Sustaining Healthy Freshwater Ecosystems
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Freshwater Ecosystems and Biodiversity
Network of Conservation Educators & Practitioners Freshwater Ecosystems and Biodiversity Author(s): Nathaniel P. Hitt, Lisa K. Bonneau, Kunjuraman V. Jayachandran, and Michael P. Marchetti Source: Lessons in Conservation, Vol. 5, pp. 5-16 Published by: Network of Conservation Educators and Practitioners, Center for Biodiversity and Conservation, American Museum of Natural History Stable URL: ncep.amnh.org/linc/ This article is featured in Lessons in Conservation, the official journal of the Network of Conservation Educators and Practitioners (NCEP). NCEP is a collaborative project of the American Museum of Natural History’s Center for Biodiversity and Conservation (CBC) and a number of institutions and individuals around the world. Lessons in Conservation is designed to introduce NCEP teaching and learning resources (or “modules”) to a broad audience. NCEP modules are designed for undergraduate and professional level education. These modules—and many more on a variety of conservation topics—are available for free download at our website, ncep.amnh.org. To learn more about NCEP, visit our website: ncep.amnh.org. All reproduction or distribution must provide full citation of the original work and provide a copyright notice as follows: “Copyright 2015, by the authors of the material and the Center for Biodiversity and Conservation of the American Museum of Natural History. All rights reserved.” Illustrations obtained from the American Museum of Natural History’s library: images.library.amnh.org/digital/ SYNTHESIS 5 Freshwater Ecosystems and Biodiversity Nathaniel P. Hitt1, Lisa K. Bonneau2, Kunjuraman V. Jayachandran3, and Michael P. Marchetti4 1U.S. Geological Survey, Leetown Science Center, USA, 2Metropolitan Community College-Blue River, USA, 3Kerala Agricultural University, India, 4School of Science, St. -
BIG RIVER ECOSYSTEM: Program 2
BIG RIVER ECOSYSTEM: A Question of Net Worth PURPOSE To explore biodiversity at the ecosystem level. KERA CONNECTIONS to Life Science Program 2 Core Content: Structure and Function in Living Systems Academic Expectations: 2.2 Patterns, 2.3 Systems, 2.4 Models & Scale ANSWERS TO Process Skills: Observation, Modeling aFIELD NOTES OBJECTIVES 1. In a hot and hostile environment, Students should be able to: the evaporated water cannot be 1.identify five “big river” organisms incorporated into living cells (as 2.construct a diagram showing interactions between living and we know them). nonliving parts of an ecosystem 2. An extremely cold environment, 3. discuss factors that affect the level of biodiversity in their river basin. or frozen desert, does not allow cells to utilize water. VOCABULARY 3. Answers will vary but should Teachers may wish to discuss the following terms: display logical flow of water and aquatic, commercial, ecosystem, water cycle and watershed. allow for recirculation in a loop. 4. Arteries and veins. aFIELD NOTEBOOK 5. A pumping heart. Ideas for Teachers 6. Diagram A shows many different A. Develop a concept map for the water cycle. Include these items in types of ecosystems in close the concept map: clouds, groundwater, apple tree, stream, precipita- proximity. tion, condensation, evaporation, harvest mouse, snowflakes, sun and 7. Add a watering hole, plant a humans. What other cycles are needed to maintain an ecosystem? miniature forest, create a B. Biospheres, containing algae, brine shrimp and water, are often meadow of wildflowers. Most shown in advertisements. Analyze how the biosphere is self-main- importantly, break up a monocul- taining. -
Effects of Eutrophication on Stream Ecosystems
EFFECTS OF EUTROPHICATION ON STREAM ECOSYSTEMS Lei Zheng, PhD and Michael J. Paul, PhD Tetra Tech, Inc. Abstract This paper describes the effects of nutrient enrichment on the structure and function of stream ecosystems. It starts with the currently well documented direct effects of nutrient enrichment on algal biomass and the resulting impacts on stream chemistry. The paper continues with an explanation of the less well documented indirect ecological effects of nutrient enrichment on stream structure and function, including effects of excess growth on physical habitat, and alterations to aquatic life community structure from the microbial assemblage to fish and mammals. The paper also dicusses effects on the ecosystem level including changes to productivity, respiration, decomposition, carbon and other geochemical cycles. The paper ends by discussing the significance of these direct and indirect effects of nutrient enrichment on designated uses - especially recreational, aquatic life, and drinking water. 2 1. Introduction 1.1 Stream processes Streams are all flowing natural waters, regardless of size. To understand the processes that influence the pattern and character of streams and reduce natural variation of different streams, several stream classification systems (including ecoregional, fluvial geomorphological, and stream order classification) have been adopted by state and national programs. Ecoregional classification is based on geology, soils, geomorphology, dominant land uses, and natural vegetation (Omernik 1987). Fluvial geomorphological classification explains stream and slope processes through the application of physical principles. Rosgen (1994) classified stream channels in the United States into seven major stream types based on morphological characteristics, including entrenchment, gradient, width/depth ratio, and sinuosity in various land forms. -
Ecosystem Services Generated by Fish Populations
AR-211 Ecological Economics 29 (1999) 253 –268 ANALYSIS Ecosystem services generated by fish populations Cecilia M. Holmlund *, Monica Hammer Natural Resources Management, Department of Systems Ecology, Stockholm University, S-106 91, Stockholm, Sweden Abstract In this paper, we review the role of fish populations in generating ecosystem services based on documented ecological functions and human demands of fish. The ongoing overexploitation of global fish resources concerns our societies, not only in terms of decreasing fish populations important for consumption and recreational activities. Rather, a number of ecosystem services generated by fish populations are also at risk, with consequences for biodiversity, ecosystem functioning, and ultimately human welfare. Examples are provided from marine and freshwater ecosystems, in various parts of the world, and include all life-stages of fish. Ecosystem services are here defined as fundamental services for maintaining ecosystem functioning and resilience, or demand-derived services based on human values. To secure the generation of ecosystem services from fish populations, management approaches need to address the fact that fish are embedded in ecosystems and that substitutions for declining populations and habitat losses, such as fish stocking and nature reserves, rarely replace losses of all services. © 1999 Elsevier Science B.V. All rights reserved. Keywords: Ecosystem services; Fish populations; Fisheries management; Biodiversity 1. Introduction 15 000 are marine and nearly 10 000 are freshwa ter (Nelson, 1994). Global capture fisheries har Fish constitute one of the major protein sources vested 101 million tonnes of fish including 27 for humans around the world. There are to date million tonnes of bycatch in 1995, and 11 million some 25 000 different known fish species of which tonnes were produced in aquaculture the same year (FAO, 1997). -
Aquatic Ecosystems
February 19, 2014 Nantahala and Pisgah NFs Assessment Aquatic Ecosystems The overall richness of North Carolina’s aquatic fauna is directly related to the geomorphology of the state, which defines the major drainage divisions and the diversity of habitats found within. There are seventeen major river basins in North Carolina. Five western basins are part of the Interior Basin (IB) and drain to the Mississippi River and the Gulf of Mexico (Hiwassee, Little Tennessee, French Broad, Watauga, and New). Parts of these five river basins are within the Nantahala and Pisgah National Forests (NFs). Twelve central and eastern basins are part of the Atlantic Slope (AS) and flow to the Atlantic Ocean. Of these twelve central and eastern basins, parts of the Savannah, Broad, Catawba, and Yadkin-Pee Dee basins are within the Nantahala and Pisgah NFs. As described later in this report, the Nantahala and Pisgah NFs, for the most part, support higher elevation coldwater streams, and relatively little cool- and warmwater resources. To gain perspective on the importance of aquatic ecosystems on the Nantahala and Pisgah NFs, it is first necessary to understand their value at regional and national scales. The southeastern United States has the highest aquatic species diversity in the entire United States (Burr and Mayden 1992; Williams et al. 1993; Taylor et al. 1996; Warren et al. 2000,), with southeastern fishes comprising 62% of the United States fauna, and nearly 50% of the North American fish fauna (Burr and Mayden 1992). Freshwater mollusk diversity in the southeast is ‘globally unparalleled’, representing 91% of all United States mussel species (Neves et al. -
Aquatic Ecology ______INTRODUCTION
Aquatic Ecology ________________________________________________________________ INTRODUCTION Aquatic Ecology Field Station Aquatics or aquatic ecology is the study of animals and plants in freshwater environments. In addition to the many common aquatic species in this Western New York region, a student of aquatics learns about watersheds, wetlands and the hydrologic cycle. Essential to understanding and appreciating the field of aquatics is a basic knowledge of the physical and chemical properties of water. Water is arguably the most valuable substance on the planet, and is the common name applied to the liquid state of the hydrogen oxygen compound H2O. It covers 70% of the surface of the Earth forming swamps, lakes, rivers, and oceans. Pure water has a blue tint, which may be detected only in layers of considerable depth. It has no taste or odor. Water molecules are strongly attracted to one another through their two hydrogen atoms. At the surface, this attraction produces a tight film over the water (surface tension). A number of organisms live both on the upper and lower sides of this film. 1 Density of water is greatest at 39.2° Fahrenheit (4° Celsius). It becomes less as water warms and, more important, as it cools to freezing at 32° Fahrenheit (0° Celsius), and becomes ice. Ice is a poor heat conductor. Therefore, ice sheets on ponds, lakes and rivers trap heat in the water below. For this reason, only very shallow water bodies never freeze solid. Water is the only substance that occurs at ordinary temperatures in all three states of matter: solid, liquid, and gas. In its solid state, water is ice, and can be found as glaciers, snow, hail, and frost and ice crystals in clouds. -
Lake Superior Phototrophic Picoplankton: Nitrate Assimilation
LAKE SUPERIOR PHOTOTROPHIC PICOPLANKTON: NITRATE ASSIMILATION MEASURED WITH A CYANOBACTERIAL NITRATE-RESPONSIVE BIOREPORTER AND GENETIC DIVERSITY OF THE NATURAL COMMUNITY Natalia Valeryevna Ivanikova A Dissertation Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY May 2006 Committee: George S. Bullerjahn, Advisor Robert M. McKay Scott O. Rogers Paul F. Morris Robert K. Vincent Graduate College representative ii ABSTRACT George S. Bullerjahn, Advisor Cyanobacteria of the picoplankton size range (picocyanobacteria) Synechococcus and Prochlorococcus contribute significantly to total phytoplankton biomass and primary production in marine and freshwater oligotrophic environments. Despite their importance, little is known about the biodiversity and physiology of freshwater picocyanobacteria. Lake Superior is an ultra- oligotrophic system with light and temperature conditions unfavorable for photosynthesis. Synechococcus-like picocyanobacteria are an important component of phytoplankton in Lake Superior. The concentration of nitrate, the major form of combined nitrogen in the lake, has been increasing continuously in these waters over the last 100 years, while other nutrients remained largely unchanged. Decreased biological demand for nitrate caused by low availabilities of phosphorus and iron, as well as low light and temperature was hypothesized to be one of the reasons for the nitrate build-up. One way to get insight into the microbiological processes that contribute to the accumulation of nitrate in this ecosystem is to employ a cyanobacterial bioreporter capable of assessing the nitrate assimilation capacity of phytoplankton. In this study, a nitrate-responsive biorepoter AND100 was constructed by fusing the promoter of the Synechocystis PCC 6803 nitrate responsive gene nirA, encoding nitrite reductase to the Vibrio fischeri luxAB genes, which encode the bacterial luciferase, and genetically transforming the resulting construct into Synechocystis. -
Linking Biological Toxicity and the Spectral Characteristics Of
Chen et al. Environ Sci Eur (2019) 31:84 https://doi.org/10.1186/s12302-019-0269-y RESEARCH Open Access Linking biological toxicity and the spectral characteristics of contamination in seriously polluted urban rivers Zhongli Chen1, Zihan Zhu1, Jiyu Song1, Ruiyan Liao1, Yufan Wang1, Xi Luo1, Dongya Nie1, Yumeng Lei1, Ying Shao1* and Wei Yang2,3 Abstract Background: Urban river pollution risks to environments and human health are emerging as a serious concern worldwide. With the aim to achieve the health of urban river ecosystem, numerous monitoring programs have been implemented to investigate the spectral characteristics of contamination. While due to the complexity of aquatic pollutants, the linkages between harmful efects and the spectral characteristics of contamination are still a major challenge for capturing main threats to urban aquatic environments. To establish these linkages, surface water (SW), sediment pore water (SDPW), and riparian soil pore water (SPW) were collected from fve sites of the seriously pol- luted Qingshui Stream, China. The water-dissolved organic carbon (DOC), total nitrogen (TN), total phosphate (TP), fuorescence excitation–emission matrix, and specifc ultraviolet absorbance were applied to analyze the spectral characteristics of urban river contamination. The Photobacterium phosphorem 502 was used to test the acute toxicity of the samples. Finally, the correlations between acute toxicity and concentrations of DOC, TN, TP, and the spectral characteristics were explored. Results: The concentrations of DOC, TN, and TP in various samples amounted from 11.41 2.31 to 3844.67 87.80 mg/L, from 1.96 0.06 to 906.23 26.01 mg/L and from 0.06 0.01 to 101.00± 8.29 mg/L, respec- tively. -
Assessment of the Trophic Status at Al-Sabil River Using the Trophic Indices in Al-Shinafiya District, Southern Iraq
EurAsian Journal of BioSciences Eurasia J Biosci 14, 5661-5667 (2020) Assessment of the trophic status at Al-Sabil River using the trophic indices in Al-Shinafiya district, Southern Iraq Khitam Abbas Marhoon 1, Eman Mohammed Hussain 2, Salwan Ali Abed 3, Salam Hussein Ewaid 4, Mudhafar A. Salim 5, Nadhir Al-Ansari 6 1,3 Environment Department, College of Science, University of Al-Qadisiyah, IRAQ 2 Biology Department, College of Science, University of Al-Qadisiyah, IRAQ 4 Technical Institute of Shatra, Southern Technical University, IRAQ 5 Arab Regional Center for World Heritage, Manama, BAHRAIN. 6 Luleå University of Technology, Luleå, SWEDEN *Corresponding author: [email protected] ; [email protected] Abstract The current study was conducted to determine the quality of the water of Al- Sabil River in Al-Shinafiya district, Province of Al- Diwaniyah, for the period from September 2018 to August 2019. Three sites were selected along the river, a quantitative and qualitative study of the diatoms as well as its indices to assess the quality of water in the river, such as trophic diatom Index (TDI), Trophic State Index (TSI), Diatomic Index (DI), and General Diatoms Index (GDI). The current study was diagnosed about 136 species of diatoms at three sites, where the central diatoms was 12 species while the pannals diatoms reached 124 species, and recorded total numbers of diatoms (35453.8, 29447.2 and 36504.76) cell*310/L, and rates (2954.48, 2453.93 and 3042.06) cells*310/L for the three locations respectively, as shown by the results of the trophic diatom Index(TDI) values ranged from (23.33 to 55.54) and the values of Trophic State Index (TSI) ranged from (0.07 to 0.81) and the Diatomic Index (DI) values ranged from (9.08 to 16.20) and the values of the General Diatoms Index (GDI) ranged from (2.23 to 3.17). -
Aquatic Ecosystem Delineation and Description Guidelines AQUATIC ECOSYSTEMS TOOLKIT • MODULE 4 •Aquatic Ecosystem Delineation and Description Guidelines
Aquatic ecosystems toolkit MODULE 4: Aquatic ecosystem delineation and description guidelines AQUATIC ECOSYSTEMS TOOLKIT • MODULE 4 •Aquatic ecosystem delineation and description guidelines Published by Department of Sustainability, Environment, Water, Population and Communities Authors/endorsement Aquatic Ecosystems Task Group Endorsed by the Standing Council on Environment and Water, 2012. © Commonwealth of Australia 2012 This work is copyright. You may download, display, print and reproduce this material in unaltered form only (retaining this notice) for your personal, non-commercial use or use within your organisation. Apart from any use as permitted under the Copyright Act 1968 (Cwlth), all other rights are reserved. Requests and enquiries concerning reproduction and rights should be addressed to Department of Sustainability, Environment, Water, Population and Communities, Public Affairs, GPO Box 787 Canberra ACT 2601 or email <[email protected]>. Disclaimer The views and opinions expressed in this publication are those of the authors and do not necessarily reflect those of the Australian Government or the Minister for Sustainability, Environment, Water, Population and Communities. While reasonable efforts have been made to ensure that the contents of this publication are factually correct, the Commonwealth does not accept responsibility for the accuracy or completeness of the contents, and shall not be liable for any loss or damage that may be occasioned directly or indirectly through the use of, or reliance on, the -
Aquatic Ecosystems Bibliography Compiled by Robert C. Worrest
Aquatic Ecosystems Bibliography Compiled by Robert C. Worrest Abboudi, M., Jeffrey, W. H., Ghiglione, J. F., Pujo-Pay, M., Oriol, L., Sempéré, R., . Joux, F. (2008). Effects of photochemical transformations of dissolved organic matter on bacterial metabolism and diversity in three contrasting coastal sites in the northwestern Mediterranean Sea during summer. Microbial Ecology, 55(2), 344-357. Abboudi, M., Surget, S. M., Rontani, J. F., Sempéré, R., & Joux, F. (2008). Physiological alteration of the marine bacterium Vibrio angustum S14 exposed to simulated sunlight during growth. Current Microbiology, 57(5), 412-417. doi: 10.1007/s00284-008-9214-9 Abernathy, J. W., Xu, P., Xu, D. H., Kucuktas, H., Klesius, P., Arias, C., & Liu, Z. (2007). Generation and analysis of expressed sequence tags from the ciliate protozoan parasite Ichthyophthirius multifiliis BMC Genomics, 8, 176. Abseck, S., Andrady, A. L., Arnold, F., Björn, L. O., Bomman, J. F., Calamari, D., . Zepp, R. G. (1998). Environmental effects of ozone depletion: 1998 assessment. Journal of Photochemistry and Photobiology B: Biology, 46(1-3), 1-108. doi: Doi: 10.1016/s1011-1344(98)00195-x Adachi, K., Kato, K., Wakamatsu, K., Ito, S., Ishimaru, K., Hirata, T., . Kumai, H. (2005). The histological analysis, colorimetric evaluation, and chemical quantification of melanin content in 'suntanned' fish. Pigment Cell Research, 18, 465-468. Adams, M. J., Hossaek, B. R., Knapp, R. A., Corn, P. S., Diamond, S. A., Trenham, P. C., & Fagre, D. B. (2005). Distribution Patterns of Lentic-Breeding Amphibians in Relation to Ultraviolet Radiation Exposure in Western North America. Ecosystems, 8(5), 488-500. Adams, N. -
Aquatic Ecosystem Part 1 a SHORT NOTE for B.SC ZOOLOGY
2020 Aquatic ecosystem part 1 A SHORT NOTE FOR B.SC ZOOLOGY WRITTEN BY DR.MOTI LAL GUPTA ,H.O.D ,DEPARTMENT OF ZOOLOGY,B.N.COLLEGE,PATNA UNIVERSITY [Type the author name] DEPARTMENT OF ZOOLOGY,B.N COLLEGE, P.U 4/16/2020 Aquatic ecosystem part 1 2 1 Department of zoology,B.N College,P.U Page 2 Aquatic ecosystem part 1 3 Contents 1. Learning Objectives 2. Introduction 3. The Lentic Aquatic System Zonation in Lentic Systems Characteristics of Lentic Ecosystem Lentic Community Communities of the littoral zone Communities of Limnetic Zone Communities of Profundal Zone 4. Lake Ecosystem Thermal Properties of Lake Seasonal Cycle in Temperate Lakes Biological Oxygen Demand Eutrophy and Oligotrophy Langmuir Circulation and the Descent of the Thermocline Types of Lakes 5. State of Freshwater Ecosystems in Present Scenario Causes of Change in the properties of freshwater bodies Climate Change Change in Water Flow Land-Use Change Changing Chemical Inputs Aquatic Invasive Species Harvest Impact of Change on Freshwater Bodies Physical Transformations 6. Summary 2 Department of zoology,B.N College,P.U Page 3 Aquatic ecosystem part 1 4 1. Learning Objectives After the end of this module you will be able to 1. Understand the concept of fresh water ecosystem. 2. Understand the characteristics of the Lentic ecosystems. 3. Know the communities of lentic ecosystems and their ecological adaptations. 4. Know properties of Lake Ecosystems and their types. 5. Understand the major changes that are causing the threats to freshwaters ecosystems. 2. Introduction Freshwater ecology can be interpreted as interrelationship between freshwater organism and their natural environments.