Thermochemical Conversion: Combustion, Torrefaction, Pyrolysis and Gasification

Ideally the ash content of biomass should be as low as possible for thermochemical conversion, as it poses many practical problems in the conversion process, ranging from slagging to corrosion of the reactor. A high nitrogen content in the biomass will lead to increased NOx emissions during combustion. Particularly undesirable in ash are Silicon (Si), Chlorine (Cl), Potassium (K) and Sulphur (S), as they form silicates, sulphates and alkali chlorides. For example, high potassium and chlorine

Table 8.6 Biomass requirements of various conversion techniques

Biomass

Conversion

type

Reactor

Type/size

Density

(kg/m3)

MC

(%)

Ash (%)

Combustion

Fixed grate

Chunks, briquettes 0 < 50 mm

As high as possible

<20

As low as possible

Suspension

boiler

Sawdust, small shavings 0 < 10 mm

150-200

<15

<5

FB or CFB boiler

Sawdust, small shavings, low alkali

0 < 50 mm

400-600

<50

<5

Gasification

Fixed bed

Wood chunks, briquettes etc. not too small 0 < 100 mm

100-600

<20

<10

Moving bed

Chips, pellets 0 < 50 mm

200-300

<15

<20

CFB

Chips

0 < 50 mm

200-500

<50

<10

Pyrolysis

Slow

Chips, pellets 0 < 70 mm

200-500

<15

<5

Alcoholic

fermentation

Fast

Pretreatment-

hydrolysis-

fermentation

Chips, pellets 0 < 5 mm Wet chips; never dried material

200-500

<10

<20

As low as possible

Anaerobic

digestion

Single stage

Chips, residues

Low

High

> 50%

N/A

contents can cause slagging and corrosion in the combustion unit (Skrifvars et al. 2004). For an efficient use of biomass for power generation, the amounts of K and Cl should thus be as low as possible. The ash content is typically also inversely related to the calorific value, making biomass with high ash content undesirable for combustion and gasification. For pyrolysis, solvent-leaching can be used as a de — ashing step for either the biomass feedstock or the char product, to increase the char adsorption properties (Carrier et al. 2012). These changes in char adsorption due to de-ashing are directly related to the pyrolysis rate and volatile yield (Raveendran and Ganesh 1998; Carrier et al. 2012).

Thermochemical conversion processes are well suited to uniform, densified feedstock, such as pyrolysis products or pellets (Stephen et al. 2010). Torrefaction is an example of such a pre-treatment step to decrease the MC of the biomass, while at the same time increasing the energy density and CV. Subsequent size reduction, such as grinding, before feeding the reactor is easier with torrefied biomass, as it is more brittle.

The Lignin content has a significant impact on the suitability of biomass for thermochemical conversion. Although the high CV of lignin makes it desirable for combustion and gasification, an increased lignin content also affects the rate of thermal degradation. As a result, biomass with a higher lignin content will pyrolyse more slowly, while wood with high cellulose content can be pyrolysed faster (Gani and Naruse 2007). The positive impact of lignin on the CV, however, generally outweighs the negative effects of reduced reaction rate.

In the case of vacuum pyrolysis of wood, extractives showed an inhibiting effect on the oil yield, as they inhibited the levoglucosan formation. Removal of extractives did modify the hemicelluloses composition significantly, as reflected by the similar acetic acid yield derived from wood and extractive-free wood material (Roy et al. 1990).