长江流域可持续发展综合分析与评价

本文分析了长江流域经济社会发展的基本态势以及存在的问题 ,研究了流域可持续发展中的资源环境因素 ,并且提出了进行流域可持续发展评价的指标体系以及评价方法 ,对近年来长江流域各地区可持续发展状况分别进行了评价 ,并在此基础上 ,提出了促进长江流域可持续发展的主要对策措施     

淮河流域人地系统的自组织分析

本文从系统论的角度出发 ,从组织序变、耗散结构、协同互补、系统演化的动力机制等方面分析了淮河流域人地系统的优化、平衡及有效调控机理 ,为实现淮河流域的可持续发展提供理论依据 ,并提出了提高系统的自组织能力、激活系统的动力机制的战略举措     

长江三角洲大都市周边地区城市定位研究——以苏州、南通为例

本文以大都市理论和区位理论为基础 ,从区域分工与协作的角度 ,探讨了在经济全球化和市场一体化背景下 ,上海大都市周边的大城市苏州和南通未来发展的城市定位以及实现定位的途径 ,为长江三角洲都市连绵区诸城市之间的协调发展提供借鉴。     

松花江干流洪水与1998年松嫩大水分析--发生规律及成因

松花江干流洪水的发生有24年和3～4年变化周期.洪水出现有明显的阶段性,在上世纪可分为4段1911-1914;1930-1940;1954-1958;1984-1998年.随着时间的推移,洪水发生频次明显增加.分析得出,嫩江流域及第二松花江和拉林河流域7,8月的过量降水是造成洪水发生的直接原因.还分析了造成洪水的高空500hPa环流背景,7,8月西藏高原至北美阿拉斯加距平场分布为“ - -“流型,鄂霍次克海为阻塞高压,东北区为低压槽控制.在大水年春季,阿留申低槽加深,并向西延伸,乌拉尔高压形成并东移加强.1998年松嫩大水的发生基本符合上述规律和环流原因.     

"数字石羊河"建立及其在沙尘暴防治中的应用

由于上游超量用水,导致石羊河下游的民勤县绿洲无水可用,生态环境严重恶化,成为我国的第四大沙尘暴策源地.本文提出了建立"数字石羊河"的概念,认为石羊河流域要建立公平的用水机制,在技术上要建立"数字石羊河",最后对"数字石羊河"在沙尘暴防治中的应用作了分析.     

乌江流域（四川部分）水土流失及其防治对策

根据径流场观测材料、调查资料及历史事实,论述了乌江流域(四川部分)的水土流失现状、特点、危害及导致水土流失的自然因素和人为因素。针对该流域水土流失特点和原因提出了防治对策。     

江苏泰州城市霾天和沙尘天气溶胶中细菌群落结构特征研究

近年来,空气污染已成为长三角地区最关键的环境问题之一,气溶胶颗粒物(PM)是最主要的污染物之一.生物气溶胶作为颗粒物的重要组成部分,可能对空气质量和人体健康产生不利影响.利用高通量测序方法研究了江苏省泰州2019年11月至2020年1月期间发生沙尘和霾污染时生物气溶胶中细菌群落结构组成特征.结果表明:冬季沙尘天和霾天气...     

淮河上游全新世黄土-土壤剖面重金属元素分布与环境变化

在野外考察研究的基础上利用X-射线荧光光谱仪测定了河南禹州全新世YPC黄土-土壤剖面Zn、Cu、Co、Ni、Nb、Pb、V、Cr、Mn、Ti重金属元素的含量及其变化,研究表明在黄土堆积期,重金属元素的含量都很低,变化幅度也很小,可作为衡量古土壤层成壤改造的背景值.在全新世古土壤和现代表土中这些元素含量却大大增加,说明在温暖湿润的时期,成壤改造使易溶易迁移元素的淋失导致重金属元素的相对富集.而Pb含量从8cm深度处向上急剧增加,增幅达60%,这是大气污染物沉降积累的客观记录.     

Heavy metals associated with reduced sulfur in sediments from different deposition environments in the Pearl River estuary, China

Distribution of acid volatile sulfur (AVS) and the simultaneously extracted metals (SEM: Cu, Pb, Zn, Cd, Ni) in sediment profiles has been studied at five sites in Pearl River estuary, China. Of the five sampling locations, Nos.1 and 2 are in the middle shoal, Nos.3 and 4 in the west shoal and No. 5 locates to the south of the estuary. The AVS content in the sediments of the middle shoal varies in a small range (0.25–4.06 μmol g⁻¹), while that of west shoal increases with depth from 0 to ultimately 26.09 μmol g⁻¹. The SEM concentration in the sediment profiles at location Nos. 1, 2 and 5 is generally in the range of 0.95±0.2 μmol g⁻¹ with a slight upward increase, while that in the sediment of west shallows are much higher (1.43–2.42 μmol g⁻¹) with a significant upward increase, especially in the upper layer of ca. 15 cm. The observed upward increase of SEM content at all the sites implies that heavy metal contamination of sediment in the Pearl River estuary is increasing. Calculations of the excess heavy metal content which is defined by SEM-AVS molar difference suggests that the upper sediment in the Pearl River estuary, especially on the west shallows, could be a source of heavy metal contaminants and may cause toxicity to the benthos. The site-specific distribution patterns in the AVS and SEM profiles were interpreted according to the hydrogeochemistry of deposition environments.     

Occurrences of pharmaceutical and personal care products as micropollutants in rivers from Romania

The occurrence of pharmaceutical and personal care products (PPCPs) was investigated in the Somes River. The aim of this study was to obtain a first overview about the contamination of Somes River (Transylvania) with PPCPs. The samples were preconcentrated by Solid Phase Extraction (SPE) procedures and analysed by GC/MS. A number of 15 compounds including pharmaceutics, metabolites, intermediates and musk fragrances were detected in concentration ranging from 30 ng/l to 10 μg/l. The detected pharmaceuticals are included in following therapeutic groups: analgesics, antiepileptics, psychiatric, stimulants, anticoagulants, antineoplastic and disinfectants.