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Mixed α-Fe2O3/Bi2WO6 oxides for photoassisted hetero-Fenton degradation of Methyl Orange and Phenol

Abstract

Mixed oxides, α-Fe2O3/Bi2WO6, were prepared using a mechanical mixing procedure by adding to the Bi2WO6 previously obtained by hydrothermal method the corresponding amount of a prepared α-Fe2O3, the latter obtained by thermal decomposition of Fe(NO3)∙9H2O. The physicochemical surface, structural, morphological characteristics and optical properties of the samples, single and mixed, were determined by BET, XRD, FE-SEM, XPS and UV–vis diffuse reflectance spectroscopy. UV–vis diffuse reflectance spectra showed that incorporating a 5%wt. of α-Fe2O3 to the corresponding amount of Bi2WO6 sample broadened the visible light absorption of Bi2WO6 as expected. The photocatalytic activity, of single and mixed catalysts, to degrade a selected dye such as Methyl Orange (MO) as well as the transparent substrate Phenol (Ph) was studied, in aqueous medium (pH ≈ 5.5) under UV and sun-like illumination conditions in the absence and presence of H2O2. In the present study the use of a α-Fe2O3-Bi2WO6/H2O2 system demonstrate much higher photocatalytic efficiency to degrade both MO and Ph than pristine Bi2WO6or α-Fe2O3, single or mixed. Using the system α-Fe2O3-Bi2WO6/H2O2, around 85% of MO was degraded in 60 min under sun-like illumination whereas 100% was degraded in 60 min under UV-illumination. However, just around 30% of Ph was degraded in 120 min in the α-Fe2O3-Bi2WO6/H2O2 system under sun-like illumination whereas around a 95% was degraded in 90 min under UV-illumination. Under UV-illumination, the generation of hydroxyl radicals is favorable; whereas under sun-like illumination, only the small fraction of the UV can produces the radical dotOH. Under illumination, the H2O2 could react with photoinduced electrons from the photocatalysts leading to the production of hydroxyl radicals (radical dotOH).

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Mixed α-Fe2O3/Bi2WO6 oxides for photoassisted hetero-Fenton degradation of Methyl Orange and Phenol

Author: Jaramillo Páez, César Augusto; Navío Santos, José Antonio; Hidalgo López, María del Carmen; Bouziani, Asmae; El Azzouzi, Mohammed
Publisher: Elsevier
Year: 2017
DOI: 10.1016/j.jphotochem.2016.09.031
Source: https://idus.us.es/bitstreams/7620c891-5f5e-4008-85e7-4f04c7ae53da/download
Mixed α-Fe2O3/Bi2WO6oxides o Pho oassis ed
He e o-Fen on Deg ada ion o Me hyl O ange and Phenol
C. Ja amillo-Páez1*, J.A. Na ío1, M.C. Hidalgo1,
Asmae Bouziani2,Mohammed EL AZZOUZI2
1Ins i u o de Ciencia de Ma e iales de Se illa, Cen o Mix o Uni e sidad de
Se illa-CSIC, Amé ico Vespucio 49, 41092 Se illa, Spain
2Depa men o Chemis y, Facul y o Sciences Raba , Uni e si y Mohammed
V 4 A enue IBN BATTOUTA B.P.1014 RPRaba , Mo occo.
Abs ac
Mixed oxides, α-Fe2O3/Bi2WO6, we e p epa ed using a mechanical mixing
p ocedu e by adding o he Bi2WO6p e iously ob ained by hyd o he mal me hod
he co esponding amoun o a p epa ed α-Fe2O3, he la e ob ainedby he mal
decomposi ion o Fe(NO3).9H2O. The physicochemical su ace, s uc u al,
mo phological cha ac e is ics and op ical p ope ies o he samples, single and
mixed, we e de e mined by BET, XRD, FE-SEM, XPS and UV-Visible di use
e lec ance spec oscopy. UV– is di use e lec ance spec a showed ha
inco po a ing a 5%w . o α-Fe2O3 o he co esponding amoun o Bi2WO6
sample b oadened he isible ligh abso p ion o Bi2WO6as expec ed. The
pho oca aly ic ac i i y, o single and mixed ca alys s, o deg ade a selec ed dye
such as Me hyl O ange (MO) as well as he anspa en subs a e Phenol
(Ph)we e s udied, in aqueous medium (pH ≈ 5.5)unde UV and sun-like
illumina ion condi ions in he absence and p esence o H2O2. In he p esen
s udy he use o aα-Fe2O3-Bi2WO6/H2O2sys emdemons a e much highe
pho oca aly ic e iciency o deg ade bo h MO and Ph han p is ineBi2WO6o α-
Fe2O3, single o mixed. Using he sys em α-Fe2O3-Bi2WO6/H2O2, a ound 85%
o MO was deg aded in 60 min unde sun-like illumina ion whe eas 100% was
deg aded in 60 min unde UV-illumina ion. Howe e , jus a ound 30% o Ph was
deg aded in 120 min in he α-Fe2O3-Bi2WO6/H2O2sys em unde sun-like
illumina ion whe eas a ound a 95% was deg aded in 90 min unde UV-
illumina ion. Unde UV-illumina ion, he gene a ion o hyd oxyl adicals is
a o able; whe eas unde sun-like illumina ion, only he small ac ion o he UV
can p oduces he •OH.Unde illumina ion, he H2O2could eac wi h
pho oinduced elec ons om he pho oca alys s leading o he p oduc ion o
hyd oxyl adicals (•OH).
Keywo ds:Bismu h Tungs a e; I on oxide; Pho oca alysis; Pho o-Fen on;
Phenol; Dyes; Hyd oxyl adicals.
* Co esponding au ho . Tel.: +34955420998
E-mail add ess: na [email p o ec ed](J.A. Na ío).
1. In oduc ion
The inc ease o indus ial ac i i ies has become a se ious p oblem ha leads o
he augmen a ion o pollu ion inai , wa e and soil. To ace his p oblem, he
scien i ic communi y wo ks o ind new me hods o undo
hecon amina ion.Du ing he pas ew decades, a a ie y o p ac ical s a egies
ha e been implemen ed o de elop iable was ewa e ea men
echnologies[1–6].
Those echnologies a e e y appealing al e na i es o he deg ada ion o
o ganic pollu an s because hey pe mi a pa ial o comple e mine aliza ion o
pollu an s. I is based on he p oduc ion o he e y eac i e and nonselec i e
en i ies (pa icula ly he hyd oxyl adicals•OH) ha ing a highe oxidizing capaci y
han adi ional oxidan s (O2, Cl2, ClO2, H2O2, O3…)[7–9].
Pho oca aly ic deg ada ion o o ganic pollu an s o pu i y was ewa e om
indus ies and household has ecei ed ex ensi e a en ion in ecen yea s. In
pa icula , he e ogeneous pho oca alysis shows p omising po en ial in dep h-
oxida ion o pollu an s o non- oxic ino ganic molecules a ambien
empe a u e[10].
Dyes a e molecules commonly ound in eal e luen s om ex ile and o he
indus ial was ewa e s[11,12]. Dyes a e majo o ganic pollu an s, which can
cause se e e en i onmen al dis up ion and heal h damages[13]. Simila ly,
phenol is one o he mos abundan pollu an s in indus ial was ewa e s and i s
oxici y, ca cinogenici y and pe sis ence, makes hiscompound dange ous o li e
a a he low concen a ions. In his sense, he e ogeneous pho oca alysis,
among a g oup o a ailable echnologies known as ad anced oxida ion
p ocesses (AOPs), is an impo an al e na i e o emo e a wide ange o
o ganic compounds, including phenolsand dyes, in pollu ed s eams. O he
echnologies as Fen on and Pho o-Fen on ha e been success ully used in
depollu ion o wa e [14–18].
To mee he equi emen o u u e en i onmen al applica ions, in he ield o
AOPs, i is s ill essen ial o no only u he imp o e he pho oca aly ic ac i i y by
syn hesizing new pho oca alys s bu also o explo e new combined p ocesses.
The de elopmen o new pho oca alys s is a ac ing as in e es . Among hem
he Bismu h ungs a e (Bi2WO6) is a ypical n- ype di ec band gap
semiconduc o wi h a band gap o 2.8 eV and has p ospec i e applica ions o
he deg ada ion o o ganic pollu an s unde isible ligh illumina ion due o hei
low alence band and high chemical s abili y[19]. In he same con ex , i on
oxide (α-Fe2O3, hema i e) wi h a na ow band gap a 2.2 eV, abso bing he ligh
up o 600 nm and collec ing abou 40% o he sola spec um ene gy, is also
ano he o he p omising ma e ials o pho oca aly ic applica ions[20].
H2O2is a dis inc i e oxida i e agen and has been equen ly used in p ac ical
wa e ea men , because i ’s a e y common sou ce o e y ac i e hyd oxyl
adicals (•OH) by i s decomposi ion a e being illumina ed wi h ul a iole (UV)
ligh .The use o H2O2in pho ochemical p ocesses (UV/H2O2) and UV (H2O2/
Fe3+ (Pho o-Fen on)) has been in es iga ed[1,21–24], howe e , long pe iods o
UV-illumina ion a e equi ed, huspoo deg ee o mine aliza ion isob ained,
makingall hese p ocesses no pe spec i es as po en ial me hods o
was ewa e pu i ica ion.
F om ano he pe spec i e, as an elec on cap u e agen , H2O2can also eac
wi h pho ogene a ed elec ons, om a pho oca aly ic p ocess, o
p oducehyd oxyl adicals (•OH) as es ablished in eq. (1-2) in which (SC) is a
gene al semiconduc o pho oca alys [25].
(SC) + h

→ (SC)(e-CB + h+VB) (ligh abso p ion) (eq. 1)
(H2O2) +e-CB → •OH+ OH-(eq.2)
(H2O) + h+VB→ •OH+ H+(eq.3)
The o ma ion, he adso p ion and he deg ada ion o H2O2on di e en samples
(TiO2and ZnO) ha e been in es iga ed o be e unde s and i s pa icipa ion in
he pho oca aly ic eac ions [26]. In a ypical UV/H2O2/TiO2sys em, he ac i e
adical o ma ion can a ises no only om he di ec UV-pho olysiswhich akes
place h oughahomoly ic p ocess (H2O2+ h → 2 •OH) bu also om he
pho oca aly ic ones (equa ion 1 o 3).
Thus, i he pho oca alys only abso bs in he UV egion, hen he hyd oxyl
adicals pho ogene a ion, du ing he combined pho ochemical p ocess
UV/(SC)/H2O2, can ake place no only by he homogeneous pho oly ic
decomposi ion o H2O2, bu also acco ding o he p ocesses indica ed in
equa ions 1 and 2. Bu i he pho oca alys abso bs in he isible egion, he
gene a ion o hyd oxyl adicals (OH.)would be expec ed o occu , unde isible
illumina ion,by he pho ogene a ed elec on cap u e o H2O2, since he pho oly ic
decomposi ion o H2O2 equi es sho e wa eleng hs[1].
The gene a ion o H2O2and hyd oxyl adicals on Bi2WO6 o phenol deg ada ion
unde isible ligh has been epo ed [27]. F om his wo k, Au ho s concluded
ha he obse ed o ganic deg ada ion o e he i adia ed Bi2WO6in ae a ed
aqueous solu ion is due o he p oduc ion o •OH and H2O2.
Bo h pho oca alys s, Bi2WO6and α-Fe2O3, display po en ial ca aly ic ac i i y o
many chemicals o ganic deg ada ion unde condi ions o sun-like illumina ion.
Howe e , due o he high ecombina ion a e o pho ogene a ed cha ge ca ie s,
he abili y is he eo limi ed. Va ious s a egies, such as he e os uc u ed
cons uc ing a e being de eloped[28–30].
The aim o his wo k is no ocused on de eloping a α-
Fe2O3/Bi2WO6he e os uc u e, bu o use a physical mix u e o bo h ma e ials
and explo e hei pho ochemical ac i i y in he p esence o absence o H2O2in
he deg ada ion o wo selec ed subs a es.
The e o e, when H2O2is co-p esen wi h single o physically mixed Bi2WO6and
α-Fe2O3, di e en ac i i ies could be displayed because, pa allel o he
mechanism o homogeneous deg ada ion by hyd oxyl adicals pho ogene a ed
by H2O2, he e ec gene a ed by he in insic pho oca aly ic ac i i y o single o
mixed sys emsisalso expec ed o occu .
Me hyl o ange (MO) and phenol (Ph) a e used o imi a e non biodeg adable,
oxic o ganic compounds. The pho oca aly ic ac i i y, unde UV o sun-like
Illumina ion, o α-Fe2O3, Bi2WO6and mixed α-Fe2O3/Bi2WO6samples, o Me hyl
O ange and Phenol deg ada ion, in he absence and p esence o H2O2is
epo ed.
2. Expe imen al de ails
2.1 P epa a ion o α-Fe2O3, Bi2WO6and mixed α-Fe2O3/Bi2WO6samples

All he eagen s used in his p ocedu e we e analy ical g ade wi hou u he
pu i ica ion. The de ailed syn hesis p ocedu e o single α-Fe2O3, Bi2WO6and
mixedα-Fe2O3/Bi2WO6sample was as ollow: The i on oxide was p epa ed by
d ying i on(III) ni a e nonahyd a e Fe(NO3).9H2O a 120°C o 2h hen
submi ing he samples o a u he calcina ions ea men a 300°C o 2h.
The Bi2WO6was p epa ed acco ding o he me hod p e iously desc ibed [31]by
dissol ing 4.85 g o Bi (NO3)3.5H2O in 10 mL o glacial ace ic acid, and 1.7 g o
Na2WO4.2H2O in 90 mL o dis illed wa e , hen hose wo solu ions we e mixed
o ming a whi e suspension (pH≈2), which was kep unde s i ing o 1h. The
whi e suspension was ans e ed in o a Te lon ecipien insideas ainless s eel
au ocla e.The hyd o he mal ea men was done a 140°C o 20h, and hen he
p ecipi a e was il e ed, washed and d ied o e nigh a 120°C. Finally he
sample was submi ed o a calcina ion ea men a 300°C o 4h.
The α-Fe2O3/Bi2WO6mixed samples we e ob ained wi h a mechanical mixing in
aga e mo a , by adding he p epa ed α-Fe2O3 o he co esponding amoun o
Bi2WO6 o a 5w . % o i on oxide in he mix u e. This sample will he ea e be
named as BW-Fe(5)-2 indica ing a 5% o i on oxide and ha Bi2WO6was
p epa ed a pH=2.
2.2. Cha ac e iza ion o he pho oca alys s
BET su ace a eas (SBET) o all samples we e e alua ed by N2adso p ion
measu emen wi h a Mic ome i ics ASAP 2010 ins umen . Degasi ica ion o he
samples was pe o med a 150 ºC o 30 min in He low.
C ys alline phase composi ion o he samples was es ima ed by X- ay di ac ion
(XRD). XRD pa e ns we e ob ained on a Siemens D-501 di ac ome e wi h Ni
il e and g aphi e monoch oma o using Cu Kα adia ion.
The mo phology o all he samples was analyzed by ield Scanning elec on
mic oscopy (FE-SEM) using a Hi achi S 4800 mic oscope.
Ligh abso p ion p ope ies o he samples we e s udied by UV–Vis
spec oscopy. The Di use Re lec ance UV–Vis Spec a (UV–Vis DRS) we e
eco ded on a Va ian spec ome e model Ca y 100 equipped wi h an
in eg a ing sphe e and using BaSO4as e e ence. Band-gaps alues we e
calcula ed om he co esponding Kubelka–Munk unc ions, F(R∞), which a e
p opo ional o he abso p ion o adia ion, by plo ing (F(R∞)×hν)1/2 agains hν.
X- ay pho oelec on spec oscopy (XPS) s udies we e ca ied ou on a Leybold-
He aeus LHS-10 spec ome e , wo king wi h cons an pass ene gy o 50 eV.
The spec ome e main chambe , wo king a a p essu e <2×10−9To , is
equipped wi h an EA-200 MCD hemisphe ical elec on analyze wi h a dual X-
ay sou ce wo king wi h Al Kα (hν=1486.6 eV) a 120 W and 30 mA. C1s signal
(284.6 eV) was used as in e nal ene gy e e ence in all he expe imen s.
Samples we e ou gassed in he p e-chambe o he ins umen a 150 ºC up o a
p essu e <2×10−8To o emo e chemiso bed wa e .All pho oelec on spec a
we e analyzed using Casa-XPS so wa e.
2.3. Pho odeg ada ion es s
The pho oca aly ic ac i i y o he ca alys s p epa ed was es ed in he pho o-
discolo a ion o a selec ed dye, Me hyl O ange (MO), as well as on he
pho odeg ada ion o Phenol (Ph) as a selec ed anspa en , oxic
subs a e.Me hyl O ange and Phenol (Reagen Plus >99%) we e supplied by
Sigma-Ald ich.Pho oca aly ic es s we e ca ied ou using a discon inuous ba ch
sys em, his includes a 250 mL Py ex eac o en eloped by an aluminum oil,
illed wi h an aqueous suspension (100 mL) con aining ei he he single
subs a es (concen a ions: 20 ppm o MO o 50 ppm o phenol) o a mix u e o
bo h (10 ppm o MO/25 ppm phenol) and he pho oca alys (1g/L). On he
expe imen s in which H2O2is co-p esen , ei he wi h subs a es o wi h
subs a es and ca alys s, be o e illumina ion, a ce ain amoun (~ 3 mM) o H2O2
(w . 30%) was added in he medium. The mixed solu ion was magne ically
s i ed in he da k o 20 min. Sys ems we e illumina ed h ough a UV-
anspa en Plexiglas® op window ( h eshold abso p ion a 250 nm) by an
Os am Ul a-Vi alux lamp (300 W) wi h sun-like adia ion spec um and a main
line in he UVA ange a 365 nm. The in ensi y o he inciden UV-Visible ligh on
he solu ion was measu ed wi h a Del a OHM pho o- adiome e HD2102.1,
being ca. 110 W/m2whe eas he in ensi y o he inciden UV ligh on he
solu ion was o ca. 90 W/m2. In o de o a o he adso p ion–deso p ion
equilib ium be ween he ca alys s and subs a es, p io o i adia ion he
suspension was magne ically s i ed o 20 min in heda k. Magne ic s i ing and
a cons an oxygen low o 20 L/h, as an oxidan , we e used o p oduce a
homogeneous suspension o he pho oca alys in he solu ion. A ank bubble
was used as a sou ce o na u al oxygen. All pho oca aly ic es s s a ed a pH
ca. 5.5 and he o al eac ion ime was 120 min.
Du ing he Me hyl O ange pho o eac ion, samples we e collec ed a di e en
imes and in o de o e alua e he dye discolo a ion a e, he concen a ion o
Me hyl O ange du ing he pho odeg ada ion eac ion was analyzed by UV–
Visible spec oscopy, conside ing he main peak o his dye in he isible ange,
loca ed a 465 nm. Fo his analysis a UV– is spec ome y wi h a Ca y 100
(Va ian) spec ome e was used.
Phenol concen a ions we e ollowed by HPLC echnique (Agilen , 1200 Se ies)
using anElipse XDB-C18 column (4.6 x 150 mm i.d., 5 μm; Agilen ) a 40ºC.
Mobile phase was wa e /me hanol (65:35) a a low a e o 0.8 ml/min. Samples
o abou 2 mL we e emo ed pe iodically du ing he expe imen and il e ed
(Millipo e Millex 25 0.45 mm memb ane il e ) p e ious o HPLC measu emen s.
Pho olysis es s o subs a es unde illumina ion and in absence o ca alys we e
ca ied ou . Unde he expe imen al condi ions used in his wo k, subs a e
pho olysis was negligible. Rep oducibili y o he measu emen s was ensu ed by
double es ing o selec ed samples.
To al o ganic ca bon was ollowed also by means o a TOC analyze (Shimadzu
5000). Mine aliza ion deg ees (%) we e e alua ed by he TOC alues upon 2 h
o illumina ion, o all he pho o-assis ed p ocesses s udied.
3. Resul s and discussion
3.1. Cha ac e iza ion
Figu e 1 shows X- ay di ac ion pa e ns (XRD) o he p epa ed ma e ials.The
XRD o he as-p epa ed i on oxide sample showed he di ac ion peaks
co esponding o he s anda d α-Fe2O3(JCPDS no. 33-0664). The main peaks
a 24.1, 33.1, 35.6, 49.5 and 54.1º was obse ed, which co espond o (012),
(104), (110), (024) and (116) di ac ion planes o hema i e espec i ely. Fo he
Bi2WO6sample all he di ac ion peaks a e in good consis en wi h he s anda d
da a o he pu e usseli e o ho hombic Bi2WO6phase (JCPDS no. 39-0256).
ca alys s, which ob iously condi ion he capaci y o su ace adso p ion o
subs a es o di e en chemical na u es. In ac , acco ding o he esul s
epo ed in he li e a u e [26], he adso p ion capaci y o H2O2seems o be
linked o he numbe o OH g oups p esen on he su ace o solids.
Rega dless o his, i is e iden ha he Bi2WO6-H2O2sys em inc eases he
deg ees o mine aliza ion o bo h subs a es, wi h espec o hose ob ained
when only he ca alys o H2O2a e used.
A p oposed mechanism o explain he combined p ocess o Bi2WO6and H2O2,
would be he gene a ion o hyd oxyl adicals, ei he by cap u ing elec ons by
H2O2and he simul aneous oxida ion o H2O by holes, as s a ed in he
equa ions 1 o 3 in which he semiconduc o (SC) would be Bi2WO3, as well as
by he di ec pho oly ic p ocesses (H2O2+ h → 2 OH.).
3.2.3 α-Fe2O3andα-Fe2O3-H2O2
Figu e 6A shows he p ocesses in he da k and unde illumina ion, which occu
o MO subs a e in he p esence o α-Fe2O3. As can be seen in he da k, a
la ge adso p ion o MO occu s a he su ace o α-Fe2O3. A en a i e explana ion
o he adso p ion p ocess in he da k would be he es ablishmen o a weak
Lewis acid-base in e ac ion be ween he elec on densi y o he ch omopho e
g oup (-N=N-) and d-o bi als o Fe3+.A e equilib a ion, he backligh , bo h in he
UV and sun-like, gene a es a pho o-deso p ion p ocess o he MO.These pho o-
deso p ion p ocesses a e accompanied by pho oca aly ic deg ada ion
p ocesses o MO, since a e 120 min unde ligh ing condi ions TOC alues
ob ained indica e ha he e has been a pe cen age o 27.4% o

mine aliza ion(Table 1).Howe e , as he TOC measu emen is pe o med on he
liquid phase, i is also possible ha MO is no comple ely deso bed and his
appa en dec ease on TOC could no be ela ed o a mine aliza ion.
This ac is impo an since i on is he second mos abundan me al on Ea h,
and he mine al hema i e is mos o en o med in na u al wa e . Thus, a na u al
pho oca aly ic deg ada ion p ocess wi h pa icles o α-Fe2O3suspended in
wa e o sedimen s could ha e a bene icial impac o he wa e ecosys em
con amina ed by MO.
In he deg ada ion es o MO wi h α-Fe2O3, an ini ial adso p ion and la e
deso p ion unde illumina ion is obse ed (Figu e 6A).This beha io obse ed
o he MO in he p esence o α-Fe2O3, is no obse ed when Phenol is used.
Figu e 6B shows he plo o he con e sion pe cen ages o Phenol, using he
p epa ed ca alys s α-Fe2O3.As wi h he use o Bi2WO6, he use o α-Fe2O3leads
o con e sion pe cen ages which a e negligible o bo h subs a es, bo h unde
UV and sun-like illumina ion. These esul s indica e ha he as p epa ed i on
oxide sample p esen s, no only a low adso p ion capabili y o Phenol bu also
a low pho oac i i y, al hough op ical abso p ion esul s, by DRS (Fig.2), indica e
a wide op ical abso p ion bo h in he ul a iole and in he isible, being in
acco dance wi h he na ow band gap a 2.2 eV. The poo pho oac i i y, es ed
o he p epa ed α-Fe2O3, simila ly o ha obse ed o Bi2WO6, could be
associa ed wi h he high ecombina ion o cha ge ca ie s in he p epa ed
samples.I is in e es ing o no e ha al hough nosigni ican deg ees o
con e sion o phenol we e obse ed, howe e TOC alues indica e ha he e
has been a ce ain deg ee o mine aliza ion (25-35%) o phenol(Table 1).
I is in e es ing o no e ha he simul aneous p esence o he ca alys (α-Fe2O3)
and H2O2, leads oa signi ican inc ease in con e sion pe cen ages o bo h
subs a es, bo h in he UV and he sun-like (Figu es 6C and 6D) and ha hey
a e di e en om hose ob ained o he wosubs a es bo h wi honly he
ca alys (Figu es 6A and 6B) and wi h H2O2alone (Figu es 4A and 4B).These
esul s a e no su p ising i hey a e explained in he con ex o a pho oassis ed
he e o-Fen on p ocess implemen ed by he α-Fe2O3/H2O2
sys em.Thus, ega dless o whe he he H2O2-pho oly ic p ocess gene a ing •OH
adicals (equa ion 7), he α-Fe2O3/H2O2sys emwould also be ac ing by
gene a ing mo e hyd oxyl adicals ia a simul aneous he e ogeneous pho o-
Fen on mechanism in ol ing Fe3+/Fe2+ pai s, as he ollowing:
H2O2+ h → 2•OH(eq. 7)
˃Fe 3+ + e-→ ˃Fe2+ [O2] → ˃Fe 3+(eq. 8)
˃Fe2+ + H2O2+ H+→ ˃Fe3+ +•OH + H2O (eq. 9)
˃Fe2+ +•OH→ ˃Fe 3+ + OH-(eq. 10)
˃OH-+ h+→ •OH(eq. 11)
In he p esence o oxygen, e-oxida ion o ˃Fe 2+ occu s a a high a e be o e
de aching om he su ace (pho oco osion).Fo his eason, he pho oco osion
o i on oxide in pho oca aly ic eac ion (unde oxygen) is gene ally e y low wi h
his p ocess being hinde ed[35–37].
3.2.4 α-Fe2O3/Bi2WO6andα-Fe2O3/Bi2WO6-H2O2
In Fig. 7, we show he MO and Phenol con e sion plo s using he mixed α-
Fe2O3/Bi2WO6pho oca alys s bo h in he absence (Figu es 7A and 7B) o in he
p esence o hyd ogen pe oxide (Figu es 7C and 7D), unde UV and sun-like
i adia ion. I is possible o obse e ha using he mixedα-Fe2O3/Bi2WO6
pho oca alys s,MO emains almos una ec ed in solu ions unde illumina ion.
Wi h BW-Fe(5)-2 unde hese condi ions, he e is a sligh imp o emen o
Phenol con e sion, a e 120 min o illumina ion (Fig.7B), compa ed wi h ha
ob ained o MO (Figu e 7A). Howe e , he small con e sion alues obse ed
a e highe unde condi ions o UV-i adia ion han ha obse ed unde sun-like
illumina ion, being compa a i ely simila o he esul s shown in Figu es 4A and
4B, as is expec ed, since he ca alys used, BW-Fe(5)-2, is a physical mix u e o
95% Bi2WO6. Thus, we can conclude ha he mechanical mix u e o Bi2WO6
and α-Fe2O3, does no a ec he in insic pho oca aly ic beha io obse ed o
single ca alys s unde he same expe imen al condi ions.
Figu es 7C an 7D shows he a ia ion o he MO (Figu e 7C) and Phenol
(Figu e 7D) con e sion wi h ime when BW-Fe(5)-2 is usedas apho oca alys in
he co-p esence o H2O2, unde UV o sun-like illumina ion. A di e en end is
obse ed o bo h subs a es. Thus, o MO he simul aneous p esence o he
mixed ca alys s BW-Fe(5)-2 and H2O2has a ma ked in luence on he
pho oassis ed discolo a ion p ocess.This e ec is mo e ma ked unde
condi ions o UV-illumina ion o which almos 100%discolo a ionis
achie edin30 min, while high con e sion alues a e ob ained (ca. 85% a 60
min) unde sun-like i adia ion.These con e sion alues u n ou o be highe
han hose ob ained o he same subs a e (MO) in homogeneous phase wi h
ligh -H2O2(Figu e 4A), in he pho oca aly ic p ocesses using single
pho oca alys s (Figu es5A and 6A) and when he single pho oca alys s a e used
wi h H2O2(Figu es 5C and 6C).These esul s indica e a syne gis ic e ec in he
mix u e o he pho oca alys sBW-Fe(5)-2 when co-exis ing wi h H2O2unde
illumina ion, a leas o he subs a e used (MO), since his syne gis ic e ec is
no obse ed o Phenol (Figu e 7D).The mos s iking esul is ha he
syne gis ic e ec occu s e en in he isible o MO.
Using his sys em BW-Fe(5)-2 + H2O2, apa om he ela i ely high alues
ob ained o pho o-bleaching o MO, unde bo h UV and unde sun-like
illumina ion, ela i ely high alues o mine aliza ion deg ees o MO a e also
ob ained(see Table 1).
This ac could be explained by assuming a con ibu ion o pho osensi iza ion o
a dye moleculesuchas MO, asi has alsobeen obse ed when using Rhodamine
B [31].
As men ioned in he in oduc ion, due o high ecombina ion a e o cha ge
ca ie s in he single oxides, α-Fe2O3and Bi2WO6, ha e de eloped s a egies
ha lead o he sepa a ion o cha ge ca ie s, such as he de elopmen o
he e os uc u al cons uc ing o bo h ca alys s [28–30]. In hese sys ems, i has
been achie ed an imp o emen in he pho oca aly ic ac i i y compa ed wi h ha
ob ained wi h he singles ca alys s. The α-Fe2O3ac s as a hole-accep ing
semiconduc o and pho ogene a ed elec ons a e injec ed wi h high e iciency
om he conduc ion band o α-Fe2O3 o he conduc ion band o Bi2WO6. In ou
wo k we used a α-Fe2O3/ Bi2WO6composi e by a mechanical mixing p ocedu e
and in o de o achie e high pe o mance, he ex a H2O2was equi ed.
Howe e , he goal is he same in bo h cases, ha is, achie e e icien
sepa a ion o he cha ge ca ie s. In ou case, H2O2ac s as an elec on
accep o , hus gene a ing •OH adicals while he H2O can ac as holes accep o ,
gene a ing mo e •OH adicals. The ad an age, o ou me hod, can be ound in
he amoun o hyd oxyl adicals gene a ed in he p ocess, he eby inc easing
pho o-assis ed deg ada ion o he subs a es. Rega dless o his, in ou wo k we
ha e assessed he pho oca aly ic ac i i y wi h wo di e en subs a es, he MO
and Phenol and no wi h he Rhodamine B, since we ha e e idence ha he
e alua ion o pho oca aly ic ac i i y wi h Rhodamine B gene a es esul s ha a e
mo e spec acula , han when a anspa en subs a e, such as Phenol is used.
The e a e o he wo ks, ha achie e imp o ed pho o-Fen on mechanism by
inco po a ing he α-Fe2O3 o a g aphene oxide (GO) [38] o o Kaolin [39]. In
bo h cases, howe e , he imp o emen ob ained could be a ibu ed o he
syne ge ic e ec s o he adso p i e powe o GO o Kaolin and he hyd oxyl
adicals p oduced by he e ogeneous pho o-Fen on eac ions. In any case, in
hese wo ks, he e alua ion o he ac i i y is done also by using RhB.
Among he mixed ca alys BW-Fe(5)-2,in he p esence o H2O2, highe
con e sion alues o MOwe e displayed, bo h unde UV and sun-like
illumina ion. XPS analyses ha e been conduc ed on he p epa ed mixed oxides
sys em BW-Fe(5)-2, jus be o e and a e he pho o-assis ed Me hyl O ange
deg ada ion unde isible illumina ion in he p esence o hyd ogen pe oxide, by
eco e ing he ca alys powde om he eac ion sys em, a e a p olonged ime
o illumina ion (Expe imen epo ed in Figu e 7C).
Figu e 8 shows he esul s o XPS analysis o he o iginal sampleo α-
Fe2O3/Bi2WO6, in which only O(1s), W(4 ), Bi(4 ) and Fe(2p) peaks we e
de ec ed bu no peaks o esidual sodium we ede ec ed. The o e iew

spec ums o he mixed sys em demons a e ha Bi, W, O and Fe exis , u he
con i ming ha he sample was composed o Bi2WO6and Fe2O3. As shown in
Figu e 8A, he cha ac e is ic peak o O 1s a ound 530.1 eV could come om he
o e lapping con ibu ions o se e al componen s, being he iden i ica ion o he
subme ged peaks pe o med by Gaussian decon olu ion and cu e i ing: hese
peaks we e loca ed a 529.32 eV, 529.65 eV, 530.32 eV, 530.98 eV and 531.26
eV which co esponds o Fe-O, Bi-O, W-O la ice oxygen, chemiso bed wa e
and •OHhyd oxyl g oups espec i ely [40,41].
The peaks loca ed a 36.02 eV and 33.91 eV wi h a spin-o bi al sepa a ion o
2.11 eV, as shown in Figu e 8B, could be assigned o he +6 oxida ion s a e o
ungs en o he W 4 5/2 and W7/2 espec i ely [40].The XPS spec um o he Bi
4 egion displayed in Figu e 8C consis ing o wo cha ac e is ic peaks wi h
binding ene gies o 159.04 eV and 164.31 eV co espond o he signals om
double s o Bi 4 7/2 and Bi 4 5/2 in he i alen oxida ion s a e, espec i ely o
pu e Bi2WO6.
Figu e 8D p o ides XPS peaks o Fe elemen , exhibi ing wo indi idual
peaksin he Fe 2p egionloca ed a 710.42 eV and 723.75 eV, which can be
assigned o Fe 2p3/2 and Fe 2p1/2 peaks in α-Fe2O3phase, espec i ely [28]
con i ming he exis ence o Fe2O3phase on he mixed sys em which was no
de ec ed by XRD echnique. Besides wo sa elli e peaks o Fe 2p loca ed a
718.8 eV and 732.9 eV a e clea ly dis inguishable. The sa elli e peaks we e he
esul o he cha ge ans e sc eening a ibu ed o he p esence o Fe in 3+
oxida ion s a e [42,43].
Howe e , he spli ed peaks o Bi 4 7/2 and 4 5/2a ibu ed o Fe3+–O–Bi3+ linkage
a lowe ene gy alues o 157.5 eV and 162.8 eV, espec i ely[44],dono
appea , indica ing ha no in e ac ion be ween α-Fe2O3and Bi2WO6exis sin he
mixed sys em, as expec ed by he p epa a ion p ocedu e.
The used α-Fe2O3/Bi2WO6sample a e pho o-assis ed discolo a ion p ocess o
Me hyl O ange unde isible illumina ion by using H2O2, was eco e ed and,
once d ied, was subjec ed o a XPS analysiswi h he esul sbeing epo ed in
Figu e 9. I is in e es ing o no e ha , in he egion o he O(1s)peak, wo dis inc
peaks appea cen e ed a ound 526.8 eV and 530.0 eV espec i ely. By a
decon olu ion analysis and i ing, se e al subme ged peaks
canbedis inguished. A clea peak cen e ed a 526.58 eV can be a ibu ed o a
pe oxide species s abilized in he sys em whichcanno be associa ed o Na2O o
Na2O2[45]since sodium was no de ec ed by XPS. No changes we e obse ed
in he oxida ion s a es o W and Bi espec i ely. Howe e , o his sample, Fe 2p
pho oelec on peaks appea ed a ound 710.6 eV and 724.0 eV wi h sa elli e
peaks. The peaks o Fe 2p1/2 and Fe 2p3/2 le els a 724.0 eV and 710.6 eV,
espec i ely, sepa a ed 13.4 eV, e i ied he p esence o Fe in 3+ oxida ion
s a e on he eco e ed α-Fe2O3/Bi2WO6ca alys s. Howe e , as shown in Figu e
9D, a shoulde a ound 706.0 eV, no p esen on he o iginal spec a (Figu e 8D)
is obse ed. This could be asc ibed o he ans o ma ion o Fe(3+) o Fe(2+)
a e he e ogeneous pho o-Fen on eac ion [46]. This inding, oge he wi h he
p esence o O(1s) peak associa ed o pe oxide species, leadus o pos ula e he
p esence o i on(II) pe oxide,Fe(O2),s abilized in he mixed sys em.
The in e ac ion o H2O2wi h i on oxide hasno been ex ensi elys udied, and
he e a e s udies ha sugges he o ma ion o Fe(O2) by compu e
calcula ions[47,48]; a ecen s udy [49]concluded ha he da k Fen on p ocess
in ol ing Fe(II) + H2O2consis s o wo egimes, a as e ous one ha is
igge ed by he eac ion o Fe2+ + H2O2and a slow e ic one ha is domina ed
by he educ ion o Fe(III).Howe e , s abiliza ion o pe oxide species as η2Fe(II)
-O22- seems unlikely, due o he ins abili y o he pe oxide species.
O he p oposals could be made, based on esul s published in he li e a u e
[50].Pigna ello e al. [51], e idenced he o ma ion o an addi ional oxidan in he
pho oassis ed Fen on eac ion. The esul s sugges he pa icipa ion o a high-
alen oxoi on complex ( e yl) in addi ion o •OHin o ganic compound
oxida ions.They e idenced ha hyd ogen pe oxide o ms a complex wi h i on,
(Fe3+-OOH)2+[K= 1.15 x10-2], ha abso bs in he isible egion and could be he
p ecu so o he p oposed e yl complex[51].
I he o ma ion o (Fe3+-OOH)2+species is assumed hen an inc easedpho o-
con e sion p ocess is likely o occu , in bo h he UV and isible, as seen in he
esul s p esen ed in Figu es 7C and 7D.
3.2.5 Mix u es o Me hyl O ange and Phenol
Finally, we ha e s udied he simul aneous deg ada ion o MO and Phenol bo h
ina mixed solu ion, using he mixed oxide pho oca alys BW-Fe(5)-2, in he
p esence o H2O2unde sun-like illumina ion condi ions. Figu e 10 epo s he
a ia ion in he concen a ion o MO and Phenol in he mix u e MO/Phenol wi h
ime unde sun-like illumina ion, using he BW-Fe(5)-2 ca alys in he p esence
o H2O2. As no ed in Fig.10, i is possible o obse e ha in mixed solu ions o
bo h subs a es, he e is an inc ease in Phenol deg ada ion in luenced by he
simul aneous p esence o MO, while he p o ile o he con e sion plo o MO is
p ac ically he same as ha ob ained o he single subs a e unde he same
expe imen al condi ions (Fig.7C). These esul s indica e ha ega dless o he
syne gis ic e ec obse ed in he physical mix u e o he wo ma e ials s udied,
BW-Fe(5)-2 in he co-p esence o H2O2, a ma ked in luence o he simul aneous
p esence o MO o e he Phenol deg ada ion, is also obse ed.
I is obse ed ha his mixed sys em, BW-Fe(5)-2, is capable o comple ely
makingMOdisappea in he mix u e, a e 120 min unde sun-like illumina ion,
leading oa esidual amoun o TOC a he inal pe iod, indica ing a pe cen age
o 50% o mine aliza ion. F om one poin o iew, ha ing a pho osensi izing
molecule, suchas MO, has p o ed o ha e some e ec in he pho odeg ada ion
o a non-pho osensi izing one, like Phenol, since by using hese condi ions, o
single phenol a con e sion alue o ca. 30% was obse ed whe eas a alue o
ca. 60% is eached in he co-p esence o MO.
Conclusions
Mixed oxides, α-Fe2O3/Bi2WO6, we e p epa ed using a mechanical mixing
p ocedu e by adding he co esponding amoun o a p epa ed α-Fe2O3 o he
Bi2WO6p e iously ob ained by hyd o he mal me hod, he o me ob ainedby
he mal decomposi ion o Fe(NO3).9H2O.
Despi e exhibi ing po en ial op ical abso p ion capaci y in he UV- is egion,
howe e , he wosingle ca alys s showed poo pho oca aly ic ac i i y, bo h in he
UV and in he isible, possibly due o high ecombina ion a e o ca ie ’s pho o-
gene a ed cha ges. Thep epa ed oxide α-Fe2O3shows a ema kable da k
adso p ion capabili y o MO, howe e unde illumina ion condi ions i displayed
a pho odeso p ion p ocess which is accompanied by a simul aneous pho o-
Figu e 1. X- ay di ac ion pa e ns (XRD) o p is ine α-Fe2O3, Bi2WO6and mixed BW-
Fe(5)-2 samples

Figu e 2.Di used e lec ance spec a (DRS) o p is ine α-Fe2O3, Bi2WO6and mixed
BW-Fe(5)-2 samples.
Figu e 3.SEM images o p is ine Bi2WO6(A and B), p is ine α-Fe2O3(C), and mixed
BW-Fe(5)-2 samples (D).
Figu e 4. Con e sion plo s o pho ochemical discolo a ion o Me hyl O ange (A) and
pho ochemical disappea ance o Phenol (B), wi h only he p esence o H2O2unde UV
o sun-like illumina ion.
A
B
Figu e 5. Con e sion plo s o pho ochemical discolo a ion o Me hyl O ange and
Phenol disappea ance, unde UV o sun-like illumina ion: wi h only he p esence o
Bi2WO6pho oca alys (A and B) o wi h he co-p esence o bo h, Bi2WO6and H2O2(C
and D).
A
B
C
D
Figu e 6. Con e sion plo s o pho ochemical discolo a ion o Me hyl O ange and
Phenol disappea ance, unde UV o sun-like illumina ion: wi h only he p esence o α-
Fe2O3pho oca alys (A and B) o wi h he co-p esence o bo h, α-Fe2O3and H2O2(C
and D).
A
B
C
D

Figu e 7.Con e sion plo s o pho ochemical discolo a ion o Me hyl O ange and
Phenol disappea ance, unde UV o sun-like illumina ion: wi h only he p esence o
mixed BW-Fe(5)-2 pho oca alys s (A and B) o wi h he co-p esence o BW-Fe(5)-2
pho oca alys s and H2O2(C and D).
A
B
C
D
Figu e 8. XPS su ace spec a o he as-p epa ed mixed BW-Fe(5)-2 pho oca alys s.
Figu e 9. XPS su ace spec a o he eco e edBW-Fe(5)-2 sample a e being used
on he pho o-assis ed discolo a ion p ocess o Me hyl O ange unde isible
illumina ion by using H2O2.
Figu e 10. Me hyl O ange and Phenol con e sion plo s in mixed solu ion wi h
BW-Fe(5)-2 unde sun-like illumina ion, in he p esence o H2O2