DOCSLIB.ORG

Aquatic Ecosystem Part 1 a SHORT NOTE for B.SC ZOOLOGY

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
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. Fresh water streams (springs, rivulets, creeks, brooks, etc.) and rivers trend over their course from being narrow, shallow and relatively rapid to increasingly broad, deep and slow moving. The degree of each feature depends upon the vertical drop over its length. This shift in movement of the water is reflected in the substrate, which trends from being rocky and without sediment to deep sediments found in the deltas at the mouth of some great rivers like Mississippi. Lentic ecosystems (pools, ponds, swamps, bogs lakes, etc.) vary considerably in physical, chemical and biological characteristics. In general, they have different zonation, unlike the rapid and the pool zones of the lotic system with different specialized lentic community. 3.The Lentic Aquatic System Lentic aquatic bodies contain stagnant waters. These are formed usually in large or small depressions formed on earth's surface where water is trapped and has no exit flow. Ponds, lakes, swamps etc. are few such water bodies. Therefore, the lentic systems are closed systems i.e. most of the aquatic forms that enter these systems rarely get out. They have to persist, decay and decompose within the lentic body. In due course of time, they change into swamps or marshy wetlands and finally into dry lands. PAGE3 Department of zoology,B.N College,P.U Page 4 Aquatic ecosystem part 1 5 Fig.1: Examples of Lentic ecosystem Zonation in Lentic Systems Fig.2: Zonation in Lentic water body The bodies like ponds and lakes have three zones: 4 Department of zoology,B.N College,P.U Page 5 Aquatic ecosystem part 1 6 1. Littoral Zone: It is the shallow water region in which the light penetrates till the bottom. Due to the availability of plenty of sunlight, this zone is marked typically by the presence of rooted plants. This may not be true in „managed‟ or „man-made ponds or lakes‟. 2. Limnetic Zone: It is the open water zone to the depth of effective light penetration called the compensation level. The compensation level is that depth at which the rate of photosynthesis becomes equal to the rate of respiration. In general, this level will be at the depth at which light intensity is about 1 per cent of full sunlight intensity. The community in this zone is composed only of planktons and the nektons and sometimes neustons. This zone is absent in small, shallow ponds. The total illuminated stratum including the littoral and the limnetic zone is termed as Eutrophic zone. 3. Profundal Zone: This is the deep bottom zone which is beyond the depth of effective light penetration. This zone is often absent in ponds. Characteristics of Lentic Ecosystem The physico-chemical environment in a lentic aquatic system is remarkable due to absence of flow of water. Some important features of a lentic water body of water are summarized below: (a) Stability in the physicochemical characteristics of water quality: Most of the water in the lentic system derives from surface runoffs, rains or from underground water sources. These sources undergo very little change in their compositions over the years. Therefore, the quality of water in lentic systems remains virtually unchanged for long duration of time. (b) Impact of Seasonal change: The productivity of a lentic body is influenced by its positive correlation with the seasonal changes in physicochemical characteristics of water. The seasonal fluctuation of the water quality greatly affects the composition of the living community. During the periods of bright sunshine, a rich growth of phytoplankton is observed which is also associated with a remarkable decline in the concentration of many plant nutrients. 5 Department of zoology,B.N College,P.U Page 6 Aquatic ecosystem part 1 7 (c) Impact of area Vs volume of water on assessment of productivity: In the assessment of the productivity of a lentic water body, the total surface area of the water body is more important than volume of water or the depth of the water body. The total stretch of the littoral and limnetic zones determines the productivity. Even the profundal zones are nutrient rich in some lentic bodies, productivity is hardly affected due to lack of enough sunshine. (d) Lentic systems are closed systems: Since there is no outlet for the water body, substances with persistent nature, products of decomposition and mineralization of the organic matter as well as the degraded or semi degraded products of pollutants that are discharged in these aquatic bodies, persist in the system. This has a significant impact on the biotic communities. (e) Thermal and nutritional Stratification: The phenomenon of stratification, also known as vertical donation, is one of the most important features of a lentic water body. This is observed in lakes and ponds which usually have deeper static waters having a depth of more than 6 to 8 meters. Stratification results in different layers of a lentic water having different temperature, oxygen content and the nutrient status. Stratification develops mainly due to following reasons: i. Seasonal change: The typical seasonal cycle results in the thermal stratification. During summers the top waters become warmer than the bottom waters, as a result, only the warm top layer circulates, and it does not mix with the more viscous cold water, creating a zone with a steep temperature gradient in between called the thermocline. The details of the same will be discussed later. ii. Light: Sunlight illuminates only the upper layers i.e., the limnetic zone, where active photosynthesis and growth takes place. This results in generation of plenty of oxygen and also rapid consumption of nutrients. On the other hand, the benthic and the profundal and benthic zones are dark and deprived of primary productivity. Some amount of atmospheric oxygen also dissolves into the upper surface water, making the upper zone rich in oxygen and poor in nutrition while the bottom zone rich in nutrition but poor in dissolved oxygen content. 6 Department of zoology,B.N College,P.U Page 7 Aquatic ecosystem part 1 8 iii. Decomposition and mineralization of organic matter: Nutrient is abundant near the bottom strata from where they diffuse towards the upper strata. Decomposition of dead organisms, mineralization of organic matter and regeneration of nutrients occur actively in the profundal and benthic zones. On the other hand, the consumption of the same is comparatively less than the surface. These zone are oxygen deficient, therefore products of anaerobic microbial activities also accumulate in these zones. iv. Atmospheric temperature and air circulation: 95% of heat is received or lost by the aquatic body through its upper surface which is in contact with atmospheric air. Therefore, the temperature of the surface layer is directly influenced by atmospheric temperatures and also the presence or absence of air circulation. Since the deeper layers are insulated from all sides, they do not undergo any rapid change in temperature. This also affects the density of water. v. Density gradient of water: When lighter or less dense layer of water is placed on heavier or denser waters, thermal stratification develops. Water has its maximum density at 4°C. Above 4°C warmer, it is lighter like every liquid but at temperature below 4°C, the situation is exactly opposite to other liquids since warmer waters are heavier than cooler ones. The conditions under which stratification develops in a static water body are: 1. When the water body having temperatures below 4°C is subjected to cooling. 2. When the water body having temperatures above 4°C is subjected to heating. In both the cases, the surface layer becomes lighter than the layer of water underneath. The lighter water tends to stay at the top and prevents free circulation and the mixing of different layers of water. The imaginary line that demarcates the two zones having different temperatures is termed as the thermocline. The zone above thermocline is known as epilimnion and the zone below this line are known as hypolimnion. 7 Department of zoology,B.N College,P.U Page 8 Aquatic ecosystem part 1 9 Fig.3: Stratification in lentic system Complete mixing of water occurs: 1.
Load more

Recommended publications
  • 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.
    [Show full text]
  • 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).
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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 ...........................................................................................................
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]