Abstract:The fuel properties of fast pyrolysis bio-oils differ significantly from those of fossil fuels. As transportation fuel, bio-oil is not suitable without upgrading because of its relatively low energy content, high water content, acidity, and poor storage stability. Upgrading of bio-oil has usually been done by treating the whole oil in a reactor. The problem with this treatment is that pyrolysis oil is a mixture of different compound groups, which all need different conditions and catalysts to react in a desira… Show more
“…7 Effective bio-oil fractionation prior to upgrading may be a valuable approach of producing liquid fuels and chemicals versus upgrading whole bio-oil. 2,8 Iowa State University has developed a fractionating bio-oil recovery system that allows for collection of bio-oil as heavy-ends (stage fraction (SF) 1 and SF 2), intermediate fractions (SF 3 and SF 4), consisting of monomeric compounds, and light ends (SF 5) that contain the majority of acids and water ( Figure 1). 9,10 Complete details on the reactor and recovery system can be found in Pollard et al 9 and Rover et al 10 The mass distribution (wet basis) when using red oak feedstock is approximately 40− 45 wt % for SF 1 and SF 2 heavy ends, 10 wt % for SF 3 and SF 4 intermediates, and 45−50 wt % of SF 5 light ends.…”
Phenolic oils were produced from fast pyrolysis of two different biomass feedstocks, red oak and corn stover, and evaluated in hydroprocessing tests for production of liquid hydrocarbon products. The phenolic oils were produced with a bio-oil fractionating process in combination with a simple water wash of the heavy ends from the fractionating process. Phenolic oils derived from the pyrolysis of red oak and corn stover were recovered with yields (wet biomass basis) of 28.7 and 14.9 wt %, respectively, and 54.3% and 60.0% on a carbon basis. Both precious metal catalysts and sulfided base metal catalyst were evaluated for hydrotreating the phenolic oils, as an extrapolation from whole bio-oil hydrotreatment. They were effective in removing heteroatoms with carbon yields as high as 81% (unadjusted for the 90% carbon balance). There was substantial heteroatom removal with residual O of only 0.4% to 5%, while N and S were reduced to less than 0.05%. Use of the precious metal catalysts resulted in more saturated products less completely hydrotreated compared to the sulfided base metal catalyst, which was operated at higher temperature. The liquid product was 42-52% gasoline range molecules and about 43% diesel range molecules. Particulate matter in the phenolic oils complicated operation of the reactors, causing plugging in the fixed-beds especially for the corn stover phenolic oil. This difficulty contrasts with the catalyst bed fouling and plugging, which is typically seen with hydrotreatment of whole bio-oil. This problem was substantially alleviated by filtering the phenolic oils before hydrotreating. More thorough washing of the phenolic oils during their preparation from the heavy ends of bio-oil or online filtration of pyrolysis vapors to remove particulate matter before condensation of the bio-oil fractions is recommended. ABSTRACT: Phenolic oils were produced from fast pyrolysis of two different biomass feedstocks, red oak and corn stover, and evaluated in hydroprocessing tests for production of liquid hydrocarbon products. The phenolic oils were produced with a bio-oil fractionating process in combination with a simple water wash of the heavy ends from the fractionating process. Phenolic oils derived from the pyrolysis of red oak and corn stover were recovered with yields (wet biomass basis) of 28.7 and 14.9 wt %, respectively, and 54.3% and 60.0% on a carbon basis. Both precious metal catalysts and sulfided base metal catalyst were evaluated for hydrotreating the phenolic oils, as an extrapolation from whole bio-oil hydrotreatment. They were effective in removing heteroatoms with carbon yields as high as 81% (unadjusted for the 90% carbon balance). There was substantial heteroatom removal with residual O of only 0.4% to 5%, while N and S were reduced to less than 0.05%. Use of the precious metal catalysts resulted in more saturated products less completely hydrotreated compared to the sulfided base metal catalyst, which was operated at higher temperature. The liquid product was 42−52% gasoline range...
“…7 Effective bio-oil fractionation prior to upgrading may be a valuable approach of producing liquid fuels and chemicals versus upgrading whole bio-oil. 2,8 Iowa State University has developed a fractionating bio-oil recovery system that allows for collection of bio-oil as heavy-ends (stage fraction (SF) 1 and SF 2), intermediate fractions (SF 3 and SF 4), consisting of monomeric compounds, and light ends (SF 5) that contain the majority of acids and water ( Figure 1). 9,10 Complete details on the reactor and recovery system can be found in Pollard et al 9 and Rover et al 10 The mass distribution (wet basis) when using red oak feedstock is approximately 40− 45 wt % for SF 1 and SF 2 heavy ends, 10 wt % for SF 3 and SF 4 intermediates, and 45−50 wt % of SF 5 light ends.…”
Phenolic oils were produced from fast pyrolysis of two different biomass feedstocks, red oak and corn stover, and evaluated in hydroprocessing tests for production of liquid hydrocarbon products. The phenolic oils were produced with a bio-oil fractionating process in combination with a simple water wash of the heavy ends from the fractionating process. Phenolic oils derived from the pyrolysis of red oak and corn stover were recovered with yields (wet biomass basis) of 28.7 and 14.9 wt %, respectively, and 54.3% and 60.0% on a carbon basis. Both precious metal catalysts and sulfided base metal catalyst were evaluated for hydrotreating the phenolic oils, as an extrapolation from whole bio-oil hydrotreatment. They were effective in removing heteroatoms with carbon yields as high as 81% (unadjusted for the 90% carbon balance). There was substantial heteroatom removal with residual O of only 0.4% to 5%, while N and S were reduced to less than 0.05%. Use of the precious metal catalysts resulted in more saturated products less completely hydrotreated compared to the sulfided base metal catalyst, which was operated at higher temperature. The liquid product was 42-52% gasoline range molecules and about 43% diesel range molecules. Particulate matter in the phenolic oils complicated operation of the reactors, causing plugging in the fixed-beds especially for the corn stover phenolic oil. This difficulty contrasts with the catalyst bed fouling and plugging, which is typically seen with hydrotreatment of whole bio-oil. This problem was substantially alleviated by filtering the phenolic oils before hydrotreating. More thorough washing of the phenolic oils during their preparation from the heavy ends of bio-oil or online filtration of pyrolysis vapors to remove particulate matter before condensation of the bio-oil fractions is recommended. ABSTRACT: Phenolic oils were produced from fast pyrolysis of two different biomass feedstocks, red oak and corn stover, and evaluated in hydroprocessing tests for production of liquid hydrocarbon products. The phenolic oils were produced with a bio-oil fractionating process in combination with a simple water wash of the heavy ends from the fractionating process. Phenolic oils derived from the pyrolysis of red oak and corn stover were recovered with yields (wet biomass basis) of 28.7 and 14.9 wt %, respectively, and 54.3% and 60.0% on a carbon basis. Both precious metal catalysts and sulfided base metal catalyst were evaluated for hydrotreating the phenolic oils, as an extrapolation from whole bio-oil hydrotreatment. They were effective in removing heteroatoms with carbon yields as high as 81% (unadjusted for the 90% carbon balance). There was substantial heteroatom removal with residual O of only 0.4% to 5%, while N and S were reduced to less than 0.05%. Use of the precious metal catalysts resulted in more saturated products less completely hydrotreated compared to the sulfided base metal catalyst, which was operated at higher temperature. The liquid product was 42−52% gasoline range...
“…Because this feedstock was used in the steam reforming experiments without any additional water, the subsequent S/C ratio was calculated to be 3.84. Aqueous pyrolysis oil obtained via water-induced phase separation has been shown to contain sugar-type compounds and light organics in a ratio of 3:1 [24]. Compared to this, the aqueous fraction that has been characterized and used in this study contained a clearly lower amount of sugar-type compounds.…”
Section: Feedstock Characterizationmentioning
confidence: 88%
“…The feedstock for the pyrolysis experiment was forest thinnings, and the pyrolysis was carried out at a temperature of 480 C. Fractional condensation of the pyrolysis vapours was achieved by operating the scrubbers at 65 C. The aqueous fraction, which was utilized in this i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 4 0 ( 2 0 1 5 ) 3 1 4 9 e3 1 5 7 study, was collected after the scrubbers via a secondary condensation system. The fractionation procedure is described in more detail by Lindfors et al [24].…”
Section: Bio-oil Preparation and Characterizationmentioning
confidence: 99%
“…'sugars' and low molecular weight oxygenates, exhibit different levels of suitability for steam reforming, it stands to reason that simply separating the pyrolysis oil into water-soluble and waterinsoluble fractions via phase separation is by no means an optimal solution. In addition to the solubility-based fractionation procedure which transfers both the sugars and the low molecular weight oxygenates into one single aqueous fraction, it is also possible to fractionate the pyrolysis oil components based on their volatility [23,24]. With this kind of approach, it is possible to manipulate the distribution of different pyrolysis oil components, and to obtain fractions which are enriched in certain products.…”
“…(2014) used a sieve-plate column (scrubber) on the pyrolysis vapor to condense it in the first stage of liquid recovery. To condense the vapor generated by the reactor in the first stage, direct and indirect cooling were applied to the liquid from the hot vapor; inlet direct cooling was applied in the sieve-plate column, then the thermal degradation reaction of the collected pyrolysis liquids was reduced (Lindfors et al, 2014). A hydrocarbon liquid was used as the liquid cooler in the scrubber.…”
Section: Lcs With Spray Quench and Distillationcolumnmentioning
Liquid smoke can be produced by using the pyrolysis process. Biomass, as the raw material, is heated in a pyrolysis reactor to generate pyrolysis vapor. The pyrolysis vapors coming from the reactor are condensed in a liquid collection system to produce liquid smoke. A liquid collection system is a device used to convert smoke into liquid. Liquid smoke is often also called bio-oil, which is widely used as a fuel, as a preservative, and as other chemical substances. The objective of this paper was to provide the latest information on improving the liquid collection system from existing papers, and conclude with some inputs and application strategies. Studies were performed using the product parameters, equipment, and operational conditions referred to in the existing journal articles. Using a proper liquid collection system will give a better result in the liquid collection process.
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