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Sulfate cycling

The results of our evaluations for the other hybrid cycles are summarized in Table 3. The advantages of the Cu-Cl cycle are its low maximum temperature requirement and its relatively high efficiencies. The Level 1 and 2 efficiencies exceed 40% (LHV). All reactions in this cycle have been proven [1, 9, 10]. The Mg-Cl cycle has a low maximum temperature requirement but comparatively low Level 1 and 2 efficiencies. The chemistry for the thermal reactions has not been demonstrated. The low maximum temperatures, 550 and 600°C, respectively, for the two chloride cycles provide more flexibility in coupling them with heat sources other than the VHTGR. The advantages of the metal sulfate cycles are their lower corrosivity and the common high temperature decomposition reaction with the sulfur cycles. Of the two metal sulfate cycles, the copper sulfate cycle appears more promising because the copper sulfate cycle requires somewhat lower temperatures than the zinc sulfate cycle. The copper sulfate cycle has also been demonstrated with recycled materials, but no experimental work has been reported for the zinc sulfate cycle [1]. [Pg.227]

There is however an intermediate decomposition step, sulfuric acid decomposing first to sulfur trioxide and steam and then further to SO2 and oxygen. This decomposition reaction at around 800°C is common to the S—I cycle described previously. To further improve the S—I and HyS cycles, metal oxides are used as catalytic materials. These cycles are then converted into metal oxide-metal sulfate cycles with the potential to achieve H2 production at moderate temperatures (Bhosale et al., 2015). [Pg.648]

Molybdate is also known as an inhibitor of the important enzyme ATP sulfurylase where ATP is adenosine triphosphate, which activates sulfate for participation in biosynthetic pathways (56). The tetrahedral molybdate dianion, MoO , substitutes for the tetrahedral sulfate dianion, SO , and leads to futile cycling of the enzyme and total inhibition of sulfate activation. Molybdate is also a co-effector in the receptor for steroids (qv) in mammalian systems, a biochemical finding that may also have physiological implications (57). [Pg.475]

The single largest market use for quaternary fatty amines is in fabric softeners. Monoalkyl quaternaries (chloride) have been used in Hquid detergent softener antistat formulations (LDSA), dialkyl dimethyl quaternaries (chloride) in the rinse cycle, and dialkyl dimethyl quaternaries (sulfate) as dryer softeners. [Pg.223]

The efficiency of the weathering of rocks in using carbonic acid produced in the carbon cycle is affected by various hydrologic, environmental, and cultural controls. The fact that the principal anion in fresh surface water worldwide almost always is bicarbonate attests to the overriding importance of this process. Exceptions are systems in which evaporite minerals are available for dissolution by groundwater or where human activities are major sources of sulfate or chloride inflow. [Pg.200]

When chlorine dioxide is used for pulp bleaching in conjunction with the Kraft (sulfide) process for chemical pulping, by-product sodium sulfate can be used as a source of makeup sulfur and sodium consumed in the chemical cycle. The demand for sodium and sulfur in pulp bleaching is related to the loss of these chemicals through carryover in unbleached pulp. As process improvements have sought to reduce pollution from pulp mills, less sodium sulfate makeup is required. The trends in pulp bleaching to increase substitution of chlorine with chlorine dioxide have caused an oversupply of sodium sulfate, so that this by-product is often regarded as waste (81). [Pg.484]

Environmental Fate. Ammonia combines with sulfate ions in the atmosphere and is washed out by rairtfall, resulting in rapid return of ammonia to the soil and surface waters. Ammonia is a central compound in the environmental cycling of nitrogen. Ammonia in lakes, rivers, and streams is converted to nitrate. [Pg.106]

R. W. FairbriiXjE, Encyclopedia of Geochemistry and Environmental Sciences, Van Nostrand, New York, 1972.. See sections on Geochemical Classification of the Elements Sulfates Sulfate Reduction-Microbial Sulfides Sulfosalts Sulfur Sulfur Cycle Sulfur Isotope Fractionation in Biological Processes, etc., pp. 1123 - 58. [Pg.648]

The most popular form of internal treatment for many years dates from the nineteenth century and is based on a combination of soda ash and caustic. This traditional program, the so-called carbonate-cycle or carbonate treatment, utilizes the addition of sodium carbonate to the BW to deliberately form carbonate sludges that can be removed by BD, rather than permit sulfate scales to develop. If sulfate scales do form in the boiler, the removal process is difficult and very time-consuming, and obviously, boiler operating efficiency will continue to decrease as the sulfate scale increases in thickness. [Pg.413]

Table 10.2 Carbonate-Cycle Program. BW Carbonate Reserve Requirements by Pressure and Sulfate Concentration... Table 10.2 Carbonate-Cycle Program. BW Carbonate Reserve Requirements by Pressure and Sulfate Concentration...

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