居住迁移对居民健康的影响研究进展述评

进入城市时代以来,居住环境与居民健康的联系愈发密切,尤其在“流动性"增强的大背景下,居住迁移对居民健康的影响问题受到广泛关注。论文结合知识图谱分析和文献研究法,系统评述居住迁移影响居民健康问题的最新进展。研究发现：① 近15 a来,该领域的文献数量逐年增多,关注度持续上升;文献空间分布主要集中在发达国家,但不同地区的研究内容存在显著差异。② 主要研究对象由“同质性群体”向“异质性群体”转变,从“一般性群体”向“特殊群体”转变;研究方法由数理统计向混合研究、综合应用转变。③ 研究视角经历“人口迁移—个体健康”“居住迁移—环境—个体健康”与“迁居轨迹—环境演变—个体健康发展”等3个演变阶段。④ 近期研究重点有：迁居行为与儿童健康,迁居时空特征与身心健康,住房生涯与身心健康,邻里环境、累积剥夺与健康发展等。结合以上分析,提出如下建议：注重“整合性”分析;关注城市内部迁居行为和多次迁居轨迹对居民健康的影响;扩大迁居引发的“环境”因素(如居住隔离、社会分异、职住空间错位等)研究;更多关注迁居对二代流动人口儿童健康的影响,侧重对非正规居住空间如“城中村”等的研究。     

台湾海峡1998年夏季温盐场的分布特征

根据１９９８年夏季台湾海峡调查所得到的温盐观测资料,分析了该海区的温盐场特征。结果表明：（１）海峡西部主要为低温高盐水分布,而在海峡东部则是受高温低盐水控制。（２）海峡西部表层水体的低温高盐特征反映出深层在台湾海峡不同区域沿陆坡爬升的动力特     

大河影响下的边缘海沉积有机碳输运与埋藏及再矿化研究进展

大河影响下的边缘海是陆源输入物质的主要储库,也是有机碳埋藏和再矿化的主要场所,在全球碳的生物地球化学循环中有着重要作用。从有机碳的输运、埋藏和再矿化等方面综述了大河影响下的边缘海沉积有机碳生物地球化学研究的最新进展。研究表明,有机碳的来源、组成、粒径和密度分布等显著影响着有机碳的分布特征和归宿,大河影响下的边缘海中移动泥等特殊沉积环境在有机碳的输运、埋藏和再矿化分解等方面发挥了独特的作用;微生物分解作用则是边缘海沉积有机碳,特别是难降解陆源有机碳发生分解的重要因素。综合运用分子生物学、有机地球化学、生物地球化学等多学科研究手段,深入研究特定微生物、浮游生物功能类群等在大河影响下的边缘海沉积有机碳生物地球化学过程中的作用,将极大地丰富对河口和陆架边缘海生源要素生物地球化学循环的认识。     

快速GNSS精密布网在偏远海岛无人机遥感监测中的应用

文章提出快速GNSS精密布网技术在无通信信号、无控制点的偏远海岛无人机遥感监测中的应用,并在浙闽交界的七星列岛进行实践,结果表明:采用GNSS精密布网技术融合无人机遥感方法,能够快速获取高精度的海岛3D(DLG、DEM、DOM)和实景三维数据,可为偏远海岛监测评价提供重要的基础地理信息,实现对偏远海岛资源环境和开发利用状况的动态监控。     

底栖有孔虫(Florilus decors)壳体微量元素/钙比值的LA-ICP-MS原位微区分析方法及应用——以长江口外海域为例

深海沉积物中有孔虫壳体的微量元素、同位素测试技术已较为成熟,而河口近海沉积物中有孔虫壳体元素微区测试却鲜有报道。本文报道了一种利用激光剥蚀电感耦合等离子体质谱（LA-ICP-MS）分析法测试取自长江口外沉积物中的有孔虫壳体元素/钙比值的技术,研究了氦气载气流量、能量密度、束斑大小、激光剥蚀频率等参数对测试结果的影响,优化了活体有孔虫原位分析方法。应用确定的测试条件对2016年7月取自长江口外的底栖有孔虫优美花朵虫样品（Florilus decors）进行测试,发现Mg、Sr等元素/钙比值在壳体不同位置上无显著差异,而Mn的数据较为离散,可能与有孔虫生长过程中经历的水环境及其变化有关。     

Smectite formation in metalliferous sediments near the East Pacific Rise at 13°N

A 43 cm long E271 sediment core collected near the East Pacific Rise(EPR) at 13°N were studied to investigate the origin of smectite for understanding better the geochemical behavior of hydrothermal material after deposition.E271 sediments are typical metalliferous sediments. After removal of organic matter, carbonate, biogenic opal,and Fe-Mn oxide by a series of chemical procedures, clay minerals(2 μm) were investigated by X-ray diffraction,chemical analysis and Si isotope analysis. Due to the influence of seafloor hydrothermal activity and close to continent, the sources of clay minerals are complex. Illite, chlorite and kaolinite are suggested to be transported from either North or Central America by rivers or winds, but smectite is authigenic. It is enriched in iron, and its contents are highest in clay minerals. Data show that smectite is most likely formed by the reaction of hydrothermal Fe-oxyhydroxide with silica and seawater in metalliferous sediments. The Si that participates in this reaction may be derived from siliceous microfossils(diatoms or radiolarians), hydrothermal fluids, or detrital mineral phases. And their δ30 Si values are higher than those of authigenic smectites, which implies that a Si isotope fractionation occurs during the formation because of the selective absorption of light Si isotopes onto Feoxyhydroxides. Sm/Fe mass ratios(a proxy for overall REE/Fe ratio) in E271 clay minerals are lower than those in metalliferous sediments, as well as distal hydrothermal plume particles and terrigenous clay minerals. This result suggests that some REE are lost during the smectite formation, perhaps because their large ionic radii of REE scavenged by Fe-oxyhydroxides preclude substitution in either tetrahedral or octahedral lattice sites of this mineral structure, which decreases the value of metalliferous sediments as a potential resource for REE.     

Spatial–temporal distribution of phytoplankton pigments in relation to nutrient status in Jiaozhou Bay,China

We conducted studies of phytoplankton and hydrological variables in a semi-enclosed bay in northern China to understand the spatial–temporal variability and relationship between these variables. Samples were collected during seven cruises in Jiaozhou Bay from November 2003 to October 2004, and were analyzed for temperature, nutrients and phytoplankton pigments. Pigments from eight possible phytoplankton classes (Diatoms, Dinoflagellates, Chlorophyceae, Prasinophyceae, Chrysophyceae, Haptophyceae, Cryptophyceae and Caynophyceae) were detected in surface water by high performance liquid chromatography (HPLC). Phytoplankton pigment and nutrient concentrations in Jiaozhou Bay were spatially and temporally variable, and most of them were highest in the northern and eastern parts of the sampling regions in spring (May) and summer (August), close to areas of shellfish culturing, river estuaries, dense population and high industrialization, reflecting human activities. Chlorophyll a was recorded in all samples, with an annual mean concentration of 1.892 μg L⁻¹, and fucoxanthin was the most abundant accessory pigment, with a mean concentration of 0.791 μg L⁻¹. The highest concentrations of chlorophyll a (15.299 μg L⁻¹) and fucoxanthin (9.417 μg L⁻¹) were observed in May 2004 at the station close to the Qingdao Xiaogang Ferry, indicating a spring bloom of Diatoms in this area. Although chlorophyll a and other biomarker pigments showed significant correlations, none of them showed strong correlations with temperature and nutrients, suggesting an apparent de-coupling between the pigments and these hydrological variables. The nutrient composition and phytoplankton community composition of Jiaozhou Bay have changed significantly in the past several decades, reflecting the increasing nutrient concentrations and decline of phytoplankton cell abundance. The unchanged total chlorophyll a levels indicated that smaller species have filled the niche vacated by the larger species in Jiaozhou Bay, as revealed by our biomarker pigment analysis.     

长江口及毗邻海域粪大肠菌和细菌总数在夏秋季的变化

2005年夏、秋季对长江口及毗邻海域(长江口、杭州湾和舟山海域)进行了粪大肠菌群和细菌总数的调查研究,并分析了近10年来的变化趋势,结果表明:夏季长江口及毗邻海域表层水体分大肠菌数平均值20个/L,仅长江口的西部海域粪大肠菌群数量在40~80个/L之间,其余海域基本未检出;秋季表层水体粪大肠菌群数量平均为101个/L,变幅范围为20~24000个/L,其中横沙一带海域存在1个数量为105个/L以上的高值区;夏季长江口及毗邻海域表层水体细菌总数平均为6.4×102cfu/mL,变幅范围为2.0×102~7.3×103cfu/mL,高值区位于舟山群岛以东海域、长江口的中北部及南部等海域,细菌总数在103cfu/mL以上;秋季表层水体细菌总数平均为4.7×103cfu/mL,明显高于夏季,变幅范围为1.3×103~1.8×104cfu/mL,高值区主要出现在长江口东南部、杭州湾西部、舟山海区的中北部等海域,细菌总数在104~105cfu/mL之间;1996—2005年期间,全海域及各海区粪大肠菌群数量在1999年均达到最高,然后逐渐下降,在1996—1999年间海域的细菌数量呈明显的上升趋势,2000年以后数量逐渐减少,估计与海域的有机污染程度下降有关。     

一株海洋细菌铁吸收调节蛋白(Fur)基因的克隆和表达

对海洋细菌来说铁是一种必需元素,对铁吸收与利用的调控在细菌生长和防止铁毒性中起重要作用,在革兰氏阴性细菌中,铁的代谢由铁吸收调节蛋白(Fur) 来调控.橙色交替单胞菌是1种具有广泛抑菌谱的有益菌,本研究克隆表达了橙色交替单胞菌的fur基因,并分析了其相关特征.该基因序列中包含447bp的开放阅读框,编码148个氨基酸残基的蛋白,推导的相对分子量为16.637 kD,与GenBank报道的革兰氏阴性菌的相应序列同源性很高,其中氨基酸序列的中段从G47位至D104位,为高度保守区域.在限铁和富铁培养条件下铁载体分泌量的结果分析表明,fur基因可在大肠杆菌中大量表达,为进一步研究Fur蛋白的结构与功能打下基础.     

Impact factors on distribution and characteristics of natural plant community in reclamation zones of Changjiang River estuary

To identify impact factors on the distribution and characters of natural plants community in reclamation area, with survey data from 67 plant quadrats in July 2009, soil properties data from 216 sampling points in April 2009, and TM (30 m) data in 2006, the composition and characteristics of natural plants community in different time of the Fengxian area in the Changjiang (Yangtze) River estuary were analyzed with two-way indicator species analysis (TWINSPAN), multivariate analysis of variance (MANOVA), detrended canonical correspondence analysis (DCCA) and canonical correspondence analysis (CCA). The results show that: 1) The plant communities in the reclaimed area are mainly mesophytes and helophytic-mesophytic transitional communities, showing a gradient distribution trend with the change in reclamation years. Species richness (MA), species diversity (H) and above-ground biomass also increase with the increase of reclamation years. Nevertheless, they appear to decline slightly in the middle and late reclamation period (> 30 years). 2) With the rise in land use levels, the changes in species richness and species diversity tend to increase at first and then decrease; species dominance (D), however, tends to decline; and above-ground biomass increases slightly. 3) The distribution of the plant community is mainly influenced by the following factors: land use levels (R = 0.55, p < 0.05), soil moisture (R = 0.53, p < 0.05), soil salinity (R = 0.43, p < 0.05) and reclamation time (R = 0.40, p < 0.05).