SCWO 2016.04.22 

The role of dissolved oxygen in supercritical water in the oxidation of ferritic–martensitic steel
The Journal of Supercritical Fluids, Volume 108, February 2016, Pages 56-60
Zhongliang Zhu, Hong Xu, Dongfang Jiang, Guoqiang Yue, Baorang Li, Naiqiang Zhang
Abstract
To assess the role of dissolved oxygen in supercritical water on the growth processes of oxide scales, a marker experiment of ferritic–martensitic steel was performed by exposing to supercritical water (H216O) containing marked 18O2 at 600 °C under 25 MPa. The oxide scale was analysed by using Secondary Ion Mass Spectrometry (SIMS). The oxygen isotope profile shows that dissolved oxygen and supercritical water react with metals simultaneously. Dissolved oxygen changes the oxidation/reduction potential of supercritical water leading to an increase in the oxidation rate. The oxidation rate increases with increase in dissolved oxygen content in supercritical water. The mechanism of the effect of dissolved oxygen on oxidation is discussed.

Hydrogen production by partial oxidation gasification of a phenol, naphthalene, and acetic acid mixture in supercritical water
International Journal of Hydrogen Energy, Volume 41, Issue 4, 30 January 2016, Pages 2238-2246
Yuzhen Wang, Shuzhong Wang, Gaoyang Zhao, Yanfeng Guo, Yang Guo
Abstract
A mixture of phenol, acetic acid, and naphthalene was partially oxidized in supercritical water in order to produce hydrogen. The effects of temperature, oxidation ratio (OR), reaction time, and reactant concentrations on gaseous distributions, gasification efficiencies, and reactants removal efficiencies were investigated. Furthermore, the effects of oxygen on the main intermediate products were analyzed, and possible degradation pathways were proposed. Results indicated that higher temperatures significantly promoted the H2 yield. In addition, small amounts of oxygen (OR <0.2) accelerated the production of H2 and CH4. The maximum H2 gasification efficiency (240.25%) and H2 yield (70.16 mmol g−1) were obtained at 560 °C, 25 MPa, reaction time of 20 s and OR of 0.2. Longer reaction time enhanced the gasification efficiencies in 10 s, while the effect was little when reaction times longer than 10 s. The concentrations of the reactants did not significantly influence the gasification efficiencies.

Supercritical water oxidation of a model fecal sludge without the use of a co-fuel
Chemosphere, Volume 141, December 2015, Pages 189-196
A. Miller, R. Espanani, A. Junker, D. Hendry, N. Wilkinson, D. Bollinger, J.M. Abelleira-Pereira, M.A. Deshusses, E. Inniss, W. Jacoby
Abstract
A continuous supercritical water oxidation reactor was designed and constructed to investigate the conversion of a feces simulant without the use of a co-fuel. The maximum reactor temperature and waste conversion was determined as a function of stoichiometric excess of oxygen in order to determine factor levels for subsequent investigation. 48% oxygen excess showed the highest temperature with full conversion. Factorial analysis was then used to determine the effects of feed concentration, oxygen excess, inlet temperature, and operating pressure on the increase in the temperature of the reacting fluid as well as a newly defined non-dimensional number, NJa representing heat transfer efficiency. Operating pressure and stoichiometric excess oxygen were found to have the most significant impacts on NJa. Feed concentration had a significant impact on fluid temperature increase showing an average difference of 46.4 °C between the factorial levels.

Salt deposition problems in supercritical water oxidation
Chemical Engineering Journal, Volume 279, 1 November 2015, Pages 1010-1022
Donghai Xu, Chuanbao Huang, Shuzhong Wang, Guike Lin, Yang Guo
Abstract
The cooled wall reactor has been modified by adding an additional upper outlet of products at 500–700 °C to improve energy recovery and make possible energy generation with the supercritical water oxidation of different waste. Experimental and modeling results of the performance of this new reactor configuration are presented as well as a theoretical analysis of the energy recovery of the reactor compared to other supercritical water oxidation reactors. Different flow distributions were tested to find the best elimination conditions. Total organic carbon removal over 99.99% was obtained at room injection temperatures, when the fraction of products leaving the reactor in the upper effluent is lower than 70% of feed flow. The performance of the reactor was tested with the oxidation of a recalcitrant compound such as ammonia. Removals higher than 99% of were achieved at temperatures near 700 °C. The behavior of the reactor working with feeds with up to 2.5% wt Na2SO4 could be injected in the reactor without plugging problems. Upper effluent always presented a concentration of salt lower than 30 ppm. Theoretical energetic analysis shows that the performance of this reactor is superior to other designs obtaining a maximum power efficiency of 27% (0.339 kW/kg-feed).

Supercritical water oxidation for energy production by hydrothermal flame as internal heat source. Experimental results and energetic study
Energy, Volume 90, Part 2, October 2015, Pages 1584-1594
Pablo Cabeza, Joao Paulo Silva Queiroz, Manuel Criado, Cristina Jiménez, Maria Dolores Bermejo, Fidel Mato, Maria Jose Cocero
Abstract
The cooled wall reactor has been modified by adding an additional upper outlet of products at 500–700 °C to improve energy recovery and make possible energy generation with the supercritical water oxidation of different waste. Experimental and modeling results of the performance of this new reactor configuration are presented as well as a theoretical analysis of the energy recovery of the reactor compared to other supercritical water oxidation reactors. Different flow distributions were tested to find the best elimination conditions. Total organic carbon removal over 99.99% was obtained at room injection temperatures, when the fraction of products leaving the reactor in the upper effluent is lower than 70% of feed flow. The performance of the reactor was tested with the oxidation of a recalcitrant compound such as ammonia. Removals higher than 99% of were achieved at temperatures near 700 °C. The behavior of the reactor working with feeds with up to 2.5% wt Na2SO4 could be injected in the reactor without plugging problems. Upper effluent always presented a concentration of salt lower than 30 ppm. Theoretical energetic analysis shows that the performance of this reactor is superior to other designs obtaining a maximum power efficiency of 27% (0.339 kW/kg-feed).

Study on catalytic and non-catalytic supercritical water oxidation of p-nitrophenol wastewater
Chemical Engineering Journal, Volume 277, 1 October 2015, Pages 30-39
Xiuqin Dong, Zhongdong Gan, Xianlin Lu, Wenzhu Jin, Yingzhe Yu, Minhua Zhang
Abstract
Catalytic and non-catalytic supercritical water oxidation of p-nitrophenol contained in wastewater was performed using compressed air and hydrogen peroxide as an oxidant, respectively. In catalytic process, the supported Mn2O3/Ti-Al oxide composite catalyst was employed to accelerate the reaction rate. Experiments were conducted to investigate the effect of temperature, pressure, oxygen excess or dosage of hydrogen peroxide and residence time on the destruction of p-nitrophenol. Appropriate reaction conditions were obtained for both processes. Based on the products generated in reaction, possible reaction pathways were speculated. A possible mechanism was also proposed for the catalytic process according to the experiments focused on the crystal structure transformation in catalyst MnO2. The comparison of the two processes indicated that hydrogen peroxide is a better oxidant without its cost taken into consideration, and the reaction rate of catalytic process is much higher than that in non-catalytic process in spite of the better oxidant used in it.

Partial oxidation of landfill leachate in supercritical water: Optimization by response surface methodology
Waste Management, Volume 43, September 2015, Pages 343-352
Yanmeng Gong, Shuzhong Wang, Haidong Xu, Yang Guo, Xingying Tang
Abstract
To achieve the maximum H2 yield (GYH2), TOC removal rate (TRE) and carbon recovery rate (CR), response surface methodology was applied to optimize the process parameters for supercritical water partial oxidation (SWPO) of landfill leachate in a batch reactor. Quadratic polynomial models for GYH2, CR and TRE were established with Box–Behnken design. GYH2, CR and TRE reached up to 14.32 mmol·gTOC−1, 82.54% and 94.56% under optimum conditions, respectively. TRE was invariably above 91.87%. In contrast, TC removal rate (TR) only changed from 8.76% to 32.98%. Furthermore, carbonate and bicarbonate were the most abundant carbonaceous substances in product, whereas CO2 and H2 were the most abundant gaseous products. As a product of nitrogen-containing organics, NH3 has an important effect on gas composition. The carbon balance cannot be reached duo to the formation of tar and char. CR increased with the increase of temperature and oxidation coefficient.

Characterization of cerium dioxide nanoparticles prepared by supercritical water oxidation
Ceramics International, Volume 41, Issue 8, September 2015, Pages 10170-10176
Hongxu Li, Chao Li, Chuanqi Jiao, Shuai Wang
Abstract
CeO2 nanoparticles with high purity and crystallinity were prepared by a continuous supercritical water oxidation (SCWO) reaction. The phase composition, microstructure, and morphology of the prepared CeO2 particles were characterized by X-Ray diffraction (XRD), field emission scanning electron microscope (FE-SEM), BET specific surface area (BET), and X-ray photoelectron spectroscopy (XPS). The size distribution of the particles is narrow with an average particle size between 10 and 13 nm; the diameter decreased gradually as the Ce(NO3)3·6H2O concentration in the preparation increased. The BET results show an increase in the products׳ specific surface area as the Ce(NO3)3·6H2O concentration increased, with an average surface area of 48 m2 g−1. SEM micrographs reveal that the CeO2 particles are spherical, and that higher Ce(NO3)3·6H2O concentrations are conducive to the formation of smaller particles. However, excess Ce(NO3)3·6H2O caused serious agglomeration, due to the higher surface energy. XPS patterns indicate that Ce(III) was almost completely oxidized to Ce(IV) in the reaction, and that the binding capacity of Ce–O reduced gradually with increasing concentrations of Ce(NO3)3.

Hydrolysis and oxidation of sodium toluene sulfonate in sub-/supercritical water in the presence of CO2 or H2O2
The Journal of Supercritical Fluids, Volume 107, January 2016, Pages 61-68
Hassan S. Ghaziaskar, Jalal Razavizade, Khosrow F. Zare
Abstract
The hydrolysis of sodium toluene sulfonate (STS) in sub-/supercritical water in the presence of CO2 was investigated using a continuous flow system at the constant pressure of 250 bar. The effect of water flow-rates, reaction temperature and CO2 flow-rates on the hydrolysis of STS was investigated. Results showed that hydrolysis of STS increases with the increase in temperature and CO2 flow rate. The optimum reaction conditions calculated by partial factorial design were 452 °C, water flow rate of 2.3 mL min−1 and CO2 flow rate of 0.08 mL min−1. Furthermore, supercritical water was used for total removal of STS from industrial wastewater using H2O2 as an oxidant. Results showed that at temperatures higher than 350 °C more than 99% of STS is oxidized while COD remains high until reaction temperature of 450 °C after which COD of solution diminished 81%.

The oxidation resistance of thermo-mechanically processed Incoloy 800HT in supercritical water
The Journal of Supercritical Fluids, Volume 101, June 2015, Pages 150-160
Hamed Akhiani, Majid Nezakat, Sami Penttilä, Jerzy Szpunar
Abstract
In this study, we evaluate the oxidation behavior of Incoloy 800HT with a view to its feasible application in the Gen IV supercritical water-cooled reactor. To evaluate the role of microstructure, we implement a specific thermo-mechanical treatment to process Incoloy 800HT. The processed samples were exposed to supercritical water for 100, 300 and 1000 h. We found that the thermo-mechanical processing not only improves the oxidation resistance, but also alleviates the oxide scale spallation. The results demonstrated that in compare with texture, grain size has stronger effect on the oxidation resistance of Incoloy 800HT in supercritical water.

A new system design for supercritical water oxidation
Chemical Engineering Journal, Volume 269, 1 June 2015, Pages 343-351
Zhong Chen, Guangwei Wang, Fengjun Yin, Hongzhen Chen, Yuanjian Xu
Abstract
As the main obstacles for the industrialization of supercritical water oxidation (SCWO) technology, corrosion and plugging are mostly occurring in the high pressure high temperature (HPHT) sections, including preheater, reactor, heat exchanger and cooler. In this paper, a lab-scale SCWO system based on dynamic gas seal wall reactor (DGSWR) has been described, tested and discussed in detail. The results showed that the preheating problems of waste with high solid content has been solved and the “gas seal” of DGSWR has been successfully verified under 28–29 MPa and around 400 °C. Sewage sludge with 2.62–11.78% dry solid has been degraded and the COD removal efficiency can reach up to 99.15%. However, the solid particle sedimentation was only partly achieved. According to the results analysis, based on the Stokes’ Law, both small particle size and counter-current of upward reaction medium and downward solids are responsible. Future improvements for the SCWO system were also discussed at the end of this article.

The treatment of landfill leachate over Ni/Al2O3 by supercritical water oxidation
The Journal of Supercritical Fluids, Volume 100, May 2015, Pages 7-14
Ferda Civan, Demet H. Özaltun, Ekin Kıpçak, Mesut Akgün
Abstract
This study presents the findings of our research regarding the catalytic treatment of landfill leachate over Ni/Al2O3 by supercritical water oxidation. Hydrogen peroxide was used as the oxygen source. The experiments were carried out at a constant pressure of 25 MPa, in the temperature range of 400–600 °C and the reaction time range of 30–150 s. The effects of temperature, reaction time, pressure, catalyst and oxidant use on the total organic carbon and total nitrogen contents of the liquid effluents were examined. As a result, it was seen that supercritical water oxidation was a very effective method for the treatment of landfill leachate. Treatment efficiencies up to 98.2% in terms of total organic carbon conversion were obtained. However nitrogen removal achieved about 57% in terms of total nitrogen conversion.

Partial oxidation of n-hexadecane through decomposition of hydrogen peroxide in supercritical water
Chemical Engineering Research and Design, Volume 93, January 2015, Pages 565-575
Y.M. Alshammari, K. Hellgardt
Abstract
This work reports the experimental analysis of partial oxidation of n-hexadecane under supercritical water conditions. A novel reactor flow system was developed which allows for total decomposition of hydrogen peroxide in a separate reactor followed partial oxidation of n-hexadecane in a gasification reactor instead of having both reactions in one reactor. The kinetics of hydrothermal decomposition of hydrogen peroxide was studied in order to confirm its full conversion into water and oxygen under the desired partial oxidation conditions, and the kinetic data were found in a good agreement with previously reported literature. The gas yield and gasification efficiency were investigated under different operating parameters. Furthermore, the profile of CC/CC ratio was studied which showed the favourable conditions for maximising yields of n-alkanes via hydrogenation of their corresponding 1-alkenes. Enhanced hydrogenation of 1-alkenes was observed at higher O/C ratios and higher residence times, shown by the increase in the CC/CC ratio to more than unity, while increasing the temperature has shown much less effect on the CC/CC ratio at the current experimental conditions. In addition, GC–MS analysis of liquid samples revealed the formation of heavy oxygenated compounds which may suggest a new addition reaction to account for their formation under the current experimental conditions. Results show new promising routes for hydrogen production with in situ hydrogenation of heavy hydrocarbons in a supercritical water reactor.

Supercritical water oxidation of a pesticide wastewater
Chemical Engineering Research and Design, Volume 94, February 2015, Pages 396-406
Donghai Xu, Shuzhong Wang, Jie Zhang, Xingying Tang, Yang Guo, Chuanbao Huang
Abstract
In this research, we studied supercritical water oxidation (SCWO) of a pesticide wastewater under a wide range of operation conditions in two reaction plants. The results show that reaction temperature, oxidant coefficient (OC), and residence time (t) can improve the wastewater XCOD (removal efficiency of chemical oxygen demand). The residence time and OC have important influences on XCOD at higher reaction temperatures (>500 °C). It is significant to increase the preheating rate for the XCOD improvement of the pesticide wastewater in SCWO. XCOD and XTN (removal efficiency of total nitrogen) are 99.42% and 86.70% at 600 °C, 25 MPa, OC = 3.0 and t = 2.0 min, respectively. More than 92 wt% total organic carbon (TOC) and 86.70 wt% total nitrogen in the wastewater are converted into CO2 and N2 under the above conditions, respectively. Inconel 625 can be used as the reactor material in the wastewater SCWO plant, and its corrosion rate is approximately 0.6 mm/year at 600 °C, 25 MPa and OC = 3.0 conditions. We also primarily design a 100 t/d SCWO plant for the tested pesticide wastewater treatment on the basis of accomplished investigations. SCWO together with traditional wastewater treatment methods is proposed to harmlessly dispose the complicated wastewater. This information is valuable for guiding the large-scale SCWO plant design for pesticide wastewater treatment.

Supercritical water oxidation with hydrothermal flame as internal heat source: Efficient and clean energy production from waste
The Journal of Supercritical Fluids, Volume 96, January 2015, Pages 103-113
J.P.S. Queiroz, M.D. Bermejo, F. Mato, M.J. Cocero
Abstract
Supercritical water oxidation (SCWO) has the potential to be considered a clean energy generation process, as the process effluent is a high temperature, high pressure stream with a high enthalpy content that can be converted to heat and shaft work. In this work the state of the art of SCWO has been reviewed, focusing on energy production. For the description of thermodynamic and transport properties, there are some methods recommended for pure substances, but the applicability of those methods for mixtures at supercritical state is yet not clear. Most of the work found in literature use cubic equations of state and linear mixing rules. The design of reactors has evolved in order to reduce the drawbacks of corrosion and salt deposition, in general, through the dilution of reaction products. In order to make the process profitable energetically different strategies must be used to keep the products at the highest temperature without compromising the safety, and the hydrothermal flames if correctly stabilized are a good choice. Reactors and reaction systems able to process feeds consisting of suspension with high inorganic contents without diluting the effluent reducing its temperature must be developed. On the other hand, the systems of energy recovery must be improved, especially the expanders, in order to recover the pressure work as well as the thermal energy. Modeling tools can help in both aspects. But for developing good models a good comprehension of thermal and transport properties of mixtures at supercritical state, as well as oxidation kinetics under that condition are essential data that must be further investigated in order to find energetically efficient processes.

Synthesis of manganese oxide microparticles using supercritical water
The Journal of Supercritical Fluids, Volume 112, June 2016, Pages 114-118
Minsoo Kim, Seung-Ah Hong, Naechul Shin, Keun Hwa Chae, Hong-shik Lee, Sun Choi, Youhwan Shin
Abstract
Manganese compounds of different oxidation states such as MnO2, MnCO3 Mn2O3, and a mixture of MnO + Mn3O4 were synthesized using supercritical water (SCW) and calcination process. The X-ray Diffraction (XRD) patterns confirmed that the use of glycerol as a reducing agent in SCW process was successful in preventing oxidation of manganese products. Scanning electron microscopy (SEM) images of the manganese products showed micro-sized particles with different morphology depending on the product. The simple two step synthesis procedure described in this paper allows easy control of manganese oxidation states with direct applicability in large scale production on an industrial level.

Catalytic cracking of heavy petroleum residue in supercritical water: Study on the effect of different metal oxide nanoparticles
The Journal of Supercritical Fluids, Volume 113, July 2016, Pages 136-143
Morteza Golmohammadi, Seyed Javad Ahmadi, Jafar Towfighi
Abstract
Cracking of heavy petroleum residue obtained from the vacuum distillation unit in supercritical water (SCW) was performed with and without catalysts. First, different nanoparticles, including CeO2, Co3O4, and MnO2 were synthesized in a batchwise SCW reactor; then, the abilities of aforementioned nanocatalysts to convert vacuum residue (VR) into the lighter fractions as well as their stability under severe condition of supercritical water were examined. The X-ray diffractometery (XRD) and transmission electron microscopy (TEM) images indicated that the obtained nanoparticles with a satisfactory size and morphology were synthesized under supercritical condition. VR cracking experiments were also conducted in a batchwise reactor under operating condition, namely temperature: 450 °C, reaction time: 60 min, catalyst/oil ratio (g/g): 1/5, and water/oil ratio (g/g): 80/3. The performance of different nanocatalysts was compared based on the yield of maltene, coke, and asphaltene obtained from VR cracking. As a result, it was determined that the efficiency of nanocatalysts in VR cracking diminishes in the order of CeO2 > Co3O4 > MnO2, while the non-catalytic cracking or SCW pyrolysis attained the lowest rank with a slight difference with the case of MnO2. Moreover, the XRD was utilized to investigate the stability of different catalysts. The results demonstrated that only CeO2 was stable, whereas the other catalysts were reduced to the lower oxidation states during the reaction. Nevertheless, the scanning electron microscopy (SEM) image and the Brunauer–Emmett–Teller (BET) surface area of spent CeO2 showed the agglomeration of nanoparticles after the reaction.

Turnover rates for the supercritical water reforming of glycerol on supported Ni and Ru catalysts
Fuel, Volume 180, 15 September 2016, Pages 417-423
F.J. Gutiérrez Ortiz, F.J. Campanario, P. Ollero
Abstract
Supercritical water reforming (SCWR) of glycerol conversion data to hydrogen are reported as reaction rates, normalized by the number of ostensible catalytic sites (i.e., as turnover rates). The process was studied in a tubular fixed-bed reactor using commercial Ni/Al2O3–SiO2 and Ru/Al2O3 catalysts. The kinetic results were captured as rate equations, and the Arrhenius parameters (pre-exponential factor and apparent activation energy) were obtained. In this way, a quantitative measure of catalytic activity of these catalysts was achieved and can be used as a reference in other studies.

Catalytic supercritical water gasification of plastics with supported RuO2: A potential solution to hydrocarbons–water pollution problem
Process Safety and Environmental Protection, Volume 102, July 2016, Pages 140-149
Jude A. Onwudili, Paul T. Williams
Abstract
Here we report on a potential catalytic process for efficient clean-up of plastic pollution in waters, such as the Great Pacific Garbage Patch (GPGP). Detailed catalytic mechanisms of RuO2 during supercritical water gasification of common polyolefin plastics including low-density polyethylene (LDPE), high-density polyethylene (HDPE), polypropylene (PP) and polystyrene (PP) have been investigated in a batch reactor at 450 °C for 60 min. All four plastics gave very high carbon gasification efficiencies (CGE) and hydrogen gasification efficiencies (HGE). Methane was the highest gas component, with a yield of up to 37 mol kg−1 LDPE using the 20 wt% RuO2 catalyst. Evaluation of the gas yields, CGE and HGE revealed that the conversion of PS involved thermal degradation, steam reforming and methanation; whereas hydrogenolysis was a possible additional mechanism during the conversion of aliphatic plastics. The process has the benefits of producing a clean-pressurized methane-rich fuel gas as well as cleaning up hydrocarbons-polluted waters.

Effects of reaction time and catalyst on gasification of glucose in supercritical water: Detailed reaction pathway and mechanisms
International Journal of Hydrogen Energy, Volume 41, Issue 16, 4 May 2016, Pages 6630-6639
Chao Zhu, Liejin Guo, Hui Jin, Jianbing Huang, Sha Li, Xiaoyan Lian
Abstract
Supercritical water gasification of glucose as a model compound for biomass was conducted in quartz reactors at 500 °C. The concentration of glucose solution was 5 wt.% and the reaction time was adjusted within the range of 10–1800 s. The effects of reaction time and catalyst on the product distribution were investigated and the formation and degradation pathways of intermediate products with and without catalyst were discussed. The results show that the gas yields increased while the yields of organic intermediates in residual liquid decreased with the reaction time. The organic intermediates in residual liquid were mainly composed of phenols, furans, organic acids, alcohols, arenes and ketones. The Ru/Al2O3 catalyst had a significant influence on the gasification of glucose, which promoted the degradation of intermediates to gaseous products, increased the yield of hydrogen and inhibited the formation of char.

Influence of the reactant carbon–hydrogen–oxygen composition on the key products of the direct gasification of dewatered sewage sludge in supercritical water
Bioresource Technology, Volume 208, May 2016, Pages 81-86
Miao Gong, Wei Zhu, Yujie Fan, Huiwen Zhang, Ying Su
Abstract
The supercritical water gasification of ten different types of dewatered sewage sludges was investigated to understand the relationship between sludge properties and gasification products. Experiments were performed in a high-pressure autoclave at 400 °C for 60 min. Results showed that gasification of sewage sludge in supercritical water consists mainly of a gasification reaction, a carbonization reaction and a persistent organic pollutants synthesis reaction. Changes in the reactant C/H/O composition have significant effects on the key gasification products. Total gas production increased with increasing C/H2O of the reactant. The char/coke content increased with increasing C/H ratio of the reactant. A decrease in the C/O ratio of the reactant led to a reduction in polycyclic aromatic hydrocarbon formation. This means that we can adjust the reactant C/H/O composition by adding carbon-, hydrogen-, and oxygen-containing substances such as coal, algae and H2O2 to optimize hydrogen production and to inhibit an undesired by-product formation.

Hydrogen production from lignin, cellulose and waste biomass via supercritical water gasification: Catalyst activity and process optimization study
Energy Conversion and Management, Volume 117, 1 June 2016, Pages 528-537
Kang Kang, Ramin Azargohar, Ajay K. Dalai, Hui Wang
Abstract
Process optimization for catalytic biomass supercritical water gasification process (SCWG) was performed. By catalysts screening using cellulose and lignin as biomass model compounds, K2CO3 and 20Ni0.36Ce/Al2O3 were identified as the best catalysts. Then, an optimization study based on Taguchi experimental design was conducted, and waste biomass including wheat straw, canola meal, and timothy grass were used as feedstock. The effect of different parameters are studied. For these parameters, the order of relative importance for hydrogen production is: temperature > catalyst loading > catalyst type > biomass type. High temperature (∼650 °C), and high catalyst loading (∼100%) are favorable for hydrogen production. The average hydrogen yield using different waste biomass was in the order of: canola meal > wheat straw > timothy grass.

Transpiring wall reactor in supercritical water oxidationReview Article
Chemical Engineering Research and Design, Volume 92, Issue 11, November 2014, Pages 2626-2639
Donghai Xu, Shuzhong Wang, Chuanbao Huang, Xingying Tang, Yang Guo
Abstract
Reactor corrosion and plugging problems have hindered the commercialization of supercritical water oxidation (SCWO) for wastewater purification. The use of transpiring wall reactor (TWR) is an effective means to overcome the above two problems by forming a protective water film on the internal surface of the reactor to aviod contacting corrosive species and precipitated organic salts. This work mainly aims to objectively review experimental investigations and numerical simulation results concerning TWR. Subsequent investigations for parameters optimizations of TWR are also proposed in order to ultimately build effective regulation methods of obtaining excellent water film properties. All this information is very important in guiding the structure design and operation parameters optimization of TWR.

The products of heavy sulfur-rich oil conversion in a counter supercritical water flow and their desulfurization by ZnO nanoparticles
The Journal of Supercritical Fluids, Volume 111, May 2016, Pages 121-128
Oxana N. Fedyaeva, Anatoly A. Vostrikov
Abstract
The conversion of heavy sulfur-rich oil (gross-formula CH1.59N0.01S0.027O0.03) under its continuous supply into a counter supercritical water (SCW) flow and the temperature gradient along the reactor axis (at the top −400 °C and at the bottom −550 °C) at 30 MPa has been studied. The products dissolved in SCW were alternately discharged from the reactor into the samplers through two parallel pipelines, on one of which the cell, heated up to 400 °C and loaded with ZnO nanoparticles, was mounted. Zinc oxide was synthesized during pumping SCW through a layer of zinc shavings at 400 °C, 30 MPa. The yields of volatile and liquid products and conversion residue have been found to be equal to 23.5, 62.8, and 11.9%, respectively, relative to the weight of oil supplied into the reactor. Upon SCW conversion the fraction of asphaltene in the liquid products was found to have decreased from 12 to 1 wt% while the fraction of saturated hydrocarbons increased by 4–5 times as much, compared to crude oil. The composition of the liquid products is defined by means of gas–liquid chromatography, IR and 1H NMR spectroscopy. When reactants were pumped through the cell loaded with ZnO, zinc sulfide was formed as a result of the interaction of S-containing products with ZnO accompanied by near complete removal of H2S, decrease in the S/C atomic ratio in group components of the liquid products and insignificant increase in the O/C atomic ratio and fraction of resin in the liquid products.

Co-oxidation of ammonia and isopropanol in supercritical water in a tubular reactor
Chemical Engineering Research and Design, Volume 92, Issue 11, November 2014, Pages 2568-2574
P. Cabeza, B. Al-Duri, M.D. Bermejo, M.J. Cocero
Abstract
Improvements in the ammonia removal were only appreciated with the lowest IPA/NH3 molar ratios (0.125 and 0.25) while the oxygen ratio did not have significant influence in the ammonia removal. Nevertheless, a direct relation between the nitrate concentration and the oxygen in excess was found. Nitrate concentration was also found to increase when the IPA/ammonia ratio increased.

Oxidation of ferritic and ferritic–martensitic steels in flowing and static supercritical water
Corrosion Science, Volume 103, February 2016, Pages 124-131
Nai-qiang Zhang, Zhong-liang Zhu, Hong Xu, Xue-ping Mao, Ju Li
Abstract
The oxidation of ferritic steel and ferritic–martensitic steel was investigated by exposure to flowing and static supercritical water (SCW) at 550–600 °C. The oxidation kinetic curves follow parabolic and near-cubic rate equations for the samples exposed to flowing and static SCW, respectively. The phase analysis shows the presence of hematite, magnetite and spinel in flowing SCW while only the magnetite and spinel phases are identified in static SCW. The mechanism of the formation of hematite and the effect of the flow state of SCW on the time exponent of oxidation kinetics are discussed.

Polycyclic aromatic hydrocarbon formation from gasification of sewage sludge in supercritical water: The concentration distribution and effect of sludge properties
The Journal of Supercritical Fluids, Volume 113, July 2016, Pages 112-118
Miao Gong, Wei Zhu, Huiwen Zhang, Ying Su, Yujie Fan
Abstract
The changes in the polycyclic aromatic hydrocarbon (PAH) concentration and distribution in 10 different types of raw sewage sludge and gasified residues were investigated, and the effects of the sludge properties and the organic matter composition were determined. The results showed that the concentrations of 2-ring and 6-ring PAHs increased significantly during the gasification process. The PAHs in raw sludge were dominated by 3-ring and 4-ring PAHs, and those after gasification were dominated by 2-ring and 3-ring PAHs. The total PAH concentration increased with the increasing volatile matter content and decreased with the increasing pH value. Phenols have been considered to be important precursors for PAH synthesis. The crude fat and carbohydrate content can promote lower-molecular-weight PAH formation, while lignin and humic substance content can promote higher-molecular-weight PAH formation, which indicates that the organic matter composition in raw sludge has a high impact on the PAH distribution.

Treatment of municipal sewage sludge in supercritical water: A reviewReview Article
Water Research, Volume 89, 1 February 2016, Pages 118-131
Lili Qian, Shuzhong Wang, Donghai Xu, Yang Guo, Xingying Tang, Laisheng Wang
Abstract
With increasing construction of wastewater treatment plants and stricter policies, municipal sewage sludge (MSS) disposal has become a serious problem. Treatment of MSS in supercritical water (SCW) can avoid the pre-drying procedure and secondary pollution of conventional methods. SCW treatment methods can be divided into supercritical water gasification (SCWG), supercritical water partial oxidation (SCWPO) and supercritical water oxidation (SCWO) technologies with increasing amounts of oxidants. Hydrogen-rich gases can be generated from MSS by SCWG or SCWPO technology using oxidants less than stoichiometric ratio while organic compounds can be completely degraded by SCWO technology with using an oxidant excess. For SCWG and SCWPO technologies, this paper reviews the influences of different process variables (MSS properties, moisture content, temperature, oxidant amount and catalysts) on the production of gases. For SCWO technology, this paper reviews research regarding the removal of organics with or without hydrothermal flames and the changes in heavy metal speciation and risk. Finally, typical systems for handling MSS are summarized and research needs and challenges are proposed.

Study of transpiring fluid dynamics in supercritical water oxidation using a transparent reactor
The Journal of Supercritical Fluids, Volume 88, April 2014, Pages 117-125
Zhong Chen, Guangwei Wang, Zakaria. A. Mirza, Shu Yang, Yuanjian Xu
Abstract
The transpiring wall reactor (TWR) is considered to be one of the most promising reactors because it minimizes both corrosion and salt precipitation problems that seriously hinder the industrialization of supercritical water oxidation technologies. A transparent reactor is built to study the fluid dynamics of transpiring flow, which are the foundation of reactor design and optimization. The results showed that the transpiring flow is anisotropic with respect to the surface of the transpiring wall due to both the static pressure and viscous resistance. Finally, the novel idea of using air as the transpiring fluid instead of water is presented in an attempt to alleviate current TWR problems such as high energy consumption, high volume of pure water consumption, and temperature fluctuation in the reaction area. A series of experiments and theoretical derivations demonstrate that this novel idea is feasible.

Chapter 10 - Oxidation in High-Temperature and Supercritical Water
Supercritical Fluid Science and Technology, Volume 5, 2014, Pages 525-568
Gerd Brunner
Abstract
In this chapter, the application of hydrothermal and supercritical water is discussed for eliminating toxic and dangerous compound by oxidation in an aqueous environment. Oxidation can be carried out as oxidation in a liquid aqueous environment in the temperature range from T = 100–374 °C, as wet air oxidation (WAO), or as oxidation in supercritical water, known as supercritical water oxidation (SCWO), and as oxidation in the so-called “hydrothermal flames.” These oxidation reactions aim at the conversion of the organic compounds to totally oxidized end products or such effluents that can be further treated with conventional wastewater cleaning methods. For some applications, for example, for conversion of methane to methanol, partial oxidation is of interest.
Oxidation in high-temperature and supercritical water refers to the oxidation of organic compounds in water at high temperatures and elevated pressures. It comprises (i) oxidation in a liquid aqueous environment in the temperature range from T = 100–374 °C, known as WAO, since in most cases, air is used as oxidation agent; (ii) oxidation in supercritical water, known as SCWO at temperatures above the critical temperature of water in the range of up to about T = 550 °C; and (iii) the oxidation of organic compounds in water in the so-called “hydrothermal flames” at temperatures higher than T = 1000 °C. All oxidation reactions aim at the conversion of the organic compounds, mostly to totally oxidized end products, but also in some cases as partial oxidation, for the purpose of forming interesting intermediate products. Nevertheless, the main goal of such oxidation processes is the conversion of waste compounds to harmless oxidation products.
In WAO, the oxidation is carried out usually at moderate pressures that can go up to P = 20 MPa, if the temperature needed for the conversion approaches the critical temperature of water. The oxidation is moderately fast and takes about t = 1–3 h for the oxidation reaction. In SCWO, pressures are higher than in WAO, but not necessarily higher than the critical pressure of water. The oxidation reaction is fast and takes typically less than t = 60 s. The special properties of water at supercritical conditions not only make possible to control the reaction via density but also make it necessary to take care of precipitating salts. In hydrothermal flames, pressures are high, typically higher than the critical pressure of water, and the reaction is very fast in the range of t = 1 ms to t = 1 s. In all three cases, corrosion is a major issue.
In this chapter, fundamentals and applications of WAO, SCWO, and hydrothermal flames are described with examples given. Process conditions as derived from basic experiments and process verifications are discussed.

Valorization of horse manure through catalytic supercritical water gasification
Waste Management, In Press, Corrected Proof, Available online 5 April 2016
Sonil Nanda, Ajay K. Dalai, Iskender Gökalp, Janusz A. Kozinski
Abstract
The organic wastes such as lignocellulosic biomass, municipal solid waste, sewage sludge and livestock manure have attracted attention as alternative sources of energy. Cattle manure, a waste generated in surplus amounts from the feedlot, has always been a chief environmental concern. This study is focused on identifying the candidacy of horse manure as a next generation feedstock for biofuel production through supercritical water gasification. The horse manure was gasified in supercritical water to examine the effects of temperature (400–600 °C), biomass-to-water ratio (1:5 and 1:10) and reaction time (15–45 min) at a pressure range of 23–25 MPa. The horse manure and resulting biochar were characterized through carbon-hydrogen-nitrogen-sulfur (CHNS), inductively coupled plasma-mass spectrometry (ICP-MS), thermogravimetric analysis (TGA), Fourier transform infrared (FTIR) spectroscopy, Raman spectroscopy and scanning electron microscopy (SEM). The effects of alkali catalysts such as NaOH, Na2CO3 and K2CO3 at variable concentrations (1–2 wt%) were investigated to maximize the hydrogen yields. Supercritical water gasification of horse manure with 2 wt% Na2CO3 at 600 °C and 1:10 biomass-to-water ratio for 45 min revealed maximum hydrogen yields (5.31 mmol/g), total gas yields (20.8 mmol/g) with greater carbon conversion efficiency (43.1%) and enhanced lower heating value of gas products (2920 kJ/Nm3). The manure-derived biochars generated at temperatures higher than 500 °C also demonstrated higher thermal stability (weight loss <34%) and larger carbon content (>70 wt%) suggesting their application in enhancing soil fertility and carbon sequestration. The results propose that supercritical water gasification could be a proficient remediation technology for horse manure to generate hydrogen-rich gas products.

Experimental study on the operating characteristics of an inner preheating transpiring wall reactor for supercritical water oxidation: Temperature profiles and product properties
Energy, Volume 66, 1 March 2014, Pages 577-587
Fengming Zhang, Chunyan Xu, Yong Zhang, Shouyan Chen, Guifang Chen, Chunyuan Ma
Abstract
A new process to generate multiple thermal fluids by supercritical water oxidation (SCWO) was proposed to enhance oil recovery. An inner preheating transpiring wall reactor for SCWO was designed and tested to avoid plugging in the preheating section. Hot water (400–600 °C) was used as auxiliary heat source to preheat the feed to the reaction temperature. The effect of different operating parameters on the performance of the inner preheating transpiring wall reactor was investigated, and the optimized operating parameters were determined based on temperature profiles and product properties. The reaction temperature is close to 900 °C at an auxiliary heat source flow of 2.79 kg/h, and the auxiliary heat source flow is determined at 6–14 kg/h to avoid the overheating of the reactor. The useful reaction time is used to quantitatively describe the feed degradation efficiency. The outlet concentration of total organic carbon (TOCout) and CO in the effluent gradually decreases with increasing useful reaction time. The useful reaction time needed for complete oxidation of the feed is 10.5 s for the reactor.

Energetic analysis of gasification of biomass by partial oxidation in supercritical water
Chinese Journal of Chemical Engineering, Volume 23, Issue 1, January 2015, Pages 205-212
Qingqing Guan, Chaohai Wei, Xinsheng Chai, Ping Ning, Senlin Tian, Junjie Gu, Qiuling Chen, Rongrong Miao
Abstract
Partial oxidation gasification in supercritical water could produce fuel gases (such as H2, CO and CH4) and significantly reduce the energy consumption. In this work, an energetic model was developed to analyze the partial oxidative gasification of biomass (glucose and lignin) in supercritical water and the related key factors on which gasification under autothermal condition depended upon. The results indicated that the oxidant equivalent ratio (ER) should be over 0.3 as the concern about energy balance but less than 0.6 as the concern about fuel gas production. Feedstocks such as glucose and lignin also had different energy recovery efficiency. For materials which can be efficiently gasified, the partial oxidation might be a way for energy based on the combustion of fuel gases. Aromatic materials such as lignin and coal are more potential since partial oxidation could produce similar amount of fuel gases as direct gasification and offer additional energy. Energy recovered pays a key role to achieve an autothermal process. Keeping heat exchanger efficiency above 80% and heat transfer coefficient below 15 kJ·s− 1 is necessary to maintain the autothermal status. The results also indicated that the biomass loading should be above 15% but under 20% for an autothermal gasification, since the increase of biomass loading could improve the energy supplied but decrease the efficiency of gasification and gaseous yields. In general, some specific conditions exist among different materials.

Treatment of sewage sludge in supercritical water and evaluation of the combined process of supercritical water gasification and oxidation
Bioresource Technology, Volume 176, January 2015, Pages 218-224
Lili Qian, Shuzhong Wang, Donghai Xu, Yang Guo, Xingying Tang, Longfei Wang
Abstract
Influences of temperature and oxidation coefficient (n) on sewage sludge treatment in supercritical water and its corresponding reaction mechanism were studied. Moreover, the combined process of supercritical water gasification (SCWG) and supercritical water oxidation (SCWO) was also investigated. The results show that ammonia nitrogen, phenols and pyridines are main refractory intermediates. The weight of solid products at 873 K and n = 4 is only 3.5 wt.% of the initial weight, which is lower than that after combustion. Volatile organics in solid phase have almost released at 723 K and n = 0. Highest yield of combustible gases was obtained at n = 0, and H2 yield can reach 11.81 mol/kg at 873 K. Furthermore, the combination of SCWG at 723 K and SCWO at 873 K with a total n = 1 is feasible for its good effluent quality and low operation costs.

Deuterium tracing study of unsaturated aliphatics hydrogenation by supercritical water in upgrading heavy oil. Part II: Hydrogen donating capacity of water in the presence of iron(III) oxide nanocatalyst
The Journal of Supercritical Fluids, Volume 110, April 2016, Pages 75-82
Morteza Hosseinpour, Shohreh Fatemi, Seyed Javad Ahmadi
Abstract
This paper is the second part of the vacuum residue (VR) cracking in supercritical water and tracking the chemical behavior of water as the hydrogen donor, using supercritical deuterium oxide (SC-D2O). In this research, hydrogen-donating capacity of water is enhanced and investigated by using heterogeneous catalyst of silica-supported iron oxide nanoparticles. Upgrading process in the absence of catalyst has been reported at Part I, where a simple comparative index, namely Hrel, was introduced in order to determine the hydrogen contribution capacity of SC-H2O versus hydrocarbons through hydrogenation of unsaturated compounds. Hexane soluble fraction (maltene) of the product was analyzed by attenuated total reflectance infrared (ATR-IR)spectroscopy, and it has revealed more than two fold increase in contribution of hydrogen of water (Hrel = 35%) in catalytic cracking with lower coke (8.4 wt%) formation, compared with non-catalytic cracking (Hrel = 16%) with 18.9 wt% of coke yield. In addition, gas chromatography analysis coupled with mass spectroscopy (GC–MS) has revealed higher fractions of n-alkane in maltene produced from catalytic cracking compared with non-catalytic process. The average physical properties of the prepared maltene such as molecular weight, density and viscosity were calculated by Aspen Plus@ engineering software and they were predicted as: 87.1 g/mol, 0.69 g/ml and 0.33 cp, respectively, for the catalytic cracking, versus; 105.54 g/mol, 0.70 g/ml and 0.47 cp in non-catalytic process. The results indicate that nano iron oxide catalyst is effective towards hydrogenation of the unsaturated fragments in VR cracking by supercritical water, with less coke formation.

Sub- and supercritical water hydrolysis of agricultural and food industry residues for the production of fermentable sugars: A reviewReview Article
Food and Bioproducts Processing, Volume 98, April 2016, Pages 95-123
Juliana M. Prado, Daniel Lachos-Perez, Tânia Forster-Carneiro, Mauricio A. Rostagno
Abstract
Bioethanol has been researched as a potential alternative to substitute liquid fossil fuels due to its eco-friendly characteristics and relatively low production cost when compared to other bio-based fuels. First generation bioethanol is produced from raw materials rich in simple sugars or starch, such as sugarcane and corn, which are food sources. To avoid the fuel versus food dilemma, second generation bioethanol aims at using non-edible raw materials, as lignocellulosic agricultural residues, as source of fermentable sugars. Hydrolysis with sub/supercritical water has demonstrated great potential to decompose the lignocellulosic complex into simple sugars with several advantages over conventional processes. This review provides an overview of the state of the art on hydrolysis with sub- and supercritical water in the context of the reuse of agricultural residues to produce suitable fermentation substrates for the production of second generation bioethanol. Recent applications and advances are put into context together, providing an insight into future research trends.

Chapter 9 - Supercritical Water Oxidation for Wastewater Destruction with Energy Recovery
Supercritical Fluid Technology for Energy and Environmental Applications, 2014, Pages 181-190
Violeta Vadillo, Jezabel Sánchez-Oneto, Juan R. Portela, Enrique J. Martínez de la Ossa
Abstract
Supercritical water oxidation (SCWO) is a promising technology that respecting the environment destroys wastes definitely and allows an energy recovery. This process has been applied to many model compounds and real wastewaters at laboratory scale. However SCWO treatments at pilot plant scale of real wastewaters are much more limited in literature. Furthermore, the application of this technology to industrial wastewaters has some drawbacks as corrosion, salt deposition, management of biphasic wastes, presence of suspended solids and high costs, so nowadays the industrial scale-up is scarce and it is being delayed. As an attempt to reduce process costs, energy recovery from the effluent of the reactor has been studied by several authors. In this chapter, the main aspects of the SCWO are briefly described and the studies regarding energy recovery are summarized.

Supercritical water oxidation of polyvinyl alcohol and desizing wastewater: Influence of NaOH on the organic decomposition
Journal of Environmental Sciences, Volume 25, Issue 8, 1 August 2013, Pages 1583-1591
Jie Zhang, Shuzhong Wang, Yang Guo, Donghai Xu, Yanmeng Gong, Xingying Tang
Abstract
Polyvinyl alcohol is a refractory compound widely used in industry. Here we report supercritical water oxidation of polyvinyl alcohol solution and desizing wastewater with and without sodium hydroxide addition. However, it is difficult to implement complete degradation of organics even though polyvinyl alcohol can readily crack under supercritical water treatment. Sodium hydroxide had a significant catalytic effect during the supercritical water oxidation of polyvinyl alcohol. It appears that the OH− ion participated in the C–C bond cleavage of polyvinyl alcohol molecules, the CO2-capture reaction and the neutralization of intermediate organic acids, promoting the overall reactions moving in the forward direction. Acetaldehyde was a typical intermediate product during reaction. For supercritical water oxidation of desizing wastewater, a high destruction rate (98.25%) based on total organic carbon was achieved. In addition, cases where initial wastewater was alkaline were favorable for supercritical water oxidation treatment, but salt precipitation and blockage issues arising during the process need to be taken into account seriously.

Mechanism of glucose conversion in supercritical water by DFT study
Journal of Analytical and Applied Pyrolysis, In Press, Corrected Proof, Available online 15 March 2016
Yayun Zhang, Chao Liu, Xi Chen
Abstract
Using density function theory (DFT) simulations with B3LYP/AGU-cc-pVDZ level of theory, six chemical reaction pathways of glucose decomposition in supercritical water were proposed to explore the formation mechanism of some main outcomes (levoglucosan, 5-hydroxymethylfurfural, hydroxylacetaldehyde, erythrose, glyceraldehyde and fructose). In addition, seven potential dehydration ways in glucose were investigated with and without the assistance of water molecule. All dehydration reactions are accelerated when water molecules take part in the reaction, because it can effectively lower the energy barrier of dehydration reaction. In supercritical water surrounding with assistant of water molecule, pathways 3 and 4 are preferred routes of glucose conversion to hydroxylacetaldehyde and erythrose with the lowest energy barrier of 127 kJ/mol. While a higher energy barrier (163 kJ/mol) is required to form glyceraldehyde and fructose in pathways 5 and 6. Levoglucosan and 5-hydroxymethylfurfural are hard to generate during this chemical processes because of their higher energy barrier without water participating in. It seems like that water molecule acts as a magic catalyst that can transfer hydrogen atom in dehydrations, keto-enol tautomerization and structure rearrangement, which reducing the distance of hydrogen atom moving, result in reducing these reactions energy barriers dramatically. The computational results open a window to produce hydroxylacetaldehyde and erythrose in theory. Moreover, it sheds some light on the various proportions of different products in conversion of glucose in supercritical water, as well as suggesting concrete reaction pathways to form these main products, contributing to the elaboration of the mechanism of glucose conversion and cellulose decomposition from a molecule level.

Hydrogen production by non-catalytic partial oxidation of coal in supercritical water: Explore the way to complete gasification of lignite and bituminous coal
International Journal of Hydrogen Energy, Volume 38, Issue 29, 30 September 2013, Pages 12786-12794
Zhiwei Ge, Simao Guo, Liejin Guo, Changqing Cao, Xiaohui Su, Hui Jin
Abstract
Supercritical water gasification (SCWG) of coal is a promising technology for clean coal utilization. In this paper, hydrogen production by non-catalytic partial oxidation of coal was systematically investigated in supercritical water (SCW) with quartz batch reactors for the first time. The influences of the main operating parameters including residence time, temperature, oxidant equivalent ratio (ER) and feed concentration on the gasification characteristics of coal were investigated. The experimental results showed that H2 yield and carbon gasification efficiency (CE) increased with increasing temperature and decreasing feed concentration. CE increased with increasing ER, and H2 yield peaked when ER equaled 0.1. CE increased quickly within 1 min and then tended to be stable between 2 and 3 min. In particular, complete gasification of lignite was obtained at 950 °C when ER equaled 0.1, as for bituminous coal, at a higher temperature of 980 °C when ER equaled 0.2.

The use of dimensionless groups to analyse the mixing of streams with large density differences in sub- and supercritical water
Chemical Engineering Journal, Volume 287, 1 March 2016, Pages 350-358
Duncan Housley, Thomas Huddle, Edward Lester, Martyn Poliakoff
Abstract
As water approaches supercritical conditions, it undergoes sharp changes in density, dielectrics, surface tension and viscosity. Thus, the mixing of supercritical and sub-critical water streams can be potentially impacted by the vast differences in the properties of each fluid.
The reactor configurations employed have been characterised using previously reported experimental techniques for assessing the mixing performance in systems with large density gradients. The results obtained have been used to construct a model framework characterised by the turbulence, relative stream momenta and relative buoyancy of the different streams. This has been applied to rationalise the observed reaction outcomes.
The results in this paper demonstrate the need for caution when comparing sets of data from supercritical water reactors, undertaken with differing reactor geometries.

Catalytic gasification of lignite in supercritical water with Ru/CeO2–ZrO2
International Journal of Hydrogen Energy, Volume 41, Issue 8, 2 March 2016, Pages 4579-4591
Jiangdong Yu, Xiuyun Lu, Yunjie Shi, Qiuling Chen, Qingqing Guan, Ping Ning, Senlin Tian, Junjie Gu
Abstract
A series of CeO2–ZrO2 (CZ) supported Ru catalysts were prepared and employed to catalytic gasification of lignite in supercritical water (SCW). The influences of Ru content, catalyst loading, reaction temperature and feed concentration on gasification of lignite were investigated. Results indicated that Ru2/CZ shows high activity for gasification of lignite and hydrogen production. At 500 °C and 17 min with a 2 wt% loading of lignite and a 2 g/g catalyst loading, carbon gasification efficiency about 86% has been achieved and the highest H2 yield (29.24 mol/kg) has been produced, representing nearly 21-fold enhancement of yield compared to that in the noncatalytic case. The kinetic study in terms of overall reaction rate was investigated and the activation energy Ea is 130 ± 26 kJ/mol. Furthermore, catalyst recycling experiments were conducted in order to evaluate the stability of Ru2/CZ catalyst. The results and XPS data indicate that ZrO2 enhance the stability of the catalyst. Thus, the Ru2/CZ catalyst seems to be a promising material for SCWG of lignite for gas fuels, especially for hydrogen.

Non-isothermal conversion of the Kashpir sulfur-rich oil shale in a supercritical water flow
The Journal of Supercritical Fluids, Volume 109, March 2016, Pages 157-165
Oxana N. Fedyaeva, Vladimir R. Antipenko, Dmitriy Yu. Dubov, Tatyana V. Kruglyakova, Anatoly A. Vostrikov
Abstract
The conversion of the Kashpir oil shale (gross-formula CH1.48N0.01S0.10O0.24) in a flow of water vapor and supercritical water at uniform increase in temperature (dT/dt = 1 °C/min) from 300 to 550 °C has been studied. Temperature dependences of the yields of the volatile and liquid products and their component and elemental compositions have been determined. The total yields of the volatile and liquid products and the conversion residue formed during the experiment have been found to be equal to 404.8, 383.8, and 543.0 mg/gC, respectively. The maximum yield of the volatile products, containing H2S, CO2, H2, and CH4 as major components, is observed at 300–360 °C. A high yield of these compounds is brought about by the redox reactions of oil shale organic matter and mineral components with water. The maximum yield of the liquid products is observed at 360–390 °C, the oil fraction in their composition increasing from 57% to 78% along with increase in temperature. The composition of the liquid products is defined by means of IR and 1H NMR spectroscopy. A new approach to the problem of the Kashpir oil shale processing in SCW in order to obtain the desired S-containing products is discussed.

Catalytic bitumen cracking in sub- and supercritical water
Fuel Processing Technology, Volume 142, February 2016, Pages 315-318
Xi-Kun Gai, Hiroyuki Arano, Peng Lu, Jian-Wei Mao, Yoshiharu Yoneyama, Cheng-Xue Lu, Rui-Qin Yang, Noritatsu Tsubaki
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Production of methane and hydrogen via supercritical water gasification of renewable glucose at a relatively low temperature: Effects of metal catalysts and supportsOriginal Research Article
Fuel Processing Technology, Volume 143, March 2016, Pages 27-34
Izad Behnia, Zhongshun Yuan, Paul Charpentier, Chunbao (Charles) Xu
Abstract
The activities of various supported catalysts were tested in a continuous flow reactor for production of CH4 and H2 from glucose via supercritical water gasification (SCWG) at a relatively low temperature (500 °C). Based on this preliminary study, among all catalysts tested in this study Ni20%Ru2%/γ-Al2O3 catalyst was found to be the most active, achieving complete conversion of all carbon in glucose at 500 °C and a weight-hourly space velocity (WHSV) of 3 h− 1. The addition of 2% Ru to Ni20%/γ-Al2O3 not only suppressed char/tar formation, promoted the carbon gasification efficiently, but also increased methane formation. Moreover, high stability of Ni20%Ru2%/γ-Al2O3 catalyst was demonstrated in the experimental runs for 20 h on-stream. The roles of ruthenium as a co-catalyst in Ni/Al2O3 were found to be not only increasing nickel dispersion, enhancing nickel's reducibility, but also preventing leaching of Al and Ni metals in SCW. However, NiRu supported on either TiO2 and activated carbon led to lower catalytic activity and frequent plugging after only 3 h on-stream.

Supercritical water reforming of glycerol: Performance of Ru and Ni catalysts on Al2O3 support
Energy, Volume 96, 1 February 2016, Pages 561-568
F.J. Gutiérrez Ortiz, F.J. Campanario, P.G. Aguilera, P. Ollero
Abstract
Supercritical water reforming of glycerol was studied in a tubular fixed-bed reactor using a Ru/Al2O3 catalyst, and was compared with our previous study using a Ni-based catalyst, with the aim of enhancing the performance of a global process designed under energy self-sufficient conditions. Relatively high glycerol concentrations of up to 25 wt.% and temperatures from 500 to 800 °C were tested. Glycerol conversion was very high (>99%) at temperatures of 600 °C and above, but low at 500 and 550 °C (<50%) using the Ru/Al2O3 catalyst. The gas product (dry basis) was mainly CH4 and CO2, while H2 production was quite low, against expectations. Under the same operating conditions, the behavior of the catalysts is quite different as the Ni catalyst promotes H2 production much more than the Ru catalyst. A detailed discussion is provided on our results and those of previous studies using the Ru/Al2O3 catalyst, thus acquiring more insight into the catalyst behavior. The Ru catalyst showed a large increase in its crystalline phase after testing, although the oxidation state of ruthenium did not change.

Catalytic supercritical water gasification of primary paper sludge using a homogeneous and heterogeneous catalyst: Experimental vs thermodynamic equilibrium results
Bioresource Technology, Volume 201, February 2016, Pages 111-120
Jeanne Louw, Cara E. Schwarz, Andries J. Burger
Abstract
H2, CH4, CO and CO2 yields were measured during supercritical water gasification (SCWG) of primary paper waste sludge (PWS) at 450 °C. Comparing these yields with calculated thermodynamic equilibrium values offer an improved understanding of conditions required to produce near-equilibrium yields. Experiments were conducted at different catalyst loads (0–1 g/gPWS) and different reaction times (15–120 min) in a batch reactor, using either K2CO3 or Ni/Al2O3–SiO2 as catalyst. K2CO3 up to 1 g/gPWS increased the H2 yield significantly to 7.5 mol/kgPWS. However, these yields and composition were far from equilibrium values, with carbon efficiency (CE) and energy recovery (ER) of only 29% and 20%, respectively. Addition of 0.5–1 g/gPWS Ni/Al2O3–SiO2 resulted in high H2 and CH4 yields (6.8 and 14.8 mol/kgPWS), CE of 84–90%, ER of 83% and a gas composition relatively close to the equilibrium values (at hold times of 60–120 min).

Effect of oxygenated treatment on corrosion of the whole steam–water system in supercritical power plant
Applied Thermal Engineering, Volume 93, 25 January 2016, Pages 1248-1253
Dongfang Jiang, Hong Xu, Bo Deng, Mengyuan Li, Zhuonan Xiao, Naiqiang Zhang
Abstract
The feedwater chemistry is critical to the overall corrosion and reliability of the fossil fired generating units. The effect of dissolved oxygen on corrosion of carbon steels in feedwater system is analyzed. The corrosion experiments of boiler tube steels in supercritical water containing different dissolved oxygen are carried out. The different effect mechanics of dissolved oxygen on corrosion in different parts of steam–water system are defined. Flow accelerated corrosion in low temperature feedwater system can be controlled by dissolved oxygen, but dissolved oxygen can accelerate failure of boiler tubes at high temperature from three aspects: corrosion rate, crack growth rate of SCC, and evaporating consumption rate of chromium. Considering the corrosion of the whole steam–water system, a more effective feedwater chemistry treatment method is proposed.

A comparative study of oxide scales grown on stainless steel and nickel-based superalloys in ultra-high temperature supercritical water at 800 °C
Corrosion Science, Volume 106, May 2016, Pages 188-207
Yashar Behnamian, Amir Mostafaei, Alireza Kohandehghan, Babak Shalchi Amirkhiz, Dominic Serate, Yifei Sun, Subiao Liu, Ermia Aghaie, Yimin Zeng, Markus Chmielus, Wenyue Zheng, David Guzonas, Weixing Chen, Jing Li Luo
Abstract
This study investigates the oxidation behavior of several stainless steels and nickel-based superalloys exposed to supercritical water at 800 °C for 12 h. Characterization of the resulting oxide layers were conducted using weight change measurements, X-ray diffraction, scanning/transmission electron microscopy, and energy dispersive spectroscopy. Although the exposure time is only 12 h, the thickness of the oxide layers formed was as high as 1 μm, comprising different spinel structures. The influence of alloying elements such as Al, Nb, Mo, Mn and Ti on the corrosion behavior is investigated and possible corrosion mechanisms for each candidate alloy are discussed.

Oxidation of alloys for energy applications in supercritical CO2 and H2O
Corrosion Science, In Press, Corrected Proof, Available online 19 March 2016
Gordon R. Holcomb, Casey Carney, Ömer N. Doğan
Abstract
To facilitate development of supercritical CO2 (sCO2) power plants, a comparison of the oxidation behavior of austenitic stainless steels and Ni-base alloys in sH2O and sCO2 were made. Experiments were conducted at 730 °C/207 bar (sCO2) and 726 °C/208 bar (sH2O). Ni-base alloys in sCO2 did not exhibit much change with pressure. Ni-base alloys in sH2O had an increase in corrosion rate and the log of the parabolic rate constant was proportional to pressure. Fine-grain austenitic stainless steels in sCO2 and sH2O were both less protective with pressure as the dense protective chromia scale was replaced with faster growing Fe-oxide rich scales.

Supercritical water gasification of phenol using a Ru/CeO2 catalyst
Chemical Engineering Journal, Volume 283, 1 January 2016, Pages 358-365
Qingqing Guan, Xiaodian Huang, Jing Liu, Junjie Gu, Rongrong Miao, Qiuling Chen, Ping Ning
Abstract
Phenols are typical aromatic pollutants and major byproducts of non-catalytic gasification and liquefaction processes. In this work, Ru/CeO2 was prepared and used to catalyze phenol gasification in supercritical water. The catalyst improves carbon efficiency by about 90% at the conditions employed: 0.5 g Ru/CeO2/g phenol catalyst loading at 550 °C with a water density of 0.0979 g/cm3 and a 5 wt% loading of phenol relative to water. This represents a more than 10-fold enhancement of carbon efficiency compared to the noncatalytic case, with CH4 as the major gaseous product. GC–MS results show suppressed formation of dimers, such as dibenzofuran and polycyclic aromatic hydrocarbons (PAHs), which may be caused by the hydrogenation activity of Ru/CeO2. Kinetic modeling of the gasification process gives an activation energy of 84.24 ± 22 kJ/mol and an frequency factor (ln A) of 12.5 ± 2.9 for gaseous product formation, compared to 60 ± 17 kJ/mol and 7.53 ± 2.7 for char formation. Ru/CeO2 is stable in supercritical water at temperatures up to 550 °C, suggesting that a Ru/CeO2 supercritical water gasification system may be a promising method for treating phenols.

Hydrothermal conversion of Ulva macro algae in supercritical water
The Journal of Supercritical Fluids, Volume 107, January 2016, Pages 182-188
Y. Graz, S. Bostyn, T. Richard, P. Escot Bocanegra, E. de Bilbao, J. Poirier, I. Gokalp
Abstract
Ulva (Ulva armoricana and Ulva rotundata) are macro algae which are responsible of environmental damages and are a cause of an eutrophication of the water in the French coast (Mediterranean sea, Brittany). In this study, Ulva were gasified in supercritical water in a batch reactor and in Hydrothermal Diamond Anvil Cell apparatus. Experimental conditions evolve between 400 and 550 °C at around 250 bar. Results show that a short time (7 min) in supercritical condition is sufficient to obtain a significant conversion rate. H2 and CH4 concentrations exceed 15 mol.% at high temperature (550 °C) and high algae concentrations are not favorable for H2 production. The solid residue represents between 7 and 20 wt.% of the initial dry material and is mainly constituted of carbon (20 wt.%) and inorganic compounds: salts (KCl, NaCl), CaSO4, SiO2 and CaCO3. The very low dissolved organic carbon (DOC) values of the liquid residue (<0.4 wt.%) confirm the high gasification rates. Thiophenes, pyridines, and pyrazines were detected in the liquid phase. Hydrothermal Diamond Anvil Cell (HDAC) experiments were performed to observe gasification stages at the supercritical state.

The reproducibility of corrosion testing in supercritical water—Results of an international interlaboratory comparison exercise
Corrosion Science, Volume 106, May 2016, Pages 147-156
D. Guzonas, S. Penttilä, W. Cook, W. Zheng, R. Novotny, A. Sáez-Maderuelo, J. Kaneda
Abstract
A major challenge in supercritical water-cooled reactor development is the lack of a consistent alloy database. An international interlaboratory comparison test was organized to study the reproducibility of weight change data obtained for identical alloys under similar conditions in different facilities. This paper presents the test procedures, conditions, results, and additional characterization data. More variation in weight change was observed than expected. The scatter was small within the same laboratory, but large between different laboratories. Much of this variation appears to be attributable to differences in test facilities. The data generally agree on the relative ranking of the corrosion resistance.

Conversion of brown coal continuously supplied into the reactor as coal–water slurry in a supercritical water and water–oxygen mixture
The Journal of Supercritical Fluids, Volume 107, January 2016, Pages 707-714
Anatoly A. Vostrikov, Andrey V. Shishkin, Mikhail Ya. Sokol, Dmitriy Yu. Dubov, Oxana N. Fedyaeva
Abstract
The results of a two-stage conversion of brown coal (gross-formula CH0.96N0.01S0.002O0.31) in supercritical water (SCW) under isobaric conditions (30 MPa) in the vertical tubular reactor of an original configuration are presented. The first stage provides for a continuous supply of coal–water slurry (CWS) into the reactor and discharging of the products with SCW into the demountable samplers. The CWS composition was as follows (weight portions): coal—100, water—125, and starch—2.25. It was found out that when increasing the temperature of coal particles up to 600 °C during their falling down along the reactor axis, the yields of volatile and liquid products were 25.4 and 27.5%, respectively, relative to the weight of organic matter supplied into the reactor. At the second stage of conversion, the SCW/O2 fluid was pumped through a layer of coal particles accumulated at the reactor bottom during the first stage. It was shown that as a result of heat emission during partial oxidation of coal residue, the autothermal conditions for conversion were realized. The yields of volatile combustible and liquid products at conversion in the SCW/O2 fluid were 25.1 and 3.4 wt.%, respectively. The increment of hydrogen in the conversion products caused by water decomposition was equal to 20% relative to the weight of hydrogen in initial coal.

Effect of supercritical water on the stability of WOX/TiO2 and NbOX/TiO2 catalysts during glycerol dehydration
The Journal of Supercritical Fluids, Volume 113, July 2016, Pages 158-165
Makoto Akizuki, Keiji Sano, Yoshito Oshima
Abstract
The catalytic stabilities of WOX/TiO2 (WTi) and NbOX/TiO2 (NbTi) during glycerol dehydration in 400 °C supercritical water at 25 MPa and 33 MPa were investigated. The effects of coking and active component leaching on catalytic activities are quantitatively discussed. The catalytic activity of NbTi did not decrease significantly with time at both pressures. At 25 MPa, the coke precursors on the NbTi surface dissolved in the supercritical water because of the middle-strength acidity of NbTi, thus preventing loss of catalytic activities due to coking. At 33 MPa, coking was more suppressed, most likely because the coke precursors were transferred from the catalyst pores more effectively than at 25 MPa. Leaching of WOX from WTi occurred at the higher reaction pressure due to high ion products of water, but leaching of Nb from NbTi did not occur because of the high chemical stability of NbOX in acid/base solutions.

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Analysis of supercritical water oxidation for detoxification of waste organic solvent in university based on life cycle assessment  Original Research Article
Journal of Hazardous Materials, Volume 194, 30 October 2011, Pages 283-289
Yasunori Kikuchi, Kohjiro Kurata, Jun Nakatani, Masahiko Hirao, Yoshito Oshima
Abstract
Spray incineration and supercritical water oxidation (SCWO) processes have been used for detoxifying waste organic fluids in the University of Tokyo. In this study, we aim to elucidate the environmental aspects of these waste treatment processes by life cycle assessment (LCA). Through the investigation of actual plants, the inventory data and other characteristics of actual plants were collected and analyzed. To confirm the potential of SCWO, three modification types of the process and operation were considered and assessed on the basis of estimated inventory data. The results demonstrate that spray incineration has less environmental impact than SCWO in all scenarios. However, SCWO has various advantages for installation as a treatment process in universities such as negligible risk of creating dioxins and particulate matter. Proper choice of the treatment method for organic waste fluid requires a comprehensive analysis of risks. Spray incineration poses the risk of providing dioxins and particulate matter, while SCWO has such risk at negligible level. This means that waste including concerned materials related to such emission should be treated by SCWO. Using the right technologies for the right tasks in the detoxification of hazardous materials should be implemented for sustainable universities.

Analysis of the scale up of a transpiring wall reactor with a hydrothermal flame as a heat source for the supercritical water oxidation  Original Research Article
The Journal of Supercritical Fluids, Volume 56, Issue 1, February 2011, Pages 21-32
M.D. Bermejo, P. Cabeza, J.P.S. Queiroz, C. Jiménez, M.J. Cocero

Abstract
Experimental data from a tubular reactor and from a transpiring wall reactor (TWR) are used to analyze the scaling up of SCWO reactors operating with a hydrothermal flame as a heat source. Results obtained with the tubular reactor show that fluid velocity inside the reactor determines the minimum injection temperature at which a stable hydrothermal flame is formed. When the fluid velocity inside of the reactor is lower, the extinction temperature of the hydrothermal flame in that reactor is also lower. Using this reactor, extinction temperatures are always near or above the critical temperature of water. Total TOC removals are possible working with isopropyl-alcohol at temperatures between 650 and 700 °C and residence times of 0.5 s. Results of the TWR show that steady operation with a hydrothermal flame inside is possible even when reagents are injected at subcritical conditions as low as 170 °C. Temperature measurements show that reaction is not initiated in the injector but in the reaction chamber, where fluid velocity is lower than 0.1 s. This was explained by estimating that the flame front velocity of a hydrothermal flame is of the order of 0.1 m/s. Thus, it is expected that the flame is stabilized in the reaction chamber and not in the injector, where fluid velocities are higher than 2 m/s. A previously developed model of the TWR was modified in order to describe the ignition in the reaction chamber and not in the injector. The model reproduces satisfactorily experimental data and it was used to propose the design of scaled up reactors for SCWO with a hydrothermal flame inside.

Supercritical water oxidation of coal: Investigation of operating parameters' effects, reaction kinetics and mechanism  Original Research Article
Fuel Processing Technology, Volume 92, Issue 3, March 2011, Pages 291-297
Shuzhong Wang, Yang Guo, Liang Wang, Yuzhen Wang, Donghai Xu, Honghe Ma

Abstract
Supercritical water oxidation (SCWO) of coal was conducted in a continuous tubular reactor under various reaction conditions. Our experimental results show that the removal rate of chemical oxygen demand (COD) had no significant dependence on the temperature variations. Effect of residence time was less significant as exceeded fixed values. Free radical mechanism of SCWO reaction may be a possible explanation for the relative low conversion rate of coal at the range of tested oxygen excess. Compared with other parameters, effect of pressure was less significant. A global power-law rate expression was regressed from experimental data. The reaction orders for coal slurry and oxidant were 1.79 and 0.28 respectively. The reaction activation energy Ea was determined to be 112.3 kJ mol−1, and the pre-exponential factor k0 was 412 (mol/L)−1.07 s−1. The deviation between the model and experimental data was within ± 9%. Free radical mechanism, oxidation and hydrolysis mechanisms and phenolic hydroxyl oxidation mechanism were considered to be the possible mechanisms for the SCWO process of coal.

Water density effects on methanol oxidation in supercritical water at high pressure up to 100 MPa  Original Research Article
The Journal of Supercritical Fluids, Volume 58, Issue 1, August 2011, Pages 142-149
Tatsuya Fujii, Rumiko Hayashi, Shin-ichiro Kawasaki, Akira Suzuki, Yoshito Oshima

Abstract
Reaction kinetics of methanol oxidation in supercritical water at high pressure condition (420 °C; 34–100 MPa; ρ = 300–660 kg/m3) was investigated. Pseudo-first order rate constant for methanol decomposition increased with increasing water density. Effects of supercritical water on the reaction kinetics were investigated using a detailed chemical kinetics model. Incorporating the effect of diffusion in a reduced model revealed that overall kinetics for SCWO of methanol is not diffusion-limited. Roles of water as a reactant were also investigated. The dependence of sensitivity coefficient for methanol concentration and rate of production of OH radical on water density indicated that a reaction, HO2 + H2O = OH + H2O2, enhanced the OH radical production and thereby facilitated the decomposition of methanol. It is presumed that concentration of key radicals could be controlled by varying pressure intensively.

Pathways and kinetics of partial oxidation of phenol in supercritical water  Original Research Article
Chemical Engineering Journal, Volume 175, 15 November 2011, Pages 201-206
Qingqing Guan, Chaohai Wei, Xin-Sheng Chai
Abstract
This study reports on the pathways and kinetics of individual gaseous species involved in the partial oxidation of phenol in supercritical water. The pathway is a combination of supercritical water oxidation (SCWO) and supercritical water gasification (SCWG) processes. A kinetic model that involves oxygen is proposed that fits the experimental data and accurately predicts the effects of the O/phenol ratio on the decomposition of phenol. Specifically, at lower O/Phenol ratios, the gasification of acids and the water gas shift reaction predominated, increasing the amount of H2 in the gaseous products. At higher O/Phenol ratios, on the other hand, the oxidation of acid intermediates and CO oxidation predominated, thereby increasing the amount of CO2, while H2 decreased.

Experimental study of hydrothermal flames formation using a tubular injector in a refrigerated reaction chamber. Influence of the operational and geometrical parameters  Original Research Article
The Journal of Supercritical Fluids, Volume 59, November 2011, Pages 140-148
M.D. Bermejo, C. Jiménez, P. Cabeza, A. Matías-Gago, M.J. Cocero

Abstract
Experimental results using three different empty tubular injectors into a refrigerated reaction chamber containing a hydrothermal flame as an internal heat source are presented. In the supercritical water oxidation process, one method of avoiding external preheating is injecting the feed at room temperature into a hydrothermal flame. In this way, plugging and corrosion problems produced during transition from subcritical to supercritical conditions in the preheating system can be avoided. The influence of feed flow, injection temperature and diameter and length of the injector has been evaluated by studying the temperature profiles along the reactor, the total organic carbon (TOC) removal and the extinction temperatures at different conditions. It was possible to inject reactants even at room temperature into the hydrothermal flame with organic destruction efficiencies higher than 99.9%, presenting better operational results than other reactors constructed by our research work. The effect of salt addition under subcritical conditions in a hydrothermal flame was also studied. Feeds containing up to 2.5 wt% Na2SO4 could be injected in the reactor without plugging problems and a TOC removal of 99.7% was achieved in these conditions. However, only about 10% of the salt introduced in the reactor could be recovered.

Hydrothermal liquefaction of biomass: A review of subcritical water technologies  Review Article
Energy, Volume 36, Issue 5, May 2011, Pages 2328-2342
Saqib Sohail Toor, Lasse Rosendahl, Andreas Rudolf

Abstract
This article reviews the hydrothermal liquefaction of biomass with the aim of describing the current status of the technology. Hydrothermal liquefaction is a medium-temperature, high-pressure thermochemical process, which produces a liquid product, often called bio-oil or bi-crude. During the hydrothermal liquefaction process, the macromolecules of the biomass are first hydrolyzed and/or degraded into smaller molecules. Many of the produced molecules are unstable and reactive and can recombine into larger ones. During this process, a substantial part of the oxygen in the biomass is removed by dehydration or decarboxylation. The chemical properties of bio-oil are highly dependent of the biomass substrate composition. Biomass constitutes of various components such as protein; carbohydrates, lignin and fat, and each of them produce distinct spectra of compounds during hydrothermal liquefaction. In spite of the potential for hydrothermal production of renewable fuels, only a few hydrothermal technologies have so far gone beyond lab- or bench-scale.

Penetration length studies of supercritical water jets submerged in a subcritical water environment using a novel optical Schlieren method  Original Research Article
The Journal of Supercritical Fluids, Volume 57, Issue 2, June 2011, Pages 175-182
Tobias Rothenfluh, Martin J. Schuler, Philipp Rudolf von Rohr

Abstract
In hydrothermal spallation deep drilling a high-velocity, hot, supercritical water jet is directed towards the rock to induce fragmentation. One major challenge in the realization of this novel technique is the entrainment of comparatively cool, aqueous drilling fluid by the hot water jet, which can lead to significant heat losses before the hot jet's energy can be transferred to the rock. The present work quantifies such entrainment effects by determining penetration lengths of supercritical water jets injected into a cool, subcritical environment using a novel optical Schlieren method. Penetration lengths of supercritical jets were found to be equal to the injector's nozzle diameter and almost independent of the jet's temperature at the nozzle exit and the jet's mass flow under almost all experimental conditions investigated. A semi-empirical model adapted from steam jet studies confirmed these findings and indicates that heat and mass transfer are primarily controlled by turbulent mixing.

Hydrogen production from bioethanol reforming in supercritical water  Original Research Article
The Journal of Supercritical Fluids, Volume 57, Issue 1, May 2011, Pages 58-65
Supaporn Therdthianwong, Nawadee Srisiriwat, Apichai Therdthianwong, Eric Croiset

Abstract
Hydrogen production by reforming and oxidative reforming of ethanol in supercritical water (SCW) at the intermediate temperature range of 500–600 °C and pressure of 25 MPa were investigated at different ethanol concentrations or water to ethanol ratios (3, 20 and 30), with the absence and the presence of oxygen (oxygen to ethanol ratio between 0 and 0.156). Hydrogen was the main product accompanied with relatively low amounts of carbon dioxide, methane and carbon monoxide. Some liquid products, such as acetaldehyde and, occasionally, methanol were present. The ethanol conversion and hydrogen yield and selectivity increased substantially as the water to ethanol ratio and the reaction temperature increased. Ethanol was almost completely reformed and mainly converted to hydrogen giving a H2/CO ratio of 2.6 at 550 °C and water to ethanol ratio of 30 without carbon formation. Coke deposition was favored at low water to ethanol ratio, especially at high temperatures (≥550 °C). The hydrogen yield improved as the ethanol was partially oxidized by the oxygen added into the feed at oxygen to ethanol ratios <0.071. It was evidenced that the metal components in Inconel 625 reactor wall reduced by a hydrogen stream acted as a catalyst promoting hydrocarbon reforming as well as water–gas-shift reactions while dehydrogenation of ethanol forming acetaldehyde can proceed homogeneously under the SCW condition. However, at high oxygen to ethanol ratio, the reactor wall was gradually deactivated after being exposed to the oxidant in the feed. The loss of the catalytic activity of the reactor surface was mainly due to the metal oxide formation resulting in reduction of catalytic activity of the reactor wall and reforming of carbon species was no longer promoted.

Supercritical water oxidation of Ion Exchange Resins in a stirred reactor: Numerical modelling  Original Research Article
Chemical Engineering Science, In Press, Corrected Proof, Available online 17 October 2011
A. Leybros, A. Roubaud, P. Guichardon, O. Boutin
Abstract
Supercritical water oxidation offers a viable alternative treatment to destroy the organic structure of Ion Exchange Resins. In order to design and define appropriate dimensions for the supercritical oxidation reactor, a 2D simulation of the fluid dynamics and heat transfer during the oxidation process has been investigated. The solver used is a commercial code, Fluent® 6.3. The turbulent flow field in the reactor, created by the stirrer is taken into account with a kω model and a swirl imposed to the fluid. Particle trajectories are modelled with the Discrete Random Walk Particle Model. For the solubilization of the particles in supercritical water, a mechanism has been proposed and implemented into Fluent® software through the Eddy Dissipation Concept approach, taking into account the identified rate determining species. Simulation results provide results on the flow, temperature fields and oxidation localization inside the reactor. For the reactive particles-supercritical water flow model, the effect of parameters, such as feed flow rates or stirring velocity, can be focussed. Reaction temperature is predicted with deviation lower than 15%. Degradation conversions are in good agreement with experimental ones.

Hydrothermal liquefaction of biomass: A review of subcritical water technologies  Review Article
Energy, Volume 36, Issue 5, May 2011, Pages 2328-2342
Saqib Sohail Toor, Lasse Rosendahl, Andreas Rudolf
Abstract
This article reviews the hydrothermal liquefaction of biomass with the aim of describing the current status of the technology. Hydrothermal liquefaction is a medium-temperature, high-pressure thermochemical process, which produces a liquid product, often called bio-oil or bi-crude. During the hydrothermal liquefaction process, the macromolecules of the biomass are first hydrolyzed and/or degraded into smaller molecules. Many of the produced molecules are unstable and reactive and can recombine into larger ones. During this process, a substantial part of the oxygen in the biomass is removed by dehydration or decarboxylation. The chemical properties of bio-oil are highly dependent of the biomass substrate composition. Biomass constitutes of various components such as protein; carbohydrates, lignin and fat, and each of them produce distinct spectra of compounds during hydrothermal liquefaction. In spite of the potential for hydrothermal production of renewable fuels, only a few hydrothermal technologies have so far gone beyond lab- or bench-scale.

Evolution of naphthalene and its intermediates during oxidation in subcritical/supercritical water  Original Research Article
Proceedings of the Combustion Institute, Volume 33, Issue 2, 2011, Pages 3185-3194
Sikun Xu, Ian Butler, Iskender Gökalp, Janusz A. Kozinski

Abstract
Oxidation of naphthalene (Nap) in supercritical water (SCW) was carried out in a batch reactor (6-ml volume) up to 400 °C and 300 atm (maximum residence time of 1800 s). Two systems were studied. System A consisted of pure naphthalene mixed with oxygen and water: 0.065 M Nap + 1.441 M O2 + 8.549 M H2O. System B included, in addition to O2 and H2O, a heavy metal and an ash to simulate their roles in the destruction of Nap: 0.065 M Nap + 1.441 M O2 + 0.008 M Cr(NO3)3 + 0.065 M Al2Si2O5·(OH)4 + 8.624 M H2O. It was shown that, in general, the oxidation process can be divided into three stages characterized by H2O2 decomposition to H2O and O2 (Stage 1), oxidation in saturated/subcritical water up to 360 °C and 225 atm (Stage 2), and fast oxidation in the supercritical region (Stage 3). The oxidation process revealed different reaction rates in different systems. Relatively low activation energy of 10–30 kJ/mol was obtained below 360 °C and 225 atm in the System A and in the whole temperature range in the System B. High activation energy (139.5 kJ/mol) was obtained for supercritical water oxidation of naphthalene in the System A. The catalytic effect of Cr3+/ash stimulated naphthalene oxidation. Time-resolved yields of major products and intermediates were obtained. The reaction pattern was proposed. It describes the evolution of naphthalene and intermediates as a sequence of reactions comprising transformations of the main compounds and their inter-conversion. This radical-involving reaction mechanism is mainly based on the quantification of the profiles of the intermediates.

Destruction of methylphosphonic acid in a supercritical water oxidation bench-scale double wall reactor  Original Research Article
Journal of Environmental Sciences, Volume 23, Issue 4, April 2011, Pages 545-552
Bambang Veriansyah, Eun-Seok Song, Jae-Duck Kim

Abstract
The destruction of methylphosphonic acid (MPA), a final product by hydrolysis/neutralization of organophosphorus agents such as sarin and VX (O-ethyl S-[2-(diisopropylamino)ethyl] methylphosphonothionate), was investigated in a a bench-scale, continuous concentric vertical double wall reactor under supercritical water oxidation condition. The experiments were conducted at a temperature range of 450-600°C and a fixed pressure of 25 MPa. Hydrogen peroxide was used as an oxidant. The destruction efficiency (DE) was monitored by analyzing total organic carbon (TOC) and MPA concentrations using ion chromatography on the liquid effluent samples. The results showed that the DE of MPA up to 99.999% was achieved at a reaction temperature of 600°C, oxygen concentration of 113% storichiometric requirement, and reactor residence time of 8 sec. On the basis of the data derived from experiments, a global kinetic rate equation for the DE of MPA and DE of TOC were developed by nonlinear regression analysis. The model predictions agreed well with the experimental data.

Exploration of the effect of process variables on the production of high-value fuel gas from glucose via supercritical water gasification  Original Research Article
Bioresource Technology, Volume 102, Issue 3, February 2011, Pages 3480-3487
Doug Hendry, Chandrasekar Venkitasamy, Nikolas Wilkinson, William Jacoby

Abstract
A new continuous supercritical water gasification reactor was designed to investigate glucose gasification in supercritical water at high temperatures and low residence times. A 23 full factorial experiment was performed to determine the effects of feed concentration, temperature, and residence time on glucose gasification. The temperature levels (750 °C and 800 °C) were higher than ever used, while the residence times (4 and 6.5 s) were shorter than ever used in previous supercritical water gasification studies. The reactor proved capable of attaining higher gasification rates than previously shown with high efficiencies and yields. In addition, the glucose gasification reaction was modeled by estimating activation energy and reaction order of glucose gasification in supercritical water.

Continuous salt precipitation and separation from supercritical water. Part 3: Interesting effects in processing type 2 salt mixtures  Original Research Article
The Journal of Supercritical Fluids, In Press, Corrected Proof, Available online 2 September 2011
Martin Schubert, John Aubert, Johannes B. Müller, Frédéric Vogel

Abstract
Using a modified continuously operated laboratory plant which had been constructed in our group to visualize the salt separation from supercritical water using neutron radiography we investigated the continuous salt separation and recovery from supercritical water for four different ternary salt and water mixtures containing either a type 1 and a type 2 salt or a mixture of two type 2 salts.
As the mixture of Na3PO4/K2SO4 (both type 2 salts) may form a mixture of K3PO4/Na2SO4 (type 1/type 2) by permutation of the ions during precipitation from supercritical water, the separation performance of the K3PO4/Na2SO4 mixture containing the same concentration in sodium, potassium, sulfate, and phosphate as the Na3PO4/K2SO4 mixture was investigated as well. Both mixtures showed the same trend in the separation performance exhibiting a maximum in the separation efficiency in the temperature range studied, and showing a preferential separation of sodium and phosphate or potassium and sulfate ions depending on the temperature of the separator vessel.
The mixtures of Na3PO4/Na2SO4 and Na2SO4/K2SO4 were “real type 2 salt mixtures”, i.e. mixtures in which the permutation of the ions does not lead to the formation of a type 1 salt in the respective mixture. The salts from the Na3PO4/Na2SO4 mixture could not be recovered as a concentrated brine. This salt mixture behaved as would be expected for the respective single type 2 salt solutions of either Na3PO4 or Na2SO4.
Interestingly, a concentrated brine could be recovered for the Na2SO4/K2SO4 mixture with the salt recovery in the brine effluent showing a maximum at a separator setpoint temperature of 450–460 °C. Beyond this temperature the salt mixture became “sticky”, thus exhibiting the behavior as would be expected for a type 2 salt mixture.


Partial oxidative gasification of phenol for hydrogen in supercritical water  Original Research Article
Applied Energy, Volume 88, Issue 8, August 2011, Pages 2612-2616
Qingqing Guan, Chaohai Wei, Huashun Shi, Chaofei Wu, Xin-Sheng Chai

Abstract
The paper reports partial oxidative gasification of phenol for hydrogen in supercritical water (SCW) at lower temperature (<753 K), at which cleavages of aromatic ring occur difficultly and tend to undesirable polymerization. The results showed that O2 is effective to gasification of phenol in SCW.
76% of phenol was gasified and 2.7 mol/mol of hydrogen was produced within 180 s with Na2CO3 as catalyst at the selected process conditions, a molar ratio of oxygen-to-phenol, 7.5–1, 723 K, and 24 MPa. It was found that unstable opening-rings products oxalic and maleic acid and stable dimmerization compounds in liquid water were formed during partial oxidation process. The process also indicated phenol was rapidly converted, and some opening-rings products were slowly gasified, which also confirmed oxygen served as effective reactant for ring-opening. Based on the given reaction conditions, a treatment process using a real wastewater from coking industry was performed. The data showed that the present technology provides an effective way to gasification of phenol wastewater for high-value energy utilization.

Green chemical processes with supercritical fluids: Properties, materials, separations and energy  Original Research Article
The Journal of Supercritical Fluids, Volume 60, December 2011, Pages 2-15
Hiroshi Machida, Masafumi Takesue, Richard L. Smith Jr.

Abstract
In this work, an overview of the properties of supercritical fluids is given on using water and carbon dioxide for developing green chemical processes. Present industrial processes and emerging technologies that use supercritical fluids are highlighted. Supercritical fluids are being used in transcritical cycles for heat transfer due to their favorable thermophysical properties and their environmental compatibility. Supercritical water is being proposed as a reaction solvent for zinc silicate industrial phosphors, since it allows production of luminescent materials at low temperatures (400 °C) and with less energy than industrial solid-state methods that require high temperatures (1200 °C). Supercritical CO2–ionic liquid systems have much potential as biphasic systems for reactions and separations, however, when used for chiral separations, the selectivity of these systems is not well understood yet. The use of supercritical CO2 for viscosity reduction in ionic liquid reaction systems seems to be a favorable research area with conversion of d-fructose to 5-hydroxymethylfurfural in high yields (>90%) being an example. Systems to convert biomass to energy by direct oxidation in supercritical water are under development. Many opportunities exist for developing green chemical processes with supercritical fluids.

Closing the phosphorus loop in England: The spatio-temporal balance of phosphorus capture from manure versus crop demand for fertiliser  Original Research Article
Resources, Conservation and Recycling, Volume 55, Issue 12, October 2011, Pages 1146-1153
Anna Bateman, Dan van der Horst, David Boardman, Arun Kansal, Cynthia Carliell-Marquet
Abstract
Every year 90 million tonnes of housed livestock manures are produced in the UK. This is a valuable reservoir of global phosphorus (P) and a point in the cycle where it is vulnerable to being lost from the terrestrial system. Improved manure management for the effective reuse of phosphorus is vital to simultaneously tackle a major source of water pollution and reduce our dependence on imported fertilisers. This paper quantifies, for the first time, the spatial and temporal challenges of recycling the required amount of manure P from areas of livestock production to areas of crop production in eight regions of England. The analysis shows that England has a P deficit and therefore the capacity to fully utilise the manure P on arable land, but that uneven spatial distribution of livestock poses a significant challenge to closing the P loop in agriculture. Two of the eight regions were shown to have surplus manure P, with the remaining six regions having P deficits, indicating that an annual export of 4.7 thousand tonnes P (2.8 million tonnes manure) must take place from the west to the east of the country each year to balance P supply and demand. Moreover, housed manure production peaks between October and February, requiring an excess of 23.0 thousand tonnes P (15 million tonnes manure) to be stored until it can be used for crop fertilisation from March onwards. The results demonstrate the scale of the challenge in managing manure P in an agricultural system that has separated livestock production from crop production, a pattern that is echoed throughout the developed world. To overcome the spatial and temporal challenges, a logistical system is recommended that will balance the nutrient potential (nitrogen and P content and availability) and pollution potential (eutrophication, greenhouse gas emissions, particulates and nitrous oxide from transport) for cost-effective and environmentally compatible redistribution of manure P from areas of surplus to areas of deficit, when required.

Evolution of naphthalene and its intermediates during oxidation in subcritical/supercritical water  Original Research Article
Proceedings of the Combustion Institute, Volume 33, Issue 2, 2011, Pages 3185-3194
Sikun Xu, Ian Butler, Iskender Gökalp, Janusz A. Kozinski

Abstract
Oxidation of naphthalene (Nap) in supercritical water (SCW) was carried out in a batch reactor (6-ml volume) up to 400 °C and 300 atm (maximum residence time of 1800 s). Two systems were studied. System A consisted of pure naphthalene mixed with oxygen and water: 0.065 M Nap + 1.441 M O2 + 8.549 M H2O. System B included, in addition to O2 and H2O, a heavy metal and an ash to simulate their roles in the destruction of Nap: 0.065 M Nap + 1.441 M O2 + 0.008 M Cr(NO3)3 + 0.065 M Al2Si2O5·(OH)4 + 8.624 M H2O. It was shown that, in general, the oxidation process can be divided into three stages characterized by H2O2 decomposition to H2O and O2 (Stage 1), oxidation in saturated/subcritical water up to 360 °C and 225 atm (Stage 2), and fast oxidation in the supercritical region (Stage 3). The oxidation process revealed different reaction rates in different systems. Relatively low activation energy of 10–30 kJ/mol was obtained below 360 °C and 225 atm in the System A and in the whole temperature range in the System B. High activation energy (139.5 kJ/mol) was obtained for supercritical water oxidation of naphthalene in the System A. The catalytic effect of Cr3+/ash stimulated naphthalene oxidation. Time-resolved yields of major products and intermediates were obtained. The reaction pattern was proposed. It describes the evolution of naphthalene and intermediates as a sequence of reactions comprising transformations of the main compounds and their inter-conversion. This radical-involving reaction mechanism is mainly based on the quantification of the profiles of the intermediates.

Destruction of methylphosphonic acid in a supercritical water oxidation bench-scale double wall reactor  Original Research Article
Journal of Environmental Sciences, Volume 23, Issue 4, April 2011, Pages 545-552
Bambang Veriansyah, Eun-Seok Song, Jae-Duck Kim

Abstract
The destruction of methylphosphonic acid (MPA), a final product by hydrolysis/neutralization of organophosphorus agents such as sarin and VX (O-ethyl S-[2-(diisopropylamino)ethyl] methylphosphonothionate), was investigated in a a bench-scale, continuous concentric vertical double wall reactor under supercritical water oxidation condition. The experiments were conducted at a temperature range of 450-600°C and a fixed pressure of 25 MPa. Hydrogen peroxide was used as an oxidant. The destruction efficiency (DE) was monitored by analyzing total organic carbon (TOC) and MPA concentrations using ion chromatography on the liquid effluent samples. The results showed that the DE of MPA up to 99.999% was achieved at a reaction temperature of 600°C, oxygen concentration of 113% storichiometric requirement, and reactor residence time of 8 sec. On the basis of the data derived from experiments, a global kinetic rate equation for the DE of MPA and DE of TOC were developed by nonlinear regression analysis. The model predictions agreed well with the experimental data.

Hydration of OH radical in high temperature water  Original Research Article
Journal of Molecular Liquids, Volume 164, Issues 1-2, 1 November 2011, Pages 34-38
J. Szala-Bilnik, D. Swiatla-Wojcik

Abstract
Molecular dynamics simulation study on the hydration and hydrogen-bonding of the OH radical is presented for the 25 MPa isobar and the temperature ranging from 373 to 673 K. For the first time the water molecule and the radical have been described by the flexible three- and two-site models, respectively, which account for short-range interaction of the hydrogen atom. We have found that the mechanism of hydration and the degree of radical–water hydrogen-bonding are closely related to the structural transformations occurring in the hydrogen-bonded network of the solvent. Compact and ordered network, typical for the liquid phase, favours the cavity localization. Up to 573 K the decrease in the number of water–water hydrogen bonds has been associated with the increase in the number of radical–water H-bonds. Unlike the hydration in the condensed liquid phase the low density of supercritical water at 673 K stimulates the radical behaviour as a structure-maker. In the presence of OH the structural inhomogeneity of the solvent has been noticeably reduced. Our work showed the importance of short-range interaction of hydrogen atoms in hydration and hydrogen bonding of OH at high temperatures and proved that neglect of the angular condition greatly overestimates the number of radical–water H-bonds, mostly of the H-acceptor type.

A review on process conditions for optimum bio-oil yield in hydrothermal liquefaction of biomass  Review Article
Renewable and Sustainable Energy Reviews, Volume 15, Issue 3, April 2011, Pages 1615-1624
Javaid Akhtar, Nor Aishah Saidina Amin
Abstract
Hydrothermal liquefaction is a technique for obtaining clean biofuel from biomass in the presence of a solvent at moderate to high temperature (250–550 °C) and pressure (5–25 MPa). Hydrothermal decomposition of biomass leads to the formation of various compounds depending upon operating parameters. The role of processing conditions including final liquefaction temperature, residence times, rate of biomass heating, size of biomass particles, type of solvent media and hydrogen donor solvents is important for the bio-oil yield and quality of the product. The effect of these parameters on the yield and composition of the liquid products is reviewed in the paper. A brief description about the decomposition mechanism is also included to highlight the product types during hydrothermal liquefaction.

Hydrothermal gasification of olive mill wastewater as a biomass source in supercritical water  
Original Research Article
The Journal of Supercritical Fluids, Volume 57, Issue 1, May 2011, Pages 50-57
Ekin Kıpçak, Onur Ö. Söğüt, Mesut Akgün
Abstract
In this study, the hydrothermal gasification of biomass in supercritical water is investigated. The work is of peculiar value since a real biomass, olive mill wastewater (OMW), is used instead of model biomass compounds. OMW is a by-product obtained during olive oil production, which has a complex nature characterized by a high content of organic compounds and polyphenols. The high content of organics makes OMW a desirable biomass candidate as an energy source. The hydrothermal gasification experiments for OMW were conducted with five different reaction temperatures (400, 450, 500, 550 and 600 °C) and five different reaction times (30, 60, 90, 120 and 150 s), under a pressure of 25 MPa. The gaseous products are mainly composed of hydrogen, carbon dioxide, carbon monoxide and C1–C4 hydrocarbons, such as methane, ethane, propane and propylene. Maximum amount of the gas product obtained is 7.71 mL per mL OMW at a reaction temperature of 550 °C, with a reaction time of 30 s. The gas product composition is 9.23% for hydrogen, 34.84% for methane, 4.04% for ethane, 0.84% for propane, 0.83% for propylene, 49.34% for carbon dioxide, and 0.88% for minor components such as n-butane, i-butane, 1-butene, i-butene, t-2-butene, 1,3-butadiene and nitrogen at this reaction conditions.

Supercritical water gasification of an aqueous by-product from biomass hydrothermal liquefaction with novel Ru modified Ni catalysts  
Original Research Article
Bioresource Technology, Volume 102, Issue 17, September 2011, Pages 8279-8287
Linghong Zhang, Pascale Champagne, Chunbao (Charles) Xu
Abstract
Supercritical water gasification (SCWG) of glucose solution (50–200 g/L), a simulated aqueous organic waste (composed of glucose, acetic acid and guaiacol) and a real aqueous organic waste stream generated from a sludge hydrothermal liquefaction process was performed in a bench-scale continuous down-flow tubular reactor with novel 0.1RuNi/γ-Al2O3 or 0.1RuNi/activated carbon (AC) catalyst (10 wt.% Ni with a Ru-to-Ni molar ratio of 0.1). 0.1RuNi/γ-Al2O3 was very effective in catalyzing SCWG of glucose solution and the simulated aqueous organic waste, attaining an H2 yield of 53.9 mol/kg dried feedstock at 750 °C, 24 MPa and a WHSV of 6 h−1. However, the γ-Al2O3-supported catalyst was not resistant to the attack of alkali and nitrogen compounds in the real waste during the SCWG of the real aqueous organic waste, whereas the AC-based catalyst exhibited higher stability. This research provides a promising approach to the treatment and valorization of aqueous organic waste via SCWG.

The behavior of phosphorus in sub- and super-critical water gasification of sewage sludge  Original Research Article
Chemical Engineering Journal, Volume 171, Issue 1, 15 June 2011, Pages 190-196
W. Zhu, Z.R. Xu, L. Li, C. He

Abstract
In this study, the behavior of phosphorus (P) during the non-catalytic sub- and supercritical water gasification of dewatered sewage sludge was investigated using a high-pressure autoclave. Various operating parameters such as reaction temperature, pressure and residence time were varied to investigate their effects on the P behaviors. The results supported that the majority of P migrated into the solid residue since the concentration of total P in the solid residue showed a significant increase (up to 20 mg-P/g). In addition, the organic P in the sludge was almost completely converted into phosphate during supercritical water gasification. A significant proportion of P remained in aqueous phase was dissoluble reactive P, which was dominated of HPO42−.

Supercritical water oxidation of phenol with air. Experimental results and modelling  Original Research Article
Chemical Engineering Journal, Volume 152, Issue 1, 1 October 2009, Pages 227-233
A. Fourcault, B. García-Jarana, J. Sánchez-Oneto, F. Marias, J.R. Portela

Abstract
Hydrothermal oxidation is an efficient and clean way for the treatment of wastewater containing organic matter. Because of its specific properties, supercritical water ensures high conversion of a wide range of organic load in the presence of an oxidant. The purpose of this work is to develop a mathematical model for a continuous flow tubular reactor devoted to hydrothermal oxidation. This reactor has a low ratio diameter length with one air injection. The mathematical model is based on plug flow assumption. The governing equations are: momentum, mass, species and energy balances. According to this model, the profiles of temperature and concentration of chemical species are computed along the reactor. The numerical predictions of the model are compared to experimental profiles obtained in the case of supercritical oxidation of phenol. These comparisons show very good agreement.

Investigation of thermochemical conversion of biomass in supercritical water using a batch reactor  Original Research Article
Fuel, Volume 90, Issue 8, August 2011, Pages 2662-2670
Chandrasekar Venkitasamy, Doug Hendry, Nikolas Wilkinson, Lakdas Fernando, William A. Jacoby

Abstract
This study focused on gasification of biomass and a biomass model compound. Data are presented that show the presence of supercritical water enhances gasification efficiency, as it participates as both a solvent and a reactant. It is established that biomass gasification efficiencies are in the same range for all types of biomass. The thermodynamic changes of state are functions of elemental composition, not biomass species. The oxidation state of carbon atom of biomass is a key variable in determining the changes in enthalpy during both conventional combustion and supercritical water gasification. The oxidation state of the feed (together with the reaction conditions that influence the degree to which water participates as a reactant) also determines the vapor product composition.
Decomposition reactions to vapor products are rapid and complete at high temperature (⩾550 °C), catalytic mediation is not required. Temperature and residence time are important operating parameters for SCW gasification. Less important are the pressure of gasification (in the range of 40–67 MPa) and the presence of catalyst. The vapor yield, gas composition, the carbon and hydrogen balance of SCW gasification are functions of gasification temperature, residence time and biomass load (concentration).


Destruction of chemical agent simulants in a supercritical water oxidation bench-scale reactor  Original Research Article
Journal of Hazardous Materials, Volume 147, Issues 1-2, 17 August 2007, Pages 8-14
Bambang Veriansyah, Jae-Duck Kim, Jong-Chol Lee
Abstract
In this paper, ammonia as an important ingredient in landfill leachate was mainly studied. Based on Peng–Robinson formulations and Gibbs free energy minimization method, the estimation of equilibrium composition and thermodynamic analysis for supercritical water oxidation of ammonia (SCWO) was made. As equilibrium is reached, ammonia could be totally oxidized in SCW. N2 is the main product, and the formation of NO2 and NO could be neglected. The investigation on SCWO of landfill leachate was conducted in a batch reactor at temperature of 380–500 °C, reaction time of 50–300 s and pressure of 25 MPa. The effect of reaction parameters such as oxidant equivalent ratio, reaction time and temperature were investigated. The results showed that COD and NH3 conversion improved as temperature, reaction time and oxygen excess increased. Compared to organics, NH3 is a refractory compound in supercritical water. The conversion of COD and NH3 were higher in the presence of MnO2 than that without catalyst. The interaction between reaction temperature and time was analyzed by using response surface method (RSM) and the results showed that its influence on the NH3 conversion was relatively insignificant in the case without catalyst. A global power-law rate expression was regressed from experimental data to estimate the reaction rate of NH3. The activation energy with and without catalyst for NH3 oxidation were 107.07 ± 8.57 kJ/mol and 83.22 ± 15.62 kJ/mol, respectively.

1.

Operating characteristics of a transpiring-wall SCWO reactor with a hydrothermal flame as internal heat source
Wellig, B. / Lieball, K. / Rudolf von Rohr, Ph., Jnl. of Supercritical Fluids, May 2005
...Fig. 5 Schematic representation of the SCWO pilot plant. FI: flow indication, PI: pressure...Operating characteristics of a transpiring-wall SCWO reactor with a hydrothermal flame as internal...A novel supercritical water oxidation (SCWO) system with a transpiring-wall reactor...

 

2.

Supercritical water oxidation improvements through chemical reactors energy integration
Lavric, E.D. / Weyten, H. / De Ruyck, J. / Plesu, V. / Lavric, V., Applied Thermal Engineering, Sep 2006
...Abstract Supercritical Water Oxidation (SCWO) is the process of complete destruction...complete oxidation. Typical products from a SCWO process include carbon dioxide, water, and inorganic salts or acids. SCWO advantages include very high destruction...

3.

Bubble points of the systems isopropanol-water, isopropanol-water-sodium acetate and isopropanol-water-sodium oleate at...
Bermejo, M.D. / Martin, A. / Florusse, L.J. / Peters, C.J. / Cocero, M.J., Fluid Phase Equilibria, Jun 2006
...15 278 42 89. Abstract Supercritical water oxidation (SCWO) is a powerful technology for destroying organic wastes...main challenges for the industrial development of the SCWO process. In SCWO heteroatoms are oxidized until high oxidation states...

4.

Phosphorus release from ash, dried sludge and sludge residue from supercritical water oxidation by acid or base
Stark, K. / Plaza, E. / Hultman, B., Chemosphere, Feb 2006
...alkaline and acid leaching between ash and SCWO residue. Table 1 Origin of the ashes Sample...Release of Fe, Al, PO4and Ca in ash A and SCWO residue HCl NaOH M Fe% Al% PO4% Ca% M Fe...0.19 NaOH HCl M Fe% Al% PO4% M Fe% PO4% SCWO 0 0.002 0.62 2.4 0 0.00 0.8 0.5 0.01 42...

6.

An anti-corrosive reactor for the decomposition of halogenated hydrocarbons with supercritical water oxidation
Lee, H.C. / In, J.H. / Lee, S.Y. / Kim, J.H. / Lee, C.H., Jnl. of Supercritical Fluids, Nov 2005
...porous ceramic tube (a) before, (b) after SCWO operation of 2,4-DCP and (c) shear strength...the general type and the floating type SCWO reactors, and photographs of head, inside...residence time at supercritical region in the SCWO of 2,4-DCP Pressure (bar) Maximum temperature...

8.

Supercritical water oxidation of o-dichlorobenzene: degradation studies and simulation insights
Svishchev, I.M. / Plugatyr, A., The Journal of Supercritical Fluids, Feb 2006
...Abstract Supercritical water oxidation (SCWO) of an aromatic chlorinated species,o-dichlorobenzene...temperature on the degradation efficiency of the SCWO process. Experiments are also performed...Introduction Supercritical water oxidation (SCWO) has shown to be one of the most effective...

9.

Delocalized organic pollutant destruction through a self-sustaining supercritical water oxidation process
Lavric, E.D. / Weyten, H. / De Ruyck, J. / Plesu, V. / Lavric, V., Energy Conversion and Management, Jun 2005
...reaction schemes. Fig. 2 The flowsheet of SCWO process with a supercritical steam turbine...scheme of closed Brayton cycle. Fig. 4 SCWO flowsheet with closed Brayton cycle. Fig...Rankine cycle with superheating. Fig. 6 SCWO flowsheet with organic Rankine cycle. Table...

10.

Environmental assessment of supercritical water oxidation and other sewage sludge handling options.
Magdalena Svanström / Morgan Fröling / Mattias Olofsson / Margareta Lundin, Waste Manag Res, Aug 2005
...resource unit. Supercritical water oxidation (SCWO) can be used for treatment of wet organic...has not yet been fully commercialized. SCWO allows for complete oxidation of all organics...life-cycle assessment (LCA) of sewage sludge SCWO (Aqua-Critox) is presented and the results...

11.

Critical review of kinetic data for the oxidation of methanol in supercritical water
Vogel, F. / Blanchard, J.L.D. / Marrone, P.A. / Rice, S.F. / Webley, P.A. / Peters, W.A. / Smith, K.A. / Tester, J.W., Jnl. of Supercritical Fluids, Jul 2005
...al.[45]. Fig. 2 Schematic of a typical SCWO tubular flow reactor set-up with separate...solid line). Fig. 6 Induction times for the SCWO of methanol observed in tubular flow reactors...amperometric detector) of reaction solutions from SCWO of methanol (upper trace), and from methanol...

12.

Supercritical water oxidation of wastewater from LCD manufacturing process: kinetic and formation of chromium oxide...
Veriansyah, B. / Park, T.J. / Lim, J.S. / Lee, Y.W., Jnl. of Supercritical Fluids, May 2005
...the continuous-flow reactor system for SCWO experiment. Fig. 2 Plots of ln(1-X) against residence time for LCD wastewater in SCWO. Fig. 3 Assumed first-order Arrhenius plot for LCD wastewater in SCWO. Fig. 4 Effect of wastewater feed concentration...

13.

The influence of Na2SO4 on the CO2 solubility in water at high pressure
Bermejo, M.D. / Martin, A. / Florusse, L.J. / Peters, C.J. / Cocero, M.J., Fluid Phase Equilibria, Dec 2005
Supercritical water oxidation (SCWO) is a very efficient process for the destruction of organic wastes. In this type of processes, conversions higher than 99% can be achieved with residence times shorter than a minute. The effluent of this...

14.

Removal and destruction of toxic micropolluting organic compounds from waste waters by a combined NF and SCWO process
Del Re, G. / Di Giacomo, G., Desalination, Sep 2001
...from waste waters by a combined NF and SCWO process Giovanni Del Re*, Gabriele Di Giacomo...Abstract Supercritical Water Oxidation (SCWO) has been proposed almost 20 years ago...substances such as carbon dioxide and water. SCWO usually operates at a pressure of about...

15.

The destruction of industrial aqueous waste containing biocides in supercritical water-development of the SUWOX process...
Baur, S. / Schmidt, H. / Kramer, A. / Gerber, J., The Journal of Supercritical Fluids, Feb 2005
...6. Fig. 3 Formation of acids during the SCWO process. Fig. 4 Formation of NaHCO 3 at...of s uper c ritical w ater o xidation (SCWO) lies in the complete destruction of persistent...Chemie, Chemisch-Physikalische Verfahren SCWO supercritical water oxidation SUWOX supercritical...

16.

Probing the chemical and electrochemical properties of SCWO systems
Macdonald, D.D. / Kriksunov, L.B., Electrochimica Acta, Dec 2001
...chemical and electrochemical properties of SCWO systems Digby D. Macdonald * * Corresponding...16802, USA Supercritical water oxidation (SCWO) is currently being developed as a means...chemical agents. The advantages offered by SCWO over incineration, for example, include...

17.

Cool wall reactor for supercritical water oxidation - Modelling and operation results
Cocero, M.J. / Martinez, J.L., The Journal of Supercritical Fluids, Sep 2004
...modelling of a supercritical water oxidation (SCWO) reactor capable of operating effectively...Reactor design Supercritical water oxidation (SCWO) Reactor modelling Reaction stable intermediates...transversal surface (m 2 ) SS Stainless Steel SCWO Supercritical water oxidation T Temperature...

18.

An assessment of supercritical water oxidation (SCWO) - Existing problems, possible solutions and new reactor concepts
Kritzer, P. / Dinjus, E., Chemical Engineering Journal, Aug 2001
...assessment of supercritical water oxidation (SCWO) Existing problems, possible solutions...process of supercritical water oxidation (SCWO) is a promising alternative to the incineration...interest during the last decade. However, SCWO as an end-of-pipe technology has some disadvantages...

 

19.

Environmental assessment of supercritical water oxidation of sewage sludge
Svanstrom, M. / Froling, M. / Modell, M. / Peters, W.A. / Tester, J., Resources, Conservation and Recycling, Jul 2004
...of using supercritical water oxidation (SCWO) to treat sewage sludge were studied using...system studied is the first commercial scale SCWO plant for sewage sludge in the world, treating...production are also important. Overall, SCWO processing of undigested sewage sludge...

 

20.

Destruction of deca-chlorobiphenyl in supercritical water under oxidizing conditions with and without Na2CO3
Fang, Z. / Xu, S.K. / Smith Jr., R.L. / Arai, K. / Kozinski, J.A., Jnl. of Supercritical Fluids, Mar 2005
Decomposition of deca-chlorobiphenyl (10-CB) during pyrolysis and oxidation in supercritical water (SCW) was studied in a hydrothermal diamond anvil cell (HDAC) and batch reactors. HDAC was coupled with optical and infrared microscopes....

 

21.

High Curie temperature in B-site ordered Sr2CrWO6 epitaxial thin films
Venimadhav, A. / Sher, F. / Attfield, J.P. / Blamire, M.G., Solid State Communications, May 2006
...Fig. 1 (a)X-ray diffractiontheta-2thetascans of SCWO films (i) on STO in Ar+O2, (ii) Ar alone, (iii...iii) shows the parasitic phase.(b)phiscan of an SCWO film(c)(i)theta-2thetascans of SCWO (111) peak on STO (ii)theta-2thetascans of SCWO...

22.

Supercritical water oxidation of phenol and 2,4-dinitrophenol
Vera Perez, I. / Rogak, S. / Branion, R., The Journal of Supercritical Fluids, Jun 2004
...pilot-scale supercritical water oxidation (SCWO) system. Treatment for approximately 40...conditions. Supercritical water oxidation (SCWO) has been proposed as a technology capable...organic hazardous wastes. The feasibility of SCWO as a waste destruction technology has been...

23.

Salt precipitation and scale control in supercritical water oxidation-part B: commercial/full-scale applications
Marrone, P.A. / Hodes, M. / Smith, K.A. / Tester, J.W., The Journal of Supercritical Fluids, May 2004
...potential of supercritical water oxidation (SCWO) as a viable technology for organic waste...expensive and frequent downtime of the SCWO system. Other solids such as oxides exhibit...that have attempted to commercialize the SCWO technology over the past two decades have...

24.

A review of secondary sludge reduction technologies for the pulp and paper industry
Mahmood, T. / Elliott, A., Water Research, Jun 2006
...modified fromNichols, 1992). Fig. 7 Schematic of a sludge to oil converter (modified fromCampbell, 1989). Fig. 8 Schematic of a SCWO system (modified fromModell et al., 1992). Fig. 9 Schematic of a wastewater treatment system with solubilization producing less...

25.

Salt precipitation and scale control in supercritical water oxidation-Part A: fundamentals and research
Hodes, M. / Marrone, P.A. / Hong, G.T. / Smith, K.A. / Tester, J.W., The Journal of Supercritical Fluids, May 2004
...02139, USA Supercritical water oxidation (SCWO) is an effective technology for treatment...of aqueous wastes. Commercialization of SCWO processes has been hindered by concerns...operational procedures. Salts are formed during SCWO when acidic solutions are neutralized to...

26.

Recent advances on heat, chemical and process integration, multiobjective and structural optimisation
Klemes, J. / Stehlik, P., Applied Thermal Engineering, Sep 2006
...Integration (CREI) analysis[20]were applied to SCWO process and the suitable network configuration...generation. Supercritical Water Oxidation (SCWO) is the process of nearly complete destruction...complete oxidation. Typical products from a SCWO process include CO2, water, and inorganic...

 

27.

A process for generating power from the oxidation of coal in supercritical water
Bermejo, M.D. / Cocero, M.J. / Fernandez-Polanco, F., Fuel, Jan 2004
...oxidation of coal by supercritical water oxidation (SCWO) is presented. Two versions of SCWO power plant are compared to two of the most efficient...state. Calculated results show that net work in SCWO power plant is 5% higher than in other power plants...

28.

Stainless steel flow reactor for supercritical water oxidation: corrosion tests
Hayward, T.M. / Svishchev, I.M. / Makhija, R.C., The Journal of Supercritical Fluids, Dec 2003
...development of supercritical water oxidation (SCWO) into a viable industrial process, is the...contributing factor to the corrosion of SCWO experiment. Supercritical water oxidation...recent years supercritical water oxidation (SCWO) has emerged as a promising new technology...

29.

Direct energy recovery from primary and secondary sludges by supercritical water oxidation.
M Svanström / M Modell / J Tester, Water Sci Technol, Feb 2004
Supercritical water oxidation (SCWO) oxidizes organic and biological materials virtually completely to benign products without the need for stack gas scrubbing. Heavy...

30.

Recycling of sludge with the Aqua Reci process.
K Stendahl / S Jäfverström, Water Sci Technol, Feb 2004
Supercritical Water Oxidation (SCWO) is an innovative and effective destruction method for organics in sewage sludge. The SCWO process leaves a slurry of inorganic ash...Reci. In a continuous pilot plant for the SCWO process digested sludge has been treated...

31.

Spatial hydration structures and dynamics of phenol in sub- and supercritical water
Andriy Plugatyr / Istok Nahtigal / Igor M. Svishchev, The Journal of Chemical Physics, Jan 2006
...Diffusion and thermal diffusion in liquids Body INTRODUCTION The continual development of the supercritical water oxidation (SCWO) technology and other innovative applications of high-temperature water (in advanced power cycles, hydrometallurgy, etc.) have...

32.

Decoloration of azo dye by a multi-needle-to-plate high-voltage pulsed corona discharge system in water
Wang, H. / Li, J. / Quan, X., Journal of Electrostatics, Jun 2006
The decoloration efficiency of azo dye (Acid Orange 7, AO7) using a multi-needle-to-plate high-voltage pulsed corona discharge system was investigated in this paper. The effect of several parameters, including peak pulse voltage and pulse...

33.

05/02800 Isolation and determination of cultural characteristics of a new highly CO2 tolerant fresh water microalgae
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

34.

05/02794 Developmental and environmental effects of the Kizildere geothermal power project, Turkey
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

35.

05/02797 Hazard assessment of substances produced from the accidental heating of chemical compounds
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

36.

In situ characterisation of the oxidation of Ni in ultrasupercritical water
Betova, I. / Bojinov, M. / Kinnunen, P. / Lehtovuori, V. / Peltonen, S. / Penttila, S. / Saario, T., Electrochemistry Communications, Feb 2006
...The major disadvantages of SCW oxidation (SCWO) revolve around high pressure (P 23MPa...waste streams, corrosion[5-7]. Although SCWO is technologically able to destroy hazardous...not be suitable for the most aggressive SCWO feed streams because they can exhibit both...

37.

Catalytic denitrogenation of hydrocarbons through partial oxidation in supercritical water
Yuan, P.Q. / Cheng, Z.M. / Zhang, X.Y. / Yuan, W.K., Fuel, Feb 2006
...hydrocarbons through catalytic SCW oxidation (SCWO), trying to provide some fundamental information...pyrolysis as well as direct oxidation under SCWO environment. In order to evaluate the contribution...oxidation to the denitrogenation under SCWO environment was hereby neglected. For the...

38.

Radiolysis of phenol in aqueous solution at elevated temperatures
Miyazaki, T. / Katsumura, Y. / Lin, M. / Muroya, Y. / Kudo, H. / Taguchi, M. / Asano, M. / Yoshida, M., Radiation Physics and Chemistry, Mar 2006
...dibenzofuran, and dibenzo-p-dioxin in the SCWO of phenol. They reported this may be due...radiolysis of phenol in aqueous solution and SCWO. However, in gas-phase reaction between...studied by this work and literature in SCWO, gas-phase reaction and pulse radiolysis...

39.

05/02796 Estimate of ecological efficiency for thermal power plants in Brazil
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

40.

05/02798 Health costs caused by oil extraction air emissions and the benefits from abatement: the case of Kazakhstan
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

41.

05/02793 Delocalized organic pollutant destruction through a self-sustaining supercritical water oxidation process
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

 

42.

05/02799 Impact of geothermal well testing on exposed vegetation in the Northern Negros Geothermal Project, Philippines
Fuel and Energy Abstracts, Nov 2005
...1345-1364. Supercritical water oxidation (SCWO) is a recent development aiming at the...paper focuses on the process simulation of SCWO with emphasis on the proper modelling of...conditions and on the possibility to make the SCWO process self-sufficient from the energetic...

43.

OPA oxidation rates in supercritical water
Veriansyah, B. / Kim, J.D. / Lee, J.C. / Lee, Y.W., Journal of Hazardous Materials, Sep 2005
...oxidation experiments conducted in the SCWO flow reactor Reaction temperature (K) Residence...investigated under supercritical water oxidation (SCWO) conditions in an isothermal tubular reactor...Studies of supercritical water oxidation (SCWO) for treating and destroying CWAs are underway...

44.

Advanced vehicle routing algorithms for complex operations management problems
Tarantilis, C.D. / Ioannou, G. / Prastacos, G., Journal of Food Engineering, Oct 2005
Vehicle routing encompasses a whole class of complex optimization problems that target the derivation of minimum total cost routes for a number of resources (vehicles) located at a central point (depot) in order to service efficiently a...

45.

Supercritical water oxidation of sulfide.
Tao Wang / Botao Xiang / Jun Liu / Zhongyao Shen, Environ Sci Technol, May 2003
Supercritical water oxidation (SCWO) of sulfide wastewater with oxygen as the...were conducted in a bench-scale continuous SCWO installation, indicated that S2- could...MPa-30.0 MPa. The reaction pathway of S2- in SCWO was determined to be S2- -- S2O3(2...

46.

Flameless incineration of pyrene under sub-critical and supercritical water conditions
Onwudili, J.A. / Williams, P.T., Fuel, Jan 2006
...5]. Many supercritical water oxidation (SCWO) experiments have been conducted at temperatures...needed for suitable application of the SCWO process. Excellent destruction efficiencies...these reports confirm the effectiveness of SCWO in the decomposition of organic pollutants...

47.

Project M3-a study for a manned Mars mission in 2031
Taraba, M. / Zwintz, K. / Bombardelli, C. / Lasue, J. / Rogler, P. / Ruelle, V. / Schlutz, J. / (...) / Sinzig, B., Acta Astronautica, Jan 2006
This study deals with a manned mission which focuses on building an orbital station around Mars. The advantages in comparison to direct-landing scenarios are outlined and the necessary technology is described. The orbiting station prohibits...

48.

Subject Index
Fluid Phase Equilibria, Dec 2005
...239 Prediction, 52 Predictive equation of state, 157 Propane, 13 Protein system, 52 PSRK, 1 Pure, 58 Pyridine, 87 SAFT, 254 SCWO, 220 Second cross virial coefficients, 229 Silybin, 186 Sodium sulphate, 220 Solubility of electrolytes, 180 Solubility, 7, 26.

49.

Supercritical water oxidation of the PCB congener 2-chlorobiphenyl in methanol solutions: a kinetic analysis.
Christopher P O'Brien / Mark C Thies / David A Bruce, Environ Sci Technol, Sep 2005
...forms. This study examined the supercritical water oxidation (SCWO) of 2-chlorobiphenyl (2-PCB), using hydrogen peroxide as the...33.2 kJ/mol. The primary organic reaction products from the SCWO of 2-PCB were biphenyl at low temperatures (

50.

OPA oxidation rates in supercritical water.
Bambang Veriansyah / Jae-Duck Kim / Jong-Chol Lee / Youn-Woo Lee, J Hazard Mater, Sep 2005
...OPA), one of high-risk wastes resulting from munitions demilitarization, was investigated under supercritical water oxidation (SCWO) conditions in an isothermal tubular reactor. H2O2 was used as the oxidant. The reaction temperatures were ranged from 684 to...

51.

Catalytic desulfurization of residual oil through partial oxidation in supercritical water
Yuan, P.Q. / Cheng, Z.M. / Jiang, W.L. / Zhang, R. / Yuan, W.K., Jnl. of Supercritical Fluids, Aug 2005
...reduction mechanism of VR through catalytic SCWO. Catalytic desulfurization of residual...were carried out under an SCW oxidation (SCWO) environment in the presence of CoMo/gamma-Al2O3catalyst...desulfurization, the stability of catalyst in an SCWO environment was examined. It was found...

52.

Kinetic model of wet oxidation of phenol at basic pH using a copper catalyst
Santos, A. / Yustos, P. / Quintanilla, A. / Garcia-Ochoa, F., Chemical Engineering Science, Sep 2005
...oxidation (WAO), supercritical water oxidation (SCWO) and incineration. AOPs are commonly used...1997 Andreozzi et al., 1999). WAO and SCWO are attractive alternatives to treat an...5-200bar for WAO and above374?Cand 221bar for SCWO), WAO seems to be more accepted than SCWO...

53.

Reaction mechanism of styrene monomer recovery from waste polystyrene by supercritical solvents
Ke, H. / Li-hua, T. / Zi-bin, Z. / Cheng-fang, Z., Polymer Degradation and Stability, Aug 2005
...results[11,12]. Supercritical water oxidation (SCWO) is a rapidly emerging-waste-treatment method that...14]obtained high yield of styrene monomer using SCWO to pyrolyse polystyrene. Though SCWO has many advantages in cracking polymeric materials...

54.

Phosphate recovery from sewage sludge in combination with supercritical water oxidation.
K Stendahl / S Jäfverström, Water Sci Technol, Feb 2003
Supercritical Water Oxidation (SCWO) is an innovative and effective destruction method for organics in sewage sludge. The SCWO process leaves a slurry of inorganic ash...sludge. In a continuous pilot plant for the SCWO process digested sludge has been treated...

55.

Co-oxidation effects of methanol and benzene on the decomposition of 4-chlorobiphenyl in supercritical water
Anitescu, G. / Munteanu, V. / Tavlarides, L.L., The Journal of Supercritical Fluids, Feb 2005
...A comparison of 4CB reaction products (SCWO) shown by two GC-MSD chromatograms in presence...RPs). Table 3 Reaction products of 4CB SCWO at 773 K, 25 MPa, and 24.5 s residence...Introduction Supercritical water oxidation (SCWO) is a process developed in particular to...

56.

Supercritical water oxidation process under energetically self-sufficient operation
Cocero, M.J. / Alonso, E. / Sanz, M.T. / Fdz-Polanco, F., The Journal of Supercritical Fluids, Sep 2002
...study of the supercritical water oxidation (SCWO) process for diluted wastewater is presented...Introduction Supercritical water oxidation (SCWO) has demonstrated to be a powerful technology...determination of reaction heats in the SCWO process. Chen et al. [4] propose an oxidation...

57.

New approach for kinetic parameters determination for hydrothermal oxidation reaction
Mateos, D. / Portela, J.R. / Mercadier, J. / Marias, F. / Marraud, C. / Cansell, F., Jnl. of Supercritical Fluids, May 2005
...of water, the process is called supercritical water oxidation (SCWO) and it typically implies pressures and temperatures varying...kinetic studies on phenol, that the parameters obtained in WAO and SCWO could not be used in operating conditions different from those...

58.

Dynamical and structural properties of benzene in supercritical water
Carlos Nieto-Draghi / Josep Bonet Àvalos / Oliver Contreras / Philippe Ungerer / Jacqueline Ridard, The Journal of Chemical Physics, Nov 2004
...temperature conditions are of particular interest. Examples are supercritical water oxidation (SCWO) and supercritical extraction, among others. For instance, SCWO becomes an important application because it provides a reliable way to destroy biochemical...

59.

Wet peroxide oxidation of chlorophenols
Garcia-Molina, V. / Lopez-Arias, M. / Florczyk, M. / Chamarro, E. / Esplugas, S., Water Research, Mar 2005
...technologies Supercritical Water Oxidation (SCWO), Subcritical Oxidation or Wet Oxidation...operating costs (Catrinescu et al., 2003). SCWO takes place above the critical point of...as oxidizing agent is common to WO and SCWO processes. There is also one more process...

60.

Evaluation of biomass gasification in supercritical water process for hydrogen production
Calzavara, Y. / Joussot-Dubien, C. / Boissonnet, G. / Sarrade, S., Energy Conversion and Management, Mar 2005
Converting biomass into hydrogen can be accomplished in supercritical water. State of the art experiments are thoroughly presented. Chars and tars formation may be the most significant technological problem. However, catalysis should be...

61.

Temperature and pressure dependence of the absorption spectra and decay kinetics of solvated electrons in ethanol from...
Han, Z. / Katsumura, Y. / Lin, M. / He, H. / Muroya, Y. / Kudo, H., Chemical Physics Letters, Mar 2005
...destruction of the hazardous chemical waste has been proposed recently by employing supercritical water oxidization process (SCWO). On the other hand, comparing to water, the primary alcohols have much milder critical points, for example, for water and ethanol...

 

62.

Isochoric heat capacity measurements for a CO2 + n-decane mixture in the near-critical and supercritical regions
Polikhronidi, N.G. / Batyrova, R.G. / Abdulagatov, I.M. / Magee, J.W. / Stepanov, G.V., Jnl. of Supercritical Fluids, Mar 2005
...number of technological applications including coal conversion, organic synthesis, destructive oxidation of hazardous wastes (SCWO processes), enhanced oil recovery, activated carbon regeneration, formation of inorganic films and powders, supercritical chromatography...

63.

Pressurized hot water extraction coupled with supercritical water oxidation in remediation of sand and soil containing...
Kronholm, J. / Kalpala, J. / Hartonen, K. / Riekkola, M.-L., The Journal of Supercritical Fluids, Jun 2002
...PHWE) and supercritical water oxidation (SCWO) equipment was constructed to extract polyaromatic...performed safely and effectively, and the PHWE-SCWO procedure gave good extraction recoveries...extraction (PHWE) Supercritical water oxidation (SCWO) Soxhlet extraction Waste treatment 1 Introduction...

64.

Hydrothermal reactions of methylamine
Benjamin, K.M. / Savage, P.E., The Journal of Supercritical Fluids, Nov 2004
...typical of supercritical water oxidation (SCWO) reactors, the reaction seems to be governed...systems is supercritical water oxidation (SCWO). This waste treatment technology uses...oxidizing harmful organic compounds [3] . SCWO exploits the unique solvating properties...

65.

Supercritical waste hydrothermal treatment modelisation of non-stationary phenomena in a reactor
Dutournie, P. / Mercadier, J., The Journal of Supercritical Fluids, Dec 2004
...temperature. Super critical water oxidation (SCWO, P = 22.1 MPa and 374 = 99.99%) in relatively...1994 and treats chemical wastewater by SCWO. This unit treats 1 m 3 h -1 of liquid...simulation tools is necessary for scaling up SCWO process. Some authors [2-4] use trading...

66.

Real options and the value of generation capacity in the German electricity market
Hlouskova, J. / Kossmeier, S. / Obersteiner, M. / Schnabl, A., Review of Financial Economics, Jan 2005
...Vehicle MSL Mars Science Laboratory MSO Mars Science Observatory NTP Nuclear Thermal Propulsion PE polyethylene S/C spacecraft SCWO Super Critical Wet Oxidation SEM Surface Excursion Module SOHO Solar and Heliospheric Observatory SOI sphere of influence SPE...

 

67.

Comparison of the effects of the addition of NaOH on the decomposition of 2-chlorophenol and phenol in supercritical...
Lee, G. / Nunoura, T. / Matsumura, Y. / Yamamoto, K., The Journal of Supercritical Fluids, Dec 2002
The effects of the addition of NaOH on the decomposition of 2-chlorophenol (2CP) and phenol in supercritical water (SCW) and under supercritical water oxidation (SCWO) conditions were investigated. The experiments were conducted in a...

68.

Oxidation of 4-chloro-3-methylphenol in pressurized hot water in liquid and vapor phases
Kronholm, J. / Huhtala, S. / Haario, H. / Riekkola, M.-L., Advances in Environmental Research, Sep 2002
4-Chloro-3-methylphenol (c=2.0 mM), representing a model pollutant, was oxidized both in liquid and vapor phases. The oxidant (hydrogen peroxide) was used in an amount equivalent to 10 times that of the model pollutant. Space times were...

69.

Reactions of vanillic acid in sub- and supercritical water
Gonzalez, G. / Salvado, J. / Montane, D., The Journal of Supercritical Fluids, Sep 2004
The hydrothermal reactions of vanillic acid in water near the critical point have been investigated in a continuous tubular reactor at temperatures between 280 and 500^oC and pressures between 225 and 300bar. Formation of...

70.

Hot compressed water—a suitable and sustainable solvent and reaction medium?
E Dinjus / A Kruse, Journal of Physics: Condensed Matter, Apr 2004
...In supercritical water oxidation (SCWO) water is used as a medium in which organic...known as supercritical water oxidation (SCWO), has been worked out since the 1980s...from [2]). see [3–10, 36]). During the SCWO process, the organic compounds react completely...

71.

Sulfur transformations during supercritical water oxidation of a Chinese coal
Wang, T. / Zhu, X., Fuel, Dec 2003
...semi-continuous Supercritical Water Oxidation (SCWO) installation, indicated that the sulfur...containing sulfur in the effluents of coal SCWO were determined as sulfide, thiosulfate...time on the sulfur transformations during SCWO of coal were also investigated. Coal Supercritical...

72.

Generalized kinetic models for supercritical water oxidation of cutting oil wastes
Portela, J.R. / Nebot, E. / Martnez de la Ossa, E., The Journal of Supercritical Fluids, Oct 2001
...Spain Supercritical Water Oxidation (SCWO) has been proved to be a powerful technology...the literature about the application of SCWO to oily wastes. Even though these industrial...found in the literature. In this work, SCWO have been tested to treat cutting oil wastes...

73.

Raman spectroscopic study of CO2-NaCl-H2O mixtures in synthetic fluid inclusions at high temperatures
Chen, J. / Zheng, H. / Xiao, W. / Zeng, Y. / Weng, K., Geochimica et Cosmochimica Acta, Mar 2004
Mixtures of CO"2-NaCl-H"2O contained in synthetic fluid inclusions are studied by laser Raman spectroscopy at high temperatures. With increasing temperature, the band splitting (X) of @u"1-2@u"2 diad of spectrum of CO"2 presents more...

74.

Corrosion in high-temperature and supercritical water and aqueous solutions: a review
Kritzer, P., The Journal of Supercritical Fluids, Apr 2004
...is given and compared with an oxidative treatment in air at the same temperatures, but ambient pressure. Taking into account SCWO-typical oxygen concentrations of around 5 mol/kg and a reaction pressure of 25 MPa, this results in an oxygen partial pressure...

75.

A double-wall reactor for hydrothermal oxidation with supercritical water flow across the inner porous tube
Fauvel, E. / Joussot-Dubien, C. / Guichardon, P. / Charbit, G. / Charbit, F. / Sarrade, S., The Journal of Supercritical Fluids, Jan 2004
...Supercritical water oxidation process (SCWO), which involves the destruction of organic...dispose of those dangerous wastes. The SCWO advantages are linked to the special physical...precipitation are the two main limitations of SCWO process. They have to be overcome in order...

76.

Catalytic supercritical water oxidation of wastewater from terephthalic acid manufacturing process
Park, T.-J. / Lim, J.S. / Lee, Y.-W. / Kim, S.-H., The Journal of Supercritical Fluids, Aug 2003
...Therefore, supercritical water oxidation (SCWO) is known to be one of the most promising...compounds including PCBs and dioxins. Nowadays, SCWO is being applied in pilot plants and a...of a heterogeneous catalyst can improve SCWO for the complete conversion of aromatic...

77.

Electrochemical study of corrosion in aqueous high pressure, high temperature media and measurements of materials...
Delville, M.H. / Botella, P. / Jaszay, T. / Frayret, J.P., The Journal of Supercritical Fluids, Jun 2003
...applications to the hydrothermal treatments of organic wastes by SCWO M.H. Delville a * * Corresponding author. Tel.: +33-5-5684-8460...are particularly dangerous and rapidly corrode the reactor of SCWO pilots. We, therefore, undertook a study of different aqueous...

78.

Kinetic comparison between subcritical and supercritical water oxidation of phenol
Portela, J.R. / Nebot, E. / Martnez de la Ossa, E., Chemical Engineering Journal, Jan 2001
...WAO) and supercritical water oxidation (SCWO) processes have been studied by numerous...referred to as super critical water oxidation (SCWO), is carried out at pressures and temperatures...for a given organic, i.e. phenol [7] . SCWO is a promising emerging technology, not...

79.

Magnetic inhomogeneity and valence state in SrCrWO double perovskite
Jinhui Wang / Gongqiang Liu / Wei Zhong / Youwei Du, Journal of Applied Physics, Dec 2002
...this article, the (designated herein as SCWO) ceramics without ferrous ion have been...per formula unit for completely ordered SCWO, only half of that of In this article...properties as well as XPS and FMR spectra for SCWO. II. EXPERIMENT The SCWO ceramics were...

80.

Editorial
Johnstone, H., Filtration and Separation, Jun 2003
...precious metals from spent catalysts is now available. We find out more about the AquaCat (R) supercritical water oxidation (SCWO) process on p.16-19. Continuing the product recovery theme we switch to the highly competitive brewing industry, where market...

81.

Experimental study, via current-potential curves, of the anodic behavior of Alloy C-276 and T60 titanium in chlorinated...
Botella, P. / Frayret, C. / Jaszay, T. / Delville, M.H., The Journal of Supercritical Fluids, Apr 2003
...build-up for supercritical water oxidation (SCWO) of organic wastes. These preliminary results...to the oxidative context of the media in SCWO processes. The determination of the corrosion...intrinsic resistance to corrosion phenomena in SCWO conditions. One of the main reasons of...

 

82.

Recovery of Precious Metal Catalysts with Supercritical Water Oxidation
Filtration and Separation, Jun 2003
...catalysts. ). The process utilizes supercritical water oxidation (SCWO) a technique previously patented by Chematur Engineering. When...Johnson Matthey and Chematur are now be able to provide an on-site SCWO plant, so that these hazardous materials can be treated at the...

83.

Destruction of PAHs from soil by using pressurized hot water extraction coupled with supercritical water oxidation
Kronholm, J. / Kuosmanen, T. / Hartonen, K. / Riekkola, M.-L., Waste Management, Jan 2003
...PHWE) and supercritical water oxidation (SCWO) are advanced techniques relying on water...effectively destructed in wastewater by SCWO: municipal and industrial wastewaters containing...oxygen are the most common oxidants used in SCWO, and the normal operating temperatures...

84.

Platinum catalysed wet oxidation of phenol in a stirred slurry reactor - The role of oxygen and phenol loads on...
Masende, Z.P.G. / Kuster, B.F.M. / Ptasinski, K.J. / Janssen, F.J.J.G. / Katima, J.H.Y. / Schouten, J.C., Catalysis Today, Apr 2003
...phenol first followed by phenol Pt platinum SCWO supercritical water oxidation S.E. stoichiometric...identified during supercritical water oxidation (SCWO) of phenol [10] . Phenol reaction networks in SCWO have been recently reviewed [10] , in which...

85.

Platinum catalysed wet oxidation of phenol in a stirred slurry reactor - A practical operation window
Masende, Z.P.G. / Kuster, B.F.M. / Ptasinski, K.J. / Janssen, F.J.J.G. / Katima, J.H.Y. / Schouten, J.C., Applied Catalysis B: Environmental, Mar 2003
...selectivity to compound i (%) Sc Schmidt number SCWO supercritical water oxidation S.E. stoichiometric...etc. [5] . Supercritical water oxidation (SCWO) processes are carried out at supercritical conditions. A recent review [6] on SCWO processes shows that complete and rapid...

86.

Uncertainty quantification in reacting-flow simulations through non-intrusive spectral projection
Reagana, M.T. / Najm, H.N. / Ghanem, R.G. / Knio, O.M., Combustion and Flame, Feb 2003
...focus on supercritical water oxidation (SCWO). Supercritical water oxidation has been...rapidly and completely. The design of the SCWO process requires the development of appropriate...hydrogen-oxygen freely-propagating flame at SCWO conditions, computed with the Chemkin PREMIX...

87.

Muonium kinetics in sub- and supercritical water
Ghandi, K. / Addison-Jones, B. / Brodovitch, J.C. / Kecman, S. / McKenzie, I. / Percival, P.W., Physica B, Feb 2003
...destruction by supercritical water oxidation (SCWO) [1-3] and NCW or SCW for cooling and power...for the design and optimization of future SCWO reactors [2,3] as well as the next generation...to provide experimental data relevant to SCWO processes and the radiolysis of water in...

88.

A computational model for supercritical water oxidation of organic toxic wastes
Zhou, N. / Krishnan, A. / Vogel, F. / Peters, W.A., Advances in Environmental Research, Jun 2000
...simulate the supercritical water oxidation (SCWO) process for organic wastes. The SUPERTRAPP...reactor geometry was performed for methane SCWO in a co-axial reactor and the optimized...heat and chemistry simulations of methanol SCWO in the CSTR at MIT Energy Lab were also...

89.

Hydrogen generation from ethanol in supercritical water without catalyst
Arita, T. / Nakahara, K. / Nagami, K. / Kajimoto, O., Tetrahedron Letters, Jan 2003
...interest has been focused on the supercritical water oxidation (SCWO) to decompose hazardous chemicals such as PCB, dioxins and chlorinated...should be further oxidized to acetic acid as was observed in SCWO. 15 Thus, the absence of acetic acid production in the present...

90.

H4SiW12O40-catalyzed oxidation of nitrobenzene in supercritical water: kinetic and mechanistic aspects
Arslan-Alaton, I. / Ferry, J.L., Applied Catalysis B: Environmental, Oct 2002
...Introduction Supercritical water oxidation (SCWO) has been gaining importance as a feasible...hazardous waste. After extended exposure to the SCWO process, organic compounds are oxidized...requirements are the major goals of catalytic SCWO and several articles describing heterogeneously...

91.

Catalytic wet oxidation of phenol in a trickle bed reactor over a Pt/TiO2 catalyst
Maugans, C.B. / Akgerman, A., Water Research, Jan 2003
...including wet air oxidation (WAO), and supercritical water oxidation (SCWO). WAO involves treating the aqueous organics with air at elevated temperature and pressures [3-12] and SCWO is the same, but occurring above the critical point of water [13-20...

92.

Potentiometric pH measurements in acidic sulfate solutions at 250 oC relevant to pressure leaching
Seneviratne, D.S. / Papangelakis, V.G. / Zhou, X.Y. / Lvov, S.N., Hydrometallurgy, Feb 2003
A flow-through yttria-stabilized zirconia (FTYSZ) electrode has been employed for pH measurements at 250 ^oC in concentrated electrolyte systems relevant to hydrometallurgical processing of nickeliferous laterites. Experiments were...

93.

Life support approaches for Mars missions
Drysdale, A.E. / Ewert, M.K. / Hanford, A.J., Advances in Space Research, Jan 2003
...elsewhere. This oxidation can be done in a variety of ways, from PC systems such as incineration and super critical wet oxidation (SCWO) to biological systems such as composting. A high degree of food closure does have the advantage that there is very little waste...

94.

Recycling efficiencies of C,H,O,N,S, and P elements in a biological life support system based on micro-organisms and...
Gros, J.B. / Poughon, L. / Lasseur, C. / Tikhomirov, A.A., Advances in Space Research, Jan 2003
...dioxide required for the plant growth. Two ways can be considered. The first consists of a physico-chemical process (wet oxidation, SCWO, combustion/incineration) (Eckart, 1994), the second consists of taking advantage of the possible ability of the liquefying compartment...

95.

Modeling of supercritical water oxidation of phenol catalyzed by activated carbon
Nunoura, T. / Lee, G.H. / Matsumura, Y. / Yamamoto, K., Chemical Engineering Science, Aug 2002
...oxygen. Thus, supercritical water oxidation (SCWO) is an efficient technology for the ultimate...the problems for the application of the SCWO. For the purpose of mitigating the severity...application of a suitable catalyst to the SCWO at a lower operating temperature is efficient...

96.

Hydrothermal flames in supercritical water oxidation: investigation in a pilot scale continuous reactor
Serikawa, R.M. / Usui, T. / Nishimura, T. / Sato, H. / Hamada, S. / Sekino, H., Fuel, Jun 2002
...Introduction Supercritical water oxidation (SCWO) has been considered an alternative to...several wastes. The public image for SCWO is still a non-flame disposal and an extension process of wet oxidation. SCWO proceeds by bringing together an oxidant...

97.

Minimization of cobalt nuclide emissions in supercritical water oxidation of spent resin
Huang, Y.-J. / Paul Wang, H. / Li, C.-T. / Chien, Y.-C., Chemosphere, Feb 2000
...organics in the supercritical water oxidation (SCWO) of the Co-exchanged resin was found experimentally...formed and separated effectively in the SCWO process, a minimal release of the nuclide...species at elevated temperatures ( 1040 K). SCWO Low-level radioactive wastes Nuclide emission...

98.

Minimization of cobalt nuclide emissions in supercritical water oxidation of spent resin.
Y J Huang / H P Wang / C T Li / Y C Chien, Chemosphere, Feb 2000
...destruction of organics in the supercritical water oxidation (SCWO) of the Co-exchanged resin was found experimentally. Due to an...solubility of CoSO4 salt formed and separated effectively in the SCWO process, a minimal release of the nuclide Co would be warranted...

99.

Pressurised hot water extraction and thermal desorption of polycyclic aromatic hydrocarbons from sediment with use of a...
Andersson, T. / Hartonen, K. / Hyotylainen, T. / Riekkola, M.-L., Analytica Chimica Acta, Aug 2002
...directly to LC or LC-GC [13] . Finally, it is worth to mention, that PHWE can be online coupled with supercritical water oxidation (SCWO), which enables successive extraction and oxidation of PAHs from soil [14] . PAHs are formed by incomplete combustion of fossil...

100.

Research trends
Membrane Technology, Apr 2002
...wastewater Supercritical Water Oxidation (SCWO) was proposed almost 20 years ago as a...substances such as carbon dioxide and water. SCWO usually operates at a pressure of about...with other waste purification processes, SCWO is characterized by high investment and...

101.

Shape selectivity of trace by-products for supercritical water oxidation of 2-chlorophenol effected by CuO/ZSM-48
Lin, K.-S. / Wang, H.P., Applied Catalysis B: Environmental, Oct 1999
...by-products in supercritical water oxidation (SCWO) of 2-chlorophenol (2CP) catalyzed by CuO...Experimentally, destruction efficiency of 2CP in the SCWO process is effectively enhanced by CuO...Cl-reinsertion) is extremely suppressed in the SCWO of 2CP compared to those observed for zeolites...

102.

Elimination of cutting oil wastes by promoted hydrothermal oxidation
Portela, J.R. / Lopez, J. / Nebot, E. / Martnez de la Ossa, E., Journal of Hazardous Materials, Nov 2001
...WAO) and supercritical water oxidation (SCWO) are two forms of hydrothermal oxidation...due to the moderate temperatures used. SCWO is a more powerful process since operating...technology. In order to enhance WAO and SCWO efficiency at mild conditions, the use...

103.

Supercritical water oxidation of 2-chlorophenol effected by Li+ and CuO/Zeolites
Lin, K.-S. / Wang, H.P. / Yang, Y.W., Chemosphere, Oct 1999
...conversion of ZCP in superchtical wmer oxidabon (SCWO) process is eictive]y enhmced n the presence...phenols and PAHs. The global reachon mte of SCWO of 2CP hz the presence of LX is expressed...O]0 45. The undesired by-pmducts in the SCWO of ZCP are also extensive]y reduced ~a...

104.

Decomposition of aniline in supercritical water
Qi, X.-H. / Zhuang, Y.-Y. / Yuan, Y.-C. / Gu, W.-X., Journal of Hazardous Materials, Feb 2002
...the oxidation behavior of aniline with supercritical water oxidation (SCWO) process was studied. SCWO technology is a novel waste treatment process developed since 1980. The SCWO process takes advantage of the fact that above the critical point of...

105.

Elimination of cutting oil wastes by promoted hydrothermal oxidation.
J R Portela / J López / E Nebot / E Martínez de la Ossa, J Hazard Mater, Nov 2001
...WAO) and supercritical water oxidation (SCWO) are two forms of hydrothermal oxidation...due to the moderate temperatures used. SCWO is a more powerful process since operating...technology.In order to enhance WAO and SCWO efficiency at mild conditions, the use...

106.

Environment
Focus on Catalysts, Feb 2002
...conversion rate. European Chemical News, 17 Dec 2001, 75 (1986), 26 SCWO process for platinum group metals recovery A facility for the...mid-2002, and the Aqua Critox supercritical water oxidation (SCWO) process will be used to recover the metals. The technology has...

107.

Development of a solution model to correlate solubilities of inorganic compounds in water vapor under high temperatures...
Shin, H.Y. / Matsumoto, K. / Higashi, H. / Iwai, Y. / Arai, Y., The Journal of Supercritical Fluids, Oct 2001
...water vapor are important in the field such as SCWO (supercritical water oxidation) technology. SCWO is an emerging technology for the treatment...complete decomposition of such wastes. In the SCWO process, when organic compounds including halogen...

108.

Organic sulfur and hap removal from coal using hydrothermal treatment
Timpe, R.C. / Mann, M.D. / Pavlish, J.H. / Louie, P.K.K., Fuel Processing Technology, Oct 2001
...study of the economics of supercritical water oxidation (SCWO) for use in waste treatment has been done. The hardware...hydrothermal treatment are quite similar to that of SCWO, although in SCWO, operating conditions are substantially more severe...

109.

Catalytic decarboxylation of acetic acid with zirconia catalyst in supercritical water
Watanabe, M. / Inomata, H. / Smith, R.L. / Arai, K., Applied Catalysis A: General, Oct 2001
...intermediate of supercritical water oxidation (SCWO) process [10] , can be a probe for testing...destruction of acetic acid is low even in SCWO condition [10] , the rate of decomposition...development of a more rapid and lower energy cost SCWO process. Belsky et al. [11] conducted the...

110.

Global reaction heat of acetic acid oxidation in supercritical water
Aymonier, C. / Gratias, A. / Mercadier, J. / Cansell, F., The Journal of Supercritical Fluids, Nov 2001
...oxidation: research Chem. Oxid. 5 1995 1 [4] Schmieder H. Abeln J. SCWO: facts and hopes Wiss. Ber.-Forschungszent. Karlsruhe 6271 1999...materials during the process of Supercritical Water Oxidation (SCWO) The 6th Meeting on Supercritical Fluids: Chemistry and Materials...

111.

Catalyst activity, stability, and transformations during oxidation in supercritical water
Yu, J. / Savage, P.E., Applied Catalysis B: Environmental, May 2001
...exposure to supercritical water oxidation (SCWO) conditions, whereas the supported CuO...treated by supercritical water oxidation (SCWO). This technology [1-3] converts organic...critical point of water (374 C, 218 atm). SCWO is effective for a wide variety of potential...

112.

Partial oxidation of propane in sub- and supercritical water
Armbruster, U. / Martin, A. / Krepel, A., The Journal of Supercritical Fluids, Nov 2001
...interest during the last 20 years especially as a reaction medium for the total oxidation of wastes (supercritical water oxidation, SCWO [1] ). Meanwhile, this technology has been developed to commercial scale. The process usually is carried out at temperatures...

113.

Phenol oxidation over CuO/Al2O3 in supercritical water
Yu, J. / Savage, P.E., Applied Catalysis B: Environmental, Dec 2000
...non-catalytic supercritical water oxidation (SCWO). It also simultaneously reduced the yield...rate law used previously for catalytic SCWO of phenol over other transition metal oxides...technology termed supercritical water oxidation (SCWO). Conventional SCWO processes, which usually...

114.

Oxidation of printed circuit board wastes in supercritical water
Chien, Y.-C. / Wang, H.P. / Lin, K.-S. / Yang, Y.W., Water Research, Dec 2000
...enhanced in the supercritical water oxidation (SCWO) process. By X-ray diffraction (XRD) spectroscopy...bromine species from the resin matrix in the SCWO process. supercritical water printed circuit...Ca 2+ or K + in the early stage of the SCWO of 2-chlorophenol was observed ( Lin et...

115.

Hydrolysis and oxidative decomposition of ethyl acetate in sub- and super-critical water
Armbruster, U. / Martin, A. / Krepel, A., Applied Catalysis B: Environmental, Jun 2001
...dealing with the treatment of contaminated aqueous effluents under super-critical conditions (super-critical water oxidation, SCWO) to realise these advantages for disposal of hazardous compounds, e.g. [3] . Results were promising, but this technology still...

116.

Heterogeneous catalysis in supercritical water
Savage, P.E., Catalysis Today, Nov 2000
...goal of supercritical water oxidation (SCWO). This technology provides an alternative...severity of the processing conditions of SCWO and thereby improve the economics has motivated...thorough review of work related to catalytic SCWO, published by early 1996. Heterogeneous...

117.

Advances with supercritical fluids [review]
Hauthal, W.H., Chemosphere, Apr 2001
...Peng-Robinson-Stryjek-Vera e.o.s RK e.o.s. Redlich-Kwong equation of state SAFT statistical associating fluid theory sc supercritical SCWO supercritical water oxidation SFC supercritical fluid chromatography SFE supercritical fluid extraction SPE solid-phase extraction...

118.

Measurement of the high-pressure-high-temperature fluid phase behavior of the systems CF4+H2O, CF4+H2O+NaCl,...
Smits, P.J. / Peters, C.J. / de Swaan Arons, J., Fluid Phase Equilibria, Sep 1998
...high-pressure-high-temperature fluid phase behavior of model systems encountered in supercritical water oxidation processes (SCWO) for the destruction of CFCs has been detertnined experimentally. For that purpose, the following systems have been selected...

119.

Selected Titles
Polymer Contents, Feb 2001
...dioxide E.L.V. Goetheer, M.W AL. Baars, L.J.P. van den Broeke, E.W. Meijer, J.T F. Keurentjes 4634 Supercritical water oxidation (SCWO) for poly( ethylene terephthalate) (PET) industry effluents M.J. Cocero, E. Alonso, R. Torío, D. Vallelado, T. Sanz. F Fih-Pnlnnrn...

120.

SUWOX--a facility for the destruction of chlorinated hydrocarbons
Casal, V. / Schmidt, H., The Journal of Supercritical Fluids, Jun 1998
...resists the attack of hydrochloric acid under SCWO conditions. Tlle i`acility is equipped...water inside an altlmina reactol where the SCWO destructiotl takes place, and an inert...C) in the presence o` oxygen [ I ] The SCWO process brings together water, organics...

121.

Oxidation of 2,4-dichlorophenol in supercritical water
Kuen, S.L. / Wang, H.P. / Li, M.C., Chemosphere, Apr 1998
...p-dioxin, from supercritical water oxidation (SCWO) of DCP at 673 K werv determined. We also...B1998 Etsevier Science Ltd Yey words: SCWO, dichlorophenol, wer air oxidation, by...that the supercritical water oxidation (SCWO) process is very adaptable to meet the...

122.

Oxidation kinetics for methane/methanol mixtures in supercritical water
Savage, P.E. / Rovira, J. / Stylski, N. / Martino, C.J., The Journal of Supercritical Fluids, Apr 2000
...models for supercritical water oxidation (SCWO). Moreover, these results show that a mechanism-based...Introduction Supercritical water oxidation (SCWO) is a technology for treating organic wastes...c =218 atm.). To design and optimize an SCWO process, it is desirable to possess mathematical...

123.

Supercritical water oxidation of high concentrations of phenol
Matsumura, Y. / Nunoura, T. / Urase, T. / Yamamoto, K., Journal of Hazardous Materials, Apr 2000
...Introduction Supercritical water oxidation (SCWO) is a promising technology for treatment...compounds. The high efficiency with which SCWO decomposes stable organic compounds with...can be decomposed to less than 1% using SCWO at 673 K. It is known that at temperatures...

 

124.

Production of useful organic matter from sludge using hydrothermal treatment
Shanableh, A., Water Research, Feb 2000
...achieved using supercritical water oxidation (SCWO). Accordingly, hydrothermal treatment using SubCWO and SCWO can provide a useful sludge management option...SubCWO) and supercritical water oxidation (SCWO). Hydrothermal oxidation generates superior...

125.

An alternative method of oxidizing aqueous waste in supercritical water: oxygen supply by means of electrolysis
Misch, B. / Firus, A. / Brunner, G., The Journal of Supercritical Fluids, Jun 2000
...the water needed to be cleaned. Supercritical water oxidation (SCWO) is preferentially used for aqueous waste streams with too low...not only in scientific but also in industrial fields [6,7] . SCWO is an efficient treatment of polycyclic aromatic hydrocarbons...

126.

[Investigation on the elimination of organic substances in urine by supercritical water oxidation]
T Wang / M Yang / B Xiang / Z Shen, Space Med Med Eng (Beijing), Oct 1997
Application of Supercritical Water Oxidation (SCWO) to processing of human metabolic wastes of Controlled Ecological...substance elimination in urine and recover potable water. The SCWO of simulated urine was investigated with oxygen as the oxidant...

127.

Thiodiglycol hydrolysis and oxidation in sub- and supercritical water
Lachance, R. / Paschkewitz, J. / DiNaro, J. / Tester, J.W., The Journal of Supercritical Fluids, Nov 1999
...Introduction Supercritical water oxidation (SCWO) is an efficient and clean technology for...oxidation reactions. A detailed description of SCWO reactions can be found in reviews by Thomason...et al. [2] and Savage et al. [3,4] . The SCWO process brings together the organic contaminant...

128.

Use of supercritical fluids for different processes including new developments-a review
Marr, R. / Gamse, T., Chemical Engineering and Processing, Jan 2000
...these salts result in a sticky mass. Inserting oxygen into supercritical water causes oxidation (Supercritical Water Oxidation SCWO) and reaction rates are very high because a lot of substances are completely miscible with water under these conditions and therefore...

129.

Factors controlling corrosion in high-temperature aqueous solutions: a contribution to the dissociation and solubility...
Kritzer, P. / Boukis, N. / Dinjus, E., The Journal of Supercritical Fluids, Jul 1999
...organic wastes (supercritical water oxidation SCWO) [21-24] . In parallel with the increasing...phosphato complexes [51,54] . The process of SCWO brought a renaissance of corrosion investigations...concentrations of dissolved compounds. In the SCWO process, hazardous organic material (e...

130.

Interferometric Measurements of Gas Diffusivity in Supercritical Water
Kuge, K. / Murayama, Y. / Honda, T. / Kato, Y. / Yoshizawa, Y., Progress in Nuclear Energy, Jan 2000
...Lide D. R. (1975), Handbook of Chemistry and Physics, 56'* Ed., CRC Press, New York. Oe T. (1997), Waste Water Treatment by SCWO. J. of Japan Institute of Energy 76, 868. Saito S. (1996), The Science and Technology of Supercritical Fluids, Sankyo Business...

131.

Wet air oxidation: past, present and future
Luck, F., Catalysis Today, Oct 1999
...contrast to supercritical water oxygen (SCWO), a complete mineralization of the waste...results obtained in the first commercial SCWO unit, which treats wastes containing long-chain...and Ti have been shown to be stable in SCWO conditions and should be selected as catalyst...

132.

Low temperature oxidation of ammonia to nitrogen in liquid phase
Ukropec, R. / Kuster, B.F.M. / Schouten, J.C. / van Santen, R.A., Applied Catalysis B: Environmental, Oct 1999
...et al. [25] studied ammonia oxidation in supercritical water (SCWO) in the temperature range of 530-700 C at 24.6 MPa. They found...10% in a tubular reactor at 680 C. An evaluation of catalytic SCWO was performed in the work of Ding et al. [26] . The same author...

133.

Decomposition of 2-aminoethanol in sub- and supercritical water with/without hydrogen peroxide
Funazukuri, T. / Takahashi, M., Fuel, Jul 1999
...Decomposition 1 Introduction Supercritical water oxidation (SCWO) has been increasingly paid attention as a new...without catalysts. There are extensive reviews on SCWO [4] and wet oxidation [5] . In SCWO of various materials, the decomposition behaviour...

134.

Optimization models for determining nitric acid equilibria in supercritical water
Ziegler, K.J. / Lasdon, L. / Chlistunoff, J. / Johnston, K.P., Computers & Chemistry, Sep 1999
...et al., 1980 Miller and Bowman, 1989 Odenbrand et al., 1986 ). Hydrothermal oxidation (HO), or supercritical water oxidation (SCWO) ( Gloyna and Li, 1993 Tester et al., 1993 ), produces less NO x species than incineration due to thermodynamic and kinetic arguments...

135.

A hard-sphere volume-translated van der Waals equation of state for supercritical process modeling 1. Pure components
Kutney, M.C. / Dodd, V.S. / Smith, K.A. / Herzog, H.J. / Tester, J.W., Fluid Phase Equilibria, Feb 1997
...modeling supercritical water oxidation (SCWO) of liquid and slurried organic wastes. Kinetic and flow simulations of the SCWO process require accurate predictions...Pr 0.35) which is of importance in SCWO processes. To preserve simplicity and...

136.

Supercritical water oxidation of polychlorinated biphenyls using hydrogen peroxide
Hatakeda, K. / Ikushima, Y. / Sato, O. / Aizawa, T. / Saito, N., Chemical Engineering Science, Jul 1999
...same conditions. Furthermore, in a flow-reactor system in addition to the batch-reactor system, supercritical water oxidation (SCWO) of polychlorinated biphenyls (PCBs) such as 3-PCB and Kanechlor KC-300 (KC-300) using hydrogen peroxide was carried out at 30...

137.

Corrosion Screening Tests of High-Performance Ceramics in Supercritical Water Containing Oxygen and Hydrochloric Acid
Boukis, N. / Claussen, N. / Ebert, K. / Janssen, R. / Schacht, M., Journal of the European Ceramic Society, Jan 1997
...simulated supercritical lteater oxidation (SCWO) environn2ent lt as sneasured. Supercritival...ric acid 11as used to simulate tl~pical SCWO con- ditions after tl2e decon2position...promising new technology' 2 often called the SCWO process. Under these conditions oxygen...

138.

Deuteration of hexane by 2HCl in supercritical deuterium oxide
Yang, Y. / Evilia, R.F., The Journal of Supercritical Fluids, Jun 1999
...Introduction The potential of supercritical water oxidation (SCWO) for the environmentally benign destruction of organic wastes...importance in understanding the physical and chemical ramifications of SCWO and other reactions in this incompletely characterized medium...

139.

An approach to legal reasoning based on a hybrid decision-support system
Pal, K., Expert Systems with Applications, Jul 1999
This paper describes argument structures to generate plausible explanations for the conclusions reached by rule-based reasoning (RBR), and provides a means of integrating with case-based reasoning (CBR). The area of application is a...

140.

Ternary phase equilibria for the sodium chloride-sodium sulfate-water system at 200 and 250 bar up to 400oC
DiPippo, M.M. / Sako, K. / Tester, J.W., Fluid Phase Equilibria, Mar 1999
...Introduction Supercritical water oxidation (SCWO) is an emerging technology for the treatment of aqueous organic waste . SCWO is defined as oxidation which occurs in...primary sources of inorganic salts in SCWO processing. First, aqueous wastes containing...

141.

Solubility of individual polychlorinated biphenyl (PCB) congeners in supercritical fluids: CO2, CO2/MeOH and...
Anitescu, G. / Tavlarides, L.L., The Journal of Supercritical Fluids, Mar 1999
The solubilities of nine individual polychlorinated biphenyl (PCB) congeners 2-chlorobiphenyl, 4-chlorobiphenyl, 2,2'-dichlorobiphenyl, 4,4'-dichlorobiphenyl, 2,4',5-trichlorobiphenyl, 3,3',4,4'-tetrachlorobiphenyl,...

142.

A Short Enantioselective Synthesis of 1-Deoxy-L-xylulose by Antibody Catalysis
Shabat, D. / List, B. / Lerner, R.A. / Barbas, C.F., Tetrahedron Letters, Feb 1999
...intadk in X biosynthesis of thiain (vitin B,)' and pyfidoxi (vitnin B,)3. Both L- md D- enmtiomers = syn0esird by a wii rmEe of Scwo~misms ~m pynvic Kid md L- or D- gly=i*&, srtiwly.' hently [his sugs he in Xund to k an ems non-~vionA biosynthetic pRCU%Or t...

143.

Corrosion of zirconia ceramics in acidic solutions at high pressures and temperatures
Schacht, M. / Boukis, N. / Dinjus, E. / Ebert, K. / Janssen, R. / Meschke, F. / Claussen, N., Journal of the European Ceramic Society, Dec 1998
...is known as supercritical water oxidation (SCWO). The major problem for the safe operation of SCWO is the corrosion of the reactor materials...available on the corrosion of zirconia ceramics in SCWO environments. Hazlebeck et al reported that...

141.

Solubility of individual polychlorinated biphenyl (PCB) congeners in supercritical fluids: CO2, CO2/MeOH and...
Anitescu, G. / Tavlarides, L.L., The Journal of Supercritical Fluids, Mar 1999
The solubilities of nine individual polychlorinated biphenyl (PCB) congeners 2-chlorobiphenyl, 4-chlorobiphenyl, 2,2'-dichlorobiphenyl, 4,4'-dichlorobiphenyl, 2,4',5-trichlorobiphenyl, 3,3',4,4'-tetrachlorobiphenyl,...

142.

A Short Enantioselective Synthesis of 1-Deoxy-L-xylulose by Antibody Catalysis
Shabat, D. / List, B. / Lerner, R.A. / Barbas, C.F., Tetrahedron Letters, Feb 1999
...intadk in X biosynthesis of thiain (vitin B,)' and pyfidoxi (vitnin B,)3. Both L- md D- enmtiomers = syn0esird by a wii rmEe of Scwo~misms ~m pynvic Kid md L- or D- gly=i*&, srtiwly.' hently [his sugs he in Xund to k an ems non-~vionA biosynthetic pRCU%Or t...

143.

Corrosion of zirconia ceramics in acidic solutions at high pressures and temperatures
Schacht, M. / Boukis, N. / Dinjus, E. / Ebert, K. / Janssen, R. / Meschke, F. / Claussen, N., Journal of the European Ceramic Society, Dec 1998
...is known as supercritical water oxidation (SCWO). The major problem for the safe operation of SCWO is the corrosion of the reactor materials...available on the corrosion of zirconia ceramics in SCWO environments. Hazlebeck et al reported that...

144.

A Combined Modeling and Experimental Approach for Achieving a Simplified Closed Ecosystem
Turc, H.A. / Pintena, J. / Bagarri, P. / Gibiat, F. / Fabreguettes, V., Advances in Space Research, Jan 1999
...flow Liquid stacking Gas stacking Inputs / Outputs Seeding Injection, high C02 v v air ( low C02 weous emuent Injection \ Flonv SCWO reactor f eRespiratioLHarvest ,/Injection ' Grinding t-'Oxidation Transpiration 7tercolateWateringDilutionj Liquid emuent Transfer...

145.

Fast catalytic oxidation of phenol in supercritical water
Zhang, X. / Savage, P.E., Catalysis Today, May 1998
...Introduction Supe}critical water oxidation (SCWO) is an emer ging "green" technology for...industrial wastewater streams [1]. The SCWO process takes advantage of the unique properties...first commercial facility employing the SCWO process became opera tional in 1994 [2...

146.

Hydrothermal oxidation of Navy excess hazardous materials
Cohen, L.S. / Jensen, D. / Lee, G. / Ordway, D.W., Waste Management, Oct 1998
...water and NaHCO3 for neutralizing acidic HTO effluents. Process description HTO, also known as supercritical water oxidation (SCWO), is a high pressure oxidation process that blends air, water, and organic waste material in an oxidizer at temperatures and...

147.

Measurements of the heat capacity at constant volume of H2O+Na2SO4 in near-critical and supercritical water
Abdulagatov, I.M. / Dvoryanchikov, V.I. / Mursalov, B.A. / Kamalov, A.N., Fluid Phase Equilibria, Sep 1998
...importance in supercritical water oxidation (SCWO) technology and other industrial applications...solutions at the conditions encountered in SCWO and sodium sulfate is one of the most common...525-535 in prospective applications of SCWO [3]. Adding an electrolyte to water results...

148.

Supercritical water oxidation for the destruction of municipal excess sludge and alcohol distillery wastewater of...
Goto, M. / Nada, T. / Ogata, A. / Kodama, A. / Hirose, T., The Journal of Supercritical Fluids, Jun 1998
...clean solid (metal oxides, salts) and clean gas (0CO2. N ,), SCWO is a proc~ess where oxidation reaction takes place in water above...conductance, and solv.ttillg ability 111,12]. We have applied SCWO ~sith hydrogen peroxide as an oxidant to the treatmerlt of sludge...

149.

Studies on experimental adjuvanted influenza vaccines: comparison of immune stimulating complexes (IscomsTM) and...
Coulter, A. / Wong, T.-Y. / Drane, D. / Bates, J. / Macfarlan, R. / Cox, J., Vaccine, Jul 1998
...other vaccine s ompo- nents and potential (.ontamimarlts ('e.g. AilCLj,l- 11 were eluted as discrete pt aks. Vaccine preparation /SCwO)llST~. Lahoraory-scallh Iscomlt' X inz ~herc prepared hasically iry the ml~lllod o' ML in / ell.4'. Briefly. to the d kired all...

150.

Product distribution and reaction pathways for methylene chloride hydrolysis and oxidation under hydrothermal...
Marrone, P.A. / Gschwend, P.M. / Swallow, K.C. / Peters, W.A. / Tester, J.W., The Journal of Supercritical Fluids, Jul 1998
...Methylene chloride Hydrolysis: Oxidatil)ll Supercritical water: Reaction pathways 1. Introduction Oxidation in supercritical water (SCWO) shovvs strong promise as an innovative and effective means ,9f destroying hazardous organic coln * Corresponding author. Fax...

151.

Phenol oxidation kinetics in supercritical water
Oshima, Y. / Hori, K. / Toda, M. / Chommanad, T. / Koda, S., The Journal of Supercritical Fluids, Jun 1998
...account, a more detailed kinel:ic . . L . . analysls IS stlll under Investlgat:lon. 4. Conclusions The kinetic parameters in SCWO of phenol were experimentally determined. By regression analysis, the global rate of phenol disappearance was found tc~ be proportional...

152.

Chemical reactions and phase equilibria of model halocarbons and salts in sub- and supercritical water (200-300 bar,...
Tester, J.W. / Marrone, P.A. / DiPippo, M.M. / Sako, K. / Reagan, M.T. / Arias, T. / Peters, W.A., The Journal of Supercritical Fluids, Jun 1998
Experimental data and theoretical predictions of hydrolysis reaction kinetics of model halocarbons and phase equilibria of their associated neutralized salt reaction products are reported for a range of hydrothermal conditions....

153.

Oxidation rates of common organic compounds in supercritical water
Rice, S.F. / Steeper, R.R., Journal of Hazardous Materials, Apr 1998
...Introduction Supercritical water oxidation (SCWO) is a developing hazardous-waste-treatment...chemical/radiological mixed waste. The SCWO process is conceptually simple [1-3]. Organic...inorganic acid anions. The development of SCWO technology depends on solving several materials...

154.

Incorporation of Parametric Uncertainty into Complex Kinetic Mechanisms: Application to Hydrogen Oxidation in...
Phenix, B.D. / Dinaro, J.L. / Tatang, M.A. / Tester, J.W. / Howard, J.B. / Mcrae, G.J., Combustion and Flame, Jan 1998
...Background Supercritical water oxidation (SCWO) is a thermally based waste treatment technology...critical point of water (374C, 221 bar). SCWO has been shown to be an effective means...pilot and production scale units. In the SCWO process, aqueous waste is brought into...

155.

A reduced mechanism for methanol oxidation in supercritical water
Brock, E.E. / Savage, P.E. / Barker, J.R., Chemical Engineering Science, Mar 1998
...1996) as being the fastest for methanol SCWO. The two additional reactions that emerge...provide a complete mechanism for methanol SCWO, how- ever, because they do not include...tions. It is well known that combustion and SCWO kinetics often exhibit an induction period...

156.

Kinetics and mechanism of methane oxidation in supercritical water
Savage, P.E. / Jianli, Y. / Stylski, N. / Brock, E.E., The Journal of Supercritical Fluids, Apr 1998
...observe that the DCKM predicts methane to be more reactive under SCWO conditions than it was observed to be experimentally. The experimental...validating the mechanism and then using it to learn more about the SCWO chemistry. Accordingly, we saw no merit in tuning the model parameters...

157.

Oxidation of methanol over iron oxide based aerogels in supercritical CO2
Wang, C.-T. / Willey, R.J., Journal of Non-Crystalline Solids, Apr 1998
...enhanced oil recovery using supercritical CO 2 , and paraffin isomerization in supercritical fluids . Supercritical water oxidation (SCWO) is a rapidly developing technology for the destruction of a wide variety of organic hazardous wastes . Oxidation of aromatic...

158.

Catalytic wet oxidation of phenol over a Pt/TiO2 catalyst
Maugans, C.B. / Akgerman, A., Water Research, Dec 1997
...WAO), supercriti- cal water oxidation (SCWO), and catalytic wet oxidation (CWO). WAO...reaction effluent requiring further treatment. SCWO occurs at operating conditions above the...point of water (Pc = 218 atm, TC = 374OC). SCWO yields complete and rapid oxidation of...

159.

Hydrothermal decomposition and oxidation of p-nitroaniline in supercritical water
Dong, S.L. / Kye, S.P. / Young, W.N. / Kim, Y.-C. / Choul, H.L., Journal of Hazardous Materials, Oct 1997
...capability of supercritical water oxidation (SCWO) has been shown by several works [1-4...critical to more comprehensive uses of SCWO process. As noted in a previous study...nitrogen (N)-con- taining compounds by SCWO is of particular concern in two respects...

160.

An advanced Pd/Pt relative resistance sensor for the continuous monitoring of dissolved hydrogen in aqueous systems at...
Liu, C. / Macdonald, D.D., The Journal of Supercritical Fluids, Sep 1995
...monitoring may be necessary. Keywords:supercritical water oxidation (SCWO), palladium, hydrogen, hydrogen sensor, high-temperatureaqueous...Wallingford, CT 06492.has beenfocusedon supercritical-wateroxidation (SCWO), in which toxic organics are oxidizedto CO*, H20, and HX (X...

 

161.

Molecular Simulation Study of Speciation in Supercritical Aqueous NaCl Solutions
Chialvo, A.A. / Cummings, P.T. / Simonson, J.M. / Mesmer, R.e., Journal of Molecular Liquids, Nov 1997
...attractive solvent and reaction medium for complete oxidation of hazardous wastes [3-6], known as the supercritical water oxidation (SCWO) process. The unique combination of the dissolving power of a liquid combined with the transport properties of a gas and the...

162.

New reactor system for supercritical water oxidation and its application on phenol destruction
Koo, M. / Lee, W.K. / Lee, C.H., Chemical Engineering Science, Apr 1997
...INTRODLJCTION Supercritical water oxidation (SCWO) is an excellent waste-treatment process...into carbon dioxide and water. The idea of SCWO for wastewater treat- ment appeared in...projects for wastewater treatment using SCWO are under opera- tion in the U.S.A. and...

163.

Separation of metal oxides from supercritical water by crossflow microfiltration
Goemans, M.G.E. / Tiller, F.M. / Lixiong, L. / Gloyna, E.F., Journal of Membrane Science, Feb 1997
...1995. The supercritical water oxidation (SCWO) pro- cess is an effective treatment technology...124 (1997) l29 145 or generated in the SCWO process-may create a corrosive and erosive...the nature of crossflow filtration under SCWO conditions dictates special design considerations...

164.

Decomposition of nitrobenzene in supercritical water
Dong, S.L. / Sang, D.P., Journal of Hazardous Materials, Nov 1996
...Introduction Supercritical water oxidation (SCWO) is a promising waste treatment process...hazardous organic substances. The early SCWO works have demonstrated that high destruction...1-4]. As the destruction capability of SCWO has been demon- strated by these early...

165.

Oxidation reactors for water and wastewater treatment
Po, L.Y., Water Science and Technology, Jan 1997
...concentrations in the wastewater. For supercritical operations (SCWO), inorganic compounds (e.g. salts) are virtually insoluble in...where normally immiscible compounds fomm homogeneous mixtures. SCWO reactors will operate homogeneously, thus eliminating mass transfer...

166.

Methanol and Hydrogen Oxidation Kinetics in Water at Supercritical States
Alkam, M.K. / Pai, V.M. / Butler, P.B. / Pitz, W.J., Combustion and Flame, Jul 1996
...computational fluid dynamic (CFD) modeling efforts in SCWO, a two-step reduced reaction mechanism was constructed...the jth reaction step (kmol/m3-s) INTRODUCTION SCWO Background In supercritical water oxidation (SCWO), di- lute organics (2%-lOSo organic by weight...

167.

Recycling of inorganic nutrients for hydroponic crop production following incineration of inedible biomass
Bubenheim, D.L. / Wignarajah, K., Advances in Space Research, Jan 1997
...The three primary physical/chemical technologies currently being investigated are incineration, super critical water oxidation (SCWO), and steam reformation (2,4). The suitability of the products resulting from processing of wastes utilizing these technologies...

168.

The Relationship Between Electrochemical Behaviour and In-service Corrosion of WC Based Cemented Carbides
Human, A.M. / Exner, H.E., International Journal of Refractory Metals and Hard Materials, Jan 1997
In long-life applications, the corrosion properties of cemented carbides can have a large influence on overall performance. Cemented carbides with improved corrosion resistance have been developed and are now commercially available....

169.

Precipitation of sodium chloride and sodium sulfate in water from sub- to supercritical conditions: 150 to 550 oC, 100...
Armellini, F.J. / Tester, J.W. / Hong, G.T., The Journal of Supercritical Fluids, Sep 1994
...during the supercritical water oxidation (SCWO) waste treatment process were performed...missions. 5-7 Supercritical-wateroxidation (SCWO) is defined as oxidation that takes place...ternary system at apressure rel- evant to the SCWO process can be formed.Figure 12 shows isothermal...

170.

The solubility of 1:1 nitrate electrolytes in supercritical water
Dell'Orco, P. / Eaton, H. / Reynolds, T. / Buelow, S., The Journal of Supercritical Fluids, Sep 1995
...In this region, the hydrothermal treatment process in which oxidation occurs is known as supercritical-wateroxidation (SCWO).SCWO has been shown on laboratory scales to be an efficient method for the treatment of hazardous organic compounds. **2 At...

171.

Supercritical water oxidation of acetic acid by potassium permanganate
Chang, K.-C. / Li, L. / Gloyna, E.F., Journal of Hazardous Materials, Jan 1993
Supercritical water oxidation (SCWO) of acetic acid by potassium permanganate (KMnO"4) was studied. The experiments were performed in a batch reactor at temperatures and pressures, respectively, ranging from 400 ^oC to 460 ^oC and from 275...

172.

Two-phase ozonation of chlorinated organics
Bhattacharyya, D. / Van Dierdonck, T.F. / West, S.D. / Freshour, A.R., Journal of Hazardous Materials, Apr 1995
...without UV), and high temperature and pressure operations such as wet air oxidation (WAO) and supercritical water oxidation (SCWO) [1,2]. * Corresponding author. Tel: 606257-2794. Fax: 606257-7251. 0304-3894/95/$09.50 ( 1995 Elsevier Science B.V., All rights...

173.

On-line failure diagnosis for compression refrigeration plants
Grimmelius, H.T. / Woud, J.K. / Been, G., International Journal of Refrigeration, Jan 1995
...variables \X, / ~F , REFRIGERANT X 4 V Pci Pcrkc Poil - pco 8 Peso 6 Apf 5 ~cj10 (Jco - Ooil.l condo1 2 Oexpj 1 3 evi I 4 f)evo I S Scwo l 6 Ocwi 1 7 (Jchwi1 8 chwe lc ll vref amb The system boundary is defined around the chiller, as indicated in Fi0ure 4. This...

174.

Supercritical water oxidation: an engineering update
Gloyna, E.F. / Li, L., Waste Management, Jan 1993
...concepts of supercritical water oxidation (SCWO), associated engineering research, and...During the last few years a growing body of SCWO knowledge has been assembled. A number...requirements, and process integration. SCWO technology relies on the unique properties...

175.

Fate of chromium and lead in supercritical water oxidation environment
Gloyna, E.F., Waste Management, Jan 1994
...lead in supercritical water oxidation (SCWO) environments, and b) the effect of additives...ids, the fate of chromium and lead in SCWO envi- ronments as oxidation and corrosion...reaction species on the potential toxicity of SCWO effluents is not clearly understood. Such...

176.

Analysis of post-combustion products from waste-derived fuel by FTIR spectroscopy
Lindner, J.S. / Cook, R.L., Waste Management, Jan 1994
...lead in supercritical water oxidation (SCWO) environments, and b) the effect of additives...ids, the fate of chromium and lead in SCWO envi- ronments as oxidation and corrosion...reaction species on the potential toxicity of SCWO effluents is not clearly understood. Such...

177.

Experimental methods for studying salt nucleation and growth from supercritical water
Armellini, F.J. / Teste, J.W., The Journal of Supercritical Fluids, Dec 1991
...formation during Supercritical Water Oxidation (SCWO), which is an emerging waste treatment...and size of particles formed during the SCWO process. Keywords:supercritical water...missions. 4~5 Supercriticalwater oxidation (SCWO) is defined as oxidation that takes place...

178.

Catalytic supercritical water oxidation of 1,4-dichlorobenzene
Jin, L. / Ding, Z. / Abraham, M.A., Chemical Engineering Science, Jun 1992
...oxidation in supercritical water, and catalytic SCWO at 374 C. F7 Catalytic supercritical water...any reaction time, - although catalytic SCWO provided s -~ comparable conversion after...surface reaction with adsorbed oxygen. In SCWO (even in the absence of the catalyst...

179.

Subcritical and supercritical water oxidation of CELSS model wastes
Takahashi, Y. / Wydeven, T. / Koo, C., Advances in Space Research, Jan 1989
...WO) and supercrltlcal water oxidation (SCWO) are presently the most hopeful candidate...the waste treatment techniques of WO and SCWO still have many problems to be solved...and nitrogen are important because WO or SCWO Is intended to work as a complete oxidizer...

180.

Incineration for resource recovery in a closed ecological life support system
Upadhye, R.S. / Wignarajah, K. / Wydeven, T., Environment International, Jan 1993
...oxidation, and supercritical water oxidation (SCWO). Nonthermal processes under investigation...Jagow 1972). Waste destruction by the SCWO process makes use of water in its supercritical...needed to yield a sterile product and 3) The SCWO process operates at a lower temperature...

181.

Variation of mean SiO bond lengths in silicon-oxygen octahedra
Baur, W.H., Journal of Solid State Chemistry, Dec 1977
...coordination against oxygen is 0.407 A. Recently Reid et al. (1) have reported on the synthesis of high-pressure pyrochlore-type ScWO!,4! and Iny'Sif'O!,4' (the superscripts refer to the coordination numbers of the atoms). This adds two more compounds to the...

182.

In situ remediation through contaminant mobilization by vacuum stripping combined with biodegradation
Akgerman, A. / Autenrieth, R. / Bonner, J., Journal of Hazardous Materials, Dec 1992
Project number 041TAM0203

183.

The telephone in question: Questions on communication
Claisse, G. / Rowe, F., Computer Networks and ISDN Systems, Jan 1987
The household use of the telephone is not well known. Who telephones? Why? To whom? Over and above the diversity of telephone conversations, is it possible to identify different telephone habits? Using a survey of telephone calls (7252...

184.

Spectrochemical Determination of Scandium in Silicate Rocks
Kvalheim, A. / Streck, L.W., Spectrochimica Acta, Jan 1939
...04 ^-o-e / / of the lines above the cathode continuum in the photographic spefctrum, because in the cathode n.a A /Sc win v'Scwo layer method the image of the arc is focused on the spectrograph slit, which is therefore not uniformly illuminated along its...

 

185.

Optimal chain partitions of trees
Misra, J. / Tarjan, R.E., Information Processing Letters, Sep 1975
...University esf Texas at ..4us#», Awtft Texar 787th USA Ead.-e TAttJAN a D1epØtwnt.of EkcdíØl Engfneeringáad Conkpt4r Scwo.saes.&tat the ñlectrnnics Rewmh LabØntory, 4lfAtfrerdty of ØfornTa at BErkeley, Berke?ey, C,A 94?20, llSA ~r ttaoeÃ...

186.

Electrochemical investigation of palladium complexes with organic sulphides and their use in extraction differential...
Budnikov, H.C. / Maystrenko, V.N. / Murinov, Y.I., Talanta, Jan 1987
...on the electrochemical reduction ofpalladium(II) complexes with organic sulphides, with composition PdL^Cl, where m=l, L=C,A,SCWO (I) C6H,COCH(CH3)CH2SC2H,lO TO C(H,COCH(CH2SC,,H,3), (ffl) m = 1, L = QHjCOC^SCgHp (IV) (QH,3),S (V) (C,Hp),S (VI) in an acetonitrile-toluene...

187.

A convenient setting for differential calculus
Seip, U., Journal of Pure and Applied Algebra, Jan 1979
Barr Received February 1977 Cartesian closed categories play an important rôle in many aspects of mathematics. They appear in algebraic geometry, in logic, in topology. Quite naturally one is tempted to use this notion also for differential calculus.

188.

Electronic structure of evaporated and annealed tungsten oxide films studied with UPS
Hochst, H. / Bringans, R.D., Applications of Surface Science, Jul 1982
...during the annealing 6~0 6.0T 5.5 5 ~ EF~0J ‘ 31 EFaCIt ‘31 3.0 A — 3.0 —~~‘ ‘\ ~ I aWO~ SCWO 3.5 pc-W03 4 ‘0 I , 4,0 • 4.0 a-w03 300 500 700 900 1100 300 500 7~0 900 1100 ANNEAL TEMP~ (K) ANNEAL TEMP(K) Fig...

 

PUB. APP. NO.

Title

1

20060162912

Heat exchanger

2

20060088460

Systems and methods for air purification using supercritical water oxidation

3

20050182147

Method for processing spent ion-exchange resins

4

20050006317

Systems and methods for water purification through supercritical oxidation

5

20040232088

Process and plant for the recovery of phosphorus and coagulants from sludge

6

20040020616

Process for recovering inorganic material from deinking sludge

7

20040011746

Method and device for oxidising materials in supercritical water

8

20030146310

Method, process and apparatus for high pressure plasma catalytic treatment of dense fluids

9

20030075514

System and method for solids transport in hydrothermal processes

10

20030057164

Hydrothermal treatment system and method

11

20020179541

Process for hydrothermal treatment of materials

12

20020162332

Hydrothermal conversion and separation

13

20020113024

Process and device for supercritical wet oxidation

14

20020086150

System and method for hydrothermal reactions-two layer liner

15

20020084559

System and method for hydrothermal reactions-three layer liner

16

20020070179

Process and device for supercritical wet oxidation

Results of Search in PGPUB Production Database for:
"Supercritical water"
: 183 applications. [2001~2006]

 

PUB. APP. NO.

Title

1

20060193928

Novel herbal compositions and process for preparation thereof

2

20060187751

Device for mixing two fluids and use thereof for cooling a very high temperature fluid

3

20060185245

Pyrolysis process for producing fuel gas

4

20060185244

Novel production method of gaseous fuels

5

20060183951

Method for producing methane gas

6

20060182677

Process for preparing fine metal oxide particles

7

20060167286

Process for epoxidation and catalyst to be used therein

8

20060163117

Fragmentation of heavy hydrocarbons using an ozone-containing fragmentation fluid

9

20060162912

Heat exchanger

10

20060149118

Process and plant for the hydrothermal treatment of asbestos and/or asbestos-containing materials in supercritical water

11

20060134415

Boron nitride-aluminum (ban) interfaces and coatings and methods for their production and use

12

20060131753

Materials and methods for forming hybrid organic-inorganic dielectric materials for integrated circuit applications

13

20060124783

Process for conversion and size reduction of solid particles

14

20060122451

Binding and in situ destruction of chemical agents and other contaminants

15

20060099434

Low-friction and low-wear solid body sliding system

16

20060097228

Continuous synthetic process of phosphor in supercritical water and apparatus being used therein

17

20060088460

Systems and methods for air purification using supercritical water oxidation

18

20060069223

Polymerization of vinylidenefluoride (VF2) in a supercritical fluid medium

19

20060065017

Method of treating waste glass

20

20060060541

Waste disposal method and apparatus using wet oxidation and deep well injection

21

20060060109

Process for producing pigment complex and pigment-containing composition

22

20060057388

Aligned and open-ended nanotube structure and method for making the same

23

20060056572

Method and device for the production of electricity from the heat produced in the core of at least one high temperature nuclear reactor

24

20060039524

Multi-layered ceramic tube for fuel containment barrier and other applications in nuclear and fossil power plants

25

20060025596

Method for deuteration or tritiation of heterocyclic ring

26

20060014275

Cell culture carrier and jig for cell culture

27

20060011890

Phosphor and production process for the same

28

20060011511

Heavy oil reforming method, an apparatus therefor, and gas turbine power generation system

29

20050277274

METHOD OF SYNTHESIZING HYBRID METAL OXIDE MATERIALS AND APPLICATIONS THEREOF

30

20050272961

Processes for the production of xylitol

31

20050269272

Apparatus and method for treatment of chemical and biological hazards

32

20050267345

Applications of light-emitting nanoparticles

33

20050267314

Process for producing methionine

34

20050266697

Light-emitting nanoparticles and method of making same

35

20050261450

Polymerization reaction apparatus, and method of producing polymer using this apparatus

36

20050260326

Method of manufacturing plant finished product

37

20050249639

Fluid element

38

20050227468

Semiconductor device with spacer having batch and non-batch layers

39

20050199263

Washing method and washing device

40

20050196332

Method and apparatus for regenerating an iron-based Fischer-Tropsch catalyst

41

20050182147

Method for processing spent ion-exchange resins

42

20050177013

Thermobaric molecular fractionation

43

20050175829

Rubber composition and tire obtained from the same

44

20050172639

Repowering steam plant through addition of gas turbine and method for remodeling plant facilities

45

20050158203

Nickel- based alloy with excellent corrosion resistance in inorganic-acid-containing supercritical water environment

46

20050154237

Process for production of hydrogen and carbonyl compounds by reacting sub-or super-critical water with alcohols

47

20050152820

High temperature high pressure capsule for processing materials in supercritical fluids

48

20050143574

Process for producing a polyester

49

20050136292

Thin film dielectrics with perovskite structure and preparation thereof

50

20050130449

Method of forming an oxide layer using a mixture of a supercritical state fluid and an oxidizing agent

51

20050119448

Method of producing lactic acid

52

20050106895

Supercritical water application for oxide formation

53

20050087217

Substrate treating method, substrate-processing apparatus, developing method, method of manufacturing a semiconductor device, and method of cleaning a developing solution nozzle

54

20050085646

Process for epoxidation and catalyst to be used therein

55

20050077241

Method and apparatus for continuous separation and reaction using supercritical fluid

56

20050075436

Homogenous compositions of polymers and crystalline solids or cross-linking agents and methods of making the same

57

20050072137

Heavy oil reforming method, an apparatus therefor, and gas turbine power generation system

58

20050064599

Matericlas handling and sampling

59

20050064577

Hydrogen production with photosynthetic organisms and from biomass derived therefrom

60

20050061461

Production of paper board and cardboard

61

20050058592

Method and apparatus for converting both halogens in organic halides and organic compounds to inorganic substances

62

20050054891

Treatment apparatus and treatment method for organic waste

63

20050047869

Containerless sheet flow water ride

64

20050042149

Nanoscale chemical synthesis

65

20050040081

Heavy oil treating method and heavy oil treating system

66

20050010025

Resin composition and manufacturing method thereof

67

20050006317

Systems and methods for water purification through supercritical oxidation

68

20050002850

Methods of oxidizing multiwalled carbon nanotubes

69

20040241070

Method for preparing single crystalline cerium oxide powders

70

20040238791

Reinforcement of the effect of optical brighteners by means of polymers

71

20040232088

Process and plant for the recovery of phosphorus and coagulants from sludge

72

20040232072

System and device for processing supercritical and subcritical fluid

73

20040232046

Method and apparatus for recycling hydrocarbon resource

74

20040221507

Method and apparatus for providing hydrogen

75

20040202604

Method and apparatus for converting both halogens in organic halides and organic compounds to inorganic substances

76

20040199030

Process for production of high-temperature and high-pressure fluid and high-temperature and high-pressure reaction system

77

20040199006

Production of aromatic carboxylic acids

78

20040188713

Poly(organosiloxane) materials and methods for hybrid organic-inorganic dielectrics for integrated circuit applications

79

20040188356

System for producing large particle precipitates

80

20040182533

Method for increasing the whiteness of paper by means of cationic polyelectrolytes

81

20040174106

Insulated box body, refrigerator having the box body, and method of recycling materials for insulated box body

82

20040170538

Method and device for decomposing environmental pollutants

83

20040154764

Method for production of coated paper with extreme whiteness

84

20040144019

High pressure extraction

85

20040137209

Porous sintered composite materials

86

20040131980

Method for forming a pattern and substrate-processing apparatus

87

20040120990

Absorbent proteins and methods for using same

88

20040110993

Hydrothermal hydrolysis of halogenated compounds

89

20040097776

Method for decomposing nonmetallic honeycomb panel, and method for recycling the same

90

20040096586

System for deposition of mesoporous materials

91

20040094144

Reaction system of organic substances employing supercritical fluid or subcritical fluid

92

20040092782

Generation of a creosote-like mixture, or recovery of metals, or both from preserved wood by reaction in supercritical water

93

20040084296

Method decomposing fluorine-containing organic material

94

20040054199

Process for epoxidation and catalyst to be used therein

95

20040036018

Device and method for detecting trace amounts of organic components

96

20040034151

Graphite composites and methods of making such composites

97

20040033269

Critical fluid antimicrobial compositions and their use and generation

98

20040033189

Graphite intercalation and exfoliation process

99

20040029026

Substrate treating method, substrate-processing apparatus, developing method, method of manufacturing a semiconductor device, and method of cleaning a developing solution nozzle

100

20040020616

Process for recovering inorganic material from deinking sludge

101

20040020615

Paper coating slip containing n-vinyl formamide

102

20040012089

Materials and methods for forming hybrid organic-inorganic dielectric materials for integrated circuit applications

103

20040011746

Method and device for oxidising materials in supercritical water

104

20040008960

Stable organic-inorganic materials for waveguides, optical devices, and other applications

105

20040005131

Materials having low optical loss for waveguides and other optical devices

106

20040002617

Integrated circuits having organic-inorganic dielectric materials and methods for forming such integrated circuits

107

20030235933

Hybrid organic -inorganic materials for waveguides, optical devices, and other applications

108

20030231851

Hydrophobic materials for waveguides, optical devices, and other applications

109

20030221361

Method of converting agricultural waste to liquid fuel cell and associated apparatus

110

20030220531

Low-temperature hydrocarbon production from oxygenated hydrocarbons

111

20030205453

Organic compound decomposing method

112

20030203156

Stretched film having independent voids and method for producing the same

113

20030188740

Method for production of enhanced traceable immunizing drinking water and other liquid and gas products, devices for production and use thereof, and use of the enhanced products for immunizing living beings

114

20030187308

PROCESS FOR SPLITTING WATER-SOLUBLE ETHERS

115

20030185733

Precious metal recovery from organics-precious metal compositions with supercritical water reactant

116

20030168381

Process and apparatus for treating heavy oil with supercritical water and power generation system equipped with heavy oil treating apparatus

117

20030164339

Process for producing sterile water for injection from potable water

118

20030162913

Method for high pressure polymerization of ethylene in the presence of supercritical water

119

20030157265

Reaction vessel of oxidization and decomposition processing equipment by supercritical water and method for manufacturing the same

120

20030155999

Reacting device

121

20030154590

Circuit member processor

122

20030148088

Light emitting photonic crystals

123

20030146310

Method, process and apparatus for high pressure plasma catalytic treatment of dense fluids

124

20030141301

High temperature high pressure capsule for processing materials in supercritical fluids

125

20030134917

Method of manufacturing rigid polyurethane foam material, method of manufacturing refrigerator, and refrigerator

126

20030129103

Method of separating electrophotographic carrier compositions and recycling the compositions

127

20030121701

Hydrothermal drilling method and system

128

20030106467

Cement, reduced-carbon ash and controlled mineral formation using sub-and supercritical high-velocity free-jet expansion into fuel-fired combustor fireballs

129

20030103721

Optical demultiplexer based on three-dimensionally periodic photonic crystals

130

20030088093

Method of production of lactam

131

20030075514

System and method for solids transport in hydrothermal processes

132

20030062163

Pretreatment processes for heavy oil and carbonaceous materials

133

20030057164

Hydrothermal treatment system and method

134

20030050520

Waste treatment process and system

135

20030044685

Carbon fiber, electrode material for lithium secondary battery, and lithium secondary battery

136

20030044615

Carbon fiber, and filter and absorbent using the same

137

20030044602

Vapor grown carbon fiber and electrode material for battery

138

20030034486

Applications of light-emitting nanoparticles

139

20030029604

Filter-heat exchanger

140

20030027294

Process for producing polyester, process for producing substituted a-hydroxy acid, and clostridium beijerinckii strain hica432

141

20030026982

Carbon fiber having catalytic metal supported thereon

142

20030022788

Ceramic catalyst body

143

20030018187

Method for forming cellulose

144

20030013280

Semiconductor thin film forming method, production methods for semiconductor device and electrooptical device, devices used for these methods, and semiconductor device and electrooptical device

145

20030012328

SUPERCRITICAL-PRESSURE WATER COOLED REACTOR AND POWER GENERATION PLANT

146

20030010024

Methods and systems for reducing or eliminating the production of pollutants during combustion of carbon-containing fuels

147

20030007905

Ceramic filter and catalyst-loaded ceramic filter

148

20030003770

Method for removing foreign matter, method for forming film, semiconductor device and film forming apparatus

149

20030003604

Method for removing foreign matter, method for forming film, semiconductor device and film forming apparatus

150

20030003300

Light-emitting nanoparticles and method of making same

151

20020182505

Electrode material for lithium secondary battery, and lithium secondary battery using the same

152

20020180609

Metal/metal oxide sensor apparatus and methods regarding same

153

20020180155

Surf toy action figure and simulated surfing game

154

20020179541

Process for hydrothermal treatment of materials

155

20020169243

RUBBER COMPOSITION AND TIRE COMPRISING THE SAME

156

20020162332

Hydrothermal conversion and separation

157

20020144664

Heating of fuels

158

20020141934

Graphitic polyhedral crystals in the form of nanotubes, whiskers and nanorods, methods for their production and uses thereof

159

20020141140

Electrode material for electric double layer capacitor and electric double layer capacitor using the same

160

20020137836

Fluorinated carbon fiber, and active material for battery and solid lubricant using the same

161

20020136882

Carbon fiber product, composite using the same, conductive resin, and method of adjusting length of carbon fiber product

162

20020136881

Expanded carbon fiber product and composite using the same

163

20020136682

Carbon fiber for field electron emitter and method for manufacturing field electron emitter

164

20020113024

Process and device for supercritical wet oxidation

165

20020086150

System and method for hydrothermal reactions-two layer liner

166

20020084559

System and method for hydrothermal reactions-three layer liner

167

20020083959

Method for removing foreign matter, method for forming film, semiconductor device and film forming apparatus

168

20020083492

Basidiomycete peroxidase gene-transferred plant and a method for decomposing and removing hazardous chemicals using the same

169

20020077409

LOW-MODULUS POLYMER COMPOSITION AND SEALANT USING THE SAME

170

20020072422

Containerless sheet flow water ride

171

20020071802

Rare earth oxide fluoride nanoparticles and hydrothermal method for forming nanoparticles

172

20020070179

Process and device for supercritical wet oxidation

173

20020062046

Alkylation and acylation reactions

174

20020057755

Nuclear power plant system and method of operating the same

175

20020040864

Pyrolysis processing for solid waste resource recovery

176

20020028968

Production of aromatic carboxylic acids

177

20020013507

Method and apparatus for converting both halogens in organic halides and organic compounds to inorganic substances

178

20020006367

APPARATUS FOR CONVERTING A PLASTIC WASTE INTO OIL

179

20010050215

Process for producing sterile water for injection from potable water

180

20010048882

Dual diaphragm pump

181

20010047980

Process for converting a metal carbide to diamond by etching in halogens

182

20010040135

Method of treating waste water and apparatus for treating waste water using the method

183

20010039327

Aliphatic polyester, method for manufacturing aliphatic polyester, and method for recycling cellulose

184

20010037860

Etching method and apparatus

185

20010036976

Method of manufacturing rigid polyurethane foam material, method of manufacturing refrigerator, and refrigerator

186

20010022206

Reaction vessel of oxidization and decomposition processing equipment by supercritical water and method for manufacturing the same

187

20010019037

Three dimensionally periodic structural assemblies on nanometer and longer scales

188

20010010306

Etching method and apparatus

189

20010007649

Organic compound decomposing method

 

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