Carbon cycling in a high-arctic marine ecosystem – Young Sound, NE Greenland

Young Sound is a deep-sill fjord in NE Greenland (74°N). Sea ice usually begins to form in late September and gains a thickness of 1.5 m topped with 0–40 cm of snow before breaking up in mid-July the following year. Primary production starts in spring when sea ice algae begin to flourish at the ice–water interface. Most biomass accumulation occurs in the lower parts of the sea ice, but sea ice algae are observed throughout the sea ice matrix. However, sea ice algal primary production in the fjord is low and often contributes only a few percent of the annual phytoplankton production. Following the break-up of ice, the immediate increase in light penetration to the water column causes a steep increase in pelagic primary production. Usually, the bloom lasts until August–September when nutrients begin to limit production in surface waters and sea ice starts to form. The grazer community, dominated by copepods, soon takes advantage of the increased phytoplankton production, and on an annual basis their carbon demand (7–11 g C m⁻²) is similar to phytoplankton production (6–10 g C m⁻²). Furthermore, the carbon demand of pelagic bacteria amounts to 7–12 g C m⁻² yr⁻¹. Thus, the carbon demand of the heterotrophic plankton is approximately twice the estimated pelagic primary production, illustrating the importance of advected carbon from the Greenland Sea and from land in fuelling the ecosystem.In the shallow parts of the fjord (<40 m) benthic primary producers dominate primary production. As a minimum estimate, a total of 41 g C m⁻² yr⁻¹ is fixed by primary production, of which phytoplankton contributes 15%, sea ice algae <1%, benthic macrophytes 62% and benthic microphytes 22%. A high and diverse benthic infauna dominated by polychaetes and bivalves exists in these shallow-water sediments (<40 m), which are colonized by benthic primary producers and in direct contact with the pelagic phytoplankton bloom. The annual benthic mineralization is 32 g C m⁻² yr⁻¹ of which megafauna accounts for 17%. In deeper waters benthic mineralization is 40% lower than in shallow waters and megafauna, primarily brittle stars, accounts for 27% of the benthic mineralization. The carbon that escapes degradation is permanently accumulated in the sediment, and for the locality investigated a rate of 7 g C m⁻² yr⁻¹ was determined.A group of walruses (up to 50 adult males) feed in the area in shallow waters (<40 m) during the short, productive, ice-free period, and they have been shown to be able to consume <3% of the standing stock of bivalves (Hiatella arctica, Mya truncata and Serripes Groenlandicus), or half of the annual bivalve somatic production. Feeding at greater depths is negligible in comparison with their feeding in the bivalve-rich shallow waters.     

遥感信息技术在公路环境评价中的应用

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陆地生态系统氮状态对碳循环的限制作用研究进展

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岩溶生态系统脆弱性研究

生态系统的脆弱性评价对于生态系统管理具有重要作用。在分析岩溶生态系统脆弱性特 征和影响因素的基础上,构建了针对岩溶自然系统的脆弱性评价指标体系, 涵盖了岩溶生态系统 的结构脆弱性、生态过程脆弱性、生态功能脆弱性和人为胁迫脆弱性4 个方面,评价指标分别是 结构稳定性、多样性生境、能量利用和积累、直接使用价值、石漠化程度和速率等。以不同类型的 原生岩溶生态系统的生态基准值作为比较基础, 评价系统将现有的退化岩溶生态系统的脆弱性 划分为轻微脆弱、中度脆弱、重度脆弱以及系统崩溃4 级。     

基于大数据的生活圈范围与服务设施空间匹配研究——以北京为例

生活圈建设是新时代国土空间规划的关键内容之一,生活圈内服务设施配置是做好生活圈规划的首要基础,居民生活圈与服务设施的空间匹配关系也是地理学“人地关系”在城市社区尺度的重要体现.学术界对生活圈与服务设施的匹配关系已有研究,但主要采用问卷调查数据,该类数据存在样本量少、地域覆盖范围小等不足.论文将采用手机信令数据和POI(...     

立式储液罐地震破坏快速评估方法

本文采用大型有限元程序ANSYS对立式储液罐的地震反应进行了非线性数值分析,考虑了罐体和内部液体的相互作用,得到了3个不同容积的储罐,在不同峰值的地震动时程输入下的反应结果。结合地震灾害中立式储罐的地震破坏现象和特点,以及现有的立式储罐地震破坏预测方法,提出了立式储罐的地震破坏快速评估方法。     

地下闭式循环地热交换发电系统简介

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中国地震次生地质灾害危险性评价

地震次生地质灾害主要指地震引起的崩塌、滑坡、塌陷、地裂缝、砂土液化。震级大于5级、烈度超过Ⅵ度的地震可能引发不同程度的地质灾害,震级和烈度越高,次生地质灾害越严重。本文根据中国历史地震次生地质灾害活动程度及发生条件,以地(市、区、盟)为单元,进行了危险性评价:高度和中度危险区主要分布在中国中部的陕甘宁川渝滇藏地区,形成一个大致NE向高危险带,其余大部分地区为轻度危险区。      

基于过程分析方法的海洋工程项目承包风险评估

运用过程分析方法和风险评估技术,结合海洋工程项目现状,对项目承包进行风险分析。首先,运用事故树方法建立项目承包各阶段的风险事故树;然后,利用风险估计方法综合得到风险事件的评定等级;最后,给出风险控制措施。通过评估结果和建议,以降低海洋工程项目承包风险发生的可能性,减少事故损失。     

Chromium(VI) reduction by sulphur(IV) in aqueous solutions

The rates of the reduction of Cr(VI) with S(IV) were measured in deaerated NaCl solution as a function of pH, temperature and ionic strength. The rates of the reaction were found to be first order with respect to Cr(VI) and second order with respect to S(IV), in agreement with previous results obtained at concentrations two order higher than the present study. The reaction also showed a first-order dependence of the rates on the concentration of the proton and a small influence of temperature with an apparent energy of activation ΔH_app of 22.8 ± 3.4 kJ/mol. The rates were independent of ionic strength from 0.01 to 1 M. The rate of Cr(VI) reduction is described by the general expression

−d[Cr(VI)]/dt=k[Cr(VI)][S(IV)]²