The study of spatial and temporal nutrient limitation in Meiliang Bay, Lake Taihu Longyuan Yang 1, Feizhou Chen 1, Yunling Zhang 1, Shixin Wang 2 (1 Nanjing.

Slides:



Advertisements
Similar presentations
– Winter Ecology. Introduction  Global Climate Change  How microbs may be affected by snowpack depth  Temperature/precipitation trends.
Advertisements

The Chemical Water Quality of Lake Nipissing Andrew Paterson Dorset Environmental Science Centre Environmental Monitoring and Reporting Branch.
Baltic Sea Research Institute Warnemünde iow iow Ecological consequences of different nutrient abatement strategies for.
Factors that Affect Productivity in Wintering Lakes: An Analysis of Lake Zones and Snow Depth Kristen Kernan Winter Ecology- Spring 2012.
Great Lakes Observing System GLRI Tributary Monitoring Project
©2010 Elsevier, Inc. Chapter 18 Trophic State and Eutrophication Dodds & Whiles.
Harmful Algal Blooms in Western Lake Erie homas Bridgeman, University of Toledo Thomas Bridgeman, University of Toledo March 16, 2012.
Recent Studies of Urban Air Pollution over the Greater Beijing Area Meigen ZHANG (State Key Laboratory of Atmospheric Boundary Layer Physics and Atmospheric.
Aquatic Succession Eutrophication.
A Study of Temporal Variability of Atmospheric Total Gaseous Mercury Concentrations in Windsor, Ontario, Canada Xiaohong (Iris) Xu, Umme Akhtar, Kyle Clark,
Relationship between Microcystis blooms and crustacean zooplankton in the subtropical lake in China Feizhou Chen Nanjing Institute of Geography and Limnology,
Urban impacts on summertime rainfall in Beijing PEI Grand Challenges program and MIRTHE (Mid Infrared Technologies for Health and Environment) Summer 2008.
Vocabulary Review Ch 21 Ecosystems. A large region characterized by a specific type of climate and certain types of plant and animal communities Biome.
Preliminary Measurement of Submarine Groundwater Discharge in Taiwan Yi-Jie Lin*,Chen-Tung Arthur Chen, Meng-Chia Chen Institute of Marine Geology and.
APPLICATION OF WATER PURIFICATION TECHNOLOGY IN INTENSIVE SHRIMP CULTURE Lai Qiuming 1 *, Yang Yi 2,3, and Qiu Yunhao 1 1.College of Ocean, Hainan University,
Integrated land-water risk analysis for the protection of sensitive catchments from diffuse pollution Reaney S M (1&2), Lane S N (1), Heathwaite A L (2)
1 Surface O 3 over Beijing: Constraints from New Surface Observations Yuxuan Wang, Mike B. McElroy, J. William Munger School of Engineering and Applied.
Hong Liao Institute of Atmospheric Physics Chinese Academy of Sciences Simulation of Air Pollutants (AP) over China using the GEOS-CHEM.
Jędrasik J., Kowalewski M., Ołdakowski B., University of Gdansk, Institute of Oceanography Impact of the Vistula River waters on the Gulf of Gdańsk during.
Temporal and Spatial Variations of Sea Surface Temperature and Chlorophyll a in Coastal Waters of North Carolina Team Members: Brittany Maybin Yao Messan.
Pomme de Terre Lake Water Quality Summary Pomme de Terre Lake Water Quality Summary US Army Corps of Engineers Environmental Resources Section.
Effect of sediment resuspension on underwater light field in shallow lakes in the middle and lower reaches of the Yangtze River: A case study in Longgan.
Biomes of the World.
By: Stephanie Paolone and Ben Clarke. small temperature range Bodies of water in the north and south have a warming affect on the Ontario Region ex. Great.
Contact information: Institution: Latvia University of Agriculture Project contact person: Zane Dimanta Address: 19 Akademijas Str., LV-3001, Jelgava,
Xinbin Feng 1, Wei Zhu 1,2, Xuewu Fu 1, Hui Zhang 1,2 1.Institute of Geochemistry, Chinese Academy of Sciences, Guiyang , PR China 2. Graduate University.
Bacterial production and Microsystin in Lake Taihu GUANG GAO Nanjing Institute of Geography & Limnology, CAS
Agricultural Pollutants and Fertilizers A farm is a high contributor to water pollution…why??? Rain typically washes nutrients and fertilizers off of.
3 Main Climate Zones 17.2 and 17.3.
Effects of nutrient enrichment from fish farming activities on macrobenthic assemblages in subtropical waters Qin Feng Gao, Siu Gin Cheung, Paul K S Shin.
 Nutrient Limitation What’s happening in the Chesapeake Bay and how does it compare to our results?
Fig. 4. A framework configured to calculate a P budget. Shelf ( 1000 m )
A GLOBAL PERSPECTIVE ON THE LINKAGE BETWEEN EUTROPHICATION AND HYPOXIA Robert Diaz College of William and Mary Virginia Institute of Marine Science
Spatial Pattern of PM2.5 over the US PM2.5 FRM Network Analysis for the First Year: July 1999-June 2000 Prepared for EPA OAQPS Richard Scheffe by Rudolf.
Introduction to Ecosystem Monitoring and Metabolism
Grain size, concentration, flux and composition of Asian dust in snow and ice cores on Tibetan Plateau Guangjian Wu, Tandong Yao, Baiqing Xu, Lide Tian,
Temporal and Spatial Variation of air-sea CO 2 Fluxes in the West Coast of Baja California, Mexico J. Martín Hernández-Ayón 1,Ruben Lara-Lara 2, Francisco.
1. The Study of Excess Nitrogen in the Neuse River Basin “A Landscape Level Analysis of Potential Excess Nitrogen in East-Central North Carolina, USA”
Kaijun Su a, Jinzhou Du a, *, Mark Baskaran b and Jing Zhang a State Key Laboratory of Estuarine and Coastal Research, East China Normal University, Shanghai.
Chapter 21 Table of Contents Section 1 Terrestrial Biomes
Nutrient Response of the Ventura River to Drought Conditions in Southern California Al Leydecker 1 and Jessica Altstatt 2 ( 1 Bren School of Environmental.
Freshwater Inflows: Relationships between Water Quality Variables in San Antonio Bay Laura Chu UT Marine Science GISWR Fall 2004.
Dramatic declines in Euphausia pacifica abundance in the East China Sea: response to global warming? Zhaoli XU, Dong ZHANG East China Sea Fisheries Research.
Bottom-up and top-down estimates of ammonia emissions over China Lin Zhang 1 Yuanhong Zhao 1, Youfan Chen 1, Yuepeng Pan 2, Yuesi.
7-8 November 2006 Belgrade, Serbia Extension of the EEA European Topic Centre’s Work Program to the West Balkan Countries in the field of water 1 EIONET-Water.
Long-term measurements of surface ozone at remote and rural sites in China Xiaobin Xu 1, Weili Lin 1,2 1 Chinese Academy of Meteorological Sciences Key.
Chapter 2 Primary Production: The Foundation of Ecosystems © 2013 Elsevier, Inc. All rights reserved. From Fundamentals of Ecosystem Science, Weathers,
Water Quality Analysis of The Lower Colorado River Paula Kulis CE 394K.1.
Monitoring and estimation of land-based nutrients loads in the yellow sea region: Methodology and case study National Marine Environmental Monitoring Center.
Chapter 3, Section 2 and 3.  Biome is a large group of ecosystems that share the same type of climate community.  Marine ecosystems  Terrestrial ecosystems.
Dr. Yan GAO Institute of Agricultural Resources and Environment Water Management and Resources Utilization Research Group.
Global Pattern of Rain Use Efficiency and Its Impact Factors Instructor: Hongyan Liu Qiuyi Wang.
Watersheds & Groundwater Vocabulary.
Sustainable Development Goal for Water: Indicator 6.3.2
Acknowledgements: Astoria Field Team, CMOP Staff
Confined Growth of Water Hyacinth for Bio-remediation in Caohai, Dianchi Lake , China: The Effects on Water Quality The topic of my presentation today.
Monitoring Water Chlorophyll-a Concentration (Chl-a) in Lake Dianchi,China from 2003 ~ 2009 by MERIS Data.
in the Neversink River Basin, New York
Water Depth and Nutrient Ratios over Space
ABSTRACT METHODS RESULTS BACKGROUND CONCLUSIONS OBJECTIVES
Part 2: Abiotic Factors affecting Aquatic Ecosystems Pg
3 Main Climate Zones 17.2 and 17.3.
1. The Study of Excess Nitrogen in the Neuse River Basin
Jim McClelland Rae Mooney University of Texas at Austin
3 Main Climate Zones 17.2 and 17.3.
Factors Affecting Aquatic Ecosystems
3 Main Climate Zones 17.2 and 17.3.
Aquatic Ecosystems.
Typology and classification of coastal waters in Estonia
3 Main Climate Zones 17.2 and 17.3.
Presentation transcript:

The study of spatial and temporal nutrient limitation in Meiliang Bay, Lake Taihu Longyuan Yang 1, Feizhou Chen 1, Yunling Zhang 1, Shixin Wang 2 (1 Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences; 2 Institute of Remote Sensing Applications, Chinese Academy of Sciences )

Purpose To measure nitrogen and phosphorus concentrations in Meiliang Bay, Lake Taihu, and analyze spatial and temporal variation of water quality parameters; To analyze the relationship between nutrient concentrations and dominant algae species. To study nutrient limitation status in Meiliang Bay, Lake Taihu.

Redfield Ratio If N:P ratio > 16, there is P limitation in the aquatic ecosystem; If N:P ratio < 16, there is N limitation in the aquatic ecosystem.

Background about limitation factor research in Lake Taihu Phosphorus is the limitation factor in Lake Taihu (traditional opinion); There is nitrogen limitation sites in some seasons and in some aquatic area (Martin Dokulil et al. 2000); There is a limitation factor change phenomenon that from Liangxi river discharge area to the main body of Lake Taihu (McCarthy et al. 2007)

Sampling sites Regular site: 25 (per 3 months) Add specific site: 20 (2 times in 2004) Total sites: 45

Distribution of sampling area NameSitesNL RangeS Number River discharge L0 K5 B3 B4 B6 B7 B Inner bay L1 L2 K2 K3 K4 K6 B5 B9 B10 B11 B Outer bay L3 L4 K1 K7 K8 B1 B2 B13 B14 B Open area L5 L6 K9 K10 K11 K12 K19 K Central area L7 L8 L9 K13 K14 K15 K16 K17 K

Function of Distribution NameFunctionDistance River Discharge Pollution area by point source from Liangxi and Lvjing River 0 km Inner B Near pollution source area of Bay 8 km Outer B Fare pollution source and near open area of Bay 16 km Open A Open area that connect with the Outer Bay 24 km Central A Main body of Lake Taihu 36 km

Results (Oct-2003 to Aug-2005) For whole research area

Spatial and temporal variation calculate of nutrients Spatial variation in research area were calculated by average of all sites in one distribution area; Annual variation were calculated by all sites in same distribution area and separated seasons.

Interval to Average Index (IA Index) I %=(C i -C m )*100/C m Where: I mean the IA index coefficient ; C i concentration of individual parameter; C m mean concentration of whole area

The ratio of nitrogen over phosphorus TN:TPWinSprSumFall MB MB MB MB MB

Annual variation characters summary In winter and spring seasons the mole ratio of TN:TP are more higher than Readfield ratio (16) ; but in summer and fall seasons the mole ratio of TN:TP are almost equal to Readfield ratio. So there is dominant P limitation in Winter and Spring seasons (Colder season, water temperature 20 o C ) except the P limitation in shore area of Lake Taihu. In open and central areas(B4 and B5) the mole ratio of TN:TP reduced serious than in river discharge area(B1) in whole year; so the open and central areas is the hot point for nitrogen limitation or nitrogen and phosphorus co- limitation mainly occur areas.

Dominant algae species in different areas (Oct. 27, 2003) AreaName% B1 Microcystis Merismopedia Scenesdesmus Cyclotella B2 Microcystis Chlamydomonas Euglena 8.08 Cyclotella 5.24 Cryptomonas 6.82 B3 Microcystis Merismopedia 1.81 Chlamydomonas 2.80 Scenesdesmus 2.12 B4 Merismopedia B5 Merismopedia Scenesdesmus 18.47

Conclusion There is a phenomenon that phosphorus limitation change to nitrogen limitation from Liangxi river discharge area to the main body (open area) of Lake Taihu; Summer and Fall seasons is the nitrogen Limitation occur season; especially in the area that far away from pollution river discharge area such as in central area of Lake Taihu The phenomenon that limitation factor changes may occur in all large shallow eutrophication lakes and estuaries in east part of China and other north temperate zones

谢谢莅临指导 ! Thank you! Welcome to Taihu Field Station ! Thank you for presentation