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Characterization of waste sludge pigment from production of ZnCl2

Abstract

This study is focused on the treatment of waste sludge from a zinc chloride production in order to prepare iron-rich pigments usable for a production of glazes. In galvanizing plants, yellow waste sludge containing significant amount of ZnO, Cl, and Fe2O3, is formed. This raw waste sludge cannot be used as a pigment in glaze. Therefore, three methods of treating this material were proposed: (a) washing with H2O, (b) calcination at 180 degrees C and washing by H2O, and (c) calcination at 900 degrees C and washing by H2O. These methods helped to reduce Zn and Cl content up to 97%. According to X-ray fluorescence analysis percentage of Fe2O3 increased from similar to 41% to similar to 98%. X-ray power diffraction analysis confirmed the formation of alpha-Fe2O3 (hematite) in the pigment prepared. Scanning electron microscopy with Energy dispersive X-ray analysis showed clusters of rounded particles, and also the change in size of particles after calcination was observed. Particle size, specific surface area, and density measurements together with thermogravimetric and differential thermal analyses were performed. Pigments prepared from the waste sludge were added to transparent glaze in amounts of 1, 5, 10, and 15 wt.%. Pigment-containing glazes were applied by spraying on fired ceramic tiles and then fired at 1060 degrees C. Color of glazes was determined by (Commission Internationale de l'Eclairage) CIE L*a*b* coordinates as colorless, light brown shades, brown-red, brown-yellow, and deep red-brown. Comparison with colors of glazes prepared using commercial pigments was also performed. Waste sludge can be used to prepare pigments and glazes containing pigments as an alternative to commercial products.

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Characterization of waste sludge pigment from production of ZnCl2

Author: Ovčačíková, Hana
Publisher: MDPI
Year: 2021
DOI: 10.3390/min11030313
Source: https://dspace.vsb.cz/bitstreams/928549d0-1c22-4245-ab5c-a1e1dbcb4b0e/download
mine als
A icle
Cha ac e iza ion o Was e Sludge Pigmen om P oduc ion
o ZnCl2
Hana O ˇcaˇcíko á1,* , Ma ek Veliˇcka 1, Pe a Maie o á1, Joze Vlˇcek 1, Jonáš Toka ský2,3 and Tomᚡ
Cegan 4


Ci a ion: O ˇcaˇcíko á, H.; Veliˇcka,
M.; Maie o á, P.; Vlˇcek, J.; Toka ský,
J.; ˇ
Cegan, T. Cha ac e iza ion o Was e
Sludge Pigmen om P oduc ion o
ZnCl2.Mine als 2021,11, 313.
h ps://doi.o g/10.3390/min11030313
Academic Edi o : Anna Candida
Felici and Lucilla P on i
Recei ed: 14 Feb ua y 2021
Accep ed: 15 Ma ch 2021
Published: 17 Ma ch 2021
Publishe ’s No e: MDPI s ays neu al
wi h ega d o ju isdic ional claims in
published maps and ins i u ional a il-
ia ions.
Copy igh : © 2021 by he au ho s.
Licensee MDPI, Basel, Swi ze land.
This a icle is an open access a icle
dis ibu ed unde he e ms and
condi ions o he C ea i e Commons
A ibu ion (CC BY) license (h ps://
c ea i ecommons.o g/licenses/by/
4.0/).
1
Depa men o The mal Enginee ing, Facul y o Ma e ials Science and Technology, VSB-Technical Uni e si y
o Os a a, 17. Lis opadu 2172/15, 708 00 Os a a, Czech Republic; [email p o ec ed] (M.V.);
[email p o ec ed] (P.M.); [email p o ec ed] (J.V.)
2Nano echnology Cen e, CEET, VSB-Technical Uni e si y o Os a a, 17. Lis opadu 2172/15,
708 00 Os a a, Czech Republic; [email p o ec ed]
3Ins i u e o En i onmen al Technology, CEET, VSB-Technical Uni e si y o Os a a, 17. Lis opadu 2172/15,
708 00 Os a a, Czech Republic
4Depa men o Non-Fe ous Me als, Re ining and Recycling, Facul y o Ma e ials Science and Technology,
VSB-Technical Uni e si y o Os a a, 17. Lis opadu 2172/15, 708 00 Os a a, Czech Republic;
[email p o ec ed]
*Co espondence: [email p o ec ed]; Tel.: +42-05-9732-1523
Abs ac :
This s udy is ocused on he ea men o was e sludge om a zinc chlo ide p oduc ion
in o de o p epa e i on- ich pigmen s usable o a p oduc ion o glazes. In gal anizing plan s,
yellow was e sludge con aining signi ican amoun o ZnO, Cl, and Fe
2
O
3
, is o med. This aw
was e sludge canno be used as a pigmen in glaze. The e o e, h ee me hods o ea ing his
ma e ial we e p oposed: (a) washing wi h H
2
O, (b) calcina ion a 180
◦
C and washing by H
2
O,
and (c) calcina ion a 900
◦
C and washing by H
2
O. These me hods helped o educe Zn and Cl
con en up o 97%. Acco ding o X- ay luo escence analysis pe cen age o Fe
2
O
3
inc eased om
~41% o ~98%. X- ay powe di ac ion analysis con i med he o ma ion o
α
-Fe
2
O
3
(hema i e) in
he pigmen p epa ed. Scanning elec on mic oscopy wi h Ene gy dispe si e X- ay analysis showed
clus e s o ounded pa icles, and also he change in size o pa icles a e calcina ion was obse ed.
Pa icle size, speci ic su ace a ea, and densi y measu emen s oge he wi h he mog a ime ic and
di e en ial he mal analyses we e pe o med. Pigmen s p epa ed om he was e sludge we e added
o anspa en glaze in amoun s o 1, 5, 10, and 15 w .%. Pigmen -con aining glazes we e applied
by sp aying on i ed ce amic iles and hen i ed a 1060
◦
C. Colo o glazes was de e mined by
(Commission In e na ionale de l’Eclai age) CIE L*a*b* coo dina es as colo less, ligh b own shades,
b own- ed, b own-yellow, and deep ed-b own. Compa ison wi h colo s o glazes p epa ed using
comme cial pigmen s was also pe o med. Was e sludge can be used o p epa e pigmen s and glazes
con aining pigmen s as an al e na i e o comme cial p oduc s.
Keywo ds: pigmen ; Fe sludge; ZnCl2; calcina ion; glaze
1. In oduc ion
P epa a ion o glaze and pigmen is an excellen al e na i e o ecycling ma e ials.
The global pigmen consump ion in he indus y is expec ed o be 282.7 housand in
2023/$8 bn, and, in Eu ope, i is expec ed o inc ease o app oxima ely 85 housand .
Pigmen s a e widely applied in nume ous indus ial sec o s, such as ci il enginee ing, p o-
duc ion o pape , pain s, dyes, ce amic ma e ials (18 housand in 2023), plas ic ma e ials,
e c. This is he consump ion o example: o mixed me al oxide pigmen s (60 housand ),
pea lescen pigmen s (71 housand ), o ganic pigmen s (44 housand ), me allic pigmen s
(94 housand ), and special y pigmen s (14 housand ) [
1
]. Pigmen s can be classi ied as in-
o ganic, o ganic, and syn he ic. They mus ul ill h ee main equi emen s: he mal s abili y,
chemical s abili y, and high colo ings powe [2].
Mine als 2021,11, 313. h ps://doi.o g/10.3390/min11030313 h ps://www.mdpi.com/jou nal/mine als
Mine als 2021,11, 313 2 o 16
Ino ganic pigmen s exhibi co e ing p ope ies, colo ing p ope ies, o o he spe-
cial ea u es, and can be di ided as ollows: (a) whi e pigmen s, (b) black pigmen s,
and (c) colo ed pigmen s. Thei o he special ea u es a e he an ico osion p ope ies
( e i e pigmen s) [
3
], bu pigmen s can be also me allic, nac eous, luminescen [
4
], mag-
ne ic [
5
], o an i- us [
6
]. The quali y o pigmen depends on he op ical and physical
p ope ies. Ino ganic pigmen s a e powde subs ances colo ing he en i onmen (binde )
in which whe e hey a e dispe sed, o colo ing he su ace on which hey a e applied.
Ce amic pigmen s a e compounds o ino ganic o igin wi h a ious c ys al s uc u es. Ce-
amic pigmen s a e o med by a he mally s able hos la ice (MgAl
2
O
4
, TiZn
2
O
4
, Z SiO
4
,
TiO
2
, e c.), which is colo less in i s pu e o m, and a ch omopho e de e mining he colo
o he esul ing pigmen and e ac i e indices o indi idual compounds. This p ope y
is e y impo an because high e ac i e index o he pigmen pa icles ela i e o he
e ac i e index o he medium whe e i is dispe sed indica es he quali y o he pigmen .
By changing he amoun o he indi idual compounds, o changing he s oichiome ic
ep esen a ion o he elemen s in he s uc u e, i is possible o p epa e pigmen shades o
colo ing ce amic glaze. Va ying calcina ion condi ions can also be used o achie e di e en
colo shades.
The mos impo an p ope y o he pigmen is he colo ( he abili y o pigmen a ion),
and he abili y o ge dispe sed in a ma ix. The he mal s abili y o pigmen s in a ce amic
ma e ial o engobe is de e mined o be be ween 1200 and 1300
◦
C. The pigmen in he
glaze and he pigmen o deco a ion mus be s able a empe a u es o 1000–1200
◦
C and
625–775 ◦C, espec i ely [7–9].
I on pigmen s, bo h na u al and syn he ic, ha e low cos o p oduc ion and signi ican
ad an ages o indus ial pu poses. The ea men o i on pigmen can esul in changes
in colo , such as black/magne i e, ed/hema i e, b own/maghemi e, yellow/goe hi e,
and o ange/lepidoc oci e [
10
,
11
]. The na u al i on pigmen s comp ise he ollowing
compounds: limoni e (Fe
2
O
3
.xH
2
O) om yellow o ed oche , goe hi e (Fe
3+
O(OH))— ed-
b own, hema i e (
α
-Fe
2
O
3
)—me allic g ey e ous mica. Na u ally-hyd a ed Fe
3+
oxides
we e used as pigmen s al eady in an Ea ly S one Age.
Many ino ganic pigmen s a e p epa ed wi h me allic oxides o sal s. In e es ing is
he p epa a ion o e ous pigmen s by chemical means om was e aw ma e ials, us-
ing p ecipi a ion eac ions, in he o m o e ous p ecu so s, e.g., magne i e (Fe
3
O
4
) [
12
,
13
],
goe hi e
α
-FeO (OH), hema i e (
α
-Fe
2
O
3
) [
14
–
16
], and maghemi e
γ
-Fe
2
O
3
[
17
,
18
].
α
-Fe
2
O
3
,
which can be u he p epa ed, e.g., by he hyd o he mal app oach [
19
], sol-gel p ocess,
chemical p ecipi a ion, high- empe a u e he mal oxida ion, e c. [20].
The pa h o he p epa a ion o i on- ich pigmen s begins wi h he p ocessing o ZnCl
2
.
The ZnCl
2
is a c ys alline and hyg oscopic powde exhibi ing he moch omic p ope ies.
ZnCl
2
is anhyd ous wi h a densi y o 1400–1700 kg/m
3
, wi h pH alue o 5. The colo o he
powde is whi e o sligh ly g eyish. Hea ed o a empe a u e o 500–700 ◦C, mol en anhy-
d ous ZnCl
2
dissol es me allic zinc. When his mel is apidly cooled, yellow diamagne ic
glass is o med. Raman spec oscopy analyses show ha he yellow glass o med con ains
zinc ions. As he empe a u e inc eases, he colo changes om whi e o yellow. This change
in colo is caused by la ice impe ec ions. Oxygen molecules a e los . The eac ion o ZnO
wi h acids p oceeds as ollows Equa ion (1) and in alkaline medium, and he ollowing
eac ion occu s, as in Equa ion (2) [21]:
ZnO + 2HCl = H2O + ZnCl2, (1)
ZnO + 2NaOH + H2O→Na2[Zn(OH)4]]. (2)
ZnCl
2
is used in indus y o me al su ace ea men and elec opla ing, as an elec-
oly e o ion exchange , in chemical syn heses, e c. [
22
–
25
]. Indus ially, ZnCl
2
is p epa ed
om so-called o e haul acids, which a e ob ained in gal anizing plan s by dissol ing
zinc coa ing on poo ly gal anized objec s (and aids and ools) in HCl. The Fe con en
Mine als 2021,11, 313 3 o 16
in o e haul acids hus p epa ed is usually >1.5%. A he beginning o p oduc ion, Fe is
neu alized by he so-called zinc ash, which is also a was e p oduc om gal anizing plan s.
Subsequen ly, he i on ions a e oxidized by H
2
O
2
. Because Fe
2+
ions hyd olyze a
highe pH han Zn
2+
ions, i is necessa y o achie e oxida ion o all Fe o he oxida ion s a e
III. Hyd oly ic p ecipi a ion is based on he di e en s abili y o he hyd oxide p ecipi a es
depending on he pH o he solu ion. The hyd oly ic p ecipi a ion o Fe can be desc ibed
as ollows in Equa ion (3):
Fe3+ +3H2O→Fe(OH)3+ 3H+. (3)
The p ecipi a e o med is il e ed on a sludge il e p ess. Subsequen ly, me als noble
han Zn a e emo ed om ZnCl
2
solu ion by cemen a ion p ocess. Zn powde is used as
a cemen ing agen . The e iciency and kine ics o he cemen a ion p ocess inc ease wi h
inc easing empe a u e, and he solu ion pH equi ed lies in he ange o 4 o 5. The eac ion
can be desc ibed by he ollowing gene al mechanism in Equa ion (4):
Zn + Me2+ →Me + Zn2+. (4)
This s udy is ocused on he ea men o was e sludge om he ZnCl
2
p oduc ion
in o de o p epa e i on pigmen s usable o a p oduc ion o glazes. The was e sludge
p ima ily con ains ZnO, Cl, and Fe
2
O
3
. In i s o iginal o m, i is yellow, due o he high
pe cen age o Cl. To ob ain pigmen o good quali y, he was e sludge calcina ion a 180
◦
C
and 900
◦
C, and subsequen washing in wa e was p oposed. The choice o empe a u es is
based on p e ious expe imen s pe o med by ou esea ch g oup. The ma e ials s udied in
his wo k we e cha ac e ized by a wide ange o me hods (X- ay powde di ac ion (XRPD),
he mog a ime ic analysis (TG), di e en ial he mal analysis (DTA), scanning elec on
mic oscopy (SEM), ene gy dispe si e X- ay analysis (EDAX), X- ay luo escence analysis
(XRF), B unaue -Emme -Telle (BET) su ace a ea analysis). Pa icle size dis ibu ion and
densi y we e also de e mined. I on- ich pigmen s success ully p epa ed om he was e
sludge we e added o a anspa en glaze and sp ayed on ce amic iles. The i ing was
pe o med a 1060
◦
C. The desc ibed p ocedu e led o ob aining glazes wi h di e en
colo and in ensi y, wi h a compac appea ance, gloss and wi hou isible de ec s on he
su ace. Colo ime ic analysis was used o compa e colo s o glazes p epa ed using ou
pigmen s wi h colo s o glazes p epa ed using comme cial pigmen s. This s udy shows
how he was e sludge can be used o p epa e p oduc s—pigmen s and pigmen -con aining
glazes—al e na i e o comme cial p oduc s.
2. Ma e ials and Me hods
2.1. Ma e ials
All ma e ials we e ob ained om he Czech Republic. Ce amic whi e slu y (la-
beled as CS) was ob ained om Pá ek Ke amika, spol. s .o. (Doub a ice nad S i a ou,
Czech Republic). T anspa en glaze (labeled as TG) is a comme cial whi e powde p o-
duced by Glazu a s. .o. company (Dobˇ ín, Czech Republic). In he expe imen , h ee ypes
o comme cial pigmen (labeled as SP1, SP2, SP3) wi h isible di e en colo SP1 ( ed),
SP2 (ligh b own), and SP3 (da k b own) we e used (Figu e 1). Ma e ials desc ibed abo e
we e used o ecipe o glazes shown in Table 1, and chemical composi ion o hese aw
ma e ials is p esen ed in Table 2, pa 3.1.
These pigmen s we e applied in hei o iginal o m. These a e syn he ic ine pigmen s,
wi hou any o he addi i es ( ille s), e y inely g ound, wi h e y good colo abili y, opaci y,
and pa icles dis ibu ion, esis an o wea he ing and chemicals, non- oxic, and he mally
s able up o 800
◦
C. Pigmen s a e de e mined acco ding o ˇ
CSN EN 12878—Pigmen s o
he colou ing o building ma e ials based on cemen and/o lime. (Eu opean S anda d
speci ying equi emen s and es ing me hods o pigmen in ended o use in he colo ing
o building ma e ials based on cemen and cemen lime combina ions. Lis o ele an
pigmen s o his applica ion is a ailable in Eu opean S anda ds EN 459 1 and EN 459 2).
Mine als 2021,11, 313 4 o 16
Pigmen s ypically belong o one o he ollowing classes: syn he ic oxides, na u al oxides,
o i on hyd oxides.
Mine als 2021, 11, 313 4 o 16
Figu e 1. Comme cial pigmen s in powde o m used o p epa a ion o glazes.
Table 1. Recipe o glazes p epa ed om was e Fe sludge (WFS) and comme cial pigmen (SP,
s anda d pigmen ).
Recipe Samples Amoun o he Ma e ials (w .%)
T anspa en Glaze (TG) Was e Fe Sludge (WFS) S anda d Pigmen s (SP)
WFS/0 WFS/180 WFS/900 SP1 SP2 SP3
R1
GP01 99 1
GP02 95 5
GP03 90 10
GP04 85 15
GPX 90 10
GOKP 90 10
R2
GPF1 90 10
GPF2 90 10
GPF3 90 10
Table 2. Chemical composi ion o ma e ials.
Amoun o Oxides in Raw Ma e ials (w .%)
Oxides Ce amic
Slu y (CS)
Was e
Fe Sludge
(WFS)
Was e
Fe Sludge
(WFS/0)
Was e
Fe Sludge
(WFS/180)
T anspa en
Glaze
(TG)
SP3
(Da k
B own)
SP2
(Ligh
B own)
SP1
(Red)
Na
2
O 1.22 5.61 4.61 5.50
MgO 2.83 1.12 0.18 <0.3 0.58 0.44 <0.001
Al
2
O
3
12.42 0.20 0.74 0.49 9.10 <0.001 0.44 <0.001
SiO
2
69.57 80.10 0.16 0.80 <0.001
P
2
O
5
<0.0012 0.06 0.16 <0.01 0.022 0.073 <0.001
SO
3
0.19 0.15 0.19 0.71 0.12 0.27 0.33 0.20
K
2
O 2.08 0.88 <0.001 <0.001 <0.001
CaO 4.52 0.02 <0.001 0.30 0.05 0.31 0.01
TiO
2
0.56 <0.001 0.13 0.67 0.59 1.311
MnO 0.07 <0.001 0.006 1.06 0.75 0.13
Fe
2
O
3
4.09 40.92 90.09 97.56 0.22 96.97 95.22 97.807
BaO 0.05 0.05
Cl 22.08 2.47 0.49 0.006 0.017 <0.001
ZnO 29.87 1.52 0.24 0.15 0.13 0.03
PbO 0.05 0.12 <0.001
V
2
O
5
<0.001 0.03 <0.001
C
2
O
3
0.14 <0.001 0.12 <0.001
NiO 0.028 0.10 <0.001
CuO <0.001 0.047 <0.001
These pigmen s we e applied in hei o iginal o m. These a e syn he ic ine pig-
men s, wi hou any o he addi i es ( ille s), e y inely g ound, wi h e y good colo abil-
i y, opaci y, and pa icles dis ibu ion, esis an o wea he ing and chemicals, non- oxic,
and he mally s able up o 800 °C. Pigmen s a e de e mined acco ding o ČSN EN 12878—
Pigmen s o he colou ing o building ma e ials based on cemen and/o lime. (Eu opean
Figu e 1. Comme cial pigmen s in powde o m used o p epa a ion o glazes.
Table 1. Recipe o glazes p epa ed om was e Fe sludge (WFS) and comme cial pigmen (SP, s anda d pigmen ).
Recipe Samples Amoun o he Ma e ials (w .%)
T anspa en Glaze (TG) Was e Fe Sludge (WFS) S anda d Pigmen s (SP)
WFS/0 WFS/180 WFS/900 SP1 SP2 SP3
R1
GP01 99 1
GP02 95 5
GP03 90 10
GP04 85 15
GPX 90 10
GOKP 90 10
R2
GPF1 90 10
GPF2 90 10
GPF3 90 10
Table 2. Chemical composi ion o ma e ials.
Amoun o Oxides in Raw Ma e ials (w .%)
Oxides Ce amic
Slu y (CS)
Was e Fe
Sludge(WFS)
Was e Fe
Sludge
(WFS/0)
Was e Fe
Sludge
(WFS/180)
T anspa en
Glaze (TG)
SP3 (Da k
B own)
SP2 (Ligh
B own) SP1 (Red)
Na2O 1.22 5.61 4.61 5.50
MgO 2.83 1.12 0.18 <0.3 0.58 0.44 <0.001
Al2O312.42 0.20 0.74 0.49 9.10 <0.001 0.44 <0.001
SiO269.57 80.10 0.16 0.80 <0.001
P2O5<0.0012 0.06 0.16 <0.01 0.022 0.073 <0.001
SO30.19 0.15 0.19 0.71 0.12 0.27 0.33 0.20
K2O 2.08 0.88 <0.001 <0.001 <0.001
CaO 4.52 0.02 <0.001 0.30 0.05 0.31 0.01
TiO20.56 <0.001 0.13 0.67 0.59 1.311
MnO 0.07 <0.001 0.006 1.06 0.75 0.13
Fe2O34.09 40.92 90.09 97.56 0.22 96.97 95.22 97.807
BaO 0.05 0.05
Cl 22.08 2.47 0.49 0.006 0.017 <0.001
ZnO 29.87 1.52 0.24 0.15 0.13 0.03
PbO 0.05 0.12 <0.001
V2O5<0.001 0.03 <0.001
C 2O30.14 <0.001 0.12 <0.001
NiO 0.028 0.10 <0.001
CuO <0.001 0.047 <0.001
Mine als 2021,11, 313 5 o 16
The ma e ial s udied was a was e Fe sludge ob ained as a seconda y p oduc du ing
p oduc ion o ZnCl
2
. Un ea ed o m o he was e sludge (labeled as WFS) om he
p oduc ion o zinc oxide (see Figu e 5, yellow colo samples) is no sui able as a pigmen .
The e o e, h ee me hods ha e been p oposed o p epa e a pigmen applicable o glazes:
(a) was e Fe sludge washed by H
2
O (labeled as WFS/0 and in an expe imen called as
he o iginal o m), (b) was e Fe sludge washed by H
2
O and calcined a 180
◦
C (labeled as
WFS/180), and (c) was e Fe sludge washed by H
2
O and calcined a 900
◦
C (labeled as
WFS/900).
2.2. Sample P epa a ion
Two ecipes o p epa ed glazes (Table 1) we e mixed. Recipe 1 con ains 6 di e en
mix u es o glazes. As a pigmen , 1, 5, 10, o 15 w .% o he was e Fe sludge was added in o
he anspa en glaze (Table 2). Recipe 2 can be called “compa a i e” because o mixing
anspa en glaze wi h 10 w .% o comme cial (s anda d) pigmen s. Indi idually p epa ed
mix u es (WFS/0; WFS/180; WFS/900 + TG) and (SP1; SP2; SP3; + TG) we e homogenized
in ball mill de ice wi h con ain he con en o 50% alumina balls by we milling (5% H
2
O)
o 30 min. The we mix u e was sie ed h ough a 0.2 mm sie e. The ob ained suspension
was mixed wi h wa e o each he composi ion exp essed by weigh o glaze. The ange
o li e weigh was de e mined o be om 1442 o 1550 g.L
−1
. The li e g a i y o glaze
was de e mined in a 1 L g adua ed cylinde . Fi s , he weigh o he emp y con aine was
de e mined. Subsequen ly, he con aine wi h he glaze in i was weighed and he weigh
o he emp y con aine was sub ac ed.
Ce amic iles we e p epa ed by cas ing in o gypsum o m ha ing dimensions
10 ×10 cm2
( i eclay slu y wi h a wa e con en o app oxima ely 34%). The ce amic iles
we e d ied a 105
◦
C and i ed in an elec ic esis ance u nace (LAC M125/13HTCe amic,
CZ) a a maximum empe a u e o 900
◦
C o 60 min. The glazes we e applied by sp aying
me hod o ensu e o compac laye s on he su aces o iles.
In his expe imen , he inal i ing was g adually speci ied. Fi ing I: This was o iginally
designed o a empe a u e o 1060
◦
C, a a a e o 3
◦
C/min, and i was wi hou a dwell a
his empe a u e. The samples glazed in his way showed c a e s on he su ace. C a e s a e
usually o med due o gas leakage om he glaze. In his case, he eason migh ha e been
he p esence o ZnO in he pigmen . Fi ing II: The op imal i ing cu e o his ype o
pigmen was wi h wo dwells: 30 min/600 ◦C and 60 min/1060 ◦C.
2.3. Cha ac e iza ion Techniques
•
Chemical composi ion o aw ma e ials was de e mined using ene gy dispe si e
luo escence spec ome e SPECTRO XEPO (SPECTRO Analy ical Ins umen s GmbH,
Kle e, Ge many), equipped wi h 50 Wa Pd X- ay ube.
•
The phase composi ion o samples was cha ac e ized using a B uke D8 Ad ance X-
ay powde di ac ome e (B uke AXS GmbH, Ka ls uhe, Ge many). The di ac ion
pa e ns in he ange o 5
◦
o 70
◦
2
θ
we e eco ded unde CoK
α
(
λ
= 1.78897 Å,
U = 35 kV
, I = 25 mA) i adia ion wi h scanning a e 2
◦
/min using as posi ion-
sensi i e de ec o VÅNTEC1.
•
The mo phology o he pa icles was cha ac e ized using he scanning elec on mic o-
scope (SEM) QUANTA 450 FEG, (FEI, Hillsbo o, OR, USA); he images we e collec ed
using a seconda y elec on de ec o .
•
The pa icle size dis ibu ion (PSD) was analyzed using Mas e size (Mal e n Panaly -
ical L d., Mal e n, UK). Measu emen s we e pe o med in an aqua ic en i onmen ,
and ul asound was used o homogeniza ion o he suspension.
•
The cha ac e iza ion o he he mal beha io was pe o med on TG/DTAanalyze
STA504 (TA Ins umen s, New Cas le, Delawa e, USA). The sample o scale placed
in alumina c ucible was analyzed in a empe a u e ange om 21 o 1100
◦
C in he
dynamic a mosphe e o N2(5 L·h−1), and he hea ing a e was 10 K·min−1.

Mine als 2021,11, 313 6 o 16
•
The e lec ance spec a o he inal glazes in he spec al ange 400–700 nm we e ob ained
using MiniScan EZ0828 spec ome e (Hun e Lab, Res on, VA, USA), model 45
◦
/0
◦
,
small obse a ion a ea. The colo o he glazes was exp essed using CIE L*a*b*
coo dina es calcula ed o 10◦obse e and D65 illuminan .
•
Speci ic su ace a ea was de e mined by BET me hod-equipmen (Quan ach ome No-
aWin Ins umen -Acquisi ion and Reduc ion o NOVA ins umen , analysis gas
ni ogen, G az, Aus ia).
•
Densi y o samples was de e mined by Pycnoma ic and Pycnoma ic ATC (Helium py-
cnome e ) POROTEC GmbH, Coconu C eek, FL, USA.
3. Resul s and Discussion
3.1. Chemical Composi ion
Chemical composi ion o o iginal ma e ials (CS, WFS, FWS/0, WFS/180, and TG)
used in expe imen s is p o ided in Table 2. The main oxides in he ce amic slu y (CS) a e
SiO
2
and Al
2
O
3 (
o e 83 w .%), and ~4 w .% o Fe
2
O
3
and CaO was also ound. T anspa en
glaze (TG) con ains ~80 w .% o SiO
2
, 9 w .% o Al
2
O
3
and 5 w .% o Na
2
O. The was e Fe
sludge (WFS) in o iginal o m (p esen ed as yellow colo in Figu e 5) con ains 41 w .% o
Fe
2
O
3
and high con en o chlo ine (22 w .%) and zinc oxide (up o 29 w .%). A e washing
he was e sludge by H
2
O (WFS/0), he amoun o chlo ine and ZnO signi ican ly dec eased
o 2.4 w .% and 1.5 w .%, espec i ely (Table 2). On he con a y, he amoun o i on oxide
eached 90 w .% a sample WFS/0 and mo e han 97 w .% a sample WFS/180 (Table 2).
The di e ences in he composi ion o he WFS/180 and WFS/900 samples did no exceed
0.5 w .%.
Comme cial pigmen s a e p epa ed by syn he ic ways. La ge amoun o Fe
2
O
3
ex-
pec ed in hese pigmen s was con i med by chemical analysis (Table 2). The ed colo
pigmen (SP1) con ains o e 97 w .% o Fe
2
O
3
. The ligh b own pigmen SP2 con ains
95 w .% o Fe2O3, and he las one, da k b own pigmen SP3, con ains 96 w .% o Fe2O3.
3.2. Phase Composi ion o Comme cial Pigmen s
X- ay di ac ion analysis showed (Figu e 2) showed he mos in ense e lec ions o
hema i e (
α
-Fe
2
O
3
) [
26
–
28
] in all h ee pigmen s. Mo eo e , magne i e was de ec ed in
samples SP2 (Figu e 2b) and SP3 (Figu e 2c). Only one phase was ound in he pigmen SP1
(Figu e 2a), i.e., hema i e wi h he mos in ense e lec ion a he posi ion o 38
◦
2
θ
. In he
case o ligh b own pigmen SP2, he p esence o h ee phases was ound:
α
-hema i e and
magne i e a posi ion 42
◦
2
θ
, and maghemi e (
γ
-Fe
2
O
3
) a posi ion 13
◦
2
θ
. The colo o
maghemi e co esponds o he colo o he SP2 pigmen . In he case o he da k b own
pigmen SP3, dominan e lec ions o hema i e and magne i e a he posi ion 42–44
◦
2
θ
a e
p esen . In addi ion, e lec ions o wüs i e (FeO) can be obse ed a he ollowing posi ions:
42◦, 50◦, and 74◦2θ.
3.3. G anulome y o Comme cial Pigmen s
The syn he ic pigmen s SP1, SP2, and SP3 a e e y ine powde s. All cu es on
(
Figu e 3
) e eal e y simila g ain size. Red pigmen s SP1 ha e g ained size
D (10) = 0.95 µm
,
D (50) = 9.38 µm
, and D
(90)
= 66.7
µ
m. The pa ame e s o ligh b ow pigmen SP2 a e
D
(10)
= 0.47
µ
m, D
(50)
= 5.83
µ
m, and D
(90)
= 19.4
µ
m, while he pa ame e s o he
dis ibu ion cu e o da k b own pigmen SP3 a e D
(10)
= 0.43
µ
m, D
(50)
= 7.02
µ
m,
and
D (90) = 28.4 µm
. The op imum size o pigmen pa icles o mos applica ions is
0.1–10 µm
. F om he measu ed da a, i can be concluded ha he syn he ic pigmen s SP1,
SP2, SP3 ha e he p ope ies decla ed by he manu ac u e .
3.4. SEM Analysis o Comme cial Pigmen s
Comme cial pigmen s show exhibi a conside able he e ogenei y o he pa icles,
as shown by SEM analysis (Figu e 4). The pa icles o hese pigmen s ha e an i egula
shape (see Figu e 4B,C-1, wi h scale 20
µ
m). Image wi h scale 200
µ
m (Figu e 4C-2) also
Mine als 2021,11, 313 7 o 16
do no show he p esence o sphe ical g ains. Based on SEM analysis, i can be s a ed
ha , in e ms o pa icle shape (a ec ing pigmen dispe sibili y), comme cial pigmen s SP1
(Figu e 4A) SP2 (Figu e 4B), and SP3 (Figu e 4C-1,C-2) a e no ideal powde sys ems.
Mine als 2021, 11, 313 7 o 16
Figu e 2. XRD pa e ns o (a) SP1 pigmen ( ed colo ); (b) SP2 pigmen (ligh b own colo ); and (c) SP3 pigmen (da k
b own colo ).
3.3. G anulome y o Comme cial Pigmen s
The syn he ic pigmen s SP1, SP2, and SP3 a e e y ine powde s. All cu es on (Fig-
u e 3) e eal e y simila g ain size. Red pigmen s SP1 ha e g ained size D
(10)
= 0.95 µm,
D
(50)
= 9.38 µm, and D
(90)
= 66.7 µm. The pa ame e s o ligh b ow pigmen SP2 a e D
(10)
= 0.47 µm, D
(50)
= 5.83 µm, and D
(90)
= 19.4 µm, while he pa ame e s o he dis ibu ion
cu e o da k b own pigmen SP3 a e D
(10)
=
0.43 µm, D
(50)
=
7.02 µm, and D
(90)
= 28.4
µm. The op imum size o pigmen pa icles o mos applica ions is 0.1–10 µm. F om he
measu ed da a, i can be concluded ha he syn he ic pigmen s SP1, SP2, SP3 ha e he
p ope ies decla ed by he manu ac u e .
Figu e 3. G ain size dis ibu ion o pigmen : 1) SP1 ( ed); 2) SP2 (ligh b own); 3) SP3 (da k
b own).
3.4. SEM Analysis o Comme cial Pigmen s
Comme cial pigmen s show exhibi a conside able he e ogenei y o he pa icles, as
shown by SEM analysis (Figu e 4). The pa icles o hese pigmen s ha e an i egula shape
(see Figu es 4B and 4C-1, wi h scale 20 µm). Image wi h scale 200 µm (Figu e 4C-2) also
do no show he p esence o sphe ical g ains. Based on SEM analysis, i can be s a ed ha ,
in e ms o pa icle shape (a ec ing pigmen dispe sibili y), comme cial pigmen s SP1
(Figu e 4A) SP2 (Figu e 4B), and SP3 (Figu e 4C-1 and 4C-2) a e no ideal powde sys ems.
Figu e 2.
XRD pa e ns o (
a
) SP1 pigmen ( ed colo ); (
b
) SP2 pigmen (ligh b own colo ); and (
c
) SP3 pigmen
(da k b own colo ).
Mine als 2021, 11, 313 7 o 16
Figu e 2. XRD pa e ns o (a) SP1 pigmen ( ed colo ); (b) SP2 pigmen (ligh b own colo ); and (c) SP3 pigmen (da k
b own colo ).
3.3. G anulome y o Comme cial Pigmen s
The syn he ic pigmen s SP1, SP2, and SP3 a e e y ine powde s. All cu es on (Fig-
u e 3) e eal e y simila g ain size. Red pigmen s SP1 ha e g ained size D
(10)
= 0.95 µm,
D
(50)
= 9.38 µm, and D
(90)
= 66.7 µm. The pa ame e s o ligh b ow pigmen SP2 a e D
(10)
= 0.47 µm, D
(50)
= 5.83 µm, and D
(90)
= 19.4 µm, while he pa ame e s o he dis ibu ion
cu e o da k b own pigmen SP3 a e D
(10)
=
0.43 µm, D
(50)
=
7.02 µm, and D
(90)
= 28.4
µm. The op imum size o pigmen pa icles o mos applica ions is 0.1–10 µm. F om he
measu ed da a, i can be concluded ha he syn he ic pigmen s SP1, SP2, SP3 ha e he
p ope ies decla ed by he manu ac u e .
Figu e 3. G ain size dis ibu ion o pigmen : 1) SP1 ( ed); 2) SP2 (ligh b own); 3) SP3 (da k
b own).
3.4. SEM Analysis o Comme cial Pigmen s
Comme cial pigmen s show exhibi a conside able he e ogenei y o he pa icles, as
shown by SEM analysis (Figu e 4). The pa icles o hese pigmen s ha e an i egula shape
(see Figu es 4B and 4C-1, wi h scale 20 µm). Image wi h scale 200 µm (Figu e 4C-2) also
do no show he p esence o sphe ical g ains. Based on SEM analysis, i can be s a ed ha ,
in e ms o pa icle shape (a ec ing pigmen dispe sibili y), comme cial pigmen s SP1
(Figu e 4A) SP2 (Figu e 4B), and SP3 (Figu e 4C-1 and 4C-2) a e no ideal powde sys ems.
Figu e 3.
G ain size dis ibu ion o pigmen : (1) SP1 ( ed); (2) SP2 (ligh b own); (3) SP3 (da k b own).
Mine als 2021, 11, 313 8 o 16
Figu e 4. SEM images o comme cial pigmen s (A) ed pigmen SP1 wi h scale 20 µm; (B) ligh b own pigmen SP2 wi h
scale 20µm; (C-1) da k b ow pigmen SP3 wi h scale 20 µm and (C-2) da k b own pigmen SP3 wi h scale 200 µm..
3.5. The T ea men o Was e Fe Sludge.
The was e Fe sludge (Figu e 5, labeled as WFS/0) was deli e ed in piece o m con-
aining o e 23% o mois u e. The aim was no only o achie e as much i on con en in he
mix u e as possible bu also o elimina e chlo ine con en . Th ee me hods we e designed
o his p ocess, wi h he esul ing colo e ec o indi idual pigmen s (see Figu e 5):
1. WFS/0—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS,
2. WFS/180—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined a
180 °C a he mode o 15 °C/min o 10 h/180 °C, and
3. WFS/900—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined a
900 °C a he mode o 15 °C/min o 3 h/900 °C.
Figu e 5. Fo m and colo o he un ea ed was e Fe sludge (WFS), was e Fe sludge washed in wa e (WFS/0), was e Fe
sludge calcined a 180 °C (WFS/180), and was e Fe sludge calcined a 900 °C (WFS/900).
Figu e 5 show un ea ed (labeled as WFS) and ea ed pigmen s (labeled as WFS/0,
WFS/180, and WFS/900). Washing he was e wi h wa e emo es soluble impu i ies.
Washing and calcina ion lead o a pa ial educ ion o he Zn and Cl amoun con ained in
he sludge. A e calcina ion, he amoun o H
2
O dec eased. WFS/180 and WFS/900 con-
ained 2.2 w .% and 0.2 w .% o H
2
O, espec i ely. Densi y o WFS/0, WFS/180, and
WFS/900 was 3.85 g/cm
3
, 4.95 g/cm
3
, and 4.46 g/cm
3
, espec i ely. Du ing calcina ion o
WFS/180, i on oxyhyd oxides dehyd a ed o Fe
2
O
3
. This sludge mus be well washed o
emo e mos o he ZnCl
2
con ained in he sludge.
As men ioned be o e, he highe he calcina ion empe a u e, he mo e signi ican
dehyd a ion occu ed. By calcina ion a 900 °C, he washed sludge was s abilized. The
p epa ed pigmen s WFS/180 and WFS/900 a e e y ine powde s. This is p o en by hei
speci ic su ace a ea (SSA) and be e abso p ion o loose mois u e compa ed o he WFS/0
sample, which was sligh ly coa se . Cl
−
bound in he s uc u e and α-FeOOH we e e-
leased du ing hea ea men s as HCl. A he same ime, he amoun o Zn is educed by
up o 97%. Du ing calcina ion o he WFS/900 sample, he Cl
−
in he mix u e was signi i-
can ly elimina ed (by almos 99%). While he o iginal was e Fe sludge WFS/0 con ained
~41 w .% o Fe
2
O
3
, usable was e sludge con aining up o 90 w .% o α-Fe
2
O
3
was ob ained
by he calcina ion.
Figu e 4.
SEM images o comme cial pigmen s (
A
) ed pigmen SP1 wi h scale 20
µ
m; (
B
) ligh b own pigmen SP2 wi h
scale 20µm; (C-1) da k b ow pigmen SP3 wi h scale 20 µm and (C-2) da k b own pigmen SP3 wi h scale 200 µm.
3.5. The T ea men o Was e Fe Sludge
The was e Fe sludge (Figu e 5, labeled as WFS/0) was deli e ed in piece o m con-
aining o e 23% o mois u e. The aim was no only o achie e as much i on con en in he
mix u e as possible bu also o elimina e chlo ine con en . Th ee me hods we e designed
o his p ocess, wi h he esul ing colo e ec o indi idual pigmen s (see Figu e 5):
1. WFS/0—Was e Fe sludge washed by H2Oby1LH2O/300 g o WFS,
2.
WFS/180—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined
a 180 ◦C a he mode o 15 ◦C/min o 10 h/180 ◦C, and
Mine als 2021,11, 313 8 o 16
3.
WFS/900—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined
a 900 ◦C a he mode o 15 ◦C/min o 3 h/900 ◦C.
Mine als 2021, 11, 313 8 o 16
Figu e 4. SEM images o comme cial pigmen s (A) ed pigmen SP1 wi h scale 20 µm; (B) ligh b own pigmen SP2 wi h
scale 20µm; (C-1) da k b ow pigmen SP3 wi h scale 20 µm and (C-2) da k b own pigmen SP3 wi h scale 200 µm..
3.5. The T ea men o Was e Fe Sludge.
The was e Fe sludge (Figu e 5, labeled as WFS/0) was deli e ed in piece o m con-
aining o e 23% o mois u e. The aim was no only o achie e as much i on con en in he
mix u e as possible bu also o elimina e chlo ine con en . Th ee me hods we e designed
o his p ocess, wi h he esul ing colo e ec o indi idual pigmen s (see Figu e 5):
1. WFS/0—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS,
2. WFS/180—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined a
180 °C a he mode o 15 °C/min o 10 h/180 °C, and
3. WFS/900—Was e Fe sludge washed by H
2
O by 1 L H
2
O/300 g o WFS and calcined a
900 °C a he mode o 15 °C/min o 3 h/900 °C.
Figu e 5. Fo m and colo o he un ea ed was e Fe sludge (WFS), was e Fe sludge washed in wa e (WFS/0), was e Fe
sludge calcined a 180 °C (WFS/180), and was e Fe sludge calcined a 900 °C (WFS/900).
Figu e 5 show un ea ed (labeled as WFS) and ea ed pigmen s (labeled as WFS/0,
WFS/180, and WFS/900). Washing he was e wi h wa e emo es soluble impu i ies.
Washing and calcina ion lead o a pa ial educ ion o he Zn and Cl amoun con ained in
he sludge. A e calcina ion, he amoun o H
2
O dec eased. WFS/180 and WFS/900 con-
ained 2.2 w .% and 0.2 w .% o H
2
O, espec i ely. Densi y o WFS/0, WFS/180, and
WFS/900 was 3.85 g/cm
3
, 4.95 g/cm
3
, and 4.46 g/cm
3
, espec i ely. Du ing calcina ion o
WFS/180, i on oxyhyd oxides dehyd a ed o Fe
2
O
3
. This sludge mus be well washed o
emo e mos o he ZnCl
2
con ained in he sludge.
As men ioned be o e, he highe he calcina ion empe a u e, he mo e signi ican
dehyd a ion occu ed. By calcina ion a 900 °C, he washed sludge was s abilized. The
p epa ed pigmen s WFS/180 and WFS/900 a e e y ine powde s. This is p o en by hei
speci ic su ace a ea (SSA) and be e abso p ion o loose mois u e compa ed o he WFS/0
sample, which was sligh ly coa se . Cl
−
bound in he s uc u e and α-FeOOH we e e-
leased du ing hea ea men s as HCl. A he same ime, he amoun o Zn is educed by
up o 97%. Du ing calcina ion o he WFS/900 sample, he Cl
−
in he mix u e was signi i-
can ly elimina ed (by almos 99%). While he o iginal was e Fe sludge WFS/0 con ained
~41 w .% o Fe
2
O
3
, usable was e sludge con aining up o 90 w .% o α-Fe
2
O
3
was ob ained
by he calcina ion.
Figu e 5.
Fo m and colo o he un ea ed was e Fe sludge (WFS), was e Fe sludge washed in wa e
(WFS/0), was e Fe sludge calcined a 180
◦
C (WFS/180), and was e Fe sludge calcined a 900
◦
C
(WFS/900).
Figu e 5show un ea ed (labeled as WFS) and ea ed pigmen s (labeled as WFS/0,
WFS/180, and WFS/900). Washing he was e wi h wa e emo es soluble impu i ies.
Washing and calcina ion lead o a pa ial educ ion o he Zn and Cl amoun con ained in he
sludge. A e calcina ion, he amoun o H
2
O dec eased. WFS/180 and WFS/900 con ained
2.2 w .% and 0.2 w .% o H
2
O, espec i ely. Densi y o WFS/0, WFS/180, and WFS/900
was 3.85 g/cm
3
, 4.95 g/cm
3
, and 4.46 g/cm
3
, espec i ely. Du ing calcina ion o WFS/180,
i on oxyhyd oxides dehyd a ed o Fe
2
O
3
. This sludge mus be well washed o emo e
mos o he ZnCl2con ained in he sludge.
As men ioned be o e, he highe he calcina ion empe a u e, he mo e signi ican
dehyd a ion occu ed. By calcina ion a 900
◦
C, he washed sludge was s abilized. The p e-
pa ed pigmen s WFS/180 and WFS/900 a e e y ine powde s. This is p o en by hei
speci ic su ace a ea (SSA) and be e abso p ion o loose mois u e compa ed o he WFS/0
sample, which was sligh ly coa se . Cl
−
bound in he s uc u e and
α
-FeOOH we e e-
leased du ing hea ea men s as HCl. A he same ime, he amoun o Zn is educed by
up o 97%. Du ing calcina ion o he WFS/900 sample, he Cl−in he mix u e was signi i-
can ly elimina ed (by almos 99%). While he o iginal was e Fe sludge WFS/0 con ained
~41 w .%
o Fe
2
O
3
, usable was e sludge con aining up o 90 w .% o
α
-Fe
2
O
3
was ob ained
by he calcina ion.
3.6. G anulome y o Was e Fe Sludge
Ino ganic pigmen s a e la gely p esen in he powde o m. The ideal powde ma e ial
con ains only pa icles o he same size; howe e , he ac ual sys em consis s o pa icles o
di e en sizes. Pa icle size dis ibu ion is a e y impo an c i e ion o powde pigmen s,
as he g ain size has a undamen al e ec on he op ical p ope ies o pigmen s. I is
associa ed wi h he sca e ing o ligh on he pa icles, so i highly a ec s he esul ing
opaci y and colo . The sample was measu ed in an aqueous medium, and wi h ega d o he
p esence o clumps in he in es iga ed pigmen s, ul asound was used o be e dispe sion.
The esul s a e p esen ed by dis ibu ion cu es in Figu e 6. Cu es 2 and 3 ha e
a iable g ain size. Pigmen WFS/0 has g ain sizes D
(10)
= 6.14
µ
m, D
(50)
= 13.8
µ
m,
and D
(90)
= 30.3
µ
m. The pa ame e s o WFS/180 a e D
(10)
= 0.898
µ
m,
D (50) = 2.61 µm
,
and D
(90)
= 7.7
µ
m, while he pa ame e s o he dis ibu ion cu e o pigmen WFS/900
a e D
(10)
= 1.98
µ
m, D
(50)
= 44.4
µ
m, and D
(90)
= 1950
µ
m. The pa icles can be di ided
in o coa se—o e 10
µ
m; la ge—10 o 3
µ
m; medium—3 o 1
µ
m; ine—1 o
0.3 µm
;
and e y ine—below 0.3 µm.
3.7. SEM Analysis o Was e Fe Sludge
The pa icle size was changed by calcina ion. The mos common mo phology o
hema i e pa icles ob ained by pep iza ion me hod and calcined a 500
◦
C was unca ed
hombohed ons, cubes, and oc ahed ons [29].
Mine als 2021,11, 313 9 o 16
Mine als 2021, 11, 313 9 o 16
3.6. G anulome y o Was e Fe Sludge
Ino ganic pigmen s a e la gely p esen in he powde o m. The ideal powde ma e-
ial con ains only pa icles o he same size; howe e , he ac ual sys em consis s o pa i-
cles o di e en sizes. Pa icle size dis ibu ion is a e y impo an c i e ion o powde
pigmen s, as he g ain size has a undamen al e ec on he op ical p ope ies o pigmen s.
I is associa ed wi h he sca e ing o ligh on he pa icles, so i highly a ec s he esul ing
opaci y and colo . The sample was measu ed in an aqueous medium, and wi h ega d o
he p esence o clumps in he in es iga ed pigmen s, ul asound was used o be e dis-
pe sion.
The esul s a e p esen ed by dis ibu ion cu es in Figu e 6. Cu es 2 and 3 ha e
a iable g ain size. Pigmen WFS/0 has g ain sizes D (10) = 6.14 µm, D (50) = 13.8 µm, and
D (90) = 30.3 µm. The pa ame e s o WFS/180 a e D (10) = 0.898 µm, D (50) = 2.61 µm, and
D (90) = 7.7 µm, while he pa ame e s o he dis ibu ion cu e o pigmen WFS/900 a e
D (10) = 1.98 µm, D (50) = 44.4 µm, and D (90) = 1950 µm. The pa icles can be di ided in o
coa se—o e 10 µm; la ge—10 o 3 µm; medium—3 o 1 µm; ine—1 o 0.3 µm; and e y
ine—below 0.3 µm.
Figu e 6. G ain size dis ibu ion o pigmen was e Fe sludge: 1) o iginal (WFS/0); 2) calcined a 180
°C (WFS/180); 3) calcined a 900 °C (WFS/900).
3.7. SEM Analysis o Was e Fe Sludge
The pa icle size was changed by calcina ion. The mos common mo phology o hem-
a i e pa icles ob ained by pep iza ion me hod and calcined a 500 °C was unca ed hom-
bohed ons, cubes, and oc ahed ons [29].
Fo ino ganic pigmen s, i is sui able ha pa icle sizes ange om 0.1 o 10 µm [30],
so he pigmen s ha e good co e ing and abso p ion quali ies. Figu e 7 shows WFS/0 sam-
ple mo phology as de e mined by SEM by all samples and EDAX by (Figu e 7A-1). SEM
images show a no qui e egula ound pa icle sys em (Figu e 7C-2). Mo eo e , pa icles
la ge han 1000 µm a e also included in his sample, as de e mined by g anulome y
(Figu e 6). Figu e 7A-1 shows mo e clea ly ha he e a e ound pa icles o di e en sizes,
o med by clus e s o smalle ound pa icles o app oxima ely 20 µm. Thus, i he pa i-
cles a e clus e ed in o e en smalle objec s, he g anulome ic cu es may be so a iable
on his basis.
Figu e 6.
G ain size dis ibu ion o pigmen was e Fe sludge: (1) o iginal (WFS/0); (2) calcined a
180 ◦C (WFS/180); (3) calcined a 900 ◦C (WFS/900).
Fo ino ganic pigmen s, i is sui able ha pa icle sizes ange om 0.1 o 10
µ
m [
30
],
so he pigmen s ha e good co e ing and abso p ion quali ies. Figu e 7shows WFS/0
sample mo phology as de e mined by SEM by all samples and EDAX by (Figu e 7A-1).
SEM images show a no qui e egula ound pa icle sys em (Figu e 7C-2). Mo eo e , pa i-
cles la ge han 1000
µ
m a e also included in his sample, as de e mined by g anulome y
(Figu e 6). Figu e 7A-1 shows mo e clea ly ha he e a e ound pa icles o di e en sizes,
o med by clus e s o smalle ound pa icles o app oxima ely 20
µ
m. Thus, i he pa icles
a e clus e ed in o e en smalle objec s, he g anulome ic cu es may be so a iable on
his basis.
The chlo ine p esen in he WFS/0 (see Figu e 7A-2) comes om he ZnCl
2
pu i ica ion
p ocess. The minimum amoun o Al p obably comes om a e y di e en compound con-
ained in he sludge p ecipi a e (Figu e 7A-2). The highes densi y, 4.95 g/cm
3
, was ound
o he WFS/180 sample, while he o iginal un ea ed WFS/0 sample had he lowes den-
si y o all. The mal calcina ion led o an inc ease in densi y by 28%. Wi h an inc ease o he
empe a u e, he SSA changes om 6.89 m
2
/g ( o WFS/0) o 23.6 m
2
/g (WFS/180) and
14.86 m
2
/g (WFS/900). The SSA o comme cial samples was de e mined o be 23.67 m
2
/g.
The SSA alue o all i on oxides p epa ed in his s udy is compa able o he comme cial
pigmen s used in his expe imen .
3.8. Phase Analysis o Was e Fe Sludge
Resul s o he XRPD phase analysis a e shown in Figu e 8. The pa e n o he sample
WFS/0 (see Figu e 8a) does no show any e lec ions. This sample con ains Fe
2
O
3
in
amo phous o m. Wide e lec ions o hema i e phase we e ound in he case o sample
WFS/180; dominan e lec ion is in he posi ion 38
◦
2
θ
(PDF-2 ca d no. 00-033-064-64).
F om he poin o iew o he XRPD measu emen , he sample WFS/180 (see Figu e 8b)
is compa able wi h he sample SP1. XRPD pa e n o he sample WFS/900 (see
Figu e 8c
)
con ains c ys alline phase o he
α
-Fe
2
O
3
(hema i e) (PDF-2 ca d no.01-076-45-79) wi h
he mos in ensi e e lec ion in he posi ion 39
◦
2
θ
. Wi h inc easing empe a u e o cal-
cina ion, he e lec ions a e na owe . In some cases, he goe hi e
α
-FeOOH ans o ms
in o c ys alline phase o hema i e, p esen as na owly shaped peaks [
31
]. Bu he goe hi e
phase was no ound in es ed pigmen s (Figu e 8). When mixing he pigmen s wi h he
anspa en glaze, ce ain phase changes occu ed. The
α
-Fe
2
O
3
o m is s able up o
800 ◦C
,
as decla ed by he manu ac u e . When i ed a 1060
◦
C, he magne i e o m changes o
hema i e, which is s able up o 1000 ◦C [24].
3.9. TG and DTA o Was e Fe Sludge
TG a DTA cu es o WFS/0 sample a e shown in Figu e 9. Signi ican endo he mic
eac ions a e p esen on he empe a u e a 110
◦
C, and 562
◦
C can be connec ed wi h
mois u e decomposi ion. Hema i e o m unde a mosphe ic condi ions and o en he
end o oxida i e ans o ma ion o o he i on oxides. Then, wi h empe a u e ising,
goe hi e can ans o m o
α
-Fe
2
O
3
o he peak is a ibu ed o he oxida ion o FeO o Fe
3
O
4
Mine als 2021,11, 313 16 o 16
40.
Pekkan, K.; Ka asu, B. E alua ion o bo ax solid was es in p oduc ion o i s sui able o as single- i ed wall ile opaque
glass-ce amic glazes. Bull. Ma e . Sci. 2010,33, 135–144. [C ossRe ]
41.
Be na din, A.M. The in luence o pa icle size dis ibu ion on he su ace appea ance o glazed ile. Dyes Pigmen .
2009
,80,
121–124. [C ossRe ]