Methods in Stream Ecology -

Methods in Stream Ecology (eBook)

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2011 | 2. Auflage
896 Seiten
Elsevier Science (Verlag)
978-0-08-054743-5 (ISBN)
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Methods in Stream Ecology provies a complete series of field and laboratory protocols in stream ecology that are ideal for teaching or conducting research. This new edition is updated to reflect recent advances in the technology associated with ecological assessment of streams, including remote sensing. In addition, the relationship between stream flow and alluviation has been added, and a new chapter on riparian zones is also included. With a student-friendly price, this Second Edition is key for all students and researchers in stream and freshwater ecology, freshwater biology, marine ecology, and river ecology. This text is also supportive as a supplementary text for courses in watershed ecology/science, hydrology, fluvial geomorphology, and landscape ecology.
* Exercises in each chapter
* Detailed instructions, illustrations, formulae, and data sheets for in-field research for students
* Taxanomic keys to common stream invertebrates and algae
* Website with tables
* Link from Chapter 22: FISH COMMUNITY COMPOSITION to an interactive program for assessing and modeling fish numbers
Methods in Stream Ecology, Second Edition, provides a complete series of field and laboratory protocols in stream ecology that are ideal for teaching or conducting research. This updated edition reflects recent advances in the technology associated with ecological assessment of streams, including remote sensing. In addition, the relationship between stream flow and alluviation has been added, and a new chapter on riparian zones is also included. The book features exercises in each chapter; detailed instructions, illustrations, formulae, and data sheets for in-field research for students; and taxanomic keys to common stream invertebrates and algae. With a student-friendly price, this book is key for all students and researchers in stream and freshwater ecology, freshwater biology, marine ecology, and river ecology. This text is also supportive as a supplementary text for courses in watershed ecology/science, hydrology, fluvial geomorphology, and landscape ecology. Exercises in each chapter Detailed instructions, illustrations, formulae, and data sheets for in-field research for students Taxanomic keys to common stream invertebrates and algae Link from Chapter 22: FISH COMMUNITY COMPOSITION to an interactive program for assessing and modeling fish numbers

Front Cover 1
Title Page 4
Copyright Page 5
Table of Contents 6
CONTRIBUTORS 10
PREFACE 14
SECTION A: PHYSICAL PROCESSES 18
CHAPTER 1: LANDSCAPES AND RIVERSCAPES 20
CHAPTER 2: VALLEY SEGMENTS, STREAM REACHES, AND CHANNEL UNITS 40
CHAPTER 3: DISCHARGE MEASUREMENTS AND STREAMFLOW ANALYSIS 68
CHAPTER 4: DYNAMICS OF FLOW 96
CHAPTER 5: TEMPERATURE, LIGHT, AND OXYGEN 120
CHAPTER 6: HYPORHEIC ZONES 136
SECTION B: MATERIAL TRANSPORT, UPTAKE, AND STORAGE 160
CHAPTER 7: FLUVIAL GEOMORPHIC PROCESSES 162
CHAPTER 8: SOLUTE DYNAMICS 186
CHAPTER 9: PHOSPHORUS LIMITATION, UPTAKE, AND TURNOVER IN BENTHIC STREAM ALGAE 204
CHAPTER 10: NITROGEN LIMITATION AND UPTAKE 230
CHAPTER 11: DISSOLVED ORGANIC MATTER 256
CHAPTER 12: TRANSPORT AND STORAGE OF FPOM 266
CHAPTER 13: CPOM TRANSPORT, RETENTION, AND MEASUREMENT 290
SECTION C: STREAM BIOTA 308
CHAPTER 14: HETEROTROPHIC BACTERIA 310
CHAPTER 15: FUNGI: BIOMASS, PRODUCTION, AND SPORULATION OF AQUATIC HYPHOMYCETES 328
CHAPTER 16: BENTHIC STREAM ALGAE: DISTRIBUTION AND STRUCTURE 344
CHAPTER 17: BIOMASS AND PIGMENTS OF BENTHIC ALGAE 374
CHAPTER 18: MACROPHYTES AND BRYOPHYTES 398
CHAPTER 19: MEIOFAUNA 432
CHAPTER 20: MACROINVERTEBRATES 452
CHAPTER 21: MACROINVERTEBRATE DISPERSAL 482
CHAPTER 22: ROLE OF FISH ASSEMBLAGES IN STREAM COMMUNITIES 506
SECTION D: COMMUNITY INTERACTIONS 552
CHAPTER 23: PRIMARY PRODUCER-CONSUMER INTERACTIONS 554
CHAPTER 24: PREDATOR-PREY INTERACTIONS 578
CHAPTER 25: TROPHIC RELATIONSHIPS OF MACROINVERTEBRATES 602
CHAPTER 26: TROPHIC RELATIONS OF STREAM FISHES 628
CHAPTER 27: STREAM FOOD WEBS 654
SECTION E: ECOSYSTEM PROCESSES 678
CHAPTER 28: PRIMARY PRODUCTIVITY AND COMMUNITY RESPIRATION 680
CHAPTER 29: SECONDARY PRODUCTION OF MACROINVERTEBRATES 708
CHAPTER 30: DECOMPOSITION OF LEAF MATERIAL 728
CHAPTER 31: RIPARIAN PROCESSES AND INTERACTIONS 738
CHAPTER 32: EFFECTS OF NUTRIENT ENRICHMENT ON PERIPHYTON 760
CHAPTER 33: SURFACE-SUBSURFACE INTERACTIONS IN STREAMS 778
SECTION F: ECOSYSTEM QUALITY 800
CHAPTER 34: ECOLOGICAL ASSESSMENTS WITH BENTHIC ALGAE 802
CHAPTER 35: MACROINVERTEBRATES AS BIOTIC INDICATORS OF ENVIRONMENTAL QUALITY 822
CHAPTER 36: ESTABLISHING CAUSE-EFFECT RELATIONSHIPS IN MULTI-STRESSOR ENVIRONMENTS 852
INDEX 872

CHAPTER 1 Landscapes and Riverscapes

Jack A. Stanford

Flathead Lake Biological Station, University of Montana

I. INTRODUCTION


Streams, rivers, and groundwater flow pathways are the plumbing of the continents. Water coalesces and flows downhill in surface channels and subsurface pathways in response to precipitation patterns and the dynamic form of river basins (catchments). Uplift of mountain ranges, caused by continental drift and volcanism, is continually countered by erosion and deposition (sedimentation) mediated by the forces of wind and water. Catchment landscapes are formed by the long geologic and biological history of the region as well as recent events such as floods, fires, and human-caused environmental disturbances (e.g., deforestation, dams, pollution, exotic species).

The term landscape is used extensively, referring generally to the collective attributes of local geography. An expansive view of a stream or river and its catchment, including natural and cultural attributes and interactions, is the “riverscape.” For a stream ecologist, a riverscape view of a catchment (river) basin encompasses the entire stream network, including interconnection with groundwater flow pathways, embedded in its terrestrial setting and flowing from the highest elevation in the catchment to the ocean, with considerable animal and human modifications of flow paths likely along the way (Fausch et al. 2002). For example, the earth’s largest catchment, the Amazon River basin, occupies over half of the South American continent. Headwaters flow from small catchments containing glaciers and snowfields over 4300 m above sea level on the spine of the Andes Mountains to feed the major tributaries. The tributary rivers converge to form the mainstem Amazon, which flows from the base of the Andes across a virtually flat plate covered by equatorial tropical forest to the Atlantic Ocean. The altitude change is less than 200 m over the nearly 3000 km length of the mainstem river from the base of the Andes to the ocean. Because of the enormous transport power of the massive water volume of the Amazon River, some channels are >100 m deep. In other places along the river corridor the channel is >5km wide, relatively shallow, and filled by sediment deposition (alluviation). Flood waters spread out over huge and heavily vegetated floodplains that support a myriad of fishes and other animals (Day and Davies 1986).

The riverscape of the Amazon River, as among all rivers, was molded over time with the river cutting steep canyons through mountain ranges while building (alluviating) expansive floodplains where the slope of the river valley decreased. Rivers drain the continents; transport sediments, nutrients, and other materials from the highlands to the lowlands and oceans; and constantly modify the biophysical character of their catchment basins. These processes occur in direct relation to a particular catchment’s global position, climate, orography, and biotic character, coupled with spatial variations in bedrock and other geomorphic features of the riverscape.

Within a catchment basin, stream channels usually grow in size and complexity in a downstream direction (Figure 1.1). The smallest or first-order stream channels in the network often begin as outflows from snowfields or springs below porous substrata forming ridges dividing one catchment from another. Two first-order streams coalesce to form a second-order channel and so on to create the network (Strahler 1963). A very large river, like the Amazon, often has several large tributaries, and each of those river tributaries may be fed by several to many smaller streams (Figure 1.1). Thus, each large catchment basin has many subcatchments.

FIGURE 1.1 Idealized view of (A) the stream network showing the coalescence of headwater streams, which begin at snowfields or groundwater discharge portals, and the longitudinal distribution of floodplains and canyons (“beads on a string”) within a headwater to ocean river ecosystem and (B) the 3D structure of alluvial floodplains (beads), emphasizing dynamic longitudinal, lateral and vertical dimensions, and recruitment of wood debris. The groups of arrows in (A) indicate the expected strength of ground- and surfacewater exchange (vertical), channel and floodplain (lateral) interactions, and upstream to downstream or longitudinal (horizontal) connectivity in the context of (B). The floodplain landscape, contains a suite of structures (see Table 1.1) produced by the legacy of cut and All alluviation as influenced by position within the natural-cultural setting of the catchment. The parafluvial zone is the area of the bankfull channel that is to some extent annually scoured by flooding. The hyporheic zone is defined by penetration of river water into the alluvium and may mix with phreatic ground water from hillslope or other aquifers not directly recharged by the river. Alluvial aquifers usually have complex bed sediments with interstitial zones of preferential groundwater flow sometimes called paleochannels. Assemblages of biota may be segregated in all three spatial dimensions including riparos (streamside or riparian), benthos (channel bottom), hyporheos (interstitial within the stream bed-sediments) and phreatos (deep groundwater) in addition to fish and other organisms in the water column of the river

(from Stanford et al. 2005b).

Erosive power generally increases with stream size. Boulders, gravel, sand, and silt are transported from one reach of the stream network to the next in relation to discharge and valley geomorphometry (e.g., slope and relative resistance of substrata to erosion). Expansive deposition zones (floodplains) form between steep canyons, where downcutting predominates.

All rivers feature this basic theme of alternating cut and fill alluviation. Floodplains occur like beads on a string between gradient breaks or transitions in the altitudinal profile of the flow pathway (Leopold et al. 1964). Rivers of very old geologic age have exhausted much of their erosive power; mountains are rounded, valleys are broadly U-shaped, and river channels are single threads in the valley bottom with ancient, abandoned floodplains called terraces rising on either side. Whereas, in geologically young, recently uplifted catchments, stream power and associated erosive influence on valley form is great; mountains are steep-sided, valleys narrowly V-shaped, and the river spills out of many interconnected channels on alluvial floodplains in aggraded areas during flooding. Of course, no two rivers are exactly alike, but a general longitudinal (upstream to downstream) pattern of cut and fill alluviation usually exists (Figure 1.1A). Many small and usually erosive streams coalesce in the headwaters to form a main channel that grows in size and power with each primary tributary. The main channel alternately cuts through reaches constrained by bedrock canyons and spills water and sediments onto aggraded floodplain reaches where the river may be quite erosive (cutting) in one place and time and building sedimentary structures (filling) in another; thus, creating a suite of dynamic habitats for biota.

The riverscape at any point within the stream network is four-dimensional (Figure 1.1B). The river continuum or corridor from headwaters to ocean is the longitudinal (upstream to downstream) dimension. The second dimension is the transitional area from the river channel laterally into the terrestrial environment of the valley uplands (aquatic to terrestrial dimension). Except where rivers flow over impervious bedrock, some amount of porous alluvium is present within the channel owing to erosion at points upstream. Hence, water from the river may penetrate deeply into the substrata of the river bottom. Moreover, substrata of floodplains are composed of alluvial gravels and/or sands and silts, which allow lateral flow of river water. Hence, interstitial flow pathways constitute a vertical dimension in the river channel and on the floodplains. All of the physical dimensions change in size over time (the fourth dimension), as floods and droughts alter hydrology, sediment transport, and distribution of vegetation and other biota (Ward 1989, Stanford et al. 2005b).

Plants and animals are distributed in relation to biophysical gradients expressed by the four-dimensional nature of the stream network within catchment basins. For example, certain species of aquatic insects reside only in the cold, rocky environs of cascading headwater streams in the high mountains (rhithron environments), whereas other species are found only in the much warmer waters of the often sandy, turbid, and meandering reaches of the lowlands near the ocean (potamon environments) (Ward 1989). Thus, riverine biota have distinct preferences for specific environmental conditions that are optimal only at certain locations within longitudinal (upstream-downstream), lateral (aquatic-terrestrial), vertical (surface-ground water), and temporal (certain time) gradients that characterize lotic ecosystems (Figure 1.1). Andrewartha and Birch (1954) observed that the essence of ecology is understanding the distribution and abundance of biota. Because environmental conditions at any point in a stream are continuously influenced by conditions at points upstream, biophysical controls on distribution and abundance of riverine biota must be examined in the context...

Erscheint lt. Verlag 27.4.2011
Sprache englisch
Themenwelt Naturwissenschaften Biologie Ökologie / Naturschutz
Naturwissenschaften Geowissenschaften
Technik
ISBN-10 0-08-054743-5 / 0080547435
ISBN-13 978-0-08-054743-5 / 9780080547435
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