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Books on the topic 'Aquatic metabolism'

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Author: Grafiati
Published: 10 December 2022
Last updated: 29 January 2023

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1

Langston, William J., and Maria João Bebianno, eds. Metal Metabolism in Aquatic Environments. Boston, MA: Springer US, 1998. http://dx.doi.org/10.1007/978-1-4757-2761-6.

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2

Erik, Kristensen, and Thamdrup Bo, eds. Aquatic geomicrobiology. San Diego, Calif: Academic Press, 2005.

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3

Lukina, L. F. Fiziologii͡a︡ vysshikh vodnykh rasteniĭ. Kiev: Nauk. dumka, 1988.

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4

Bioenergetics of aquatic animals. London: Taylor & Francis, 1996.

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5

J, Lucas W., Berry Joseph A. 1941-, American Society of Plant Physiologists., University of California Davis, and Carnegie Institution of Washington. Dept. of Plant Biology., eds. Inorganic carbon uptake by aquatic photosynthetic organisms: Proceedings of an International Workshop on Bicarbonate Use in Photosynthesis, August 18-22, 1984, commemorating the seventy-fifty anniversary of the University of California, Davis, 1909-1984. Rockville, Md: American Society of Plant Physiologists, 1985.

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6

service), SpringerLink (Online, ed. Molecular Biomineralization: Aquatic Organisms Forming Extraordinary Materials. Berlin, Heidelberg: Springer-Verlag Berlin Heidelberg, 2011.

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7

service), SpringerLink (Online, ed. Biological Materials of Marine Origin: Invertebrates. Dordrecht: Springer Science+Business Media B.V., 2010.

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8

W, Hochachka Peter, and Mommsen T. P, eds. Analytical techniques. Amsterdam: Elsevier, 1994.

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9

Bebianno, Maria J., and William J. Langston. Metal Metabolism in Aquatic Environments. Springer London, Limited, 2013.

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10

Langston, William J. Metal Metabolism in Aquatic Environments. Springer, 2010.

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11

J, Langston William, and Bebianno Maria João, eds. Metal metabolism in aquatic environments. London: Chapman & Hall, 1998.

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12

Schlenk, Daniel K. Xenobiotic biotransformation in aquatic organisms. 1989.

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13

Usha, Varanasi, ed. Metabolism of polycyclic aromatic hydrocarbons in the aquatic environment. Boca Raton, Fla: CRC Press, 1989.

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14

A, Lucas, and I. G. Priede. Bioenergetics of Aquatic Animals. Taylor & Francis Group, 1996.

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15

(Editor), William J. Langston, and Maria J. Bebianno (Editor), eds. Metal Metabolism in Aquatic Environments (Chapman & Hall Ecotoxicology Series, No. 7). Springer, 1998.

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16

Burton, Derek, and Margaret Burton. Metabolism, homeostasis and growth. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780198785552.003.0007.

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Metabolism consists of the sum of anabolism (construction) and catabolism (destruction) with the release of energy, and achieving a fairly constant internal environment (homeostasis). The aquatic external environment favours differences from mammalian pathways of excretion and requires osmoregulatory adjustments for fresh water and seawater though some taxa, notably marine elasmobranchs, avoid osmoregulatory problems by retaining osmotically active substances such as urea, and molecules protecting tissues from urea damage. Ion regulation may occur through chloride cells of the gills. Most fish are not temperature regulators but a few are regional heterotherms, conserving heat internally. The liver has many roles in metabolism, including in some fish the synthesis of antifreeze seasonally. Maturing females synthesize yolk proteins in the liver. Energy storage may include the liver and, surprisingly, white muscle. Fish growth can be indeterminate and highly variable, with very short (annual) life cycles or extremely long cycles with late and/or intermittent reproduction.
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17

Kristensen, Erik, Don Canfield, and Bo Thamdrup. Aquatic Geomicrobiology, Volume 48 (Advances in Marine Biology). Academic Press, 2005.

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18

Kristensen, Erik, Don Canfield, and Bo Thamdrup. Aquatic Geomicrobiology, Volume 48 (Advances in Marine Biology). Academic Press, 2005.

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19

Müller, Werner E. G. Molecular Biomineralization: Aquatic Organisms Forming Extraordinary Materials. Springer Berlin / Heidelberg, 2013.

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20

L, Behrends Leslie, and Tennessee Valley Authority, eds. Seasonal trends in growth and biomass accumulation of selected nutrients and metals in six species of emergent aquatic macrophytes. [Muscle Shoals, Ala.?: Tennessee Valley Authority, 1999.

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21

Acute metabolic responses to water aerobics and land aerobics. 1993.

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22

W, Hochachka Peter, and Mommsen T. P, eds. Metabolic biochemistry. Amsterdam: Elsevier, 1995.

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23

Comparison of energy expenditure between treadmill running and water running. 1991.

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24

Comparison of energy expenditure between treadmill running and water running. 1991.

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25

Comparison of energy expenditure between treadmill running and water running. 1986.

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26

(Editor), P. W. Hochachka, and T. P. Mommsen (Editor), eds. Metabolic Biochemistry (Biochemistry and Molecular Biology of Fishes). Elsevier Science, 1995.

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27

Lighton, John R. B. Measuring Metabolic Rates. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198830399.001.0001.

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Measuring Metabolic Rates demystifies the field of metabolic rate measurement, explaining every common variation of the art, from century-old manometric methods through ingenious syringe-based techniques, direct calorimetry, aquatic respirometry, stable-isotope metabolic measurement, and every type of flow-through respirometry. Each variation is described in enough detail to allow it to be applied in practice. Special chapters are devoted to metabolic phenotyping and human metabolic measurement, including room calorimetry. Background information on different analyzer and equipment types allows users to choose the best instruments for their application. Respirometry equations—normally a topic of terror and confusion to researchers—are derived and described in enough detail to make their selection and use effortless. Tools and skills—many of them open source—that will amplify the innovative researcher’s capabilities are described. Vital topics such as manual and automated baselining, implementing multi-animal systems, common pitfalls, and the correct analysis and presentation of metabolic data are covered in enough detail to turn a respirometry neophyte into a hardened metabolic warrior, ready to take on the task of publication in peer-reviewed journals with confidence.
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28

Peng, Bo, Xinhua Chen, and Hetron M. Munang’andu, eds. Metabolic Regulation of Drug Resistance and Pathogenicity in Aquatic Pathogens. Frontiers Media SA, 2022. http://dx.doi.org/10.3389/978-2-88974-584-5.

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29

(Editor), P. W. Hochachka, and T. P. Mommsen (Editor), eds. Molecular Biology Frontiers (Biochemistry and Molecular Biology of Fishes). Elsevier Science, 1993.

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30

W, Hochachka Peter, and Mommsen T. P, eds. Analytical techniques. Amsterdam: Elsevier, 1994.

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31

(Editor), P. W. Hochachka, and T. P. Mommsen (Editor), eds. Analytical Techniques (Biochemistry and Molecular Biology of Fishes). Elsevier Science, 1994.

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32

(Editor), P. W. Hochachka, and T. P. Mommsen (Editor), eds. Analytical Techniques (Biochemistry and Molecular Biology of Fishes). Elsevier Science, 1994.

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33

W, Hochachka Peter, and Mommsen T. P, eds. Environmental and ecological biochemistry. Amsterdam: Elsevier, 1995.

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34

W, Hochachka Peter, and Mommsen T. P, eds. Molecular biology frontiers. Amsterdam: Elsevier, 1993.

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35

Mommsen, T. P., and T. W. Moon. Environmental Toxicology. Elsevier Science & Technology Books, 2005.

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36

The cardiovascular and metabolic responses of men with cardiovascular disease to aqua dynamic exercise. 1990.

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37

The cardiovascular and metabolic responses of men with cardiovascular disease to aqua dynamic exercise. 1992.

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38

Cardiorespiratory and metabolic responses to treadmill versus water immersion to the neck exercise in elite distance runners. 1993.

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39

Jacobsen, Dean, and Olivier Dangles. Strategies and adaptations to aquatic life at high altitude. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780198736868.003.0005.

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Chapter 5 is focused on how organisms cope with the environmental conditions that are a direct result of high altitude. Organisms reveal a number of fascinating ways of dealing with a life at high altitude; for example, avoidance and pigmentation as protection against damaging high levels of ultraviolet radiation, accumulation of antifreeze proteins, and metabolic cold adaptation among species encountering low temperatures with the risk of freezing, oxy-regulatory capacity in animals due to low availability of oxygen, and root uptake from the sediment of inorganic carbon by plants living in waters poor in dissolved carbon dioxide. These and more adaptations are carefully described through a number of examples from famous flagship species in addition to the less well-known ones. Harsh environmental conditions work as an environmental filter that only allows the well-adapted species to slip through to colonize high altitude waters.
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40

Ehrlich, Hermann. Biological Materials of Marine Origin: Vertebrates. Springer, 2016.

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41

Biological Materials of Marine Origin: Vertebrates. Springer, 2014.

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42

Ehrlich, Hermann. Biological Materials of Marine Origin: Vertebrates. Springer, 2014.

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43

Clarke, Andrew. Temperature, growth and size. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780199551668.003.0013.

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Growth involves two flows of energy. The first is chemical potential energy in the monomers used to construct the proteins, lipids, polysaccharides and nucleic acids forming the new tissue. The second is the metabolic energy (ATP or GTP) used to construct the new tissue; this is the metabolic cost of growth and can be expressed as a dimensionless fraction of the energy retained in the new tissue. Its value is ~0.33. Typical temperature sensitivities for growth in the wild lie in the range Q10 1.5 – 3. Within species there may be evolutionary adjustments to growth rate to offset the effects of temperature, though these involve trade-offs with other physiological factors affecting fitness. Outside the tropics, many mammals and birds exhibit a cline in size, with larger species at higher latitudes (Bergmann’s rule). Carl Bergmann predicted such a cline from biophysical arguments based on endotherm thermoregulatory costs; Bergmann’s rule thus applies only to mammals and birds. Many ectotherms grow more slowly but attain a larger adult size when grown at lower temperatures (the temperature-size rule). The large size of some aquatic invertebrates at lower temperatures (notably in the polar regions and the deep sea) is associated with a higher oxygen content of the water.
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44

Kirchman, David L. Degradation of organic matter. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198789406.003.0007.

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The aerobic oxidation of organic material by microbes is the focus of this chapter. Microbes account for about 50% of primary production in the biosphere, but they probably account for more than 50% of organic material oxidization and respiration (oxygen use). The traditional role of microbes is to degrade organic material and to release plant nutrients such as phosphate and ammonium as well as carbon dioxide. Microbes are responsible for more than half of soil respiration, while size fractionation experiments show that bacteria are also responsible for about half of respiration in aquatic habitats. In soils, both fungi and bacteria are important, with relative abundances and activity varying with soil type. In contrast, fungi are not common in the oceans and lakes, where they are out-competed by bacteria with their small cell size. Dead organic material, detritus, used by microbes, comes from dead plants and waste products from herbivores. It and associated microbes can be eaten by many eukaryotic organisms, forming a detritus food web. These large organisms also break up detritus into small pieces, creating more surface area on which microbes can act. Microbes in turn need to use extracellular enzymes to hydrolyze large molecular weight compounds, which releases small compounds that can be transported into cells. Fungi and bacteria use a different mechanism, “oxidative decomposition,” to degrade lignin. Organic compounds that are otherwise easily degraded (“labile”) may resist decomposition if absorbed to surfaces or surrounded by refractory organic material. Addition of labile compounds can stimulate or “prime” the degradation of other organic material. Microbes also produce organic compounds, some eventually resisting degradation for thousands of years, and contributing substantially to soil organic material in terrestrial environments and dissolved organic material in aquatic ones. The relationship between community diversity and a biochemical process depends on the metabolic redundancy among members of the microbial community. This redundancy may provide “ecological insurance” and ensure the continuation of key biogeochemical processes when environmental conditions change.
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45

Clarke, Andrew. Temperature regulation. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780199551668.003.0009.

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For many organisms there is a fitness advantage to being warm. Many organisms use behavioural thermoregulation to maintain a high body temperature during the day, basking in the sun to warm up and retreating to the shade to avoid overheating. This option is not open to most aquatic organisms, or those living in soil or sediment. It is also generally not possible for small or nocturnal organisms. A small number of active predatory fish utilise a counter-current heat exchanger (rete mirabile) to retain metabolic heat and warm their muscles, brain or eyes. A few have modified optical muscles as heater organs, and a range of plants generate heat to aid dispersal of scent and attract pollinators. A wide range of larger insects use rapid but unsynchronised muscle contraction to elevate their body temperature prior to flight, or other activity. In hot climates organisms may need to dissipate heat to avoid overheating. The major behavioural mechanism is shade-seeking, or for small organisms stilting or climbing onto objects such as plants to move out of the hottest air net to the ground. Larger mammals may tolerate a limited degree of warming during the day, releasing this in the cool of the night. Evaporative cooling is very effective at losing heat, but because it loses valuable water it can only be used sparingly in arid areas.
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46

Kirchman, David L. Community structure of microbes in natural environments. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198789406.003.0004.

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Community structure refers to the taxonomic types of microbes and their relative abundance in an environment. This chapter focuses on bacteria with a few words about fungi; protists and viruses are discussed in Chapters 9 and 10. Traditional methods for identifying microbes rely on biochemical testing of phenotype observable in the laboratory. Even for cultivated microbes and larger organisms, the traditional, phenotype approach has been replaced by comparing sequences of specific genes, those for 16S rRNA (archaea and bacteria) or 18S rRNA (microbial eukaryotes). Cultivation-independent approaches based on 16S rRNA gene sequencing have revealed that natural microbial communities have a few abundant types and many rare ones. These organisms differ substantially from those that can be grown in the laboratory using cultivation-dependent approaches. The abundant types of microbes found in soils, freshwater lakes, and oceans all differ. Once thought to be confined to extreme habitats, Archaea are now known to occur everywhere, but are particularly abundant in the deep ocean, where they make up as much as 50% of the total microbial abundance. Dispersal of bacteria and other small microbes is thought to be easy, leading to the Bass Becking hypothesis that “everything is everywhere, but the environment selects.” Among several factors known to affect community structure, salinity and temperature are very important, as is pH especially in soils. In addition to bottom-up factors, both top-down factors, grazing and viral lysis, also shape community structure. According to the Kill the Winner hypothesis, viruses select for fast-growing types, allowing slower growing defensive specialists to survive. Cultivation-independent approaches indicate that fungi are more diverse than previously appreciated, but they are less diverse than bacteria, especially in aquatic habitats. The community structure of fungi is affected by many of the same factors shaping bacterial community structure, but the dispersal of fungi is more limited than that of bacteria. The chapter ends with a discussion about the relationship between community structure and biogeochemical processes. The value of community structure information varies with the process and the degree of metabolic redundancy among the community members for the process.
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