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VGB POWERTECH 10 (2020) - International Journal for Generation and Storage of Electricity and Heat

VGB PowerTech - International Journal for Generation and Storage of Electricity and Heat. Issue 7 (2020). Technical Journal of the VGB PowerTech Association. Energy is us! Power plant products/by-products.

VGB PowerTech - International Journal for Generation and Storage of Electricity and Heat. Issue 7 (2020).
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Wood fly ash as cement replacement <strong>VGB</strong> PowerTech <strong>10</strong> l <strong>2020</strong><br />

the water soluble concentrations in Ta -<br />

b l e 2 shows that in WA1 17 % Na <strong>and</strong><br />

85 % K are soluble, whereas in WA2 >74 %<br />

Na <strong>and</strong> 58 % K are soluble. Steenari et al.<br />

[1997] reported that in several WA samples<br />

K- <strong>and</strong> Na-feldspars, such as KAlSi,O,<br />

<strong>and</strong> (Na,Ca)Al(Si,Al),O, were found. These<br />

minerals are the main constituents <strong>of</strong> gravel<br />

<strong>and</strong> s<strong>and</strong>, which contaminate the fuel.<br />

Thus, K <strong>and</strong> Na can occur in WAs both in<br />

the <strong>for</strong>m <strong>of</strong> salts <strong>and</strong> feldspars, <strong>and</strong> the latter<br />

may be part <strong>of</strong> the insoluble fraction<br />

containing the two elements in the investigated<br />

WAs. The amorphous phase <strong>of</strong> the<br />

WAs might also contain K <strong>and</strong> Na, soluble<br />

as well as insoluble in water. The sum <strong>of</strong><br />

concentrations <strong>of</strong> the water soluble Cl,<br />

SO 4 , Na <strong>and</strong> K (Ta b l e 2 ) account <strong>for</strong> 82 %<br />

<strong>and</strong> 77 % <strong>of</strong> the total soluble mass (also<br />

given in Ta b l e 2 ). Other possible soluble<br />

phases are different oxides <strong>and</strong> hydroxides<br />

seen from the high pH (>13.5), which<br />

shows that hydroxides are leached or<br />

<strong>for</strong>med as pH is measured in a suspension<br />

<strong>of</strong> WA in distilled water.<br />

3.1.4 Mineral phases in WAs<br />

Ta b l e 4 shows the phases identified by<br />

XRD in the ashes. In cases with a concentration<br />

less than 5 % (calculated on basis <strong>of</strong><br />

the Reference Intensity Ratio (RIR) given<br />

in Ta b l e 4 ) the approximate concentration<br />

is noted, <strong>and</strong> the presence <strong>of</strong> these<br />

phases must be regarded with some uncertainty.<br />

The investigated WAs contained quartz<br />

(SiO 2 ) <strong>and</strong> calcite (CaCO 3 ), which is in<br />

consistency with findings from other WAs<br />

[Berra et al. 2015; Ol<strong>and</strong>ers & Steenari,<br />

1995, Steenari <strong>and</strong> Lindqvist, 1997]. In addition<br />

to CaCO 3 other Ca-containing phases<br />

(CaSO 4 , CaO or Ca(OH) 2 ) have been<br />

reported in [Berra et al. 2015; Ban & Ramli,<br />

2011; Elinwa <strong>and</strong> Ejeh, 2004; Etiégni<br />

<strong>and</strong> Campbell, 1991]. CaSO 4 was not identified<br />

in the investigated ashes, <strong>and</strong> it<br />

shows that if present, the concentration <strong>of</strong><br />

this phase is less than 1 % CaO was identified<br />

in WA2 <strong>and</strong> Ca(OH) 2 in WA1. This difference<br />

is due to the hydration <strong>of</strong> CaO to<br />

Ca(OH) 2 <strong>of</strong> WA1 from the water spraying<br />

just after the incineration.<br />

The soluble salts K 2 SO 4 <strong>and</strong> KCl were identified<br />

in both <strong>of</strong> the investigated WAs (Ta -<br />

b l e 4 ), though KCl in low concentration<br />

in WA2, which is in consistency with a<br />

lower Cl concentration in this WA (Ta -<br />

b l e 2 ). The two soluble salts have been<br />

reported in other WAs, as well, e.g. [Sigvardsen<br />

et al. 2019]. In summary, the mineral<br />

phases identified in the investigated<br />

WAs have previously been reported in other<br />

WAs.<br />

3.1.5 Changes in WA phases from<br />

pretreatment<br />

Visually the ashes as received differed <strong>and</strong><br />

WA1 contained larger lumps (<strong>of</strong> sizes up to<br />

5 cm) <strong>of</strong> agglomerated ash particles (F i g -<br />

u r e 1 ). This was on the contrary to WA2,<br />

which was without such lumps, however,<br />

after wetting, lumps also <strong>for</strong>med in WA2.<br />

The lumps in WA1 were likely <strong>for</strong>med<br />

when the WA was wetted at the incineration<br />

facility. This is in consistency with previously<br />

reported by [Steenari et al. 1999]:<br />

a spontaneous agglomeration will occur<br />

during storage <strong>of</strong> the wetted ash in contact<br />

with air. The self-hardening property <strong>of</strong><br />

WA is caused by <strong>for</strong>mation <strong>of</strong> new phases<br />

[Steenari et al. 1997]: First hydration <strong>of</strong><br />

CaO <strong>for</strong>ming Ca(OH) 2 is a rapid <strong>and</strong> exothermic<br />

process. Carbonation <strong>of</strong> Ca(OH) 2<br />

occurs in presence <strong>of</strong> water <strong>and</strong> carbon<br />

Tab. 4. Phases identified in the different ashes <strong>and</strong> pretreated ashes. Color identification:<br />

orange phase disappeared during pretreatment <strong>and</strong> green indicates a new phase <strong>for</strong>med<br />

during pretreatment.<br />

Quartz<br />

SiO 2<br />

Calciumoxide<br />

CaO<br />

RIR WA1 Dried<br />

WA1<br />

550°<br />

C<br />

WA1<br />

Water<br />

wash<br />

WA1<br />

Acid<br />

wash<br />

WA1<br />

WA2<br />

Hydra<br />

ed<br />

WA2<br />

550°<br />

C<br />

WA2<br />

Water<br />

wash<br />

WA2<br />

3.11 X ~1 % X ~1 % X X X X X X<br />

4.42 X X ~5 %<br />

Calcium<br />

hydroxide 3.5 X X X ~4 % X X ~3 %<br />

Ca(OH) 2<br />

Calcite<br />

CaCO 3<br />

3.21 X X X X X X X X X X<br />

Gypsum<br />

Ca(SO 4 (H 2 O) 0.5 )<br />

Periclase<br />

MgO<br />

3.04 X ~3 % X ~2 % X X X X X<br />

Magnesium<br />

hydroxide<br />

X X ~4 %<br />

Mg(OH) 2<br />

Sylvite<br />

KCl<br />

3.9 X X X ~4 % X ~5 %<br />

Arcanite<br />

K 2 SO 4<br />

1.19 X X X X X X<br />

X<br />

Acid<br />

wash<br />

WA2<br />

dioxide. The CaCO 3 hereby <strong>for</strong>med precipitates<br />

in a layer on the ash surfaces <strong>and</strong> in<br />

the pores. Ta b l e 4 shows that CaCO 3 was<br />

identified in both the investigated WAs.<br />

Ettringite <strong>for</strong>mation contributes to the early<br />

solidification; however, if the pH is too<br />

low or soluble Al is lacking, CaSO 4 is<br />

<strong>for</strong>med instead [Steenari et al. 1997]. Hydration<br />

<strong>of</strong> amorphous silicate phases may<br />

also contribute [Etiégni & Campbel, 1991]<br />

<strong>and</strong> C-S-H gel was identified by SEM-EDX<br />

[Ramos et al. 2013] [Chea & Ramli, 2013].<br />

Neither CaSO 4 nor C-S-H gels were though<br />

identified in the investigated hydrated<br />

WAs. The importance <strong>of</strong> each reaction <strong>and</strong><br />

the relation between WA properties <strong>and</strong> its<br />

self-hardening behavior is not yet not fully<br />

understood [Illikainen et al. 2013], deeper<br />

knowledge is necessary in order to underst<strong>and</strong><br />

<strong>and</strong> evaluate the quality <strong>of</strong> WA <strong>for</strong><br />

use in concrete, however, changes in mineralogy<br />

after wetting <strong>of</strong> WA must be expected.<br />

After wetting <strong>of</strong> WA2, the CaO disappeared<br />

<strong>and</strong> Ca(OH) 2 showed as a new<br />

mineral, which confirms the hydration.<br />

Thus after wetting WA2, the major Ca containing<br />

minerals were the same in WA2 as<br />

in the already hydrated WA1 (Ca(OH) 2 <strong>and</strong><br />

CaCO 3 ). MgO, which was identified in<br />

WA2 (as received) <strong>and</strong> did not hydrate to<br />

Mg(OH) 2 during the wetting procedure.<br />

The XRD peak <strong>for</strong> KCl disappeared after<br />

wetting <strong>of</strong> WA2, which may indicate that Cl<br />

<strong>and</strong> K ions from this soluble salt precipitated<br />

again into other compounds. The<br />

drying <strong>of</strong> WA1, with an original water content<br />

<strong>of</strong> 19 % did, as expected, not change<br />

the phases present (Ta b l e 4 ).<br />

<strong>Heat</strong>ing to 550 o C was carried out to remove<br />

the organic fraction in the ashes, but<br />

it did also change the identified minerals in<br />

both ashes (Ta b l e 4 ). In WA1, the peak<br />

<strong>for</strong> Ca(OH) 2 had disappeared after the<br />

heating. The reaction Ca(OH) 2 CaO +<br />

H 2 O is reversible, <strong>and</strong> <strong>for</strong> a H2O partial<br />

pressure <strong>of</strong> 1 atm the correspondent equilibrium<br />

temperature is 5<strong>10</strong> to 512 °C<br />

[Schaube et al. 2012], i.e. lower than the<br />

temperature <strong>for</strong> the heating in the present<br />

investigation. The peak <strong>for</strong> CaO do though<br />

not appear in WA1 after the heating, <strong>and</strong><br />

reveals that Ca <strong>for</strong>ms other compounds. In<br />

WA1, the peaks <strong>for</strong> KCl <strong>and</strong> the small peak<br />

<strong>for</strong> SiO 2 also disappeared after the heating.<br />

There is no obvious explanation <strong>for</strong> the disappearance<br />

<strong>of</strong> the SiO 2 peak, <strong>and</strong> it might<br />

be due to variations within the WA, since<br />

the peak in the WA1 as received was very<br />

small to begin with. The melting point <strong>for</strong><br />

KCl is 770 °C <strong>for</strong> KCl, i.e. higher than the<br />

current treatment <strong>and</strong> only hereafter mass<br />

loss from heating is seen [Li et al. 2019].<br />

Thus, evaporation is not expected to explain<br />

the disappearance <strong>of</strong> KCl as mineral<br />

in the XRD measurements (Ta b l e 4 ). The<br />

two elements must participate in the <strong>for</strong>mation<br />

<strong>of</strong> other phases, which can be<br />

amorphous, since no new peaks containing<br />

Cl or K appear. The same goes <strong>for</strong> K 2 SO 4<br />

with a melting point <strong>of</strong> 1,069 °C. The heat-<br />

54

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