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Proceedings World Bioenergy 2010

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Chlorine Index: Cl content (%) of the sample dry weight.<br />

According to [1], [7]:<br />

if Cl < 0.2 low slagging trend<br />

if 0.2 < Cl < 0.3 medium trend<br />

if 0.3 < Cl < 0.5 high trend<br />

if Cl > 0.5 very high trend<br />

; whereas [11 ] gives a more conservative threshold:<br />

if Cl > 0.1 corrosion and HCl emissions<br />

2.2.Ash Fusion Temperatures.<br />

Ashes fusion is a continuous process which can be<br />

characterized by the following temperatures, according to<br />

norms ISO 540:2008 and DIN 51730:1998-04:<br />

Deformation temperature (DT). Temperature at<br />

which the first signs of rounding, due to melting, of the<br />

tip or edges of the test piece occur.<br />

Sphere temperature (ST). The temperature at which<br />

the edges of the test piece become completely round,<br />

with its height being equal to the width of the base line.<br />

Hemisphere temperature (HT). The temperature at<br />

which the test piece is approximately hemispherical, with<br />

the height being equal to half the base diameter.<br />

Flow temperature (FT). The temperature at which the<br />

test piece material has spread out so that its height is onethird<br />

of that at the hemisphere temperature.<br />

A large number of authors have proposed predictive<br />

functions of ash fusion temperatures from ash<br />

composition for coals (i.e. see [4] for a comprehensive<br />

review). Information on such predictive functions for<br />

biomass, however, remains scarce (i.e. [12], [13]).<br />

.Mineral composition in biomass differs significantly<br />

from coal, especially in the amount of potassium, calcium<br />

and chlorine, therefore, most appropriate slagging indices<br />

definition and threshold calibration, as well as ash fusion<br />

predictive functions must be different [9].<br />

Additionally, biomass disintegration laboratory tests have<br />

recently been proposed as a complementary means to<br />

characterize slagging tendency of biomass fuels, with<br />

significant potential to reproduce sintering and fouling<br />

behaviour observed in biomass boiler combustion tests<br />

[14].<br />

Results using the above mentioned methodologies for<br />

characterizing slagging and fouling tendency of various<br />

Mediterranean biomass fuels are presented.<br />

The effect of ash composition on ash behaviour as<br />

characterized by laboratory ash fusion and ash<br />

disintegration tests and boiler combustion tests, as well as<br />

the potential of biomass ash slagging indices to predict<br />

ash behaviour in terms of slagging and fouling hazard is<br />

discussed below.<br />

2. SLAGGING AND FOULING RISK OF<br />

MEDITERRANEAN BIOMASSES IN COMBUSTION<br />

Various recent studies (i.e. [01], [02], [03] and [04]) have<br />

recently analyzed the slagging and fouling tendency of<br />

several forest and agricultural residues and energy crops<br />

by means of laboratory ash characterization tests and<br />

combustion tests in Spain.<br />

The results of the ash composition of some of the main<br />

Mediterranean biomasses analyzed by these studies are<br />

synthezised in Table I below.<br />

Table I: Ash composition (wt% dry basis) at 550 ºC of<br />

various Mediterranean Biomasses from studies [01], [02],<br />

[03] and [04] in Spain.<br />

Sample SiO2 Al2O3 Fe2O3 CaO MgO Na2O K2O P2O5 Ref.<br />

Poplar I 2.80 -- -- 33 3.70 0.14 18 -- [14]<br />

Poplar II 4.20 0.34 0.36 29 3.00 0.14 16 3.00 [15]<br />

Eucalyptus 41 -- -- 18 4.20 1.90 8.70 -- [14]<br />

Thistle I 13 -- -- 14 2.50 9.20 15 -- [14]<br />

Thistle II 20 -- -- 33 3.30 4.70 6.60 -- [14]<br />

Almond<br />

shell I<br />

Almond<br />

shell II<br />

Olive<br />

stontes<br />

4.60 -- -- 15 1.50 0.30 22 -- [14]<br />

3.50 0.49 0.27 16 2.60 0.49 31 2.40 [17]<br />

24 -- -- 4.40 1.70 0.52 27 -- [14]<br />

Brassica I 7.60 0.61 0.28 23 3.20 0.69 21 9.10 [15]<br />

Brassica II 1.30 0.16 0.60 25 2.70 1.10 27 8.40 [16]<br />

Wheat<br />

straw<br />

44 -- -- 8.10 2.40 0.22 18 -- [14]<br />

Rice straw 51 -- -- 8.9 3.5 2.8 16 -- [14]<br />

Sorghum 40 2.60 1.00 5.50 2.50 0.29 23 2.10 [16]<br />

Forest biomasses (i.e. Poplar, Eucalyptus chips) have<br />

very beneficial properties for combustion, namely a high<br />

Ca content, low silica content, and generally lower K<br />

content when compared to most agricultural feedstocks<br />

and residues, this resulting in high initial deformation<br />

and ash fusion temperatures, generally well above 1200-<br />

1400 ºC, as shown in Table II.<br />

It has to be noted, however, that woody fuels can often be<br />

contaminated during harvest operations with soil<br />

particles, resulting in a higher silica content (i.e.<br />

Eucalyptus sample in Table I), which can lower the ash<br />

fusion temperatures. This situation has been noted by<br />

various authors (i.e. [18]. More careful harvest methods<br />

need to be implemented in order to minimize soil<br />

contamination.<br />

Herbaceous fuels such as brassica, wheat and sorghum<br />

have large contents of both silica and potassium, resulting<br />

in the potential formation of K silicates (i.e. [4], [8],<br />

[19]). These compounds create deposits in the boiler,<br />

potentially causing slagging and fouling problems at<br />

temperatures above 700-800ºC, as illustrated by the<br />

sintering temperatures DT in Table II.<br />

Table II. Ash fusibility temperature of various<br />

Mediterranean feedstocks from Spain.<br />

world bioenergy <strong>2010</strong><br />

13

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