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Chemical Constituents in Particulate
Emissions from an Integrated Iron and Steel Facility
Tsai Jiun-Horng*、Lin
Kuo-Hsiung11、Chen Chih-Yu11、Ding
Jian-Yuan11、Choa Ching-Guan11、Chiang
Hung-Lung22
*Department of Environmental Engineering,
Sustainable Environment Research Center, National Cheng-Kung
University, Tainan, Taiwan
1Department of
Environmental Engineering, Fooyin University, 831, Kaohsiung,
Taiwan
2Department of Risk Management, China Medical
University, 40402, Taichung, Taiwan
Email: jhtsai@mail.ncku.edu.tw
Journal
of Hazardous Materials. 147, 111–119 (2007).
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The
iron and steel industry produces important materials for automotive,
construction and consumer product applications. But it is also one
of the most energy-intensive industries and produces significant
pollution emissions. The major operations of an integrated iron and
steel industry include coke making, sintering, iron making, steel
making, and rolling. Figure 1 presents the main processes of the
integrated iron and steel plant in Taiwan.
Iron ore is the
raw material, which consists mainly of hematite (Fe2O3) and
magnetite (Fe3O4) or goethite (FeOOH). The sinter process, coke
making, the heating furnace and the blast furnace are the major air
pollution sources which contribute over 90% of the emissions from
the integrated iron and steel plant. Coke ovens also emit a lot of
PAH.
This study sampled the particles emitted from these
processes and idenyified the constituents as the fingerprints of
various emission sources. There were 21 element species, 11 ionic
species, elemental carbon, organic carbon and 16 polyaromatic
hydrocarbons (PAHs), measured to create “fingerprints” in these
processes.
The elemental compositions of particles for the
four processes are shown in Table 1. Sulfur, iron, and sodium are
the major elements in the coke making process. The contribution of K
and Pb is higher in the sintering process than in the other
processes, especially the K contribution (157 mg/g), which is about
15% of the particle mass in the sintering process. Furthermore, S,
Fe, Na, K and Ni contribute 147 -21 mg/g, to the particles in the
cold forming process. In hot forming, S, Fe, Na and Ca are the major
particle elements (60-14 mg/g). In general, sulfur had a higher mass
contribution than the other elements, which resulted from the use of
coal, flux, heavy oil, and many recycled materials in the iron and
steel plant. The particle mass contribution of potassium in the
sinter plant was higher than in other processes; this may be
attributed to the lower boiling point and volatility of potassium.
In addition, many recycled materials were fed into the sinter plant,
causing a high concentration of potassium in the particle
phase.
The sulfate concentration is higher than in other
ionic compounds, with concentrations ranging from 122 to 349 mg/g in
the four processes. This may be due to the sulfur content in the raw
materials, which oxidizes to form SO2 and adsorbs or deposits on
particles and then forms sulfate. In another pathway, SO2 may be
catalyzed (e.g., Fe, Ni, etc.) to form sulfate in the particle
phase. There is a substantial sulfate contribution to the particle
mass. In addition, the concentrations of K+ and Cl- were higher than
that of S (199 and 173 mg/g, respectively), in the sintering
process. The return fines from the sintering plant, blended ore,
serpentine, limestone and coke breeze were also recycled and mixed
to make sinter. A large amount of recycled material is used in
sinter plants, which may contain and potassium chloride
compounds.
The elemental carbon ranged from 9 to 137 mg/g and
organic carbon from 16 to 64 mg/g; the total carbon content ranged
from 40 to 170 mg/g. The low carbon content was due to the high
temperature (> 850 oC) manufacturing processes and the carbon
burnoff. The coke making and cold forming processes revealed high
carbon content, which was caused by the reduction reaction of coke
formation and low thermal temperature treatment for the cold forming
process.
Sixteen PAHs were analyzed in this study, and eight
PAH compounds were detected in the four processes (Table 2). The
sequence of PAH content in the particle phase was as follows for the
four processes: cold forming (6.2 mg/g) > coke making (1.8 mg/g)
> hot forming (1.6 mg/g) > sintering (0.5mg/g). This may be
due to the oil added into the cold-rolled process and the lower
operating temperature, which enhances PAH formation. Figure 2 shows
the ring distribution of the PAHs. The percentage of the mass
contribution of the 16 PAHs was 3-ring (88-69%)> 5-ring
(3-13%)> 4- ring (8-24%) in this study. AcPy (3 ring) was the
predominant PAH species. In addition, the carcinogenic compound
Benzo(a)pyrene (BaP) was detectable only in the sintering process
(0.041 mg/g). High carbon content was found in the coke making and
cold forming processes as a result of the high PAH content of the
two processes.
This study provides the detailed particle
compositions and the baseline information on emissions from
integrated iron and steel facilities. Detailed particle composition
can be used as a “fingerprint” to identify the contribution from
various pollution sources to the airborne particle in the vicinity
of an integrated iron and steel plant.
Table 1 Elemental concentration in particulate emissions
from various processes in steel plant
a mean value ± standard
deviation
bND: not detectable
cEach processor took 3 samples
and each sample took 3 duplicate analyses.
dMDL: Method detection
limit; Al, Ca, Fe, K, Mg, Na, and S were measured by ICP-AES and Co,
Zn, Pb, Cu, Sr, As, Cr, Ba, Mn, Ni, Se, Cd, Sb, and V were measured
by ICP-MS.
Table 2 PAHs concentrations in the four
processes
*ND: not detectable
** Naphthalene (NaP),
Acenaphthene (Acp), Anthracene (Ant), Fluoranthene (FL),
Benzo(a)anthracene (BaA), Indeno(1,2,3-cd)pyrene (IND),
Dibenzo(a,h)anthracene (DBA), and Benzo(g,h,i)pyrene (BghiP) were
not detected in these samples.
*** Each processor took 3 samples
and each sample took 3 duplicate analyses
Figure 1 The main processes of the integrated iron and
steel plant
Figure 2 Distribution of various classes of
PAHs
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