Aquatic Ecosystem Part 1 a SHORT NOTE for B.SC ZOOLOGY
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Pond and Lake Ecosystems a Pond Or Lake Ecosystem Includes Biotic
Pond and Lake Ecosystems A pond or lake ecosystem includes biotic (living) plants, animals and micro-organisms, as well as abiotic (nonliving) physical and chemical interactions. Pond and lake ecosystems are a prime example of lentic ecosystems. Lentic refers to stationary or relatively still water, from the Latin lentus, which means sluggish. A typical lake has distinct zones of biological communities linked to the physical structure of the lake. (Figure below) The littoral zone is the near shore area where sunlight penetrates all the way to the sediment and allows aquatic plants (macrophytes) to grow. Light levels of about 1% or less of surface values usually define this depth. The 1% light level also defines the euphotic zone of the lake, which is the layer from the surface down to the depth where light levels become too low for photosynthesizers. In most lakes, the sunlit euphotic zone occurs within the epilimnion. However, in unusually transparent lakes, photosynthesis may occur well below the thermocline into the perennially cold hypolimnion. For example, in western Lake Superior near Duluth, MN, summertime algal photosynthesis and growth can persist to depths of at least 25 meters, while the mixed layer, or epilimnion, only extends down to about 10 meters. Ultra-oligotrophic Lake Tahoe, CA/NV, is so transparent that algal growth historically extended to over 100 meters, though its mixed layer only extends to about 10 meters in summer. Unfortunately, inadequate management of the Lake Tahoe basin since about 1960 has led to a significant loss of transparency due to increased algal growth and increased sediment inputs from stream and shoreline erosion. -
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. -
Florida Lakes and Ponds Guidebook
Florida Lakes and Ponds Guidebook Florida has thousands of lakes and ponds that provide opportunities for recreation and valuable habitat for a wide diversity of plants and animals. However, over the years, many citizens of Florida have observed a decline in the health of their lakes and ponds. By choosing to read this guide you are taking the first step towards protecting your lake or pond. This manual is a starting point for concerned citizens who wish to learn about lake ecology and ways they can protect the future of their lake or pond. Photography provided courtesy of Pinellas County Communications Department u The first two chapters will help you understand the basic concepts of watersheds and the ecology of lakes and ponds. It covers the importance of a watershed approach to lake and pond protection and the ecology and cycles within a lake system. The following chapters address the main causes of reduced water quality and outline ways that you, as a concerned citizen, can adopt a proactive role in preventing further degradation to our waterbodies. The last section provides guidance for people who wish to go one step further and begin or join a lake association, apply for a grant or obtain additional education publications. Words in italics are defined in the glossary in the back of the book. By taking action today, we can protect our lakes and ponds for tomorrow. 1 Table of Contents Introduction Chapter 1: Understanding Watersheds 1.1 Watershed Information Chapter 2: Lake Basics 2.1 The Hydrologic Cycle 2.2 Thermal Stratification -
Lake Ecology
Fundamentals of Limnology Oxygen, Temperature and Lake Stratification Prereqs: Students should have reviewed the importance of Oxygen and Carbon Dioxide in Aquatic Systems Students should have reviewed the video tape on the calibration and use of a YSI oxygen meter. Students should have a basic knowledge of pH and how to use a pH meter. Safety: This module includes field work in boats on Raystown Lake. On average, there is a death due to drowning on Raystown Lake every two years due to careless boating activities. You will very strongly decrease the risk of accident when you obey the following rules: 1. All participants in this field exercise will wear Coast Guard certified PFDs. (No exceptions for teachers or staff). 2. There is no "horseplay" allowed on boats. This includes throwing objects, splashing others, rocking boats, erratic operation of boats or unnecessary navigational detours. 3. Obey all boating regulations, especially, no wake zone markers 4. No swimming from boats 5. Keep all hands and sampling equipment inside of boats while the boats are moving. 6. Whenever possible, hold sampling equipment inside of the boats rather than over the water. We have no desire to donate sampling gear to the bottom of the lake. 7. The program director has final say as to what is and is not appropriate safety behavior. Failure to comply with the safety guidelines and the program director's requests will result in expulsion from the program and loss of Field Station privileges. I. Introduction to Aquatic Environments Water covers 75% of the Earth's surface. We divide that water into three types based on the salinity, the concentration of dissolved salts in the water. -
Freshwater Ecosystem: Part 2
Paper : 12 Principles of Ecology Module : 22 Types of Ecosystems: Aquatic Ecosystem-Fresh Water Ecosystem: Part 2 Development Team Principal Investigator : Prof. Neeta Sehgal Department of Zoology, University of Delhi Co-Principal Investigator : Prof. D.K. Singh Department of Zoology, University of Delhi Paper Coordinator : Prof. D.K. Singh Department of Zoology, University of Delhi Content Writer : Dr. Sushma Bhardwaj , Deshbandhu College, DU Ms. Harshita Mishra, Research Scholar, DU Content Reviewer : Prof. K.S. Rao Department of Botany, University of Delhi 1 Principles of Ecology ZOOLOGY Aquatic Ecosystem: Freshwater Ecosystem: Part 2 Description of Module Subject Name ZOOLOGY Paper Name Zool 12 Principles of Ecology Module Name/Title Types of Ecosystems: Aquatic Ecosystem Module Id M22: Aquatic Ecosystem: Freshwater Ecosystem: Part 2 Keywords Lentic, lotic, community, lake, temperate lake, zone, eutrophy, Langmuir circulation Contents 1. Learning Objectives 2. Introduction 3. The Lentic Aquatic System 3.1. Zonation in Lentic Systems 3.2. Characteristics of Lentic Ecosystem 3.3. Lentic Community 3.3.1. Communities of the littoral zone 3.3.2. Communities of Limnetic Zone 3.3.3. Communities of Profundal Zone 4. Lake Ecosystem 4.1. Thermal Properties of Lake 4.2. Seasonal Cycle in Temperate Lakes 4.3. Biological Oxygen Demand 4.4. Eutrophy and Oligotrophy 4.5. Langmuir Circulation and the Descent of the Thermocline 4.6. Types of Lakes 5. State of Freshwater Ecosystems in Present Scenario 5.1. Causes of Change in the properties of freshwater bodies 5.1.1. Climate Change 5.1.2. Change in Water Flow 5.1.3. Land-Use Change 5.1.4. -
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. -
Outline for Capitol Lake Faunal Analysis
FINAL REPORT Implications of Capitol Lake Management for Fish and Wildlife Prepared by: The Washington Department of Fish and Wildlife Marc P. Hayes Timothy Quinn Tiffany L. Hicks Prepared for: Capital Lake Adaptive Management Program Steering Committee 11 September 2008 Table of Contents Executive Summary ................................................................................................................ iii 1 Introduction ................................................................................................................... 1 1.1 Historical Background and Physical Setting of Capitol Lake ................................... 1 1.2 Prior Faunal Surveys and Research ...................................................................... 7 1.3 Objectives .................................................................................................................. 7 2 Methods ......................................................................................................................... 8 2.1 Species Assessment ................................................................................................... 8 2.2 Ecosystem Assessment ............................................................................................. 9 3 Results and Discussion ............................................................................................... 10 3.1 Species Present and Their Response .......................................................................... 10 3.1.1 Vertebrates ........................................................................................................... -
Comparison of Littoral and Limnetic Zooplankton Communities of Lake Mead
Publications (WR) Water Resources 5-1987 Comparison of littoral and limnetic zooplankton communities of Lake Mead Patrick Joseph Sollberger University of Nevada, Las Vegas Follow this and additional works at: https://digitalscholarship.unlv.edu/water_pubs Part of the Biology Commons, Environmental Indicators and Impact Assessment Commons, Environmental Monitoring Commons, Fresh Water Studies Commons, Natural Resources and Conservation Commons, Terrestrial and Aquatic Ecology Commons, and the Water Resource Management Commons Repository Citation Sollberger, P. J. (1987). Comparison of littoral and limnetic zooplankton communities of Lake Mead. Available at: https://digitalscholarship.unlv.edu/water_pubs/84 This Thesis is protected by copyright and/or related rights. It has been brought to you by Digital Scholarship@UNLV with permission from the rights-holder(s). You are free to use this Thesis in any way that is permitted by the copyright and related rights legislation that applies to your use. For other uses you need to obtain permission from the rights-holder(s) directly, unless additional rights are indicated by a Creative Commons license in the record and/ or on the work itself. This Thesis has been accepted for inclusion in Publications (WR) by an authorized administrator of Digital Scholarship@UNLV. For more information, please contact [email protected]. QL. Comparison of Littoral and Limnetic Zooplankton Communities of Lake Mead by x Patrick Joseph Sollberger A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science in Biological Sciences Department of Biological Sciences University of Nevada, Las Vegas May, 1987 UNIVERSITY OF NEVADA, LAS VEGAS LIBRARY thesis of Patrick Joseph Sollberger for the degree of tester of Science in the Biological Sciences is approved. -
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 -
Ecological Features and Processes of Lakes and Wetlands
Ecological features and processes of lakes and wetlands Lakes are complex ecosystems defined by all system components affecting surface and ground water gains and losses. This includes the atmosphere, precipitation, geomorphology, soils, plants, and animals within the entire watershed, including the uplands, tributaries, wetlands, and other lakes. Management from a whole watershed perspective is necessary to protect and maintain healthy lake systems. This concept is important for managing the Great Lakes as well as small inland lakes, even those without tributary streams. A good example of the need to manage from a whole watershed perspective is the significant ecological changes that have occurred in the Great Lakes. The Great Lakes are vast in size, and it is hard to imagine that building a small farm or home, digging a channel for shipping, fishing, or building a small dam could affect the entire system. However, the accumulation of numerous human development activities throughout the entire Great Lakes watershed resulted in significant changes to one of the largest freshwater lake systems in the world. The historic organic contamination problems, nutrient problems, and dramatic fisheries changes in our Great Lakes are examples of how cumulative factors within a watershed affect a lake. Habitat refers to an area that provides the necessary resources and conditions for an organism to survive. Because organisms often require different habitat components during various life stages (reproduction, maturation, migration), habitat for a particular species may encompass several cover types, plant communities, or water-depth zones during the organism's life cycle. Moreover, most species of fish and wildlife are part of a complex web of interactions that result in successful feeding, reproduction, and predator avoidance. -
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.