Impacts of a Large River-To-Lake Water Diversion Project on Lacustrine
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Hangzhou: West Lake and More
HANGZHOU: WEST LAKE AND MORE World Similar BASIC INFORMATION Rank To Dallas-Fort Worth, Urban Area Population (2007)* 4,200,000 60 Alexandria, Milan Boston, St. Petersburg, Projection (2025) 5,020,000 80 Barcelona Urban Land Area: Square Miles 250 Sapporo, Copenhagen, 150 Urban Land Area: Square Kilometers 650 Lima, Grand Rapids Density: Per Square Mile 16,800 Ankara, Osaka-Kobe-Kyoto, 300 Density: Per Square Kilometer 6,500 Novosibersk *Continuously built up area (Urban agglomeration) Land area & density rankings among the approximately 750 urban areas with 500,000+ population. Data from Demographia World Urban Areas data. See:1 Demographia World Urban Areas Population & Density Demographia World Urban Areas: 2025 & 2030 Population Projections 9 December 2008 LOCATION AND SETTING Hangzhou is the capital of Zhejiang Province, in the southern part of the Yangtze Delta region. Hangzhou is approximately 400 airline miles (625 kilometers) southwest of Shanghai and is the largest urban area in Zhejiang (Slide 2). The province itself is named for the Zhe River (now called the Qiantang River), which runs through the southern part of the Hangzhou urban area. The historic core is located approximately 100 miles to the southwest of Shanghai. Most of the Hangzhou urban area is flat, but there are intermittent hills. There are more significant hills to the west of the urban area, especially beyond West Lake (aerial photograph, Slide 3). 1 http://www.demographia.com/db-worldua.pdf and http://www.demographia.com/db-worldua2015.pdf. Urban Tours by Rental Car: Hangzhou 1 Hangzhou’s most famous feature and tourist attraction is West Lake, which is immediately to the west of the historic center. -
Jiangsu(PDF/288KB)
Mizuho Bank China Business Promotion Division Jiangsu Province Overview Abbreviated Name Su Provincial Capital Nanjing Administrative 13 cities and 45 counties Divisions Secretary of the Luo Zhijun; Provincial Party Li Xueyong Committee; Mayor 2 Size 102,600 km Shandong Annual Mean 16.2°C Jiangsu Temperature Anhui Shanghai Annual Precipitation 861.9 mm Zhejiang Official Government www.jiangsu.gov.cn URL Note: Personnel information as of September 2014 [Economic Scale] Unit 2012 2013 National Share (%) Ranking Gross Domestic Product (GDP) 100 Million RMB 54,058 59,162 2 10.4 Per Capita GDP RMB 68,347 74,607 4 - Value-added Industrial Output (enterprises above a designated 100 Million RMB N.A. N.A. N.A. N.A. size) Agriculture, Forestry and Fishery 100 Million RMB 5,809 6,158 3 6.3 Output Total Investment in Fixed Assets 100 Million RMB 30,854 36,373 2 8.2 Fiscal Revenue 100 Million RMB 5,861 6,568 2 5.1 Fiscal Expenditure 100 Million RMB 7,028 7,798 2 5.6 Total Retail Sales of Consumer 100 Million RMB 18,331 20,797 3 8.7 Goods Foreign Currency Revenue from Million USD 6,300 2,380 10 4.6 Inbound Tourism Export Value Million USD 328,524 328,857 2 14.9 Import Value Million USD 219,438 221,987 4 11.4 Export Surplus Million USD 109,086 106,870 3 16.3 Total Import and Export Value Million USD 547,961 550,844 2 13.2 Foreign Direct Investment No. of contracts 4,156 3,453 N.A. -
Supplement of a Systematic Examination of the Relationships Between CDOM and DOC in Inland Waters in China
Supplement of Hydrol. Earth Syst. Sci., 21, 5127–5141, 2017 https://doi.org/10.5194/hess-21-5127-2017-supplement © Author(s) 2017. This work is distributed under the Creative Commons Attribution 3.0 License. Supplement of A systematic examination of the relationships between CDOM and DOC in inland waters in China Kaishan Song et al. Correspondence to: Kaishan Song ([email protected]) The copyright of individual parts of the supplement might differ from the CC BY 3.0 License. Figure S1. Sampling location at three rivers for tracing the temporal variation of CDOM and DOC. The average widths at sampling stations are about 1020 m, 206m and 152 m for the Songhua River, Hunjiang River and Yalu River, respectively. Table S1 the sampling information for fresh and saline water lakes, the location information shows the central positions of the lakes. Res. is the abbreviation for reservoir; N, numbers of samples collected; Lat., latitude; Long., longitude; A, area; L, maximum length in kilometer; W, maximum width in kilometer. Water body type Sampling date N Lat. Long. A(km2) L (km) W (km) Fresh water lake Shitoukou Res. 2009.08.28 10 43.9319 125.7472 59 17 6 Songhua Lake 2015.04.29 8 43.6146 126.9492 185 55 6 Erlong Lake 2011.06.24 6 43.1785 124.8264 98 29 8 Xinlicheng Res. 2011.06.13 7 43.6300 125.3400 43 22 6 Yueliang Lake 2011.09.01 6 45.7250 123.8667 116 15 15 Nierji Res. 2015.09.16 8 48.6073 124.5693 436 83 26 Shankou Res. -
Mobile Monitoring of Urban Air Quality at High Spatial Resolution by Low
Mobile monitoring of urban air quality at high spatial resolution by low-cost sensors: Impacts of COVID-19 pandemic lockdown Shibao Wang1, Yun Ma1, Zhongrui Wang1, Lei Wang1, Xuguang Chi1, Aijun Ding1, Mingzhi Yao2, Yunpeng Li2, Qilin Li2, Mengxian Wu3, Ling Zhang3, Yongle Xiao3, Yanxu Zhang1 5 1School of Atmospheric Sciences, Nanjing University, Nanjing, China 2Beijing SPC Environment Protection Tech Company Ltd., Beijing, China 3Hebei Saihero Environmental Protection Hi-tech. Company Ltd., Shijiazhuang, China Correspondence: Yanxu Zhang ([email protected]) Abstract. The development of low-cost sensors and novel calibration algorithms provides new hints to complement 10 conventional ground-based observation sites to evaluate the spatial and temporal distribution of pollutants on hyperlocal scales (tens of meters). Here we use sensors deployed on a taxi fleet to explore the air quality in the road network of Nanjing over the course of a year (Oct. 2019–Sep. 2020). Based on GIS technology, we develop a grid analysis method to obtain 50 m resolution maps of major air pollutants (CO, NO2, and O3). Through hotspots identification analysis, we find three main sources of air pollutants including traffic, industrial emissions, and cooking fumes. We find that CO and NO2 concentrations show a pattern: 15 highways > arterial roads > secondary roads > branch roads > residential streets, reflecting traffic volume. While the O3 concentrations in these five road types are in opposite order due to the titration effect of NOx. Combined the mobile measurements and the stationary stations data, we diagnose that the contribution of traffic-related emissions to CO and NO2 are 42.6 % and 26.3 %, respectively. -
A New Type of Haze? the December 2015 Purple (Magenta) Haze Event in Nanjing, China
atmosphere Communication A New Type of Haze? The December 2015 Purple (Magenta) Haze Event in Nanjing, China Duanyang Liu 1,2,*, Xuejun Liu 3, Hongbin Wang 1, Yi Li 4, Zhiming Kang 2, Lu Cao 2, Xingna Yu 5 and Hao Chen 2 1 Key Laboratory of Transportation Meteorology, China Meteorological Administration, Nanjing 210008, China; [email protected] 2 Jiangsu Meteorological Observatory, Nanjing 210008, China; [email protected] (Z.K.); [email protected] (L.C.); [email protected] (H.C.) 3 College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China; [email protected] 4 Department of Atmospheric Science, Colorado State University, Fort Collins, CO 80523, USA; [email protected] 5 Key Laboratory for Aerosol-Cloud-Precipitation of China Meteorological Administration, Nanjing University of Information Science and Technology, Nanjing 210044, China; [email protected] * Correspondence: [email protected]; Tel.: +86-25-8328-7206 Academic Editors: Yuxuan Wang and Robert W. Talbot Received: 25 December 2016; Accepted: 6 April 2017; Published: 14 April 2017 Abstract: A special and unusual purple (magenta) haze episode was observed in Nanjing, China, at 17:00 on 22 December 2015. Many local and national news outlets reported this event. Based on an analysis of the pollution features and meteorological factors, including boundary layer characteristics, we concluded that this haze event was similar in most respects to other local haze episodes. We discuss the reasons and the possibilities about this rare color haze at the end of the paper. One way to attain a combination of blue and red light is to have the green wavelengths selectively absorbed, and this seems unlikely for typical atmospheric constituents. -
The Evaluation and Improvement Method of Waterfront Urban Landscape, 49Th ISOCARP Congress 2013
Zhao Ye, The Evaluation and Improvement Method of Waterfront Urban Landscape, 49th ISOCARP Congress 2013 The Evaluation and Improvement Method of Waterfront Urban Landscape: the Case of Urban Landscape Planning for West Lake in Hangzhou, China Ye ZHAO, School of Architecture and Planning, Southeast University, China Jianguo WANG, School of Architecture and Planning, Southeast University, China Abstract Urban landscape usually contains two layers of meaning: landscape and viewing, especially in waterfront zone. Traditional design focuses on landscape design which purely improve the quality of objects in static, passive way much more than noticing the initiative viewer as subject. Actually, landscape and viewing are dialectic. Interactive design using reasonable visual evaluation methods, integrated with “positive” human activity optimization as well as “passive” landscape improvement, can be helpful to enhance the quality and controllability. West Lake in Hangzhou is the famous cultural heritage in China with humanities and nature fitting each other perfectly, which also represents the model of blending natural scenery and modern city. However, it faces some urgent problems in modern urban development, the relationship between West Lake and the city has become extremely uncoordinated, as it suffered very serious “pressure” from the city. This paper takes West Lake as example, basing on lots of survey, analyzes the visual effect from every grid viewpoint on the lake (using GPS to locate), and tries to find out the both way of adjustment from the respects of viewer and landscape, and finally proposes some thinking of the design method. Being water-adjacent is one of the critical principles for ancient cities. In contemporary city, although the functional factor has gradually declined, the landscape meaning is getting greater. -
Fishing Down Or Fishing up in Chinese Freshwater Lakes
View metadata, citation and similar papers at core.ac.uk brought to you by CORE Fisheries Management provided by Institute of Hydrobiology, Chinese Academy Of Sciences and Ecology Fisheries Management and Ecology, 2014, 21, 374–382 Fishing down or fishing up in Chinese freshwater lakes Y. WANG School of Nature Conservation, Beijing Forestry University, Beijing, China J. XU Donghu Experimental Station of Lake Ecosystems, State Key Laboratory of Freshwater Ecology and Biotechnology of China, Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan, China X. YU Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing, China G. LEI School of Nature Conservation, Beijing Forestry University, Beijing, China Abstract Changes in mean trophic level (MTL) of catches have been widely used to reflect the impact of industrial fisheries on aquatic ecosystems because this measure represents the relative abundance of fished species across the trophic level spectrum. In this study, fisheries data from six important freshwater lakes at the middle-lower Yangtze River and Huaihe River reach of Southern China from 1949 to 2009 were used to evaluate changes in catch MTL. After fishery markets opened at 1985, fish catches increased significantly in all the lakes. Lakes Poyang and Dongting, which were dominated by omnivores and connected to the Yangtze River, showed no significant change in catch MTL before and after 1985. Catch MTL in lakes Taihu and Hongze increased significantly due to an increase in the proportion of pelagic zooplanktivorous. Catches in Lake Chaohu were dominated by zooplankton-feeding lake anchovy, Coilia ectenes Temminck & Schlegel and icefish, Neosalanx taihuensis Chen, while Lake Donghu was dominated by phytoplanktivorous carps. -
2005 Report on the State of the Environment in China
2005 Report on the State of the Environment in China State Environmental Protection Administration Table of Contents Environment....................................................................................................................................7 Marine Environment ....................................................................................................................35 Atmospheric Environment...........................................................................................................43 Acoustic Environment ..................................................................................................................52 Solid Wastes...................................................................................................................................56 Radiation and Radioactive Environment....................................................................................59 Arable Land/Land Resources ......................................................................................................62 Forests ............................................................................................................................................67 Grassland.......................................................................................................................................70 Biodiversity....................................................................................................................................75 Climate and Natural Disasters.....................................................................................................81 -
1. Welcome 2. Forum Committee
19-21 August 2009 Nanjing China Building a Harmonious Future for Human Well-being http://www.gfeef.org 1. Welcome You are cordially invited to participate in GFEEF 2009 of IUFRO, which will take place in Nanjing, China. The First Global Forum of Ecological Economics in Forestry (GFEEF): “Harmonious Future for Human Well-being” will be held in Nanjing, China, during the period August 19-21, 2009. Being organized by The International Union of Forest Research Organizations (IUFRO), Nanjing Forestry University(NJFU), China, Seoul National University(SNU), South Korea, as well as sponsored by various international societies. Ecological economics is a transdisciplinary academic field that aims to address the relationships and interdependence between economies and ecosystems. The goal is to promote a state of harmonious development between ecology and economy. Ecological economics aims to balance ecological sustainability, social justice, and economic efficiency, and to learn how to operate an economy within the ecological constraints of the earth’s natural resources and systems. The forum will focus on the harmonious development between ecology and economy in forestry, and will cover all aspects of research on ecological economic theory, forest ecosystem management, sustainable forest industries, measurement and monitoring technologies, and forest ecosystem policies. The GFEEF will include keynote presentations by internationally distinguished researchers and significant contributed papers emphasizing all core areas of ecological economics in forestry. Presentations and discussions will emphasize theories and practices that are needed to achieve sustainable development, guide ecological economic analysis, and incorporate irreversibility of environmental change and uncertainty of long-term outcomes in forest management and policy. -
Report on the State of the Environment in China 2016
2016 The 2016 Report on the State of the Environment in China is hereby announced in accordance with the Environmental Protection Law of the People ’s Republic of China. Minister of Ministry of Environmental Protection, the People’s Republic of China May 31, 2017 2016 Summary.................................................................................................1 Atmospheric Environment....................................................................7 Freshwater Environment....................................................................17 Marine Environment...........................................................................31 Land Environment...............................................................................35 Natural and Ecological Environment.................................................36 Acoustic Environment.........................................................................41 Radiation Environment.......................................................................43 Transport and Energy.........................................................................46 Climate and Natural Disasters............................................................48 Data Sources and Explanations for Assessment ...............................52 2016 On January 18, 2016, the seminar for the studying of the spirit of the Sixth Plenary Session of the Eighteenth CPC Central Committee was opened in Party School of the CPC Central Committee, and it was oriented for leaders and cadres at provincial and ministerial -
Mapping Spatiotemporal Trends in the Abundance and Distribution of Macrophytes in Hongze Lake
第 42 卷 第 6 期 水 生 生 物 学 报 Vol. 42, No. 6 2018 年 11 月 ACTA HYDROBIOLOGICA SINICA Nov., 2018 doi: 10.7541/2018.141 MAPPING SPATIOTEMPORAL TRENDS IN THE ABUNDANCE AND DISTRIBUTION OF MACROPHYTES IN HONGZE LAKE GUO Chuan-Bo1, LI Wei1, ZHANG Ying-Xue1, 2, XIA Wen-Tong1, 2, XIN Wei1, CHEN Yu-Shun1, 2 and LI Zhong-Jie1, 2 (1. State Key Laboratory of Freshwater Ecology and Biotechnology, Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan 430072, China; 2. University of Chinese Academy of Sciences, Beijing 100049, China) Abstract: A comprehensive investigation on macrophyte community in Hongze Lake was conducted seaso- nally from May 2010 to February 2011. Overall, twelve species representing eight families of macrophytes were identified in Hongze Lake, including nine species of submerged plants, two species of floating-leaved plants, and one species of emerging plant. In general, Potamogeton malaianus, P. maackianu, P. pectinatus and P. crispus were the four dominant species throughout the whole year, the highest biomass of macro- phytes was presented in autumn, followed by summer and winter, while spring had the lowest biomass of macrophytes. Based on field data, we used kriging interpolation in ArcGis to map the spatiotemporal distribu- tion of the entire macrophyte community as well as each of the four dominant species. From the GIS maps we observed that the northern area of the lake, namely the Chengzihu region, had the highest biomass of macro- phytes potentially as a result of better water quality and greater transparency. Potential factors that affected the community structure, biomass, and distribution patterns of macrophytes considerably were then discussed. -
Study on Environmental Pollution and Control Countermeasures of Agricultural and Rural Areas in Jiangsu Province
Advances in Engineering Research, volume 170 7th International Conference on Energy and Environmental Protection (ICEEP 2018) Study on Environmental Pollution and Control Countermeasures of Agricultural and Rural Areas in Jiangsu Province Juan Chen a, Guosheng Ma b,* Suzhou Polytechnic Institute of Agriculture, Suzhou, Jiangsu,215008 aemail:[email protected], bemail:[email protected], *Corresponding author Keywords: Jiangsu Province, agricultural and rural areas, ten years, environmental pollution, control countermeasures. Abstract. Based on the combination of typical research and literature, this paper analyzes the current situation of agricultural and rural environmental pollution in Jiangsu Province in the past decade and the causes of environmental pollution in agricultural and rural areas of this province. Then it puts forward countermeasures for environmental pollution control. Studies have shown that in the past ten years, the complex causes of environmental pollution in Jiangsu's agricultural and rural areas include the large proportion of nitrogen and phosphorus pollution, the large amount of livestock and poultry manure, the heavily polluted aquaculture and non-point source of planting, the domestic pollution, and lack of laws and regulations, policy input mechanism and effective governance measures. The countermeasures put forward are mainly included in effective development of ecological recycling agriculture, establishment of rural environmental management system, implementation of the policy of ecological direct subsidy and supervision of capital investment. Introduction In the past ten years, with the rapid economic and social development of Jiangsu Province, the problem of agricultural and rural environmental pollution has gradually emerged. The cyanobacteria of lakes such as Taihu Lake and Hongze Lake have erupted year after year, and the environmental conditions are not optimistic.