古昆虫植食的自然历史

昆虫植食是昆虫与植物相互作用关系中最重要的组成部分。探索地史时期陆地生态系统中昆虫植食行为的起源与演化是探究古环境重建及古气候变化的重要切入点，其结果将更好地揭示现生昆虫取食行为背后的生物学及生态学意义。本文梳理了昆虫植食的研究历史；阐述了植物化石上的生物损伤与非生物损伤的主要区别；介绍了昆虫植食研究的化石证据以及功能性取食组 损伤类型研究体系(Functional feeding group damage type, FFG DT)。昆虫植食多样性在地质历史时期的演化过程分为8个阶段：① 志留纪—泥盆纪(444~359 Ma)为昆虫植食的起源时期；② 石炭纪(359~299 Ma)为昆虫植食的扩张时期；③ 二叠纪(299~252 Ma)为昆虫植食的稳定时期；④ 三叠纪(252~201 Ma)晚期，昆虫植食再次多样化；⑤ 侏罗纪(201~145 Ma)昆虫植食程度进一步加强；⑥ 白垩纪(145~66 Ma)裸子植物逐渐为被子植物所替代，昆虫植食大幅度增加；白垩纪末期，昆虫植食水平下降；⑦ 古近纪(66~23 Ma)昆虫植食水平提高；⑧ 新近纪(23~26 Ma)昆虫植食与现代基本相似。影响昆虫植食的主要因素包括气候环境、昆虫和植被多样性、昆虫口器类型、植物群落组成和微生物等。目前，统一昆虫植食研究体系和方法、填补各历史阶段的缺失信息等问题在昆虫植食研究中亟待解决。     

高围压下冻土强度弱化的机理分析

围压作用下,影响冻结砂土强度弱化的主要原因是孔隙冰的压融,矿物颗粒细化的微裂隙的发育。影响冻结粉质粘土强度弱化的主要原因是孔隙冰的压融和微裂隙的发育,这些过程是不独立存在的,而是共同影响,共同作用,从而导致了冻土强度的弱化。     

变质作用矿床概述

近代矿床学研究已初步摆脱经典和相对立的内生及外生作用矿床的研究范围,走向一个以整体地质环境为背景,以各种地质作用相互联系为基础的动力学研究方向,并从矿床的源区和源岩出发,在不同的地质作用下特别是与挥发组分的参与相结合,追溯其矿床的形成过程。变质作用矿床是一类中间型的矿床,属于近源迁移型。在原有地壳中含矿建造和矿源层的基础上,经历了变质作用和它的后期混合岩作用过程,并通过变质作用传导体制的不同阶段中出现的流体的参与,形成一系列由前变质矿床直至混合岩化期后矿床。文中对影响变质作用矿床的控制因素及其地位作了扼要的叙述,进行了变质作用分类的探讨,并从其传导体制中出现的热流及其形成环境上,与岩浆型花岗岩期后热液型进行对比和讨论。     

List of Forthcoming Papers

Other Index

List of Forthcoming Papers     

基于太阳能无人艇的海洋气象观测系统及其初步试验

中国沿海地区以及濒临海域经常发生多种灾害性天气,包括大风、暴雨、大雾和海上强对流天气等,原位探测资料的缺乏极大影响了这些天气生消演变规律的深入研究以及预报准确性的提高。为了实现海上自动部署、机动安全和实时的多要素原位探测,研发了一种基于太阳能无人艇的海洋气象水文探测系统,工程样机命名为MWO-I(Marine Weather Observer-I),2015—2019年该系统进行了多次海上试验。本文对这一长航时海洋气象探测系统进行介绍,并给出2018年4月一次海上探测试验个例的初步结果。     

潜源划分进展及我国海域和邻近海域区划潜源划分问题研究

对于陆域地区，我国已进行5次全国范围大面积地震区划研究工作，获得了丰富研究成果。但对于海域地区地震区划的研究较薄弱，较少涉及海域潜源划分模型。随着经济发展，涉及海域地区的经济活动日益频繁，对海域地区潜源划分研究及进一步地震区划研究工作的需求越来越强烈。为此，详细介绍代表性国家在潜源划分方面采取的原则和方法，总结我国海域地区地震地质背景及相应的研究现状，并在此基础上提出我国海域地区潜源划分可考虑的原则和基本思路，为后续我国海域地区区划研究提供方案。     

Flow Characteristics of Large-Scale Liquefaction-Slip of the Loess Strata in Shibei Tableland, Guyuan City, Induced by the 1920 Haiyuan M8 1/2 Earthquake

Based on the dynamic triaxial liquefaction test of the loess samples which are taken from Shibei tableland, Guyuan City, Ningxia, China, the characteristics of dynamic strain, dynamic stress and pore water pressure are studied under cyclic loading. Triaxial shear test is conducted immediately after the sample reaches liquefaction point. During the test, the property of the liquefied soil is analyzed through fluid mechanics method, whereby the fluidity of the liquefied soil is represented by apparent viscosity.The results show that the fluidity of liquefied loess changes from "shear thickening" to "shear thinning" as the shear force continues, and the fluidity of liquefied loess is closely related to its structure. In addition, in the process of forming a new stable state, the apparent viscosity and deviant stress change with axial strain in a similar approach. When the sample reaches its stable state, it meanwhile shows a relatively stable apparent viscosity. According to the fluid mechanics and the law of conservation of energy, the slip distance of the liquefied soil is estimated, and the results are in good agreement with the field investigation results.     

MJO对2018年华北夏季降水的影响

本文基于华北夏季降水资料和热带大气季节内振荡（Madden–Julian Oscillation，简称MJO）指数、NCEP/NCAR（美国国家环境预报中心/美国国家大气研究中心）再分析环流资料，采用多种统计方法分析MJO与2018年华北夏季降水的关系及影响机制。结果表明:（1）MJO与华北夏季降水有密切的联系。虽然MJO不能移到较高纬度直接影响华北夏季降水，但MJO对流区的气旋会在其北侧激发出反气旋环流，这对“气旋—反气旋对”在缓慢东移过程中，处于较高纬度的反气旋会直接影响华北夏季降水。即MJO会间接影响华北夏季降水，表现为当夏季MJO进入5、6位相时，华北地区夏季会出现明显降水过程，但降水强弱与MJO振幅大小有关。（2）影响机制方面。在850 hPa，伴随MJO的“气旋—反气旋对”的东移，它会造成华北夏季偏南风水汽输送加强（对应RMM1）或东南风水汽输送加强（对应RMM2），从而有利于降水过程发生。在500 hPa层，MJO通过中层扰动向中高纬的传播，诱导副热带高压移到朝鲜半岛附近并加强，对西来高空槽形成阻挡作用，有利于华北地区产生上升运动，从而有利于华北夏季降水过程发生。（3）可以用MJO制作华北夏季延伸期降水过程预报。     

基于年际增量法的华西秋雨预测模型建立及检验

利用1962—2018年华西地区301个气象台站秋季降水量资料和国家气候中心整理的130项气候系统指数，采用年际增量法建立了华西秋雨预测模型。首先通过相关分析挑选了4个与华西秋雨年际增量前3主模态密切相关的影响因子，进而采用多元线性回归方法进行建模，拟合时段和后报时段分别选为1962—1991年和1992—2018年。华西秋雨年际增量前3主模态累积值的预测模型通过了α=0.01的显著性水平检验，表明该模型具有较高的拟合预测能力。然后用相同的预测因子分别建立华西地区301个气象站点的华西秋雨年际增量预测模型，大部分模型都通过了显著性检验。用PS评分指标对预测效果进行检验，结果显示后报期年平均PS评分达74.5分。从空间分布来看后报期大部分站点的PS评分都超过60分，其中四川盆地南部、贵州东部和湖南西部等地超过80分。与华西各省和国家气候中心发布的近6年秋季降水预测PS评分进行比较，发现模型后报结果有显著优势。总体来看，用年际增量法建立的华西秋雨预测模型具有较高的预测技巧和实际应用价值。     

The status of the ecological environment and a proposed protection strategy in Sanya Bay,Hainan Island,China

Sanya Bay encompasses a high diversity of natural habitats, ranging from coral reefs, rocky and sandy shores and mudflats to mangroves. Seasonal physicochemical and biological investigations were conducted from 1998 to 1999 and again in April 2000. Water-related environmental quality in Sanya Bay is in good condition. The levels of dissolved oxygen, nitrogen, phosphorus and heavy metals are within the first class of National Seawater Quality Standards for China. Annual mean values of chlorophyll a of 0.93 mg m(-3) and phytoplankton primary productivity of 440.8 mgC m(-2)d(-1), respectively, were found in the waters, both of which show a significant correlation with inorganic nitrogen. A mean new productivity of 144.6 mgC m(-2) d(-1) was recorded in summer. Sanya Bay is rich in natural resources and biodiversity with 235 species of phytoplankton and 129 species of zooplankton identified in the survey. The annual mean abundance of phytoplankton and zooplankton were 1564 x 10 cells m(-3) and 121 individuals m(-3), respectively, with an annual mean zooplankton biomass of 129 mg m(-3). A total of 243 species of fish were sampled in the survey including many of high economic value. Three hundred and eighty-four species of benthos in 121 families were found by mud sampling and trawling. The average biomass of benthic organisms was 11.55 gm(-2), with a density of 31 individuals m(-2). Molluscs were the dominant group, followed by crustaceans; coelenterates exhibited the lowest biomass. One hundred and twenty-six species from 48 families of intertidal organisms were collected by frame sampling, with a mean annual biomass of 644.7 gm(-2) and average density of 816 individuals m(-2). The highest biomass of 1673.5 gm(-2) was collected in a coral reef region, while the highest density of 1219 individuals m(-2) occurred in a mangrove region. The coastline is characterized by coral reefs that accounts for 30% of the total coastline length in the bay, so coral reefs are a key ecosystem that are important for maintaining the regional marine resources and biodiversity. We need to pay much more attention to such diverse marine resources to maintain the integrity and function of these coastal ecosystems.