The
effect of bituminous coal and pickling sludge co-combustion
on the distributions of Cr, Ni, Mn, As, Cu, Sb, Pb, Cd, Zn, and Sn
in flue gas, fly ash, and bottom ash were studied in a drop-tube furnace.
To simulate combustion conditions in suspension-firing boilers, experiments
were carried out at temperatures ranging from 1100 to 1400 °C,
with sludge amounts ranging from 0% to 10% by weight. The results
show that the 10 selected heavy metals could be divided into three
distinct classes according to bottom ash mass percentage, except for
Sn, which showed an irregularity. Class I included Cr, Ni, Mn, and
As and were identified as less volatile heavy metals because more
than 95% was retained in the bottom ash; these heavy metals exhibit
high-temperature stability. Class II contained Cu, Sb, Pb, and Cd
and were identified as semivolatile heavy metals; nearly 20–40%
was distributed among flue gas and fly ash. In addition, the bottom
ash heavy metal percentage decreased markedly with increasing temperature.
Zn belongs to class III and was identified as a volatile heavy metal;
less than 20% was retained in bottom ash under all experimental conditions.
Thermodynamic equilibrium calculations were used to forecast heavy
metal compounds, and most calculation results were consistent with
the actual outcomes. X-ray diffraction results indicated that Cr and
Ni mainly reacted with MgO and Fe2O3 to form
MgCr2O4 and NiFeO4 in solid phase
during the co-combustion process. The heavy metal emissions in flue
gas meet the national standard, while the bottom ash leaching results
indicate that the bottom ash from bituminous coal and pickling sludge
co-combustion cannot be disposed of as common waste through landfill
disposal without further treatment.