Steam gasification of meat and bone meal in a two-stage fixed-bed reactor system

2011 ◽  
Vol 6 (1) ◽  
pp. 71-77 ◽  
Author(s):  
Chirayu G. Soni ◽  
Ajay K. Dalai ◽  
Todd Pugsley ◽  
Terry Fonstad
Fuel ◽  
2009 ◽  
Vol 88 (5) ◽  
pp. 920-925 ◽  
Author(s):  
C.G. Soni ◽  
Z. Wang ◽  
A.K. Dalai ◽  
T. Pugsley ◽  
T. Fonstad

2014 ◽  
Vol 39 (25) ◽  
pp. 13128-13135 ◽  
Author(s):  
Shaomin Liu ◽  
Jinglin Zhu ◽  
Mingqiang Chen ◽  
Wenping Xin ◽  
Zhonglian Yang ◽  
...  

2012 ◽  
Vol 608-609 ◽  
pp. 201-205
Author(s):  
Liu Yun Li ◽  
Hiroo Kunii ◽  
Masamitsu Yamauchi ◽  
Hee Joon Kim ◽  
Tadaaki Shimizu

Light gases were produced from biomass tar gasification using limonite and dolomite as catalysts. Experiments were performed in a fixed bed reactor with the gasification temperatures of 600–800 °C. Limonite gave the obvious effect on the tar gasification, and the light gases of hydrogen and carbon oxides were mainly obtained. Also, the gas yields depended on the catalytic temperature. Hydrogen yields tend to increasing with temperatures from 650 to 800 °C. The reaction equilibrium was changed by dolomite addition in the reactor system; hydrogen gas was doubled with the limonite and dolomite mixture compared to limonite only.


2013 ◽  
Vol 133 ◽  
pp. 127-133 ◽  
Author(s):  
Jingbo Wang ◽  
Bo Xiao ◽  
Shiming Liu ◽  
Zhiquan Hu ◽  
Piwen He ◽  
...  

2010 ◽  
Vol 35 (2) ◽  
pp. 397-404 ◽  
Author(s):  
Adam Smoliński ◽  
Krzysztof Stańczyk ◽  
Natalia Howaniec

Soil Systems ◽  
2020 ◽  
Vol 4 (2) ◽  
pp. 34
Author(s):  
Despina Vamvuka ◽  
Stelios Alexandrakis ◽  
George Alevizos ◽  
Antonios Stratakis

In the context of the current environmental policies of the European Union promoting the recycling and reuse of waste materials, this work aimed at investigating the environmental impact of ashes produced from the co-combustion of municipal solid wastes with olive kernel in a fixed bed unit. Lignite fly ash, silica fume, wheat straw ash, meat and bone meal biochar, and mixtures of them were used as stabilizing ash materials. All solids were characterized by physical, chemical and mineralogical analyses. Column leaching tests of unstabilized and stabilized ash through a quarzitic soil were conducted, simulating field conditions. pH, electrical conductivity, chloride, sulphate and phosphate ions, major and trace elements in the leachates were measured. The results showed that alkaline compounds were partially dissolved in water extracts, increasing their pH and thus decreasing the leachability of heavy metals from the ash. Cr leached from unstabilized ash reached a hazardous level. Upon the stabilization of ash, the concentrations of heavy metals in the extracts were reduced between 9% and 100%, and were below legislation limits for disposal, apart from Cr. The latter was achieved only when meat and bone meal biochar was used as stabilizer. Entrapment of ash elements was assigned to the amorphous silica and to the phosphates of the stabilizing materials, as well as complexed silicates formed during the process.


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