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M’MOFs

The complete reaction scheme is shown in Fig. 5.3-7, while Fig. 5.4-51 gives a simplified representation. 1-naphthol (A) is primarily coupled with diazotized sulphanilic acid (B) to form monoazo dyes coupled in para and ortho positions (p-R and o-R, respectively). This reaction is first order in both A and B. Each of the primary products can react with diazotized sulphanilic acid to form bisazo dye (5). Rate constants at 298 K and pH 10 are ku = 10600 m mof s k2i = 1 22 = 1.7 m mor s (see Fig. 5-4-51). [Pg.341]

Figure 3. Top AE for CO2 adsorption (in kj/mol) in M-MOF-74. Bottom Magnitude of the adsorption energy of C02 relative to H20. A positive value in this plot means that C02 binds more strongly than H20 (Adapted from [139]). Figure 3. Top AE for CO2 adsorption (in kj/mol) in M-MOF-74. Bottom Magnitude of the adsorption energy of C02 relative to H20. A positive value in this plot means that C02 binds more strongly than H20 (Adapted from [139]).
No information concerning the transport and partitioning of 1,2-diphenylhydrazine in the environment was located in the literature. In water, 1,2-diphenylhydrazine is not expected to volatilize because of its rapid oxidation in aerated water (near-surface water) to azobenzene and its low calculated Henry s Law constant (9.42 x 10 atm-m mof) (Lyman et al. 1982). The calculated log Koc (2.76) suggests that 1,2-diphenylhydrazine may sorb to sediments or suspended particles. This is based on the analysis of Kenaga (1980), who stated that chemicals with a K°<= <100 tend to be mobile in soil, while those with a K°<= >L000 tend to sorb. In soil, 1,2-diphenylhydrazine is not expected to leach to groundwater, based on its physical and chemical properties (i.e.. 1,2-diphenylhydrazine reacts rapidly under environmental conditions and, based on its K°c will not rapidly leach downward in the soil column). [Pg.51]

Isophorone has a water solubility of 12,000 ppm, a log octanol/water partition coefficient of 1.67, a Henry s Law constant of 4.55 X 10 atm m mof, a vapor pressure of 0.3 mm Hg at 20 C, a log sediment sorption coefficient of approximately 1.46, and a log bioconcentration factor (BCF) of 0.85. Isophorone is released to air and water from its manufacturing and use. Based on its water solubility, some isophorone may wash out of the atmosphere however, only limited amounts will be washed out because of the short atmospheric half-life of isophorone. Particularly during the day, when hydroxyl radical (HO) concentrations are highest, very little atmospheric transport will occur due to its fast reaction with HO. ... [Pg.72]

Oy (J m mof ) and b-, (m mol ) are the parameters of the Redlich-Kwong-Soave equation of state they are easily calculated from the critical temperature and pressure and the acentric factor of the adsorbate... [Pg.234]

In 1965, Adams et al. [62] obtained the absolute rate constants for the reaction of OH with a number of solutes, using the competition method the reactions of OH with C03, SCN , and Se03 that give the absorbing radicals C03 ", (SCN)2" and Se03 , respectively, were used as references. Similarly, Thomas [63] determined the rate constant for the reaction of OH with 1 by following the formation of l2 (2max 385 nm, max 940 m moF ) [56], and from that derived the rate constants for other reactions of the OH radical [63]. The NDRL/NIST Database cited above contains 1787, 715, and 171 entries for the reactions of OH, H , and 0 , respectively [7a]. [Pg.602]

Remarkably, the electrocatalytic process is modulated by electrolyte counterions. This can be seen in Figure 5.18, which displays CVs at (m-MOF-modi Tied paraffin-impregnated graphite electrodes immersed into 1.0 mM H O plus Oj-saturatcd (a) 0.10 M Et4NC104/MeCN and (b) 0.10 M LiClO4/MeCN solutions. In the presence of size-hindered Et4N+ ions, only the oxygen-localized reversible reduction process at a midpoint potential of ca. -0.80 V is observed. In the presence of Li+ ions, however, two reduction waves at ca. -0.60 and -1.20 V are recorded, followed, in the subsequent anodic scan, by anodic peaks at -0.85, -0.45, -1-0.40, -1-0.90, and -1-1.40 V. [Pg.113]

Molar volume [m moF ] 398x10 766x10- 106x10- 106x10 ... [Pg.216]

Figure 19 Specific rate of sugar production ql blue darkgray in the print version) lines) and the observable yield of sugar on photons absorbed n ph red dark gray in the print version) lines) as a function of photon flux density /ph- The solid lines follow the model of Jassby and Platt the dashed lines follow the Blackman model. Parameter values based on high-light acclimated Chlorella sorokiniana Ux=3.5 m mof T ph,m=0.10 molj fnolph qs,m = 1-25x 10 mols mol s /Mx=24 g moix . Figure 19 Specific rate of sugar production ql blue darkgray in the print version) lines) and the observable yield of sugar on photons absorbed n ph red dark gray in the print version) lines) as a function of photon flux density /ph- The solid lines follow the model of Jassby and Platt the dashed lines follow the Blackman model. Parameter values based on high-light acclimated Chlorella sorokiniana Ux=3.5 m mof T ph,m=0.10 molj fnolph qs,m = 1-25x 10 mols mol s /Mx=24 g moix .
DFT studies have been carried out to demonstrate the bonding of CO2 to Metal Organic Frameworks (MOF). A bridged coordination has been proposed by Hou et al. [22] in the interaction of CO2 with M-MOF-74 (M = Mg and Zn), which shows a high CO2 adsorption capacity. Metal ions are supposed to interact with the O atoms of CO2, whereas the carbon atom of CO2 gives strong interactions with the O atoms of the organic linkers of the MOF. [Pg.45]

Zhang Q, Li B, Chen L (2013) First-principle study of microporous magnets M-MOF-74 (M = Ni Co, Fe, Mn) the role of metal centers. Inoig Chem 52 9356-9362... [Pg.130]


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