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Use of nanofiltration membrane technology for ceramic industry wastewater treatment

Abstract

A study has been undertaken of an advanced wastewater treatment approach using polymer nanofiltration membranes, in an attempt to obtain water of sufficient quality to allow it to be reused in the same production process or, alternatively, to be discharged without any problems. The study has initially focused on the removal of organic matter (reduction of COD) and the most representative ions present in the wastewater, such as Na+ , Mg2+, Cl- , and SO4 2- . In a first part of the study, with a view to optimising the experimental phase, a simulation has been performed of the nanofiltration process using the NanoFlux software. Among other things, the simulation allows the most suitable membranes to be selected as a function of the permeate flow rate and desired level of retention in the substances to be removed. The subsequent experimentation was carried out in a laboratory tangential filtration system that works with flat membranes. It was found that retention values of about 90% were obtained for the studied substances, with a good permeate flow rate, using low operating pressures. These results demonstrate the feasibility of the studied technology and its potential as a treatment for improving ceramic industry wastewater quality

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Use of nanofiltration membrane technology for ceramic industry wastewater treatment

Author: Moliner Salvador, R.; Deratani, A.; Palmeri, J.; Sánchez-Vilches, Enrique
Publisher: Sociedad Española de Cerámica y Vidrio
Year: 2012
Source: http://repositori.uji.es/bitstreams/8091c4cc-e5a6-4dc3-8295-ebb559a1aade/download
103
Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
BOLETIN DE LA SOCIEDAD ESPAÑOLA DE
ARTICULO
Ce ámica y Vid io
Use o nano il a ion memb ane echnology o ce amic indus y
was ewa e ea men
R. MOLINER-SaLVaDOR (1), a. DERaTaNI (2), J. PaLMERI (3), E. SáNCHEz (1)
(1) Ins i u o de Tecnología Ce ámica. Asociación de In es igación de las Indus ias Ce ámicas. Uni e si a Jaume I. Cas ellón. Spain
(2) Ins i u Eu opéen des Memb anes, UMR CNRS-ENSCM-Uni e si é Mon pellie 2, 34095 Mon pellie , F ance
(3) Labo a oi e de Physique Theo ique, UMR CNRS-Uni e si é Paul Saba ie , 31062 Toulouse, F ance
A s udy has been unde aken o an ad anced was ewa e ea men app oach using polyme nano il a ion memb anes, in
an a emp o ob ain wa e o su icien quali y o allow i o be eused in he same p oduc ion p ocess o , al e na i ely, o be
discha ged wi hou any p oblems. The s udy has ini ially ocused on he emo al o o ganic ma e ( educ ion o COD) and
he mos ep esen a i e ions p esen in he was ewa e , such as Na
+
, Mg
2+
, Cl
-
, and SO
4
2-
.
In a i s pa o he s udy, wi h a iew o op imising he expe imen al phase, a simula ion has been pe o med o he
nano il a ion p ocess using he NanoFlux so wa e. Among o he hings, he simula ion allows he mos sui able memb anes
o be selec ed as a unc ion o he pe mea e low a e and desi ed le el o e en ion in he subs ances o be emo ed. The
subsequen expe imen a ion was ca ied ou in a labo a o y angen ial il a ion sys em ha wo ks wi h la memb anes.
I was ound ha e en ion alues o abou 90% we e ob ained o he s udied subs ances, wi h a good pe mea e low a e,
using low ope a ing p essu es. These esul s demons a e he easibili y o he s udied echnology and i s po en ial as a
ea men o imp o ing ce amic indus y was ewa e quali y.
Key wo ds: Nano il a ion, Memb ane, Was ewa e , Ce amic Tiles Indus y, Red/Whi e Ce amics
Uso de la ecnología de nano il ación a a és de memb anas pa a el a amien o de aguas esiduales de la indus ia
ce ámica
Es e es udio ha sido emp endido con el in de ace ca la nano il ación a a és de memb anas polimé icas al a amien o de
las aguas esiduales indus iales de la indus ia ce ámica, espe ando ob ene un agua con la su icien e calidad como pa a se
eu ilizada en el p opio p oceso p oduc i o o, al e na i amen e, pode e e la. El es udio se ha cen ado en la eliminación
de ma e ia o gánica ( educción de D.Q.O) y algunos iones p esen es en las aguas esiduales, ales como Na
+
, Mg
2+
, Cl
-
y SO
4
2-
.
En p ime luga , se ha ealizado una simulación del p oceso de nano il ación usando el so wa e NanoFlux. En e o as
cosas, la simulación pe mi e selecciona las memb anas más ap opiadas en unción del caudal de pe meado ob enido y
en unción del ni el de e ención de la sus ancia que se desea elimina . En una segunda pa e, se ealiza on los ensayos
expe imen ales en un sis ema de labo a o io de il ación angencial que abaja con memb anas planas.
La e ención ob enida pa a las sus ancias es udiadas es de ap oximadamen e el 90%. Todo ello, con un buen caudal de
pe meado y usando bajas p esiones de abajo. Es os esul ados demues an la iabilidad de la ecnología y su po encial
como a amien o pa a mejo a la calidad de las aguas esiduales de es a indus ia.
Palab as Cla e: Nano il ación, Memb ana, Aguas Residuales, Baldosas Ce ámicas, Ce ámica Roja/Blanca.
1. INTRODUCTION
Wa e managemen has become an inc easingly c i ical
issue in mos adi ional indus ial sec o s, owing o he la ge
quan i ies o was ewa e hey p oduce. In he case o he
ce amic ile indus y, mos o he was ewa e a ises in he
washing ope a ions o he acili ies used o he p epa a ion
and applica ion o glazes and o he coa ings. In addi ion, a
conside able amoun o g oundwa e is used as he esh wa e
sou ce o glaze and o he coa ings p epa a ion. Howe e as
he g oundwa e esou ce becomes mo e and mo e limi ed,
ce amic indus y has o ind solu ion o lowe i s g oundwa e
bole ín de la Sociedad Española de Ce ámica y Vid io
Vol 51, 2, 103-110, Ma zo-ab il 2012 ISSN 0366-3175. eISSN 2173-0431.
doi: 10.3989/cy .152012
consump ion. One possibili y is, o ins ance, o use ecycled
wa e in glazing ope a ions.
The composi ion o hese ce amic indus y was ewa e s
a ies widely and may include suspended solids and
elec oly es o e y di e en na u e, as well as o ganic
subs ances ha mos ly come om he addi i es used in
deco a ing he iles. Howe e , he ea men echniques ha
a e cu en ly used (gene ally physico-chemical ea men s)
a e no en i ely e ec i e, in pa icula wi h ega d o non-
biodeg adable o ganic compounds ha inc ease he wa e
Es e abajo ha sido p esen ado como comunicación o al, as su e aluación po el Comi é Cien í ico,
en el XII Fo o Global del Recub imien o Ce ámico. QUALICER (13 y 14 eb e o 2012. Cas ellón. España).
104 Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
R. MOLINER-SALVADOR, A. DERATANI, J. PALMERI, E. SÁNCHEz
COD, ce ain ions such as alkaline and alkaline-ea h ca ions,
bo on compounds, chlo ides, sulpha es, e c. This inadequa e
was ewa e ea men makes i impossible o euse his wa e
in he same p oduc ion p ocess and may e en impede wa e
discha ge. As a esul , his wa e needs ex e nal handling o
addi ional ea men , en ailing high economic cos s and/o
en i onmen al impac .
Memb ane echnology is an ad anced me hod o wa e
ea men . I has been demons a ed ha ions and molecules
can be selec i ely emo ed om pollu ed wa e s using
memb ane p ocesses. Selec ion o he app op ia e memb ane
sui able o add ess he desi ed sepa a ion is de e mined by
he eed composi ion o wa e o be ea ed and he objec i e
o pu i ica ion o be eached, as well. Nano il a ion (NF),
which has ecen ly been de eloped, p esen s signi ican
ad an ages on compa ing wi h o he memb ane p ocesses.
NF p ocess allows an almos comple e emo al o mul i alen
ions and o ela i ely small o ganic compounds, and a good
ejec ion o mono alen ions depending on he memb ane
and he ope a ing condi ions while i equi es lowe ope a ing
p essu e han e e se osmosis (RO).
In his wo k i is p oposed o make a p elimina y e alua ion
o he applica ion o nano il a ion echnique o was ewa e s
om he ce amic ile indus y wi h a iew o emo ing
o ganic ma e ( educing COD) as well as dissol ed sal s in
o de o enhance he euse o ea ed wa e in he ce amic
indus y. Bo on compounds we e no included in he s udy
because he was ewa e con aining hese needs o unde go
a p e- ea men . E icien pu i ica ion has o dec ease he
o ganic pollu ion and he o al dissol ed sal s (TDS) unde
a ce ain limi ha can be es ima ed o he mos commonly
cleaning uses o be abou 50 mg O2/l o COD and 500 mg/l
o TDS. This objec i e can be, in p inciple, eadily ob ained
using a NF s age.
2. METHODOLOGY
2.1 Memb ane p ocesses in wa e ea men
Pu i ica ion o wa e by ea men s using memb ane
ma e ials began o be impo an in 60’s because o he good
pe o mances ha o e ed syn he ic memb anes. Memb ane
sepa a ion p ocess has he ollowing ad an ages: cos ly
e icien , en i onmen ally benign and clean echnology since
no addi ional chemicals a e needed, easy o ope a e and
no much sensi i e o composi ion a iabili y, allowing he
p oduc ion o high quali y wa e . Ne e heless, i has been in
he las yea s when he memb ane ea men has begun o be
applied in he was ewa e pu i ica ion. The de elopmen o
memb ane echnology o new applica ions has been he esul
o nume ous ad ances in he ield o memb anes elabo a ion.
A memb ane can be de ined as a selec i e ba ie ha
sepa a es wo phases. F om his de ini ion i appea s ha
anspo o species om ups eam o downs eam is
es ic ed in a selec i e manne due o di e ences in physical
and/o chemical p ope ies be ween he memb ane and he
pe mea ing species (1). Dissol ed solids and compounds in he
eed phase can hen be o ally o pa ially e ained in e en a e,
whe eas pe mea e will be ee o compounds ejec ed by he
memb ane. Shape, size and cha ge a e he main cha ac e is ics
ha de e mine memb ane ejec ion. Di e en d i ing o ces
such as p essu e, elec ical ield, and concen a ion g adien
can o igina e he anspo h ough he memb anes, he
p essu e d i en p ocesses being he mos de eloped in he
case o wa e memb ane ea men . The ollowing sec ion
will desc ibe he di e en ypes o p essu e d i en memb ane
p ocesses commonly used in wa e ea men .
2.1.1 CLASSIFICATION OF MEMBRANE PROCESSES IN
WATER TREATMENT
As p e iously ou lined, memb ane can ac as a sie ing
ba ie . The selec i e anspo ac oss he memb ane is hen
mainly go e ned om he a io be ween he size o dissol ed
species and ha o he memb ane po es. The ollowing
classi ica ion in memb ane p ocesses can a ise depending
on he memb ane po e adius size ( p): mic o il a ion,
ul a il a ion, nano il a ion and e e se osmosis. (Fig 1)
Mic o il a ion (MF) memb anes ha e he p anging
om 0.1 o 10 µm and he la ges memb ane pe meabili y.
In MF p ocess he applied p essu e is low ( om 0.2 o 1 ba )
and he componen s a e e ained by a sie ing mechanism.
Consequen ly only componen s wi h a size highe han he
memb ane po e size a e e ained. MF memb anes ypically
ejec suspended solids, la ge pa icles, colloids and some
mic o o ganisms as bac e ia. MF memb anes a e he a mos
widely used memb ane p ocess wi h he main applica ions o
cla i ica ion, disin ec ion and as an e icien p e- ea men o
u he memb ane ea men s eps.
Ul a il a ion (UF) memb anes ha e smalle p ( om 2 o
100 nm) and lowe pe meabili y han MF memb anes. This
ea u e implies ha UF p ocess equi es highe ope a ing
p essu es ( om 0.5 o 5 ba ) han MF p ocess. In his case,
sie ing mechanisms a e also mainly in ol ed o ejec ing he
eed componen s. These memb anes can e ain small bac e ia,
i uses and soluble mac omolecules such as p o eins.
NF p ocess (NF) is an in e media e echnique be ween
UF and e e se osmosis (RO) ha has been mo e ecen ly
de eloped. NF memb anes ha e p smalle han 2 nm. In
his case in e ac ions in addi ion o s e ic hind ance ake
place due o he small size o memb ane po es. Thus he
anspo mechanism is mainly desc ibed by sie ing and
elec ic (Donnan exclusion) e ec s among o he s. The e is
equilib ium be ween he cha ged memb ane and he solu ion.
Fo his eason a lo o ionic species a e ejec ed, e en species
wi h size smalle han ha o memb ane p.
Finally, he RO memb anes consis in a dense ba ie
wi hou p ede ined po es. The anspo mechanism
is he e o e comple ely di e en and is belie ed o occu
acco ding o a solu ion-di usion mechanism (2-3). I esul s
ha pe meabili y is much lowe in his case han o he
abo e men ioned memb anes. On he o he hand, ejec ion o
he cha ged solu es con ained in he eed solu ion is almos
comple e. I should be no ed ha RO usually equi es high
p essu es (up o 120 ba ) depending o he osmo ic p essu e
o he eed solu ion ha makes his echnique qui e ene gy
consuming.
2.1.2 NANOFILTRATION
As seen in Fig. 1, NF is a echnique o sepa a ion by
memb anes loca ed be ween RO and UF. Ini ially i was
included wi h RO bu oday i is ega ded as a di e en
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USE OF NANOFILTRATION MEMBRANE TECHNOLOGY FOR CERAMIC INDUSTRY WASTEWATER TREATMENT
echnique conside ing ha he anspo in ol es an ac ually
di e en mechanism as ou lined be o e.
NF is mainly cha ac e ized by a anspo mechanism
based no only on s e ic hind ance bu also acco ding o he
solu e cha ge wi h he ollowing implica ions:
• Neu al solu es a e ejec ed acco ding o he sie ing
e ec due o he memb ane po e size
• A selec i e sepa a ion akes place be ween eadily
ejec ed mul i alen ions and pa ially ejec ed
mono alen ions
• A pa o cha ged species a e anspo ed ac oss he
memb ane dec easing he osmo ic p essu e.
• The ope a ing p essu es a e lowe (3 o 20 ba s)
han hose used in RO and highe pe mea e a e a e
ob ained wi h his echnique leading o a mo e ene gy
e iciency compa ed o RO.
This echnique can be applied in a lo o sec o s such
as bio echnology and ood indus y o ex ac ion and
pu i ica ion o aluable low molecula weigh compounds,
wa e and was ewa e ea men o he d inking wa e
p oduc ion and he en i onmen al p o ec ion (4).
2.2 NanoFlux
NanoFlux (5,6) is a compu e simula ion p og am
de eloped in he Eu opean Ins i u e o Memb anes in
Mon pellie (F ance) o model solu e anspo in he NF ange
(and in some cases, loose RO and igh UF). I can be used o
cha ac e ize NF memb anes and also p edic hei pe o mance
is-à- is complex mix u es o neu al molecules and ions. This
p og am allows one o calcula e, s a ing om s anda d eed
inpu da a, all he necessa y NF p ocess ou pu (ionic and
molecula ejec ion, o passages, luxes,…) om he le el
o a single memb ane elemen up o ha o mul i-module/
mul i-s age plan s. I is possible o ob ain quick and eliable
simula ion esul s hanks o bo h he powe ul and obus
compu a ional algo i hms inco po a ed in o he p og am and
he in e nal NanoFlux da abase ha con ains he p incipal
comme cial memb anes. NanoFlux is also easy o use, hanks
o i s e gonomic g aphical use in e ace and has been es ed
and alida ed using eal case s udies (5-7). Pe iodic addi ions
a e made and up-da es o he NanoFlux da abase pe o med
in o de o ollow echnical and ma ke e olu ions. This
modeling p og am is hus a powe ul aid in decision-making
and inno a ion, when i comes o economically choosing he
igh memb ane and op imizing nano il a ion p ocesses. I
can also be used o minimize signi ican ly di icul and cos ly
pilo s udies, he eby educing he o al cos and ime needed
o choose he app op ia e memb ane and o scale-up and
ope a e NF plan s.
The modeling me hod used in NanoFlux consis s in
i s es ima ing he po e size om he ejec ion o model
neu al solu es (5,6). A memb ane-sal cha ac e iza ion s ep
by s udying he ejec ion o a limi ed numbe o simple
sal s (NaCl, MgSO4, Na2SO4, CaCl2) is o be subsequen ly
ca ied ou . The expe imen al esul s o hese 1:1, 2:2, 1:2,
2:1 ( ) sal s a e analyzed using NanoFlux ia a
nume ical i ing p ocedu e in o de o de e mine he op imal
alues o he wo pa ame e s (e ec i e memb ane cha ge
densi y and hickness) ha cha ac e ize he memb ane/
sal pai . Theo e ical ion ejec ion p edic ions o elec oly e
solu ions a e ob ained by sol ing nume ically he “Hinde ed
T anspo ” Ex ended Ne ns -Planck ion lux equa ions. The
bes i pa ame e alues, which minimize he di e ence
be ween he expe imen al and heo e ical ejec ions, a y as
a unc ion o he sal concen a ion and pH o he eed. This
analysis allows us o c ea e he in e nal NanoFlux da abase.
The e ec i e memb ane cha ge and e ec i e hickness o ion
mix u es a e hen de e mined as a unc ion o eed solu ion
pH, ionic s eng h and composi ion using he single sal
da abase combined wi h an in e pola ion and weigh ing
Fig. 1 Classi ica ion o memb ane ea men s
106 Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
R. MOLINER-SALVADOR, A. DERATANI, J. PALMERI, E. SÁNCHEz
scheme. The ejec ion and solu ion lux o complex mul i-
elec oly e mix u es can be well p edic ed using he in e nal
single sal da abase (5,6). NanoFlux can he e o e be a he
basis o a combined expe imen al and heo e ical me hod o
cha ac e izing, simula ing, and op imizing he pe o mance o
cha ged nano il e s.
NanoFlux a emp s o ill in a gap in me hods o p edic ing
and op imizing NF pe o mance ha has a isen due o he
complexi y o he undamen al ion anspo p ocesses and has
mos likely slowed he widesp ead indus ial de elopmen o
NF.
2.3 Me hod
2.3.1. APPARATUS
The il a ion pilo plan (Fig. 2) used o NF expe imen s
consis s o a Sepa CF II labscale 316 SS cell sys em [10], a
eed ank [3] wi h a s ainless s eel imme sed coil [5] and a
olume ic pump [8] (ca pump 231, cons an low 9 L/min).
The closed loop o he eed solu ion is made o esis ing ubing
o high empe a u e (up o 60°C) and p essu e (up o 20 ba ).
The eed solu ion is hea ed o cooled in he 30 li es
eed ank by a ci cula ing he mal ba h [1] (F igi he m-10
P- Selec a) by means o he imme ged coil. The empe a u e
eed ank is measu ed and con olled by an ex e nal PT100
P osenso p obe [4] imme ged in he eed solu ion. The
e en a e empe a u e when i ci cula es back o he eed ank
is also measu ed. The p essu e o he eed solu ion and he
e en a e, modi ied by he al e [11], a e gi en by p essu e
gauges [9]. The pe mea e mass is measu ed by a balance [12]
(Sa o ius CP323S) a s eady s a e and he mass lux calcula ed
is egis e ed in a compu e [13] ia an RS232 ou pu .
2.3.2. MEMBRANES
In his s udy DOW FILMTEC memb anes ha e been used.
These memb anes a e la and ha e an e ec i e su ace a ea
o 133 cm2. NanoFlux p edic ion and p elimina y es s showed
ha he NF-90 memb ane was he mos sui able o ou
applica ion. The ob ained da a we e hen compa ed o hose
ob ained o ano he memb ane NF-200. Speci ica ions gi en
by he manu ac u e o hese wo memb anes a e ga he ed in
he able I.
1- Ci cula ing he mal ba h, 2- Bill-pos e empe a u e, 3- Feed ank, 4- Tempe a u e p obe, 5- Coil, 6- Pu ge, 7- Th ee-way al e, 8- High-p essu e
pump, 9- Manome e , 10- Sepa CF II Cell (Osmonics), 11- P essu e Con ol Val e, 12- Balance, 13- Pe sonal compu e
Fig. 2. Schema ic diag am o he NF pilo .
Table I. speCI ICaTIons o The n memb anes gI en by The manu aCTu e
Memb ane Pe mea e Flow Ra e
(L/(h m2 ba )
S abilized Sal
Rejec ion
(%)
NF-90 8,68 > 97
NF-200 5,99 97
No e: Pe mea e low and sal ejec ion based on he ollowing es condi ions:
2000 ppm MgSO4, 25°C and 15 % eco e y.
Pe mea e lows o indi idual elemen s may a y by -15 %/+50 %
2.3.3 EXPERIMENTAL PROCEDURE
The app oach used consis s o wo s ages:
• P edic ion o he memb ane pe o mances o NF o
he s udied was ewa e (simpli ied composi ion) using
NanoFlux. This s age allowed us o selec he mo e
app op ia e memb ane and ope a ing condi ions o he
second s age.
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USE OF NANOFILTRATION MEMBRANE TECHNOLOGY FOR CERAMIC INDUSTRY WASTEWATER TREATMENT
• Expe imen al alida ion using he selec ed memb ane
and ope a ing condi ions o he ea men o eal
was ewa e s.
The expe imen al p ocedu e ollowed du ing he es o
he memb anes included he ollowing s eps:
• Memb ane condi ioning: be o e using new memb anes a
condi ioning s ep mus be made o elimina e p ese a ion
p oduc s and o compac he memb ane. Memb ane is
placed in he memb ane cell and pu e wa e is ci cula ed
h ough he memb ane o 1 hou . Applied empe a u e
and p essu e (30 ºC and 17.5 ba ) we e highe han hose
in he no mal ope a ing condi ions. This s ep was only
ca ied ou once when he memb ane is new.
• Pu e wa e pe meabili y: a e he condi ioning s ep and a e
e e y es , pu e wa e pe meabili y was de e mined o
ensu e abou he memb ane s abili y and in eg i y. These
measu emen s we e pe o med using demine alised wa e .
• Flow and ejec ion measu emen s o se e al eed
was ewa e s ( ixed ope a ing condi ions): when he
desi ed empe a u e was eached, he eed was ci cula ed
and he p essu e inc eased s ep by s ep ill he desi ed
p essu e was eached. The eed solu ion ci cula es a
cons an angen ial eloci y (1,23 m/s), which allows o
neglec concen a ion pola iza ion e ec s in memb ane
su ace. A e a ound 5 min o ci cula ion, i was
assumed ha he s eady s a e was eached. The pe mea e
ac ion was e-ci cula ed in o he eed o keep he
solu ion concen a ion cons an . The pe mea e lux was
de e mined om mass measu emen s. A sample was hen
collec ed o calcula e ejec ion.
• Rejec ion calcula ion: collec ed samples in he p e ious
s ep we e analysed and esul s we e compa ed wi h he
eed samples analyses. Then ejec ion (%) we e calcula ed
acco ding o he ollowing equa ion:
whe e and a e he concen a ion o
pe mea e and eed espec i ely.
2.3.4 ANALYSES
Conduc i i y and pH o solu ions we e de e mined using a
conduc ime e JF 340 WTW and a pHme e PHN 81 Tacussel,
espec i ely. Me hods and equipmen used o analyze he
di e en pa ame e s and species in he was ewa e s a e lis ed
in able II:
3. RESULTS AND DISCUSSION
3.1 Ce amic indus y was ewa e composi ion
Was ewa e s can be analysed using di e en pa ame e s
like pH, conduc i i y and chemical oxygen demand (COD),
hese wo pa ame e s being indica i e o o al dissol ed
sal s (TDS) and o he o ganic pollu ion, espec i ely. The
hand ope a ed cleaning usually made in ce amic indus y
and he la ge ange o p oduc s en ail a wide a iabili y in
composi ion. Table III shows he mean a e age alues o he
pa ame e s desc ibing he was ewa e composi ion (8): pH,
conduc i i y, he mo e abundan ions and TDS and COD.
Table II. meThods and equIpmenT o wasTewaTe analysIs
Pa ame e Me hod Equipmen
COD UNE 77-004/89 -
B Azome ine-H me hod by UV-VIS spec opho ome y UV-160A Shimadzu
SO4
2- and Cl-Ionic ch oma og aphy ICS-100 Dionex
Na+, K+, Mg2+ and Ca2+ A omic abso p ion spec opho ome y UNE 77-056 1100B Pe kin Elme
Table III. Ce amIC IndusT y wasTewaTe ComposITIon
Pa ame e Va ia ion in e al
pH 7-9
Conduc i i y (µS/cm) 2000-5000
Chlo ides (mg /L) 100-1100
Sulpha es (mg /L) 100-1000
Calcium (mg /L) 50-500
Magnesium (mg /L) 10-100
Sodium (mg /L) 50-750
Bo on (mg /L) 1-75
TDS (mg/L) 300-3700
COD (mg O2/L) 100-1300
3.2 NanoFlux p edic ion
As abo e-men ioned NanoFlux compu e simula ion
p og amme allows us o p edic he pe o mances o NF
memb anes o pe mea ion o neu al and cha ged species.
Model solu ions con aining wo neu al solu es o di e en
molecula size we e chosen o mimicking he emo al o
o ganic ma e om he was ewa e s. As an example, Table
IV gi es he p edic ed ejec ion da a o pe mea ion o wo
neu al species (e hyl alcohol and poly(e hyleneglycol), PEG-
400) using wo NF memb anes (NF-90 and NF-200). I should
be no ed ha PEG- de i a i es a e compounds o in e es in
he ce amic indus y since hey a e used in he deco a ion
s age o he ile manu ac u ing p ocess. As i can be seen

108 Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
R. MOLINER-SALVADOR, A. DERATANI, J. PALMERI, E. SÁNCHEz
NanoFlux p edic s ha PEG 400 is 100 % ejec ed by bo h
memb anes whe eas a small molecule as e hyl alcohol is mo e
signi ican ly ejec ed by he NF-90 memb ane
In he same way, p edic ion o memb ane pe o mances
can be ob ained o pe mea ion o cha ged species. F om he
able III, i appea s ha a mix u e o he anions Cl- and SO4
2-
and he ca ions Na+ and Mg2+ can gi e a good model solu ion
o he s udied was ewa e s. Table V p esen s simula ion da a
ob ained o he wo same memb anes (NF-90 and NF-200)
o a solu ion con aining an equimola mix u e o NaCl and
MgSO4 wi h a o al sal concen a ion o 0.03M (2.69 g/l).
Table I . nano lux p edICTIon o pe meaTIon o Two neuT al speCIes (eThyl alCohol and peg-400) on n -90 and n -200 memb anes.
Memb ane P essu e
(ba ) Flux
(L/h·m2)Rejec ed species Mola mass (g/mol) Rejec ion
(%)
NF-90
< 5 - PEG-400 400 100
5 23 E hyl alcohol 46 80
NF-200
< 5 - PEG-400 400 100
5 25 E hyl alcohol 46 62
Table V. NaNo lux p edicTioN o aN equimola mixTu e o NaCl aNd MgSO4 wiTh a ToTal salT coNceNT aTioN o 0.03m (2,69 g/L)
Memb ane P essu e
(ba ) Flux
(L/h·m2)Ions Rejec ion
(%)
NF-90
5 23
Na+90
Cl-87
Mg2+ 97
SO4
2- 100
11 60
Na+90
Cl-90
Mg2+ 100
SO4
2- 100
NF-200
5 27
Na+47
Cl-60
Mg2+ 85
SO4
2- 98
11 75
Na+72
Cl-65
Mg2+ 94
SO4
2- 100
Again he memb ane NF-90 shows he be e pe o mances
in ejec ing he conside ed ions e en a ela i ely low ope a ing
p essu e (5 ba ) and wi h simila pe mea e lux. I was hen
decided o alida e he simula ion by pe o ming pe mea ion
o eal was ewa e s on NF-90.
3.3 Resul s wi h eal was ewa e s o he ce amic indus y
The NF ea men was ca ied ou a low p essu e wi h
was ewa e samples collec ed in wo di e en companies
a e he physico-chemical ea men s age. The ope a ing
condi ions o bo h samples a e summa ized in able VI. (*)
109
Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
USE OF NANOFILTRATION MEMBRANE TECHNOLOGY FOR CERAMIC INDUSTRY WASTEWATER TREATMENT
Table VII ga he s he pa ame e da a ob ained o he
wo samples be o e and a e he NF pu i ica ion on NF-90
memb ane. These esul s show a educ ion o mo e han 90
% o he o al dissol ed sal s (TDS). As expec ed, mul i alen
ions (SO4
2-, Mg2+ and Ca2+) a e almos o ally ejec ed du ing
he NF pe mea ion. On he o he hand, he mono alen
ones (Cl-, Na+ and K+) a e abou 90 % ejec ed by he NF-90
memb ane as p edic ed by he NanoFlux simula ion so wa e.
When conside ing he COD pa ame e , i appea s ha he
NF pe mea ion pe mi s an e icien emo al o he o ganic
pollu ion since his pa ame e gi es alues lowe han 50
mg O2/l. This e ec is pa icula ly s iking in he case o he
highe loaded solu ion (was ewa e 1) wi h a COD educ ion
o mo e han 90%.
Finally, i has o be no ed ha hese esul s we e ob ained
only by using NanoFlux p edic ion and wi hou any
expe imen al op imisa ion o he p ocess.
4. CONCLUSIONS
Ad anced p ocess based on memb ane sepa a ion
echnique may be use ul o ce amic indus y o imp o e
managemen o hei was ewa e s. This imp o emen can
allow o companies a g ea e eusabili y o ea ed was ewa e s
gi ing ise o impo an economic sa ings and educing he
en i onmen al impac .
Expe imen al indings ob ained in his s udy show ha NF
can be a good echnique o pu i ica ion o ce amic indus y
was ewa e s because a e y signi ican o al dissol ed sal s
(TDS) and COD educ ion ( e en ion alues o abou 90%)
is achie ed. On he o he hand, hese esul s also p o e ha
NanoFlux is a good ool o p edic ion ha can sa e ime
and money in expe imen al s udies, because p edic ions
done by he p og am a e qui e nex o he esul s ob ained
expe imen ally.
ACkNOWLEDGMENTS
The au ho s wish o hank he Valencian Ins i u e o Small
and Medium-Sized En e p ises (IMPIVA) in Comunidad
Valenciana (Spain) and Eu eka P og am o i s inancial help
(IMAETA/2005/11,IMIDIE/2009/3and∑!4121).
Table II. pu I ICaTIon daTa o wasTewaTe s usIng nano IlT aTIon on n -90 memb ane
Analysed pa ame e s
Was ewa e 1 Was ewa e 2
A e physico-
chemical
ea men
A e NF ea men wi h
NF90/5 ba
A e physico-
chemical
ea men
A e NF ea men wi h
NF90/4 ba
Analyses Analyses Rejec ion Analyses Analyses Rejec ion
pH 8,35 7,44 - 7,95 7,03 -
Conduc i i y (mS/cm) 3,5 0,16 95% 2,33 0,17 93%
B (mg/L) 5,9 3,9 34% 3,6 2,8 22%
SO4
2-
(mg/L) 258 < 10 >96% 304 <10 >97%
Cl- (mg/L) 932 36 96% 619 41 93%
Na+ (mg/L) 555 28,4 95% 304 30,4 90%
k+ (mg/L) 16,8 0,9 95% 18,8 2,1 89%
Mg2+ (mg/L) 28 0,3 99% 24,8 0,3 99%
Ca2+ (mg/L) 75 <0.1 >99% 101 <0.1 >99%
COD (mg/L) 1156 44 96% 129 < 30 > 77%
Table I. ope aTIng CondITIons used In TesTs wITh wasTewaTe samples
Sample P essu e
(ba ) Tempe a u e
(°C) Flux
(L/(h m2 ba ))
was ewa e 1 5 25 2,27
was ewa e 2 4 25 3,45
110 Bol. Soc. Esp. Ce am. Vid . Vol 51. 2, 103-110, Ma zo-Ab il 2012. ISSN 0366-3175. eISSN 2173-0431. doi: 10.3989/cy .152012
R. MOLINER-SALVADOR, A. DERATANI, J. PALMERI, E. SÁNCHEz
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Acep ado: 11/04/2012