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).
Technical Journal of the VGB PowerTech Association. Energy is us!
Power plant products/by-products.
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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 />
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