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Anaerobic decay

Explain how the CO2 content and pH of natural waters is affected by processes and reactions including the dissolution of C02(g), photosynthesis and respiration, aerobic decay, anaerobic decay (fermentation), nitrate reduction, and denitrification and sulfate reduction. [Pg.189]

A number of biological processes result in the marine production of gases that have a greenhouse role, similar to water vapour and COj. In low oxygen environments, of the sort discussed in the next section, methane is produced by anaerobic bacterial decay ... [Pg.23]

HzS 0-40 pptv Biological decay of protein in anaerobic water Oxidation to SO2... [Pg.146]

The second mechanism often invoked to explain the increase in n y of simple Fe porphyrins at potentials more reducing than that of the Fe couple (under anaerobic conditions) is based on the fact that at such potentials the fraction of the catalyst in the 5 -coordinate ferrous state is maximal because (i) the equilibrium (18.9) is shifted completely to the ferrous form and (ii) the concentration of O2 in the catalytic film is low owing to mass transport limitations. The higher the concentration of the 5-coor-dinate ferrous porphyrin in the catalytic film, the greater the probability that any released H2O2 will re-enter the catalytic cycle by coordinating to a molecule of ferrous porphyrin and decay according to (18.13b) instead of (18.17). [Pg.660]

Aquifer sediments in the model are confined by and interleaved with fine-grained sediments that contain sedimentary organic matter. The organic matter decays gradually by microbial fermentation and anaerobic oxidation,... [Pg.477]

Fig. 3. Decay of the H202 concentration versus time during the anaerobic oxidation reaction with cysteine in the presence of CuS04. First stage of constant rate (first-order in [Cu]) during the period of oxidation, second stage of increasing rate after completion of the oxidation of cysteine to cystine. Reprinted from Journal of Molecular catalysis, vol. 11, Zwart, J. van Wolput, J. H. M. C. van der Cammen, J. C. J. M. Koningsberger, D. C. Accumulation and Reactions of H202 During the Copper Ion Catalyzed Autoxidation of Cysteine in Alkaline Medium, p. 69, Copyright (2002), with permission from Elsevier Science. Fig. 3. Decay of the H202 concentration versus time during the anaerobic oxidation reaction with cysteine in the presence of CuS04. First stage of constant rate (first-order in [Cu]) during the period of oxidation, second stage of increasing rate after completion of the oxidation of cysteine to cystine. Reprinted from Journal of Molecular catalysis, vol. 11, Zwart, J. van Wolput, J. H. M. C. van der Cammen, J. C. J. M. Koningsberger, D. C. Accumulation and Reactions of H202 During the Copper Ion Catalyzed Autoxidation of Cysteine in Alkaline Medium, p. 69, Copyright (2002), with permission from Elsevier Science.
In a recent study, spectral evidence was found for the formation of a [RS Cu1 RS] dimer when cysteine was added to Cu(II) under anaerobic conditions and at pH 7.4 (73). On exposure to air, the dimer slowly decayed after the cysteine excess was consumed. This may indicate that indeed all the reaction proceeds via an intra-molecular mechanism. [Pg.430]

UOP FCC unit, 11 700-702 UOP/HYDRO MTO process, 18 568 UOP Olex olefin separation process, 17 724 Up-and-Down Method, 25 217 U/Pb decay schemes, 25 393-394 Updraft sintering, 26 565 Upflow anaerobic sludge blanket (UASB) in biological waste treatment, 25 902 Upgraded slag (UGS), 25 12, 33 Upland Cotton, U.S., 8 13 U-Polymer, 20 189 Upper critical solution temperature (UCST), 20 320, 322 Upper explosive limit (UEL), 22 840 Upper flammability limit, 23 115 Upper flammable limit (UFL), 22 840 Upper Freeport (MVB) coal... [Pg.989]

Many wastewater flows in industry can not be treated by standard aerobic or anaerobic treatment methods due to the presence of relatively low concentration of toxic pollutants. Ozone can be used as a pretreatment step for the selective oxidation of these toxic pollutants. Due to the high costs of ozone it is important to minimise the loss of ozone due to reaction of ozone with non-toxic easily biodegradable compounds, ozone decay and discharge of ozone with the effluent from the ozone reactor. By means of a mathematical model, set up for a plug flow reactor and a continuos flow stirred tank reactor, it is possible to calculate more quantitatively the efficiency of the ozone use, independent of reaction kinetics, mass transfer rates of ozone and reactor type. The model predicts that the oxidation process is most efficiently realised by application of a plug flow reactor instead of a continuous flow stirred tank reactor. [Pg.273]

Anaerobic digestion, like pyrolysis, occurs in the absence of air. But, the decomposition is caused by bacterial action rather than high temperatures. This process takes place in most biological materials, but it is accelerated by warm, wet and airless conditions. It occurs naturally in decaying vegetation in ponds, producing the type of marsh gas that can catch fire. [Pg.114]

The major fossil fuels are coal and petroleum. Marine organisms were typically deposited in mud and under water, where anaerobic decay occurred. The major decomposition products are hydrocarbons, carbon dioxide, water, and ammonium. These deposits form much of the basis for our petroleum resources. Many of these deposits are situated so that the evaporation of the more volatile products such as water and ammonia occurred, giving petroleum resources with little nitrogen- or oxygen-containing products. By comparison, coal is formed from plant material that has decayed to graphite carbon and methane. [Pg.525]

Almost any chemical not arising from natural sources is a pollutant in water. Agricultural wastes from fertilizers and pesticides are the major pollution sources nationally. Fertilizers add nutrients that promote algae growth whose decay can cause the lake or river to become anaerobic through the overall reactions... [Pg.349]

In scrupulously anaerobic basic solutions, NO can combine directly with thiolates to form thionitrites (S-nitrosothiols) [25], which can decay by several modes to yield NO. [Pg.151]


See other pages where Anaerobic decay is mentioned: [Pg.277]    [Pg.206]    [Pg.351]    [Pg.277]    [Pg.206]    [Pg.351]    [Pg.258]    [Pg.213]    [Pg.2254]    [Pg.23]    [Pg.27]    [Pg.241]    [Pg.447]    [Pg.1169]    [Pg.135]    [Pg.866]    [Pg.32]    [Pg.36]    [Pg.227]    [Pg.418]    [Pg.420]    [Pg.427]    [Pg.529]    [Pg.35]    [Pg.81]    [Pg.104]    [Pg.82]    [Pg.315]    [Pg.350]    [Pg.351]    [Pg.102]    [Pg.23]    [Pg.27]    [Pg.393]    [Pg.395]   
See also in sourсe #XX -- [ Pg.27 ]

See also in sourсe #XX -- [ Pg.27 ]

See also in sourсe #XX -- [ Pg.27 ]

See also in sourсe #XX -- [ Pg.295 ]




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