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Proposed degradation pathway for

Figure 6 (a) Proposed degradation pathway for luteolin by R. meliloii. (b) Proposed... [Pg.206]

Fig. 3.77. Proposed degradation pathways for MeOr and MeRed during photocatalysis. The schemes illustrate that two mechanisms of degradation are independently active. Reprinted with permission from R. Comparelli et al. [143],... Fig. 3.77. Proposed degradation pathways for MeOr and MeRed during photocatalysis. The schemes illustrate that two mechanisms of degradation are independently active. Reprinted with permission from R. Comparelli et al. [143],...
Fig. 3.153. The proposed degradation pathway for copper phtalocyanine dyes using P. chrysosporum (white-rot fungi). Reprinted with permission from A. Conneely el al. [194]. Fig. 3.153. The proposed degradation pathway for copper phtalocyanine dyes using P. chrysosporum (white-rot fungi). Reprinted with permission from A. Conneely el al. [194].
Figure 36 Proposed degradation pathways for an amine oxide degradation product. The counterion (chloride) is not shown for simplicity. Figure 36 Proposed degradation pathways for an amine oxide degradation product. The counterion (chloride) is not shown for simplicity.
Fig. (S). Proposed degradative pathway for the formation of the side chain in salpichrolides E (95) and F (96). Starting from salpichrolide A (91) the first two intermediates correspond to compounds 97 and 98. Fig. (S). Proposed degradative pathway for the formation of the side chain in salpichrolides E (95) and F (96). Starting from salpichrolide A (91) the first two intermediates correspond to compounds 97 and 98.
Scheme 3, Proposed degradation pathways for atrazine under illumination of T1O2 slurries. All compounds were experimentally identified during the degradation process and their kinetics of appearance and of subsequent disappearance was measured. Adapted from ref.[28,57]. Scheme 3, Proposed degradation pathways for atrazine under illumination of T1O2 slurries. All compounds were experimentally identified during the degradation process and their kinetics of appearance and of subsequent disappearance was measured. Adapted from ref.[28,57].
Figure 17. The proposed microbial degradation pathway for carbazole. Figure 17. The proposed microbial degradation pathway for carbazole.
Fig. 3. A proposed biochemical pathway for aerobic degradation of dimethyl terephthalate (DMT) by Pasteurella multocida Sa isolated from mangrove sediment (Li and Gu 2006). Fig. 3. A proposed biochemical pathway for aerobic degradation of dimethyl terephthalate (DMT) by Pasteurella multocida Sa isolated from mangrove sediment (Li and Gu 2006).
Figure 10 Proposed acid-catalyzed degradation pathways for duloxetine. Figure 10 Proposed acid-catalyzed degradation pathways for duloxetine.
Figure 69 Proposed aqueous solution (aqueous autoclave conditions, 120°C (degradation pathway for timolol maleate. Figure 69 Proposed aqueous solution (aqueous autoclave conditions, 120°C (degradation pathway for timolol maleate.
Figure 6.43 Degradation pathway for butorphanol tartrate in long-term stability samples (LTSS). The dashed area indicates the substructure involved in the proposed ring contraction. (Reprinted with permission from Volk et al., 1996. Copyright 1996 Elsevier.)... Figure 6.43 Degradation pathway for butorphanol tartrate in long-term stability samples (LTSS). The dashed area indicates the substructure involved in the proposed ring contraction. (Reprinted with permission from Volk et al., 1996. Copyright 1996 Elsevier.)...
The FTIR results lend credence to this proposed mechanism. More intriguing however is the degradation pathway for naphthoquinone to phthalic acid. NQ... [Pg.326]

D Hennezel et al. [203] proposed a possible degradation pathway for the photo oxidation of gaseous toluene (Scheme 6). Their work was carried out over water and used TiC>2 which had been pre-treated with HC1 as it has been shown that this pre-treatment enhanced the removal rate of the toluene. Using GC-FIC, GC-MS and HPLC-UV they found that the intermediate products formed were benzoic acid, benzaldehyde and benzyl alcohol with trace derivatives of these products and of toluene that were nonhydroxylated on the ring. [Pg.408]

Fig. 2. A proposed mechanistic pathway for the microbiological or chemically mediated degradation of sterols in seawater and sediments. Compounds in parentheses are intermediates not isolated. Fig. 2. A proposed mechanistic pathway for the microbiological or chemically mediated degradation of sterols in seawater and sediments. Compounds in parentheses are intermediates not isolated.
Figure 2. Proposed reaction pathway for enzymatic, oxidative phenol degradation, according to the literature (21, 24,25, 26 ... Figure 2. Proposed reaction pathway for enzymatic, oxidative phenol degradation, according to the literature (21, 24,25, 26 ...
Scheme 3.10 Proposed metabolic pathways for alkane degradation by microorganisms, ADH (alcohol dehydrogenase) AldDH (aldehyde dehydrogenase) and BVMO (Baeyer-Villiger monooxygenase). Scheme 3.10 Proposed metabolic pathways for alkane degradation by microorganisms, ADH (alcohol dehydrogenase) AldDH (aldehyde dehydrogenase) and BVMO (Baeyer-Villiger monooxygenase).
In the pentose plu phatc pathway for degrading sugars, ribulose 5-phosphate is converted to ribose 5-phosphale. Propose a mechanism for the isomerization. [Pg.1173]

Another step in the pentose phosphate pathway for degrading sugars (see Problem 29.38) is the conversion of ribose S-phosphate to glyceraldehyde 3-phosphate. What kind of organic process is occurring Propose a mechanism for the conversion. [Pg.1174]

This has received widespread application, and a single example has been chosen as representative. The pathway for the degradation of morpholine by Mycobacterium aurum MOl sadMycobacterium strain RPl was examined using whole cells, and this confirmed its identity to the one that had been proposed earlier for M. chelonae (Combourieu et al. 1998 Poupin et al. 1998). [Pg.285]


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