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Oxide scale phosphate solution

The use of organic solvents to produce surface layers has clear disadvantages if the aim is to use such techniques on an industrial scale (due to both environmental emission and disposal issues). Moreover, for applications in areas such as medical devices and implants, the presence of even minor organic solvent residues in the adlayers cannot be tolerated, in view of potential cell-toxicity effects and other biological risks. On the other hand, self-assembled monolayers, in particular of molecules with functional terminal groups, are of great interest for the modification and functionalization of biomaterials and medical devices. Therefore, a technique based on the deposition of SAMs from aqueous alkyl phosphate solutions has been developed and successfully applied to a variety of metal oxide substrates. ... [Pg.54]

Solvent extraction by tributyl phosphate (TBP) (13, 96), dithizone (20, 71, 72), cupferron (89), thenoyl trifluoroacetone (TTA) (55), diiso-propyl ketone (26), mesityl oxide (92), tri-n-benzylamine and methyl di-n-octylamine (99), diisopropyl and diisobutyl carbinol (100) have all found some application on the trace scale. Acetylaeetone and methyl isobutyl ketone extract milligram amounts of polonium almost quantitatively from hydrochloric acid, but the stable polonium-organic compounds which are formed make it difficult to recover the polonium in a useful form from solutions in these ketones (7). Ion exchange (22, 115, 119) and paper chromatography (44, 87) have also been used for trace scale separations of polonium, but the effects of the intense alpha-radiation on organic com-... [Pg.202]

Early antisealants used sodium hexametaphosphate (SHMP) as a threshold agent to inhibit the growth of calcium carbonate and sulfate-based scales.6 Most antisealants on the market today contain sulfonate, phosphate, or carboxylic acid functional groups. Perhaps the most effective antisealants today contain and blend of polyacrylic acid (PAA) and phosphoric acid or polyacrylate and a hydroyethylidene diphosphonate (HEDP).12 The polyacrylate-HEDP blends also claim to have good dispersion qualities toward silts and clays.12 Some new inhibitors include a chelant and disper-ant to keep suspended solids such as iron and manganese oxides in solution. These newer antisealants are generally more effective than SHMP for a variety of potential scales.6... [Pg.178]

The acid concentration of the feed solution is an important processing parameter. Acid concentrations in the range 0.01-0.70 M were investigated in the development tests. In each test, the curium sorbed on the resin was sufficient to produce acceptable oxide products. However, the acid concentration of the feed is maintained in the range 0.20 to 0.35 M in the production runs. In one of the earlier production runs at lower acidity, a precipitate formed in the feed solution. This was thought to be caused by an unknown contaminant, probably a phosphate species from an earlier solvent extraction step. In the production runs, the reduced actinide capacity of the resin is noticeable at the higher acidities. Convenient batch sizes and short loading times for the current scale of production are achieved with actinide concentrations of about 10 g/L, but actinide concentration is not considered an important variable. [Pg.180]

Similar to dissociation of water, all soluble acid phosphates, and soluble oxides dissociate or dissolve in water. When acid phosphates dissociate in water, they lower the pH of the solution by releasing protons (H ), while most of the oxides or hydroxides when mixed with water release hydroxyl ions (OH ) by removing protons from the solution. As a result, initially neutral water becomes richer in protons when acid phosphates are dissolved in it and the pH becomes < 7. On the other hand, for certain oxides such as those of alkaline elements (e.g., Na, K, Mg, and Ca), the pH is increased because the solution becomes deficient in protons. Thus, the pH scale is a good indicator of the extent of release of protons and hydroxyl ions and will be used throughout this book to represent the extent of acid-base reactions. [Pg.45]

In vitro a crystalline iron core can be laid down in apoferritin by the addition of an oxidant, such as O2, to an aqueous solution of a ferrous salt and apoferritin (32, 132, 140). The reconstituted core of horse ferritin prepared in the absence of phosphate and with O2 as oxidant is very similar to the native core in terms of its size and Mossbauer properties (85). Electron microscopy, however, reveals that it is less well ordered. Reconstitution in the presence of phosphate leads to smaller cores. Reconstituted A. vinelandii cores in the absence of phosphate were more ordered than were the native cores, and clearly contained ferrihydrite particles and, in some cases, crystal domains (85). Thus the nature of the core is not determined solely by the protein coat the conditions of core formation are also important. This is also indicated by Mossbauer spectroscopy studies of P. aeruginosa cells grown under conditions different than those employed for the large-scale pu-... [Pg.423]

We have shown that phytic acid readily hydrolyzes to produce phosphate with a projected lifetime of 100-150 years in the absence of microbiological effects, that actinide-phytate compounds are insoluble, and that europium and uranyl phytates are converted to phosphates within a month at 85 °C. Thorium solubility, on the other hand, is controlled by hydroxide or oxide species. Furthermore, the solubilities of radiotracer europium and uranyl are reduced by phosphate dosing of a simulated groundwater solution, even in the presence of citric acid. In the same systems, neptunium(V) solubility is only affected by 0.01 M phosphate at pH greater than 7. The results of these tracer-scale immobilization experiments indicate that phosphate mineral formation from representative deposits is under thermodynamic control. [Pg.283]

Figure 31-UV- visible spectra of catalase in PBS (pH 7)phosphate buffer solution(curve a) and Cat-NiO film on ITO electrode(curve b). Reprinted from Biophysical Chemistry, 125, A.Salimi, E. Sharifi, A. NoorBakhash, S. Soltanian, Direct electrochemistry and electrocatalytic activity of catalase immobilized onto electrodeposited nano-scale islands of nickel-oxide, 542, Copyright( 2007), with permission from Elsevier. Figure 31-UV- visible spectra of catalase in PBS (pH 7)phosphate buffer solution(curve a) and Cat-NiO film on ITO electrode(curve b). Reprinted from Biophysical Chemistry, 125, A.Salimi, E. Sharifi, A. NoorBakhash, S. Soltanian, Direct electrochemistry and electrocatalytic activity of catalase immobilized onto electrodeposited nano-scale islands of nickel-oxide, 542, Copyright( 2007), with permission from Elsevier.
As for the correctness of the above experiments, it should be mentioned that the positions of some Lux acids in this scale are incorrect this concerns V205, acidic phosphates, sodium meta- and pyro-phosphate, whose dissolution in the melt is accompanied by the evolution of gaseous iodine. In the case of V205 the reason consists in its strong oxidation properties in acidic solutions. As regards the iodine evolution upon dissolution of the various phosphates, in the case of acidic phosphates it is explained by the pyrohydrolysis of the melt by water formed by dehydration of the acidic salts—for example, potassium... [Pg.93]

Pore-water concentration profiles of redox-sensitive ions (nitrate, Mn, Fe, sulphate and sulphide) and nutrients (ammonium and phosphate) demonstrate the effects of degradation of OM. In freshwater sediments, the redox zones generally occur on a millimetre to centimetre scale due to the high input of reactive OM and the relatively low availability of external oxidators, especially nitrate and sulphate, compared to marine systems. A typical feature for organic-rich freshwater sediments deposited in aerobic surface waters, is the presence of anaerobic conditions close to the sediment-water interface (SWI). This is indicated by the absence of dissolved oxygen and the presence of reduced solutes (e.g. Mn, Fe and sulphides) in the pore water. Secondary redox reactions, like oxidation of reduced pore-water and solid-phase constituents, and other postdepositional processes, like precipitation-dissolution... [Pg.520]

However, even the precipitation of 99.8 pure ceric salts does obviously not remove all the cerium from the solution, and additional steps are necessary. A very effective way is air oxidation and solvent extraction. It has become apparent that TBP (tributyl phosphate, see also in Sect. 4.2.3.1) is the best extractant for large scale operations (Gupta and Krishnamurthy 2005). [Pg.84]

Figure 5.16 Synthesis of PCL-grafted CNTs by the ROP approach and degradation of PCL chains by PS lipase (top), and representative SEM images of the control experiment sample which was collected from the phosphate buffer solution of MWCNT-g-PCL (52.7 wt% of PCL) without PS lipase after 96 h (a), and the samples of MWCNT-g-PCL degraded with PS lipase for 24 h (b), 48 h (c) and 96 h (d). The scale bars in (a), (b), (c) and (d) represent 1000, 500, 500 and 500 nm, respectively. The marked tubes 1 and 2 have diameters of ca. 90.3 and 85.5 nm, respectively. After 24 h of degradation with PS lipase (b), the diameters of tubes 3 and 4 are ca. 83.3 and 75.7 nm, respectively. After 48 h of degradation (c), the diameters of tubes 5 and 6 are only ca. 54.1 and 50.5 nm, respectively. After 96 h of degradation (d), little residual polymer on the surfaces of MWCNTs can be detected, and many tubes with diameters of ca. 20-30 nm are found (tubes 7 and 8 have diameters of 22.7 and 28.2 nm, respectively). In this case, the average diameter of the degraded tubes is almost equal to that of the oxidized tubes. Reprinted with permission from Zeng et al. ... Figure 5.16 Synthesis of PCL-grafted CNTs by the ROP approach and degradation of PCL chains by PS lipase (top), and representative SEM images of the control experiment sample which was collected from the phosphate buffer solution of MWCNT-g-PCL (52.7 wt% of PCL) without PS lipase after 96 h (a), and the samples of MWCNT-g-PCL degraded with PS lipase for 24 h (b), 48 h (c) and 96 h (d). The scale bars in (a), (b), (c) and (d) represent 1000, 500, 500 and 500 nm, respectively. The marked tubes 1 and 2 have diameters of ca. 90.3 and 85.5 nm, respectively. After 24 h of degradation with PS lipase (b), the diameters of tubes 3 and 4 are ca. 83.3 and 75.7 nm, respectively. After 48 h of degradation (c), the diameters of tubes 5 and 6 are only ca. 54.1 and 50.5 nm, respectively. After 96 h of degradation (d), little residual polymer on the surfaces of MWCNTs can be detected, and many tubes with diameters of ca. 20-30 nm are found (tubes 7 and 8 have diameters of 22.7 and 28.2 nm, respectively). In this case, the average diameter of the degraded tubes is almost equal to that of the oxidized tubes. Reprinted with permission from Zeng et al. ...
There has been continued interest in developing a process for direct esterification of terephthalic acid with ethylene glycol. It does not appear, however, that this is currently practiced on a commercial scale in the U.S. In Japan, a process was commercialized where terephthalic acid is reacted with two moles of ethylene oxide to form the dihydroxy ester in situ, as the starting material. One mole of ethylene glycol is then removed under vacuum in the subsequent condensation process. Also, it was reported that the polymer can be prepared by direct esterification at room temperature in the presence of picryl chloride. The reaction can also be performed at about 120 C in the presence of diphenyl chloro-phosphate or toluenesulfonyl chloride. This is done in solution, where pyridine is either the solvent or the cosolvent. Pyridine acts as a scavenger for HCl, that is a byproduct of the reaction, and perhaps also as an activator (by converting the acid into a reactive ester intermediate). [Pg.292]

The first patent on ammonia oxidation wras issued to Khulman in 1839 in this case platinum was used as a catalyst to oxidize ammonia with air. The ammonia-oxidation method using a platinum catalyst qn a commercial scale, developed by Oswald and Brauer and first operated in Germany about 1908, is at present the principal industrial method of nitric acid producticxi. The main use for nitric acid is in fertiDzer production, mainly for ammonium nitrate as such or in compound fertilizers, nitrogen solutions, or mixed salts. About 75% of total nitric acid production is consumed for nitrate fertilizers, mainly as 509 5% concentration acid. Smaller fertilizer uses are for calcium and potassium nitrates. A primary use is in addulation of phosphate rock for production of nitrophosphates. Plant capacities for weak nitric acid i Bed for fertilizer production are in the range of 35 to 1,380 tpd althoi h capacities of 2,000 tpd have been designed. [Pg.209]


See other pages where Oxide scale phosphate solution is mentioned: [Pg.552]    [Pg.60]    [Pg.27]    [Pg.224]    [Pg.631]    [Pg.631]    [Pg.98]    [Pg.66]    [Pg.37]    [Pg.107]    [Pg.883]    [Pg.241]    [Pg.296]    [Pg.151]    [Pg.152]    [Pg.92]    [Pg.47]    [Pg.558]    [Pg.107]    [Pg.273]    [Pg.631]    [Pg.573]    [Pg.210]    [Pg.201]    [Pg.471]   
See also in sourсe #XX -- [ Pg.200 , Pg.201 , Pg.204 , Pg.217 , Pg.218 , Pg.226 , Pg.227 ]




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Oxide scales scale

Oxidizing solutions

Phosphate solutions

Phosphatizing solution

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