VGB POWERTECH 7 (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! Maintenance. Thermal waste utilisation
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!
Maintenance. Thermal waste utilisation
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The Bi<strong>of</strong>ficiency Project | Part 1 <strong>VGB</strong> PowerTech 7 l <strong>2020</strong><br />
Tab. 5. Overview on biomass ashes selected <strong>for</strong> Bi<strong>of</strong>ficiency.<br />
Full-scale unit Capacity / MW el Biomass fuel Combustion<br />
system<br />
Rodenhuize<br />
150 MW<br />
Wood pellets 1<br />
Wood pellets 2<br />
Wood pellets 3<br />
Wood pellets 4<br />
<strong>of</strong> different techniques is important. For<br />
example, with XRF analyses, the presence<br />
<strong>of</strong> carbonate, hydrate, hydroxide <strong>and</strong> UBC<br />
must be taken into account.<br />
There may be some differences in the ashes<br />
produced in laboratory-, bench-, pilot-, <strong>and</strong><br />
full-scale boilers. In small scale, the fuel<br />
can be more homogeneous than in fullscale,<br />
which consumes several truckloads<br />
<strong>of</strong> biomass per hour. On the other h<strong>and</strong>, the<br />
fly ash from the pilot-scale combustors may<br />
contain significant amounts <strong>of</strong> stainless<br />
steel corrosion products such as Cr <strong>and</strong> Ni.<br />
At full-scale plants, the biomass fuels are<br />
combusted at temperatures about between<br />
850 °C <strong>and</strong> 1,500 °C depending on the combustion<br />
technology, <strong>and</strong> include processes<br />
<strong>of</strong> evaporation <strong>and</strong> condensation <strong>of</strong> compounds<br />
<strong>of</strong> Na, K, Cl, S, P, etc. Evaporation<br />
occurs at the high combustion temperatures<br />
<strong>and</strong> condensation upon cooling <strong>of</strong> the<br />
flue gases. At higher combustion temperatures,<br />
there is more evaporation <strong>of</strong> K, Na,<br />
Cl, S, P, which condensate on the ashes<br />
upon cooling <strong>of</strong> the flue gases, <strong>and</strong> hence<br />
more salts are present in the fly ash.<br />
Fly ashes produced at higher combustion<br />
temperatures (PF) differ markedly from<br />
those produced at lower combustion temperatures<br />
(CFB), not only regarding salt<br />
content, but also, regarding reactivity at<br />
temperatures above 850 °C. This was demonstrated<br />
by TGA/DTA/DSC analyses,<br />
which show exothermic reactions with<br />
CFBC fly ashes at temperatures above 850 °C.<br />
Problematic components regarding exact<br />
<strong>and</strong> repeatable analysis are <strong>of</strong>ten B, Cl<br />
<strong>and</strong> F, which require further attention.<br />
Additives<br />
Avedøre 2 400 MW Wood pellets PF Bituminous coal fly ash<br />
Herning 78 MW Wood chips Grate none<br />
Pulp&paper mill<br />
power plant<br />
PF<br />
none<br />
none<br />
none<br />
none<br />
87 MW Bark CFB none<br />
Pilot-scale unit Fuel input / kW th Biomass fuel<br />
Valmet pilot plant<br />
VTT pilot plant<br />
TUM pilot plant<br />
4000 kW<br />
50 kW<br />
200 kW<br />
Bark<br />
EFB<br />
EFB <strong>and</strong> coal<br />
Bark<br />
Torrewashed bark<br />
Torrewashed bark<br />
Torrewashed straw<br />
Straw<br />
Bark<br />
SE bark<br />
SE bark<br />
Combustion<br />
system<br />
CFB<br />
CFB<br />
PF<br />
Additives<br />
none<br />
none<br />
none<br />
none<br />
none<br />
Sulphur<br />
Kaolin<br />
Kaolin<br />
none<br />
Kaolin<br />
Coal fly ash<br />
With increasing combustion temperature,<br />
more Cr(VI) is anticipated. This is critical,<br />
since Cr(VI) is known to be carcinogenic<br />
<strong>and</strong> toxic. Consequently, more work on the<br />
aspect <strong>of</strong> Cr(VI) in ash is required.<br />
By water-leaching <strong>of</strong> the biomass fuel i.e. in<br />
pre-treatment, fly ashes will contain less<br />
Na, K, Cl <strong>and</strong> S, <strong>and</strong> hence less salts will be<br />
present in the fly ashes.<br />
2.4.2 Novel applications <strong>for</strong> biomass ash<br />
In the course <strong>of</strong> the project existing valorisation<br />
options <strong>for</strong> biomass ashes such as<br />
use as fertiliser, filler materials or construction<br />
materials were identified.<br />
However, many <strong>of</strong> these applications can<br />
be considered as “creative” l<strong>and</strong> filling, at<br />
least by authorities <strong>and</strong> NGOs. Some <strong>of</strong><br />
these applications are not specific <strong>for</strong> biomass<br />
ash. New potential applications were<br />
identified that exlude applications including<br />
l<strong>and</strong> filling <strong>and</strong> applications that are<br />
not specific <strong>for</strong> biomass ash.<br />
––<br />
Leaching, with recovery <strong>of</strong> valuable elements<br />
<strong>and</strong> compounds, especially P <strong>and</strong> K<br />
––<br />
Application in traditional ceramics <strong>and</strong><br />
traditional glass<br />
––<br />
Application in geo-polymers<br />
––<br />
Recycling elements back to the soil, <strong>for</strong><br />
limiting depletion<br />
––<br />
Application as or in fertiliser<br />
––<br />
Application in calcium silicate bricks<br />
In the project these proposed valorisation<br />
options were evaluated. Due to the new EU<br />
fertiliser regulation 2019, the application<br />
<strong>of</strong> biomass ashes in top-soils seems to be<br />
restricted. Biomass ashes will most probably<br />
exceed limits <strong>for</strong> allowed concentrations<br />
<strong>of</strong> toxic heavy metals.<br />
On the other h<strong>and</strong>, the use <strong>of</strong> biomass ash<br />
in construction materials seems promising,<br />
especially in calcium silicate blocks <strong>and</strong><br />
geo-polymers. To achieve a higher added<br />
value in this field <strong>of</strong> application, biomass<br />
ash should be used as binder rather than as<br />
filler material. It could potentially replace<br />
limestone, which is currently mined <strong>and</strong><br />
calcined with high fossil CO 2 emissions.<br />
Fly ash from wood <strong>and</strong> bark were tested in<br />
these novel applications during the Bi<strong>of</strong>ficiency<br />
project. It was demonstrated that<br />
ashes from biomass fuels can be used in<br />
construction materials, like fired bricks,<br />
calcium silicate blocks <strong>and</strong> geo-polymers<br />
(see F i g u r e 6 ). Calcium silicate materials<br />
<strong>and</strong> geo-polymers with high compressive<br />
strengths <strong>of</strong> more than 50 MPa, even<br />
more than 100 MPa, were obtained.<br />
Additionally also the feasibility <strong>of</strong> the use<br />
<strong>of</strong> biomass ash in top soils was investigated<br />
Fig. 6. Fired bricks made from two different Dutch clays (Maas <strong>and</strong> Waal), <strong>and</strong> with 0, 5 <strong>and</strong><br />
25 wt.-% wood fly ash from a PF boiler.<br />
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