GLORIA

GEOMAR Library Ocean Research Information Access

feed icon rss

Your email was sent successfully. Check your inbox.

An error occurred while sending the email. Please try again.

Proceed reservation?

Export
  • 1
    Online Resource
    Online Resource
    San Diego :Elsevier Science & Technology,
    Keywords: Limnology -- Textbooks. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (591 pages)
    Edition: 1st ed.
    ISBN: 9780080477909
    Series Statement: Aquatic Ecology Series
    DDC: 577.6
    Language: English
    Note: Front Cover -- Freshwater Ecology: Concepts and Environmental Applications -- Copyright Page -- Contents -- Preface -- Acknowledgments -- Chapter 1. Why Study Continental Aquatic Systems? -- Human Utilization of Water: Pressures on a Key Resource -- What Is the Value of Water Quality? -- Summary -- Questions for Thought -- Chapter 2. Properties of Water -- Chemical and Physical Properties -- Relationships among Water Viscosity, Inertia, and Physical Parameters -- Movement of Water -- Forces That Move Water -- Summary -- Questions for Thought -- Chapter 3. Movement of Light, Heat, and Chemicals in Water -- Diffusion in Water -- Light and Heating of Water -- Summary -- Questions for Thought -- Chapter 4. Hydrology and Physiography of Groundwater and Wetland Habitats -- Habitats and the Hydrologic Cycle -- Movement Through Soil and Groundwater -- Wetlands -- Summary -- Questions for Thought -- Chapter 5. Physiography of Flowing Water -- Characterization of Streams -- Stream Flow and Geology -- Movements of Materials by Rivers and Streams -- Summary -- Questions for Thought -- Chapter 6. Physiography of Lakes and Reservoirs -- Formation: Geological Processes -- Lake Habitats and Morphometry -- Stratification -- Water Movement and Currents in Lakes -- Summary -- Questions for Thought -- Chapter 7. Types of Aquatic Organisms -- The Species Concept -- Major Taxonomic Groups -- Classification of Organisms by Functional Significance -- Organisms Found in Freshwater Systems -- Summary -- Questions for Thought -- Chapter 8. Microbes and Plants -- Viruses -- Archaea -- Bacteria -- Protoctista -- Fungi -- Plantae -- Summary -- Questions for Thought -- Chapter 9. Animals -- Invertebrates -- Phylum Chordata, Subphylum Vertebrata -- Summary -- Questions for Thought -- Chapter 10. Biodiversity of Freshwaters -- Measures of Diversity. , Temporal and Spatial Factors Influencing Evolution of Freshwater Organisms -- Short-Term Factors Influencing Local Distribution of Species -- Invasions of Nonnative Species -- Extinction -- What Is the Value of Freshwater Species Diversity? -- Summary -- Questions for Thought -- Chapter 11. Aquatic Chemistry Controlling Nutrient Cycling: Redox and O2 -- Chemicals in Freshwaters -- Redox Potential, Potential Energy, and Chemical Transformations -- Oxygen: Forms and Transformations -- Photosynthesis -- Distribution of Dissolved Oxygen in the Environment -- Summary -- Questions for Thought -- Chapter 12. Carbon -- Forms of Carbon -- Transformations of Carbon -- A General Introduction to Nutrient Cycling and the Carbon Cycle -- Summary -- Questions for Thought -- Chapter 13. Nitrogen, Sulfur, Phosphorus, and Other Nutrients -- Nitrogen -- Sulfur -- Phosphorus -- Silicon, Iron, and Other Trace Nutrient Cycles -- Gradients of Redox and Nutrient Cycles and Interactions among the Cycles -- Summary -- Questions for Thought -- Chapter 14. Effects of Toxic Chemicals and Other Pollutants on Aquatic Ecosystems -- Basic Toxicology -- Bioassessment -- Acid Precipitation -- Metals and Other Inorganic Pollutants -- Organic Pollutants -- Suspended Solids -- Thermal Pollution -- Summary -- Questions for Thought -- Chapter 15. Unusual or Extreme Habitats -- Adaptations to Extremes -- Saline Lakes -- Hot Springs -- Cold Habitats -- Temporary Waters and Small Pools -- Ultraoligotrophic Habitats -- Deep Subsurface Habitats -- The Water Surface Layer -- Summary -- Questions for Thought -- Chapter 16. Nutrient Use and Remineralization -- Use of Nutrients -- Nutrient Limitation and Relative Availability -- Relative Availability of Nutrients -- Resource Ratios and Stoichiometry of Primary Producers -- Nutrient Remineralization. , Stoichiometry of Heterotrophs, Their Food, and Nutrient Remineralization -- Summary -- Questions for Thought -- Chapter 17. Trophic State and Eutrophication -- Definition of Trophic State -- Why Is Nutrient Pollution Resulting in Algal Blooms in Lakes Important? -- Natural and Cultural Processes of Eutrophication -- Relationships among Nutrients, Water Clarity, and Phytoplankton: Managing Eutrophication in Lakes -- Mitigating Lake Eutrophication -- Managing Eutrophication in Streams and Wetlands -- Case Studies of Eutrophication -- Eutrophication and Wetlands -- Summary -- Questions for Thought -- Chapter 18. Behavior and Interactions among Microorganisms and Invertebrates -- Behavior of Microorganisms -- Interaction Types in Microbial Communities -- Predation and Parasitism -- Competition -- Mutualism: Facilitation and Syntrophy -- Chemical Mediation of Microbial Interactions -- Summary -- Questions for Thought -- Chapter 19. Predation and Food Webs -- Herbivory -- Detritivory and Omnivory -- Adaptation to Predation Pressure -- Adaptations of Predators -- Nonlethal Effects of Predation -- Trophic Levels, Food Webs, and Food Chains -- The Trophic Cascade -- Theoretical Community Ecology and Aquatic Food Webs -- Summary -- Questions for Thought -- Chapter 20. Nonpredatory Interspecific Interactions among Plants and Animals in Freshwater Communities -- Competition -- Mutualism and Facilitation -- Other Species Interactions -- Complex Community Interactions -- Summary -- Questions for Thought -- Chapter 21. Fish Ecology and Fisheries -- Biogeographical Determinants of Fish Assemblage Diversity -- Physiological Aspects Influencing Growth, Survival, and Reproduction -- Population Dynamics of Fishes -- Regulating Exploitation of Fish Stocks -- Stocking Fish for Fisheries -- Aquaculture -- Summary -- Questions for Thought. , Chapter 22. Freshwater Ecosystems -- General Approaches to Ecosystems -- Groundwater Ecosystems -- Streams -- Lakes and Reservoirs -- Wetlands -- Comparison of Freshwater Ecosystems -- Summary -- Questions for Thought -- Chapter 23. Conclusions -- Appendix: Experimental Design in Aquatic Ecology -- Natural Experiments -- Simulation Modeling -- Manipulative Experiments -- Summary -- Glossary -- References -- Index.
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 2
    Electronic Resource
    Electronic Resource
    s.l. : American Chemical Society
    Journal of the American Chemical Society 80 (1958), S. 253-253 
    ISSN: 1520-5126
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 3
    Electronic Resource
    Electronic Resource
    [s.l.] : Nature Publishing Group
    Nature 177 (1956), S. 379-380 
    ISSN: 1476-4687
    Source: Nature Archives 1869 - 2009
    Topics: Biology , Chemistry and Pharmacology , Medicine , Natural Sciences in General , Physics
    Notes: [Auszug] In the following experiments an adrenocorticotrophic hormone preparation of Schering (1 mgm. = 3 i.tr.) and ascorbic acid B.P. (Roche) were used; for each group of tests, 0 -42 mgm. of the former was dissolved in (a) 3-1 ml. pure Ringer (solution A),(6) 3*1 ml. Ringer containing 8-4 mgm. ...
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 4
    Electronic Resource
    Electronic Resource
    [S.l.] : American Institute of Physics (AIP)
    Journal of Applied Physics 90 (2001), S. 3816-3821 
    ISSN: 1089-7550
    Source: AIP Digital Archive
    Topics: Physics
    Notes: AgInSbTe films have recently attracted considerable interest as advanced materials for phase change recording. For this application the determination of crystallization kinetics is of crucial importance. In this work the temperature dependence of structural and electrical properties of sputtered AgInSbTe films has been determined. Temperature dependent measurements of the electrical resistance have been employed to study the kinetics of structural changes of these films. Upon annealing a major resistivity drop is observed at around 160 °C which can be attributed to a structural change as corroborated by x-ray diffraction. X-ray diffraction shows an amorphous phase for as-deposited films, while crystalline films with hexagonal structure (a=4283 Å, c=16 995 Å) are obtained upon annealing above 160 °C. By applying Kissinger's method, an activation energy of 3.03±0.17 eV is obtained for the crystallization. X-ray reflection measurements reveal a density increase of 5.2%±0.2% and a thickness decrease of 5.5%±0.2% upon crystallization. © 2001 American Institute of Physics.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 5
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Science Ltd
    Freshwater biology 48 (2003), S. 0 
    ISSN: 1365-2427
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: 1. Nutrient diffusing substrata were used to determine the effect of added inorganic nitrogen (N) and phosphorus (P) on the development of epilithic and epixylic biofilms in 10 North American streams. Four treatments of diffusing substrata were used: Control (agar only), N addition (0.5 m NaNO3), P addition (0.5 m KH2PO4), and N + P combined (0.5 m NaNO3 + 0.5 m KH2PO4). Agar surfaces were covered with glass fibre filters (for epilithon) or discs of untreated white oak wood veneer (for epixylon).2. We found that if algae showed significant response to nutrient addition, N limitation (either N alone or N with P) was the most frequent response both on GF/F filters and on wood. Despite the low dissolved nutrient concentrations in our study streams, more than a third of the streams did not show any response to N or P addition. In fact, P was never the sole limiting nutrient for algal biofilms in this study.3. Nutrient addition influenced algal colonisation of inorganic versus organic substrata in different ways. The presence of other biofilm constituents (e.g. fungi or bacteria) may influence whether algal biomass on wood increased in response to nutrient addition. Algae on organic and inorganic substrata responded similarly to nutrient addition in only one stream.4. Fungal biomass on wood was nutrient limited in six of 10 study streams. N limitation of fungal biomass (with or without secondary P limitation) was most frequent, but P limitation did occur in two streams.5. Our results show that biomass responses to nutrient addition by the heterotrophic and autotrophic components of the epixylic biofilm were different, though both experienced the same stream nutrient conditions. For algae and fungi growing on wood, limiting nutrients were rarely similar. Only three of nine streams showed the same biomass response to nutrient addition, including two that showed no significant change in biomass despite added nutrients.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 6
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Science Ltd
    Freshwater biology 49 (2004), S. 0 
    ISSN: 1365-2427
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: 1. The indirect effects of predators on lower trophic levels have been studied without much attention to phenotypically plastic traits of key food web components. Phenotypic plasticity among species creates phenotypic diversity over a changing environmental landscape.2. We measured the indirect effects of planktivorous larval walleye (Stizostedion vitreum) on phytoplankton biomass through their effects on the dominant herbivore species, Daphnia pulicaria and D. mendotae.3. Fish had no effect on phytoplankton biomass or overall Daphnia density. We observed a compensatory response to predation by functionally comparable species within a trophic level in the form of shifting dominance and coexistence of Daphnia species. We hypothesized that this phenotypically plastic response to predation decoupled a potential trophic cascade in this freshwater pelagic system. Daphnia pulicaria density decreased over time with fish predation, but D. mendotae density increased over time with fish predation.4. Phenotypically plastic life history trait shifts and reproductive rates differed between species in fishless and fish enclosures, accounting for population trends. Daphnia pulicaria were also proportionally higher in walleye larvae stomachs than in the enclosures, indicating that walleye preferred to feed on D. pulcaria over D. mendotae. The resultant shift in dominance may partially explain the overall benign effect of fish on grazers and supports the hypothesis that trophic level diversity can decouple a trophic cascade.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 7
    ISSN: 1365-2427
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: 1. The Lotic Intersite Nitrogen eXperiment (LINX) was a coordinated study of the relationships between North American biomes and factors governing ammonium uptake in streams. Our objective was to relate inter-biome variability of ammonium uptake to physical, chemical and biological processes.2. Data were collected from 11 streams ranging from arctic to tropical and from desert to rainforest. Measurements at each site included physical, hydraulic and chemical characteristics, biological parameters, whole-stream metabolism and ammonium uptake. Ammonium uptake was measured by injection of 15N-ammonium and downstream measurements of 15N-ammonium concentration.3. We found no general, statistically significant relationships that explained the variability in ammonium uptake among sites. However, this approach does not account for the multiple mechanisms of ammonium uptake in streams. When we estimated biological demand for inorganic nitrogen based on our measurements of in-stream metabolism, we found good correspondence between calculated nitrogen demand and measured assimilative nitrogen uptake.4. Nitrogen uptake varied little among sites, reflecting metabolic compensation in streams in a variety of distinctly different biomes (autotrophic production is high where allochthonous inputs are relatively low and vice versa).5. Both autotrophic and heterotrophic metabolism require nitrogen and these biotic processes dominate inorganic nitrogen retention in streams. Factors that affect the relative balance of autotrophic and heterotrophic metabolism indirectly control inorganic nitrogen uptake.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
  • 8
    ISSN: 1435-0629
    Keywords: Key words: nitrogen cycle; nitrogen export; C:N ratio; stream; aquatic insects; trophic structure.
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Nitrogen (N) was added for 35 days in the form of 15NH4Cl to Kings Creek on Konza Prairie, Kansas. Standing stocks of N in key compartments (that is, nutrients, detritus, organisms) were quantified, and the amount of labeled N entering the compartments was analyzed. These data were used to calculate turnover and flux rates of N cycling through the food web, as well as nutrient transformation rates. Inorganic N pools turned over much more rapidly in the water column of this stream than in pelagic systems where comparable measurements have been made. As with other systems, the mass of ammonium was low but it was the key compartment mediating nutrient flux through the ecosystem, whereas dissolved organic N, the primary component of N flux through the system, is not actively cycled. Nitrification was also a significant flux of N in the stream, with rates in the water column and surface of benthos accounting for approximately 10% of the total ammonium uptake. Primary consumers assimilated 67% of the inorganic N that entered benthic algae and microbes. Predators acquired 23% of the N that consumers obtained. Invertebrate collectors, omnivorous crayfish (Orconectes spp.), and invertebrate shredders dominated the N flux associated with primary consumers. Mass balance calculations indicated that at least 23% of the 309 mg of 15N added during the 35 days of release was retained within the 210-m stream reach during the release. Overall, the rates of turnover of N in organisms and organic substrata were significantly greater when C:N was low. This ratio may be a surrogate for biological activity with regard to N flux in streams.
    Type of Medium: Electronic Resource
    Location Call Number Limitation Availability
    BibTip Others were also interested in ...
Close ⊗
This website uses cookies and the analysis tool Matomo. More information can be found here...