Thư viện tri thức trực tuyến
Kho tài liệu với 50,000+ tài liệu học thuật
© 2023 Siêu thị PDF - Kho tài liệu học thuật hàng đầu Việt Nam

Stream Ecology Structure and Function of Running Waters
Nội dung xem thử
Mô tả chi tiết
Stream
Ecology
Stream
Ecology
Structure and
function of
running waters
Second Edition
J. David Allan
School of Natural Resources & Environment,
The University of Michigan,
Ann Arbor, MI, U.S.A.
MarI¤aM. Castillo
Departamento de Estudios Ambientales,
Universidad Simo¤n BolI¤var,
Caracas,Venezuela
A C.I.P. Catalogue record for this book is available from the Library of Congress.
ISBN 978-1-4020-5583-6 (e-book)
Published by Springer,
P.O. Box 17, 3300 AA Dordrecht, The Netherlands.
www.springer.com
Printed on acid-free paper
The cover photograph shows the Autana River, a blackwater river in the Orinoco basin
of Venezuela. In the background is the Autana Mountain, sacred to the Piaroa people,
whose culture and livelihood are closely connected to the river. Photograph by M M Castillo
All Rights Reserved
2007 Springer
No part of this work may be reproduced, stored in a retrieval system, or transmitted
in any form or by any means, electronic, mechanical, photocopying, microfilming,
recording or otherwise, without written permission from the Publisher, with the
exception of any material supplied specifically for the purpose of being entered
and executed on a computer system, for exclusive use by the purchaser of the work.
ISBN 978-1-4020-5582-9 (PB)
Dedicated to our families, with gratitude for their support
Contents
Preface to the Second Edition xiii
1 An introduction to fluvial ecosystems 1
Fluvial Ecosystem Diversity 1
The fluvial hierarchy 2
Longitudinal patterns 5
The stream and its valley 5
The Fluvial Ecosystem 6
Energy sources 6
Food webs and biological communities 7
The river ecosystem 8
The Status of Rivers Today 9
2 Streamflow 13
The Water Cycle 14
Global water cycle 16
Water balance of a catchment 16
Surface versus groundwater pathways 18
Streamflow 19
The hydrograph 21
Flow Variation 22
The likelihood of extreme events 23
Effect of land use on streamflow 24
The flow regime 25
Environmental flows 30
Summary 31
3 Fluvial geomorphology 33
The Drainage Network 34
The Stream Channel 35
Hydraulic geometry 36
Sinuosity 38
Pool–riffle features 39
The floodplain 41
Sediments and their Transport 41
vii
Bed material 41
Bank and bed erosion 43
Sediment load 44
Factors influencing sediment concentrations and loads 46
Fluvial Processes along the River Continuum 49
Fluvial processes and channel morphologies 50
Channel dynamics over long timeframes 53
Channel classifications and their uses 53
Riverine landscape diversity 55
Summary 55
4 Streamwater chemistry 57
Dissolved Gases 57
Major Dissolved Constituents of River Water 59
Variability in ionic concentrations 62
The dissolved load 64
Chemical classification of river water 65
The Bicarbonate Buffer System 65
Influence of Chemical Factors on the Biota 68
Variation in ionic concentration 68
Salinization 69
Effects of acidity on stream ecosystems 70
Summary 74
5 The abiotic environment 75
The Flow Environment 76
Channel and near-bed flow environments 79
Hydraulic variables 79
Quantification of flow conditions 81
Influence of flow on the biota 82
Substrate 88
Inorganic substrates 89
Organic substrates 90
The influence of substrate on stream assemblages 92
Temperature 94
Influence of thermal regime on the biota 98
Summary 102
6 Primary producers 105
Benthic Algae 105
Benthic algal distribution and abundance 107
Light 109
Nutrients 112
Current 115
Substrate 120
Contents
viii
Temperature 120
Grazers 120
Temporal and spatial variation in benthic algae 121
Primary production by benthic algae 122
Fate of benthic primary production 124
Macrophytes 125
Limiting factors for macrophytes 126
Macrophyte production and its fate 128
Phytoplankton 129
Limiting factors for phytoplankton 130
Primary production by river phytoplankton 132
Summary 133
7 Detrital energy sources 135
The Decomposition of Coarse Particulate Organic Matter 135
Stages in the breakdown and decay of CPOM 139
The influence of detritivores on litter decomposition 144
Other CPOM 146
Fine Particulate Organic Matter 147
FPOM originating from leaf decomposition 148
Other sources of FPOM 149
Dissolved Organic Matter 150
Uptake of DOC 152
Biofilms 154
Bacterioplankton 158
Summary 160
8 Trophic relationships 163
Microbial Food Webs 164
Invertebrate Feeding Roles 167
Consumers of CPOM 168
Consumers of FPOM 173
Herbivory 177
Predaceous invertebrates 180
Vertebrates in Lotic Food Webs 183
Fishes 184
Other vertebrates 188
Secondary Production 190
Summary 195
9 Species interactions 197
Herbivory 197
Grazer responses to food supply 197
Grazer effects on periphyton 199
Structural responses 200
Contents
ix
Functional responses 202
Disturbance and herbivory 203
Top-down and bottom-up effects on periphyton 204
Predation 205
The predator–prey interaction 206
Vertebrate predators 206
Invertebrate predators 207
Prey defenses 209
Effects of predation on prey populations 210
Nonconsumptive effects of predation 211
Experimental scale 213
Trophic cascades 214
Competition 217
Resource partitioning 217
Algae 217
Invertebrates 218
Fishes 219
Experimental studies of competition 222
Summary 225
10 Lotic communities 229
Regional Patterns in Species Diversity 230
Species–area relationships 230
Latitudinal gradients 231
History 231
Local Diversity 233
Community Structure 238
Consistency in assemblage composition 239
The habitat template and species traits 240
Disturbance 242
Species-level effects of disturbance 244
System-wide effects 245
Food Webs 246
Resource subsidies 249
Landscape position 250
Community Composition and Ecosystem Function 251
Summary 253
11 Nutrient dynamics 255
Sources and Cycling of Nitrogen and Phosphorus 256
Nitrogen sources and quantities 257
Nitrogen cycling 259
Phosphorus sources and quantities 261
Phosphorus cycling 264
Transport and Spiraling 265
Contents
x
Physical transport 265
Nutrient spiraling 267
Methodological issues 268
Factors Influencing Nutrient Dynamics 269
Abiotic controls of nutrient dynamics 269
Hydrologic processes 270
Biotic controls of nutrient cycling 272
Assimilatory uptake 273
Dissimilatory transformations 275
Role of consumers 277
Nutrient Budgets 279
Nitrogen 280
Phosphorus 283
Summary 284
12 Stream ecosystem metabolism 287
Autochthonous Production 289
Algae 289
Macrophytes 290
Allochthonous Inputs 291
Coarse particulate organic matter 291
Fine particulate organic matter 292
Dissolved organic matter 294
Processes 297
Benthic respiration 297
Coarse particulate organic matter dynamics 298
Fine particulate organic matter dynamics 299
Benthic organic matter retention 300
Dissolved organic matter dynamics 302
Stream Ecosystem Metabolism 303
Organic matter budgets 303
The P/R ratio 308
Stream ecosystem efficiency 313
The fate of organic matter 314
Summary 315
13 Human impacts 317
Freshwater Biodiversity 318
Species imperilment 319
Imperilment of major groups 320
Threats to Rivers 321
Habitat alteration 321
Altered hydrology 323
Channelization 327
Land use 330
Contents
xi
Nonindigenous species 333
Causes of species invasions 333
Invasion success 334
Impacts of invasive species 337
Pollution 339
Point source contaminants 339
Runoff from the land 339
Atmospheric deposition 341
Overexploitation 342
Climate change 345
River Management 347
Bioassessment 348
Restoration and recovery of lotic ecosystems 350
Protected areas 354
Summary 356
14 The foundations of stream ecology 359
The Spatial Framework 360
Community Assembly is Determined by the Species Pool,
Habitat Sorting, and Species Interactions 362
Streams are Transporting Systems 364
Primary Production and Allochthonous Detritus are Basal Resources
in Lotic Ecosystems 366
Rivers are the Product of their Landscapes 369
References 373
Subject Index 429
Contents
xii
Preface to
the Second
Edition
The diversity of running water environments is
enormous. When one considers torrential mountain brooks, large rivers of lowlands, and great
rivers whose basins occupy subcontinents, it is
apparent how location-specific environmental
factors contribute to the sense of uniqueness
and diversity of running waters. At the same
time, however, our improved understanding of
ecological, biogeochemical, hydrological, and
geomorphological processes provides insight
into the structural and functional characteristics
of river systems that brings a unifying framework
to this field of study. Inputs and transformations
of energy and materials are important in all river
systems, regional species richness and local species interactions influence the structure of all
riverine communities, and the interaction of physical and biological forces is important to virtually every question that has been asked. It seems
that the processes acting in running waters are
general, but the settings are often unique.
We believe that it helps the reader, when some
pattern or result is described, to have some
image of what kind of stream or river is under
investigation, and also where it is located.
Stream ecology, like all ecology, depends greatly
on context: place, environmental conditions,
season, and species. This text includes frequent
use of descriptors like ‘‘small woodland stream,’’
‘‘open pastureland stream,’’ or ‘‘large lowland
river,’’ and we believe that readers will find
these useful clues to the patterns and processes
that are reported. For most studies within the
United States we have included further regional
description, but have done so less frequently for
studies from elsewhere around the globe. We
apologize to our international readers for this
pragmatic choice, and we have made every
effort to include examples and literature from
outside of North America.
Some locations have established themselves as
leading centers of study due to the work of many
researchers carried out over decades. The Hubbard Brook Experimental Forest in New Hampshire, Coweeta Hydrologic Laboratory in North
Carolina, and some individual streams including
Walker Branch in Tennessee, Sycamore Creek in
Arizona, Rı´o las Marı´as in Venezuela, and the
Taeri and Whatawhata in New Zealand are locations that appear frequently in the pages that
follow. Knowing what these places are like, and
how they may or may not be typical, in our view
justifies the frequent use of place names and
brief descriptions. The names of organisms also
appear frequently and may at first overwhelm
the reader. It may be easiest to pay them little
attention until they gradually become familiar.
Ultimately, it is difficult to really comprehend
the outcome of a study without some appreciation for the organisms that were present.
xiii
As is true for every area of ecology at present,
the study of streams and rivers cannot be
addressed exclusive of the role of human activities, nor can we ignore the urgency of the need
for conservation. This is a two-way street. Ecologists who study streams without considering
how past or present human modifications of
the stream or its valley might have contributed
to their observations do so at the risk of incomplete understanding. Conservation efforts that
lack an adequate scientific basis are less likely
to succeed. One trend that seems safe to forecast
in stream ecology is toward a greater emphasis
on understanding human impacts. Fortunately,
signs of this trend are already apparent.
We have organized the flow of topics in a way
that is most logical to us, but no doubt some
readers will prefer to cover topics in whatever
order they find most useful. For this reason, we
have striven to explain enough in each chapter so
that it is comprehensible on its own. This leads to
a certain amount of intentional repetition, which
we hope will provide clarification or a reminder
that will benefit the reader’s understanding.
We are extremely grateful to the many colleagues who shared ideas, provided references, and
reviewed chapters in draft form. Space does not
permit us to thank everyone who answered a
query with a helpful explanation and suggestions for source material; however, we do wish
to acknowledge the persons who carefully read
and improved our chapters. Any remaining shortcomings or errors are the authors’ responsibility,
but hopefully these are few, thanks to the efforts
of Robin Abell, Brian Allan, Fred Benfield, Barb
Downes, David Dudgeon, Kurt Fausch, Stuart
Findlay, Alex Flecker, Art Gold, Sujay Kaushal,
Matt Kondolf, Angus McIntosh, Peter McIntyre,
Rich Merritt, Judy Meyer, Pat Mulholland, Bobbi
Peckarsky, LeRoy Poff, Brian Roberts, Doug
Shields, Al Steinman, Jan Stevenson, Jen Tank,
Paul Webb, Jack Webster, Kevin Wehrly, and Kirk
Winemiller. All were generous with their time
and knowledge, and we are indebted to them.
We also wish to thank those who provided
helpful reviews of chapters in the first edition of
this book, including Fred Benfield, Art Benke, Art
Brown, Scott Cooper, Stuart Findlay, Alex Flecker,
Nancy Grimm, David Hart, Chuck Hawkins, Bob
Hughes, Steve Kohler, Gary Lamberti, Rex Lowe,
Rich Merritt, Diane McKnight, Judy Meyer, Bobbi
Peckarsky, Pete Ode, Walt Osterkamp, ML
Ostrofsky, Margaret Palmer, LeRoy Poff, Karen
Prestergaard, Ike Schlosser, Len Smock, Al Steinman, Scott Wissinger, and Jack Webster.
Others provided invaluable assistance with
important aspects of manuscript production.
Jennifer Allan, Mary Hejna and Jamie Steffes did
extensive proofreading and arranged all the figure permissions. Haymara Alvarez, Susana Martinez, and Dana Infante assisted with production
of figures, and Jesus Montoya did a superb job of
taking figures made in many different styles and
redrafting them to a common style and high
quality. Funding for MMC release time and travel
to Michigan was provided by Direccio´n de
Desarrollo Profesoral of Universidad Simo´n
Bolı´var, and the Horace H. Rackham School of
Graduate Studies of the University of Michigan.
We also wish to thank our editors at Springer,
Suzanne Mekking and Martine van Bezooijen,
and our prior editor Anna Besse-Lototskaya, for
their support, encouragement, and patience. It
has been a pleasure to work with them all.
Lastly, our deepest thanks go to our families
for their love and support, and especially for
their help and understanding during the time
this edition was completed. David wishes to
express his appreciation to Susan for the unflagging encouragement that has been a constant
throughout our lives together. Marı´a Mercedes
wishes to thank her parents for their unconditional support in the development of her career.
It has been an enjoyable experience for both of
us, and we hope that this edition will serve as a
useful guide for the next generation of stream
ecologists.
xiv
Preface to the Second Edition
Chapter one
An
introduction
to fluvial
ecosystems
This chapter provides an overview of the diversity of rivers and streams, including some of the
causes of this diversity, and some of the consequences. The intent is to provide a road map for
the individual chapters that follow, rather than
define terms and explain principles in detail. By
sketching out the broadest patterns of fluvial
ecosystems and providing at least a glimpse of
the underlying processes, we hope this introduction will serve as a framework for the entire
book. Some of these generalizations may later
be qualified to recognize their exceptions and
limitations. Yet, it is through this effort to elucidate the working principles of fluvial ecosystems
and how environmental context governs their
expression that river ecologists hope to comprehend the enormous variety of streams and rivers,
and provide the needed guidance to ensure their
sustained well-being.
1.1 Fluvial Ecosystem Diversity
Streams and rivers occur in almost bewildering
variety. There is no real distinction between
streams and rivers, except that the former are
smaller. Some use the term ‘‘great river’’ to distinguish rivers such as the Mekong, the Amazon,
and the Mississippi from rivers of more usual
size. Partly because the vast majority of river
length is in the smaller headwater streams, and
partly because these smaller systems have
received considerably more study, many and
perhaps most researchers consider themselves
‘‘stream ecologists.’’ Attempting to understand
how the principles of fluvial systems are manifested across scale is one of the primary themes
of this book.
Fluvial ecosystems vary in many additional
features. Some have the color of tea due to
high concentrations of dissolved plant matter,
while others have fewer chemical constituents
and so remain clear; these are known as blackwater and clearwater rivers, respectively. Rivers
can tumble and cascade down steep slopes over
large boulders, meander through gentle valleys,
or flow majestically across broad flats as they
approach the sea. Food webs in forested streams
derive much of their food base from autumn leaf
fall, whereas streams that are open, shallow, and
stony typically develop a rich film of algae and
microbes. Rivers that still have an intact floodplain exchange organic matter and nutrients
1
with the adjacent land, and all fluvial ecosystems
exhibit high connectivity laterally, longitudinally,
and vertically (Figure 1.1).
River science attempts to catalog this diversity, reveal the underlying processes that are responsible for the variety of patterns that we
observe, and understand how those processes
interact with different environmental settings
and across scale from the smallest headwater
streams to great rivers. Numerous classification
systems for rivers have been developed to better
comprehend natural patterns of variation, as
well as guide management activities including
restoration and assessments of river health. At
the time of this writing it is not possible to
describe one, overarching river classification. Indeed, this may not be an attainable goal: the
variation of fluvial ecosystems is continuous,
the variables often are too independent to form
recognizable clusters, and different classifications have different purposes (Kondolf et al.
2003a, b). With these limitations in mind, however, a number of broad generalizations can be
made that help to organize the variety and variability of fluvial ecosystems.
1.1.1 Thefluvialhierarchy
Streams and the landscape units they drain form
nested hierarchies. The smallest permanently
flowing stream is referred to as first order. The
union of two first-order streams results in a second-order stream, the union of two streams of
second order results in a third-order stream, and
so on (Figure 1.2). Stream order is an approximate measure of stream size, conceptually attractive, and correlates with a number of other, more
precise size measures including the area drained,
volume of water discharged, and channel dimensions. As a simple classification system it provides an informative tally of the numbers of
small streams and large rivers (Table 1.1). The
great majority of the total length of river systems
is comprised of lower-order or headwater systems, each of short length and small drainage
area. Rivers that we might consider to be of
medium size, fourth through sixth order, are
FIGURE 1.1 The fluvial ecosystem with its three major
axes: upstream/downstream, channel/margins, and surficial/underground environments. (Reproduced from
Pie´gay and Schumm 2003.)
FIGURE 1.2 A drainage network illustrating stream channel order within a fourth-order catchment. The terminus
may be a lake or the junction with a larger river. Intermittent streams occur upstream of the first-order tributaries, and often extend nearly to the catchment divide.
An introduction to fluvial ecosystems
2