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14 декабря, 2021
Two main types of processes for production of bio-oils from biomass are flash pyrolysis and hydrothermal conversion, as shown in Fig.1. Both of the processes belong to the thermochemical platform in which feedstock organic compounds are converted into liquid products. An advantage of the thermochemical process is that it is relatively simple, usually requiring only one reactor, thus having a low capital cost. However, this process is nonselective, producing a wide range of products including a large amount of char (Huber & Dumesic, 2006).
The characteristic and technique feasibility of the two thermochemical processes for bio-oil production are compared in table 1. Flash pyrolysis is characterized by a short gas residence time (~1s), atmospheric pressure, a relatively high temperature (450-500 °C). Furthermore, feedstock drying is necessary. Hydrothermal processing (also referred to in the literature as liquefaction, hydrothermal pyrolysis, depolymerisation, solvolysis and direct liquefaction), is usually performed at lower temperatures (300-400 °C), longer residence times (0.2-1.0 hr.), and relatively high operating pressure (5-20 Mpa). Contrary to flash pyrolysis and gasification processes, drying the feedstock is not needed in the hydrothermal process, which makes it especially suitable for naturally wet biomass. However, a reducing gas and/or a catalyst is often included in the process in order to increase the oil yield and quality.
The reaction mechanisms of the two processes are different, which have been studied by many investigators (Demirba§, 2000a; Minowa et al., 1998). The hydrothermal process occurred in aqueous medium which involves complex sequences of reactions including solvolysis, dehydration, decarboxylation, and hydrogenation of functional groups, etc. (Chornet and Overend, 1985). The decomposition of cellulose was studied by Minowa et al. (1998). The effects of adding a sodium carbonate catalyst, a reduced nickel catalyst, and no
catalyst addition in the decomposition of cellulose in hot-compressed water were investigated. They found that hydrolysis can play an important role in forming glucose/oligomer, which can quickly decompose into non-glucose aqueous products, oil, char and gases (Fig. 2). Without a catalyst, char and gases were produced through oil as intermediates. However, in the presence of an alkali catalyst, char production was inhibited because the oil intermediates were stabilized, resulting in oil production. Reduced nickel was found to catalyze the steam reforming reaction of aqueous products as intermediates and the machination reaction. Typical yields of liquid products for hydrothermal conversion processes were in the range of 20-60%, depending on many factors including sustrate type, temperature, pressure, residence time, type of solvents, and catalysts employed (Xu and Etcheverry, 2008).
Methods |
Treatment condition/ requirement |
Reaction mechanism /process description |
Technique Feasibility |
|
Pros. |
Cons. |
|||
Flash/Fast Pyrolysis |
Relatively high temperature (450500 °C); a short residence time (~1s); atmosphere pressure; drying necessary |
The light small molecules are converted to oily products through homogeneous reactions in the gas phase |
High oil yield up to 80% on dry feed; lower capital cost; Commercialized already |
Poor quality of fuels obtained |
Hydrothermal Processing (HTU)/ liquefaction /hydrotherma l pyrolysis |
Lower temperature (300-400 °C); longer residence time (0.2-1.0 hr.); High pressure (5-20 Mpa); drying unnecessary |
Occurs in aqueous medium which involves complex sequences of reactions |
Better quality of fuels obtained (High PTU, low moisture content) |
Relatively low oil yield (2060%); Need high pressure equip, thus higher capital cost |
Table 1. Comparison of two typical thermochemical processes for bio-oil production |
Fig. 2. Reaction pathway for the hydrothermal processing of cellulose
With flash pyrolysis, the light small molecules are converted to oily products through homogeneous reactions in the gas phase. The principle of the biomass flash pyrolysis process is shown in Fig.3. Biomass is rapidly heated in the absence of air, vaporizes, and quickly condenses to bio-oil. The main product, bio-oil, is obtained in yields of up to 80% wt on dry feed, together with the by-product char and gas (Bridgewater and Peacocke, 2000).
Fig. 3. Reaction pathway for the biomass flash pyrolysis process
4.1 Related research development of flash pyrolysis and hydrothermal process
Flash pyrolysis for the production of liquids has developed considerably since the first experiments in the late 1970s. Several pyrolysis reactors and processes have been investigated and developed to the point where fast pyrolysis is now an accepted, feasible and viable route to renewable liquid fuels, chemicals and derived products. Since the 1990s, several research organizations have successfully established large-scale fast pyrolysis plants. Bridgwater and Peacocke (2000) have intensively reviewed the key features of fast pyrolysis and the resultant liquid product, and described the major reaction systems and processes that have been developed over the last 20 years.
Unlike flash pyrolysis, technological developments in the area of hydrothermal conversion present new ways to turn wastes to fuel. Hydrothermal processing was initially developed for turning coal into liquid fuels, but recently, the technique has been applied to a number of feedstocks, including woody biomass, agricultural residues, and organic wastes (e. g., animal wastes, municipal solid wastes (MSW), and sewage sludge). Table 2 summarizes representative literature data of hydrothermal processing of common types of biomass and the most influential operating parameters. As can be seen from Table 2, organic waste materials are more favourable than woody biomass and agricultural residues for hydrothermal processing, owing to their higher oil yield and the higher heating value of their bio-oil products.
This earlier work was very promising, showing that hydrothermal technology can be used as an efficient method to treat different types of biomass and produce a liquid biofuel. In particular, hydrothermal conversion processes present a unique approach to mitigate the environmental and economic problems related to disposing of large volumes of organic wastes. It not only reduces the pollutants, but also produces useful energy in the form of liquid fuel. Compared with flash pyrolysis, hydrothermal conversion is at an early developmental stage, and the reaction mechanisms and kinetics are not yet fully understood.
Raw Materials |
Reactor Capacity |
Temp. (°C) |
Pressure (Mpa) |
Time (min) |
Oil Yield (%) |
Heating Value(MJ/kg) |
Reference |
a) Woods |
|||||||
Beech |
— |
277-377 |
— |
25 |
13.8-28.4 |
27.6-31.3 |
Demirba§, et al., 2005a |
Spruce |
277-377 |
— |
25 |
13.8-25.8 |
28.3-33.9 |
Demirba§, et al., 2005b |
|
Sawdust |
0.2 L |
280 |
N/A |
7.2 |
— |
Karagoz et al., 2005 |
|
b) Agricultural residues |
|||||||
Corn stalk |
0.3 L |
300 |
10 Mpa |
30 |
28.3 on organic basis |
29.7 |
Minowa et al., 1998 |
Rice husk |
0.3 L |
300 |
10 Mpa |
30 |
28.8 on organic basis |
30.8 |
Minowa et al., 1998 |
Rice straw |
1.0 L |
260-350 |
6-18 Mpa |
3-5 |
13.0-38.35 |
27.6-35.8 |
Yuan et al., 2007 |
c) organic wastes |
|||||||
Swine manure |
1-L autoclave |
260-340 |
0-90 |
14.9-24.2 |
36.1 |
Xiu et al., 2010a |
|
Swine manure |
Continuous mode |
285-305 |
9-12 |
40-80 |
2.8-53.3 |
25.2-33.1 |
Ocfemia et al., 2006 |
Dairy manure |
Batch/ continuous mode |
250-380 |
10-34 |
50 |
Appell, et al., 1980 |
||
Sewage sludge |
5 t/d |
300 |
10 |
— |
48 |
37-39 |
Itoh, et al., 1994 |
Garbage |
0.3 L autoclave |
250-340 |
6-18 |
6-120 |
27.6 |
36 |
Minowa, et al., 1995 |
Sewage sludge |
0.3 L autoclave |
150-300 |
— |
0-180 |
44.5 |
35.7 |
Suzuki, et al., 1990 |
Sewage sludge |
4.2L microwave |
250-350 |
8-20 |
— |
30.7 |
36.4 |
Bohlmann, et al., 1999 |
MSW |
autoclave |
260-340 |
13-34 |
— |
32 |
46 |
Gharieb, et al., 1995 |
MSW |
autoclave |
295-450 |
— |
20-90 |
35-63.3 |
— |
Kranich et al., 1984 |
Sewage sludge |
20 kg/hr. |
300-360 |
10-18 |
5-20 |
~ |
30-35 |
Goudriaan et al., 2000 |
Table 2. Overview of literature on hydrothermal processing of common types of biomass |