (over 50%) from November to May.     

CONTROLLING MECHANISMS FOR THE TRACE METALS,(Cu,Zn, Cd, Fe, Co AND Ni) IN ANOXIC SEA WATER IN SAANICH INLET, BRITISH COLUMBIA, CANADA

A study was conducted on Cu, Zn, Cd, Fe, Co and Ni levels in Saanich Inlet anoxic seawaler. Data on the concentrations of these trace metals and H2S, and other oceanographic parameters were obtained in four cruisesEquilibrium models are presented together with in situ data. The" results strongly support the assumption that the solubilities of Cu, Zn, Cd, Fe, Co and Ni are controlled by bisulfide and /or polysulfide complexes. The species of Cu, Zn, Cd and Ni are shown to be Cu(S4)23- and Cu(S4S5)3-, Zn(HS)20 and ZnHS2-, Cd(HS)20 and Ni(HS)20 respectively. The solid species controlling Fe2 + and Co2+ are respectively the pyrohotites FeS and CoS. The data illustrates that thermodynamic equilibrium has been established in the H2S-controlled seawater of Saanich Inlet, and that equilibrium has not been established in the H2S-O2-coexisted seawater of Saanich Inlet. The lack of equilibrium in the H2S-O2-coexisted seawater is a result of the flushing or mixing of oxygenated seawater with anoxic water. The new s     

石漠化的成因机理与防治对策

从石漠化的研究现状出发,依据我国西南岩溶石山地区石漠化特征,着重分析其主要控制介质为岩性、构造、地貌、气候、岩溶、地下水、植被等自然介质因子与森林砍伐、高坡开垦等人为介质因子.石漠化是以岩溶山区脆弱的岩溶生态环境为基础,以内、外地质作用和人类恶性生态地质作用为驱动力,以资源退化和恶化为本质,基岩不断裸露,生态环境不断恶化,周而复始的恶性循环过程.提出对石漠化的研究重点是成因机理研究,对石漠化的防治应着重于对石漠化的驱动力及其主导因子的防治,阐述了治山必须先治水等防治对策与建议.     

Plate subduction,oxygen fugacity,and mineralization

Plate subduction is the largest natural factory that processes elements, which controls recycling and mineralization of a variety of elements. There are three major ore deposit belts in the world: the circumPaci?c, the central Asian, and the Tethys belts. All the three belts are closely associated with plate subductions, the mechanism remains obscure. We approached this problem from systematic studies on the behaviours of elements during geologic processes. This contribution summaries the recent progress of our research group. Our results suggest that porphyry Cu deposits form through partial melting of subducted young oceanic crust under oxygen fugacities higher than ? FMQ ～+1.5, which is promoted after the elevation of atmospheric oxygen at ca. 550 Ma. Tin deposits are associated with reducing magmatic rocks formed as a consequence of slab rollback. The Neo-Tethys tectonic regime hosts more than 60% of the world's total Sn reserves. This is due to the reducing environment formed during the subduction of organic rich sediments. For the same reason, porphyry Cu deposits formed in the late stages during the closure of the Neo-Tethys Ocean. Tungsten deposits are also controlled by slab rollback, but is not so sensitive to oxygen fugacity. Subduction related W/Sn deposits are mostly accompanied by abundant accessory ?uorites due to the breakdown of phengite and apatite. Decomposition of phengite is also signi?cant for hard rock lithium deposits, whereas orogenic belt resulted from plate subduction promote the formation of Li brine deposits. Cretaceous red bed basins near the Nanling region are favorable for Li brines. Both Mo and Re are enriched in the oxidationreduction cycle during surface processes, and may get further enriched once Mo-, Re-enriched sediments are subducted and involved in magmatism. During plate subduction, Mo and Re fractionate from each other. Molybdenum is mainly hosted in porphyry Mo deposits and to a less extent, porphyry Cu-Mo deposits, whereas Re is predominantly hosted in porphyry Cu-Mo deposits and sedimentary sul?de deposits.