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   The gasification of biomass materials was initially
    used commercialy in the 1940’s as a source of
    gaseous fuels for internal combustion engines,
    over the next 30-40 years, a number of small
    and medium sized biomass gasification units
    were introduced for heat and power generation
    applications.
   With the increasing interest in the development
    of renewable energy technologies over the past
    20 years or so, there has been a significant
    increase in the technical interest in biomass
    gasification processes, particularly in North
    America and in Europe.
Based on scale of operation and the product gas quality
    requirements, which operate under very different
    condition;
• Fixed bed and moving bed systems, which tend, for
biomass, to be at the smaller end of the scale, from a few
kWth up to around 10 MWth, principally for the production of
heat, but also for small scale power generation.
•Fluidised bed gasifier, generally operate in the MW range,
and are generally of two types,i.e. bubbling fluidised bed
(BFB) gasifiers and circulating fluidised bed (CFB) gasifiers. In
the main, the CFB units tend to be towards the larger end of
the scale, i.e. above around 15 MWth
•Entrained flow gasifier are generally larger units for power
generation and operate at very high temperatures, in excess
of 1200 C and for very short residence times. These are
normally fired with fossil fuels, and are co-fired with
biomass materials at relatively low co-firing ratios.
Scheme




 Updraft moving
  bed gasifier
circulating fluidized
    bed gasifier
Entrained flow gasifier
   The fusion or partial fusion of the ash
    components can result in the formation of ash
    agglomerates in fixed bed and fluidised bed
    reactors, leading to poor air distribution and
    difficulties with ash removal from the system.
   The formation of ash deposits on the furnace and
    heat exchanger surfaces,
   The carryover of particulate material and of
    nitrogen, sulphur and chlorine-containing
    species, along with condensable organic species,
    into the heat exchangers and gas clean-up
    systems, and
   The utilisation/disposal of the solid residues
    from the plant.
A. Fixed Bed Gasifier
Because the temperatures in the oxidation zone
   can be up to around 1200 C or so,
   particularly in updraft gasifiers, there’s
   potential for significant ash fusion to occur
   in these system. The succesful operation of
   fixed bed reactors depends to a large extent
   on maintenance of a good bed structure,
   good air and gas distribution through the
   bed and the effective operation of the ash
   take-off system
Fluidised Bed Gasifier
The fouling of furnace and heat exchanger surfaces,
 and the formation of ash agglomerates and the
 subsequent defluidisation of the bed, are key
 processes issues, and these have been fairly
 extensively studied at laboratory, pilot plant and
 industrial scale.
-For the biomass ashes rich in silica or using a silica
 bed material, the risks of bed agglomeration were
 high, with significant melting of the ash
 temperatures at around 800 C, i.e. at normal bed
 temperatures for fluidised bed gasification system
 for biomass materials,
-For the biomass ashes rich in CaO or when
 processes using a CaO-rich bed material, the risks
 of bed agglomeration at normal bed temperatures
 were significantly lower.
In practice, the key to avoiding bed agglomeration is the
  establishment of good fuel and air distributors, and operation at
  a bed temperature that is appropriate for the chemistry and
  fusion behaviour of the fuel ash, and bed material. It is also
  apparent that circulating fluidised beds, which operate at
  significantly higher fluidisation velocities, are generally less
  prone to bed agglomeration problems than are bubbling beds.
 Entrained flow gasifier.
More commonly,biomass and waste material have been co-fired in
  large coal-fired integrated gasification combined cycle (IGCC)
  plants and significant technical work has been done on the ash-
  related impacts. The majority of the entrained flow gasification
  systems for coal fire dry milled fuel or aqueous slurries, and are
  designed to operate at very high temperatures and for short
  residence times. The pre-milled biomass materials are normally
  mixed with the fossil fuel feed material. A portion of the ash is
  retained within the reactor and is drawn off at a slag tap at the
  bottom. The fly ash carried over from the reactor normally
  comprises small molten ash particles entrained in the syngas.
The fouling of heat exchangers and other plant components has
  been one of the most common problem areas with
  gasification systems for biomass at industrial scale. The
  syngas produced from the gasification of biomass materials
  can have significant levels of both inorganic and organic
  volatile species, which can condense on cooled surfaces in
  the syngas coolers and gas cleaning system. This has been a
  significant issue in industrial plants, both in dedicated
  biomass gasification system and in the co-gasification of
  biomass with coal in large gasifier, and has been the subject
  of intensive study over the past few years. The deposition
  mechanisms and the design of the syngas coolers had been
  seriously underestimated by the plant designers and that
  these issues should be the subjects of significant further
  study.
The Major undesirable constituents of the syngas are :
-Particulate materials entrained in the syngas
-Low and high molecular weight organic compounds
  (tars),
-H2S, COS and other sulphur gas,
-NH3, HCN, and ther nitrogen-containing species,
-Other impurities, including HCl, and volatilised alkali
  metals and heavy metals.
Fabric and ceramic filters, and electrostatic
  precipitator, are capable of particulate collection
  efficiencies are capable of particulate collection
  efficiencies appropriate to the utilisation of the
  syngases in gas engine and gas turbine applications.
-As with the ash residues from combustion
   processes, the preferred route for utilisation
   of the gasifier residues is to recycle them
   directly to the land on which the fuel was
   produced, or utilise the residues as low grade
   fertiliser.
 -Biomass gasifier and boiler system generates
   two major solid discard streams:
a. The biomass/waste gasifier bottom ash
b. The boiler filter ash
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Overview biomass ash in gasification system

  • 1.
  • 2. The gasification of biomass materials was initially used commercialy in the 1940’s as a source of gaseous fuels for internal combustion engines, over the next 30-40 years, a number of small and medium sized biomass gasification units were introduced for heat and power generation applications.  With the increasing interest in the development of renewable energy technologies over the past 20 years or so, there has been a significant increase in the technical interest in biomass gasification processes, particularly in North America and in Europe.
  • 3. Based on scale of operation and the product gas quality requirements, which operate under very different condition; • Fixed bed and moving bed systems, which tend, for biomass, to be at the smaller end of the scale, from a few kWth up to around 10 MWth, principally for the production of heat, but also for small scale power generation. •Fluidised bed gasifier, generally operate in the MW range, and are generally of two types,i.e. bubbling fluidised bed (BFB) gasifiers and circulating fluidised bed (CFB) gasifiers. In the main, the CFB units tend to be towards the larger end of the scale, i.e. above around 15 MWth •Entrained flow gasifier are generally larger units for power generation and operate at very high temperatures, in excess of 1200 C and for very short residence times. These are normally fired with fossil fuels, and are co-fired with biomass materials at relatively low co-firing ratios.
  • 4. Scheme Updraft moving bed gasifier
  • 5. circulating fluidized bed gasifier
  • 7. The fusion or partial fusion of the ash components can result in the formation of ash agglomerates in fixed bed and fluidised bed reactors, leading to poor air distribution and difficulties with ash removal from the system.  The formation of ash deposits on the furnace and heat exchanger surfaces,  The carryover of particulate material and of nitrogen, sulphur and chlorine-containing species, along with condensable organic species, into the heat exchangers and gas clean-up systems, and  The utilisation/disposal of the solid residues from the plant.
  • 8. A. Fixed Bed Gasifier Because the temperatures in the oxidation zone can be up to around 1200 C or so, particularly in updraft gasifiers, there’s potential for significant ash fusion to occur in these system. The succesful operation of fixed bed reactors depends to a large extent on maintenance of a good bed structure, good air and gas distribution through the bed and the effective operation of the ash take-off system
  • 9. Fluidised Bed Gasifier The fouling of furnace and heat exchanger surfaces, and the formation of ash agglomerates and the subsequent defluidisation of the bed, are key processes issues, and these have been fairly extensively studied at laboratory, pilot plant and industrial scale. -For the biomass ashes rich in silica or using a silica bed material, the risks of bed agglomeration were high, with significant melting of the ash temperatures at around 800 C, i.e. at normal bed temperatures for fluidised bed gasification system for biomass materials, -For the biomass ashes rich in CaO or when processes using a CaO-rich bed material, the risks of bed agglomeration at normal bed temperatures were significantly lower.
  • 10. In practice, the key to avoiding bed agglomeration is the establishment of good fuel and air distributors, and operation at a bed temperature that is appropriate for the chemistry and fusion behaviour of the fuel ash, and bed material. It is also apparent that circulating fluidised beds, which operate at significantly higher fluidisation velocities, are generally less prone to bed agglomeration problems than are bubbling beds.  Entrained flow gasifier. More commonly,biomass and waste material have been co-fired in large coal-fired integrated gasification combined cycle (IGCC) plants and significant technical work has been done on the ash- related impacts. The majority of the entrained flow gasification systems for coal fire dry milled fuel or aqueous slurries, and are designed to operate at very high temperatures and for short residence times. The pre-milled biomass materials are normally mixed with the fossil fuel feed material. A portion of the ash is retained within the reactor and is drawn off at a slag tap at the bottom. The fly ash carried over from the reactor normally comprises small molten ash particles entrained in the syngas.
  • 11. The fouling of heat exchangers and other plant components has been one of the most common problem areas with gasification systems for biomass at industrial scale. The syngas produced from the gasification of biomass materials can have significant levels of both inorganic and organic volatile species, which can condense on cooled surfaces in the syngas coolers and gas cleaning system. This has been a significant issue in industrial plants, both in dedicated biomass gasification system and in the co-gasification of biomass with coal in large gasifier, and has been the subject of intensive study over the past few years. The deposition mechanisms and the design of the syngas coolers had been seriously underestimated by the plant designers and that these issues should be the subjects of significant further study.
  • 12. The Major undesirable constituents of the syngas are : -Particulate materials entrained in the syngas -Low and high molecular weight organic compounds (tars), -H2S, COS and other sulphur gas, -NH3, HCN, and ther nitrogen-containing species, -Other impurities, including HCl, and volatilised alkali metals and heavy metals. Fabric and ceramic filters, and electrostatic precipitator, are capable of particulate collection efficiencies are capable of particulate collection efficiencies appropriate to the utilisation of the syngases in gas engine and gas turbine applications.
  • 13. -As with the ash residues from combustion processes, the preferred route for utilisation of the gasifier residues is to recycle them directly to the land on which the fuel was produced, or utilise the residues as low grade fertiliser. -Biomass gasifier and boiler system generates two major solid discard streams: a. The biomass/waste gasifier bottom ash b. The boiler filter ash