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Membrane fractioning of pre-treated waste activated sludge for the recovery of valuable biocompounds

Abstract

The authors are grateful for the financial support from the Spanish Ministry of Science, Innovation and Universities through the projects MCIU-19-RTI2018-094218-B-I00 and MCIU-22-PID2021-125942OBI00. Authors also want to acknowledge the Employment, Industry and Tourism Office of the Principality of Asturias, Spain, for their financial support through the project AYUD/2021/51041. The author Daniel Núnez ˜ thanks the Principality of Asturias, Spain, for their financial support through the Severo Ochoa scholarship no BP19-093.

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Membrane fractioning of pre-treated waste activated sludge for the recovery of valuable biocompounds

Author: Núñez Díaz, Daniel,Oulego Blanco, Paula,Nikbakht Fini, M.,Muff, J.,Collado Alonso, Sergio,Riera Rodríguez, Francisco Amador,Díaz Fernández, José Mario
Publisher: Universidad de Oviedo
Year: 2023
DOI: 10.1016/j.jwpe.2023.104086
Source: https://digibuo.uniovi.es/dspace/bitstream/10651/70212/1/1-s2.0-S2214714423006062-main.pdf
Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
A ailable online 4 Augus 2023
2214-7144/© 2023 The Au ho s. Published by Else ie L d. This is an open access a icle unde he CC BY license (h p://c ea i ecommons.o g/licenses/by/4.0/).
Memb ane ac ioning o p e- ea ed was e ac i a ed sludge o he
eco e y o aluable biocompounds
Daniel Nú˜
nez
a
, Paula Oulego
a
, Mahdi Nikbakh Fini
b
, Jens Mu
b
, Se gio Collado
a
,
F ancisco A. Rie a
a
, Ma io Díaz
a
,
*
a
Depa men o Chemical and En i onmen al Enginee ing, Uni e si y o O iedo, c/Juli´
an Cla e ía 8, 33006 O iedo, Spain
b
Depa men o Chemis y and Bioscience, Aalbo g Uni e si y Esbje g, Niels Boh s Vej 8, Esbje g 6700, Denma k
ARTICLE INFO
Keywo ds:
Biomolecules
Modelisa ion
Ul a il a ion
Was e alo isa ion
We oxida ion
ABSTRACT
The eco e y o added- alue biocompounds om was e ac i a ed sludge (WAS) is a p omising al e na i e o i s
cu en managemen . In his s udy, WAS was pa ially we oxidised p oducing a highly complex s eam mainly
composed o humic acids, p o eins and ca bohyd a es. This s eam was ul a il e ed o assess he in luence o
memb ane ma e ial and molecula weigh cu -o (MWCO) on i s ac ioning based on he di e en sizes o he
biomolecules con ained in he oxidised WAS.
Fla -shee polye he sul one (PES), pe manen ly hyd ophilic polye he sul one (PESH), and polyac yloni ile
(PAN) memb anes wi h a MWCO o 50 KDa we e e alua ed. The bes pe o mance was ob ained wi h PES
memb ane, achie ing high e en ion alues (a ound 70 % o p o eins and ca bohyd a es, and 47 % o humic
acids) and high di e ences in selec i i y be ween p o eins and ca bohyd a es wi h humic acids (a ound 23 %).
Fo he size ac ioning expe imen s, PES memb anes o 10 and 3 kDa (PES10 and PES3) we e used, ob aining he
bes esul s when il e ing he PES50 memb ane pe mea e wi h he PES3 memb ane, e aining 83 % o ca bo-
hyd a es, 87 % o p o eins and 69 % o humic acids. These esul s open he possibili y o sepa a ing ca bohy-
d a es, p o eins and humic acids h ough an in eg a ed memb ane p ocess.
Besides, memb anes we e cha ac e ized by a omic o ce mic oscopy, in a ed spec oscopy, and con ac angle
measu emen s.
Mul iple ouling models we e assessed, and he main ouling in PAN memb ane, and o a lesse ex en in PES,
was e e sible. Con e sely, PESH memb ane ouling had a s ongly i e e sible cha ac e . Cake il a ion can be
conside ed he main ouling mechanism in all expe imen s.
1. In oduc ion
The bio e ining o biowas es has been p oposed as a sus ainable
means o was e alo isa ion, ob aining ene gy and biochemical e-
sou ces while he olume o inal was e is educed [1]. Al hough i is ye
a i s concep ual phase [2], he s eady ising end o he bio e ine y
ma ke alue, expec ed o show an annual g ow h o 2.2 % un il
eaching a o al alue o USD 52680 million by 2027 [3], is a eliable
ma ke o i s po en ial. Was e ac i a ed sludge (WAS) is a p omising
aw ma e o bio e ine y, as i is a sou ce o biomolecules (p o eins,
lipids, ca bohyd a es, humic acids and enzymes), phospho us, bio-
plas ics, bio-pes icides and also ene gy [4–10]. The cu en global
ma ke size o jus he biomolecules p esen in WAS is o almos USD 200
billion, u ning i s eco e y economically appealing [11].
WAS mainly consis s o locs o bac e ial cells, which a e o med by
weak physical chemical in e ac ions wi h ex acellula polyme ic sub-
s ances [12] (a complex mix u e o polyme s gene a ed by bac e ial
exc e ion, eleased a e cell lysis o p esen in he incoming was ewa e
[13]). Thus, in o de o eco e he abo e-men ioned biocompounds, a
p io solubilisa ion o he sludge is needed in o de o b eak bo h he
s uc u e o med by he ex acellula polyme ic subs ances and he cell
walls, hus eleasing hei in acellula con en o he liquid medium.
Se e al solubilisa ion me hods ha e been es ed o WAS, including
ul a-sonica ion [14,15], ca i a ion [16], alkali ea men [15,17],
ozonolysis [18], we oxida ion (WO) and he mal hyd olysis [19].
Among hese echniques, WO is pa icula ly in e es ing, due o i s
easibili y o be used a an indus ial scale o sludge s abilisa ion [20].
I should be no ed ha his solubilisa ion esul s in a complex ma ix,
* Co esponding au ho .
E-mail add ess: [email p o ec ed] (M. Díaz).
Con en s lis s a ailable a ScienceDi ec
Jou nal o Wa e P ocess Enginee ing
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h ps://doi.o g/10.1016/j.jwpe.2023.104086
Recei ed 19 Decembe 2022; Recei ed in e ised o m 3 July 2023; Accep ed 22 July 2023
Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
2
whe e in e ac ions be ween he di e en eleased biomolecules can
di icul hei pu i ica ion. Fo ins ance, elec os a ic in e ac ions be-
ween p o eins and humic acids occu while binding o hea y me als
such as Cu
2+
, Zn
2+
, and Cd
2+
[21]; and e en agg ega es a e o med
when complexed wi h Cu
2+
[22], hinde ing a sui able sepa a ion o
hese molecules by immobilised me al a ini y ch oma og aphy. Besides,
a selec i e p ecipi a ion is also no possible om his complex ma ix, as
p o eins, ca bohyd a es and humic acids co-p ecipi a e wi h se e al
p ecipi a ion me hods [19]. These molecules ha e impo an indus ial
applica ions sepa a ely: p o eins a e used in cosme ics, ood indus y,
pha maceu icals and animal eed; humic acids can be applied in ag i-
cul u e, pha maceu icals o ecological emedia ion, among o he uses;
and ca bohyd a es a e o en used in he ood indus y [11]. Thus, hei
sepa a ion is o g ea in e es o he inco po a ion o WAS as a aluable
aw ma e ial in a con ex o ci cula economy. Besides, lipid eco e y o
i s use as bio uel om WAS aces di icul ies du ing i s pu i ica ion wi h
sol en ex ac ion, as o he lipidic con aminan s such as wax es e s,
e penoids and polycyclic a oma ic hyd oca bons a e ex ac ed oge he
wi h he desi ed lipids [4].
Fo hese easons, ac ioning he solubilised WAS would imp o e
he e iciency o u he sepa a ion and pu i ica ion s eps. To ha end,
memb ane il a ion is a sui able echnology o his pu pose due o i s
ad an ages, such as high selec i i y, low ene gy consump ion, low cos ,
and mild ope a ing condi ions [23]. Ne e heless, he pe o mance o
he memb ane il a ion is a ec ed by se e al ac o s, especially he
choice o memb ane ma e ial and i s molecula weigh cu -o (MWCO)
[24–26]. Mos memb anes a e polyme ic, and he choice o his polyme
is c i ical o he e iciency o he ope a ion, since i a ec s he pe me-
abili y a e, he sepa a ion abili y o he ouling p ocess, key pa ame e s
in he il a ion p ocess [23].
Despi e hei u e impo ance, polyme ic ma e ials ha e no ye
been s udied o he il a ion o solubilised WAS, and he e ec o
MWCO has been sca cely s udied. Hence, only Li e al. ha e es ed he
use o 1, 10, 30, and 50 kDa polysulphone memb anes o concen a e
humic acids [27,28]. The e o e, he objec i e o his wo k was o s udy
he in luence o he memb ane ma e ial and MWCO on he ac iona ion
o hyd o he mally solubilised WAS in o de o sepa a e ca bohyd a es,
p o eins, and humic acids based on hei size di e ences aiming o
ob ain pa ially pu i ied s eams o hese compounds. In his sense, 3
di e en polyme ic ma e ials: polye he sulphone, hyd ophylic poly-
e he sulphone and polyac yloni ile, wi h a MWCO om 3 KDa o 50
KDa, we e e alua ed, paying special a en ion o ouling modelling.
Hyd ophilic polye he sul one and polyac yloni ile ha e a hyd ophilic
cha ac e , unlike polye he sul one, which is a hyd ophobic ma e ial.
Besides, an in eg a ed memb ane p ocess o he eco e y o bio-
molecules om WAS was also p oposed.
2. Expe imen al
2.1. Oxidised was e ac i a ed sludge
Was e ac i a ed sludge was collec ed om he hickening uni o a
was ewa e ea men plan loca ed in no he n Spain (Baí˜
na, As u ias).
The collec ion was pe o med by ained plan pe sonnel o ensu e he
ep esen a i eness o he samples. WAS was immedia ely solubilised by
a pa ial WO a 160 ◦C and 40 ba o 80 min. These oxida ion condi ions
we e selec ed o maximise he p oduc ion o he a ge molecules: i he
in ensi y o he ea men is oo high, he a ge molecules ge oxidised
o mine alised; i he in ensi y is oo low, he sludge does no comple ely
solubilise [29]. Addi ionally, as he oxida ion in ensi y inc eases, he
pa icle size dec eases, educing he e en ion capabili ies o he mem-
b anes. A cons an low o 1200 mL/min o O
2
sa u a ed wi h s eam was
main ained du ing he en i e eac ion. The con en o he eac o was
kep s i ing a 150 pm. A mo e de ailed desc ip ion o he eac o can
be ound in [30]. A e he eac ion, he oxidised WAS was cen i uged in
o de o wo k wi h he liquid phase. Sodium azide 0.1 % (w/ ) was
added o he oxidised WAS in o de o p e en mic obiological g ow h.
The oxidised sludge was s o ed a 4 ◦C o 15 days and hen eplaced
wi h esh oxidised sludge.
2.2. Memb ane il a ion
2.2.1. Memb anes
MQ (Synde Fil a ion) polye he sul one (PES), UH050 (Mic odyn
Nadi ) hyd ophylic polye he sul one (PESH), and MW (Suez) poly-
ac yloni ile (PAN) la -shee memb anes wi h MWCO o 50 kDa (named
as PES50, PESH50, and PAN50, espec i ely) we e employed o pe o m
he ma e ial sc eening expe imen s. Addi ionally, ST (Synde Fil a ion)
and VT (Synde Fil a ion) PES la -shee memb anes wi h MWCO o 3
and 10 kDa, espec i ely (named as PES3 and PES10), we e used o he
cu -o size sc eening expe imen s. All memb anes we e cu o a ci cula
shape o 9 cm o diame e , and a il a ion a ea o 63.62 cm
2
.
Memb ane hyd ophilici y was cha ac e ized by con ac angle mea-
su emen s. The images we e ob ained wi h a CAM 200 op ical con ac
angle me e (KSV Ins umen s L d., Finland). Sessile wa e d ople s we e
d opped on he clean and ouled memb ane su aces using a sy inge and
le o sp ead eely. Images o he d ople s we e aken by a high-
esolu ion CCD came a a 40 ms in e als o he i s 0.36 s, and a 1
s in e als o he subsequen 19 s. Equilib ium sessile d op con ac
angles we e de e mined om he s eady-s a e angles using he KSV CAM
200 so wa e by measu ing he angle be ween he baseline o a liquid
d op and he angen a he solid–liquid bounda y. All con ac angle
measu emen s we e pe o med in iplica e using h ee di e en mem-
b ane samples.
2.2.2. Equipmen and il a ion condi ions
Fil a ion expe imen s we e ca ied ou in duplica e using an FT17
C oss- low Fil a ion Uni (A m ield L d., Uni ed Kingdom), which al-
lows o pe o m angen ial low il a ions wi h la shee memb anes.
P io o conduc ing he expe imen s, all polyme ic memb anes we e p e-
condi ioned by unning he equipmen wi h no p essu e o 30 min using
dis illed wa e . Subsequen ly, wa e was il e ed unde he ope a ional
condi ions (indica ed below) o an addi ional 30 min. The lux ob ained
in his s ed was conside ed as he lux a =0. The pe mea e lux o he
clean memb anes was measu ed du ing his s ep o u he ouling
modelling. All he ma e ial sc eening il a ion expe imen s we e pe -
o med unde he ollowing condi ions: empe a u e o 50.0 ±0.4 ◦C,
ansmemb ane p essu e (TMP) o 4.0 ±0.2 ba and c oss low eloci y
(CFV) o 3.00 m/s. The oxidised WAS was il a ed wi hou pe mea e
eci cula ion un il a olume concen a ion a e (VCR) o 2.5 was
eached.
Du ing he MWCO sc eening expe imen s, he oxidised WAS was
il e ed wi h he PES50, PES10 and PES3 memb anes. Besides, in o de
o assess he iabili y o he ac ioning o he oxidised WAS, he
pe mea e ob ained a e he il a ion wi h PES50 was subsequen ly
il e ed wi h he PES10 o wi h he PES3 memb anes, naming hese
pe mea es as PES50-10 and PES50-3, espec i ely. The expe imen s
we e pe o med unde he same condi ions han hose used in he ma-
e ial sc eening ones. Only o ob aining he PES50-3 pe mea e, p essu e
was se a 30 ba and a VCR alue o 1.25 was achie ed.
Pe mea e low was de e mined by g a ime ic measu emen s o he
pe mea e, which we e collec ed au oma ically by he FT17 C oss- low
Fil a ion Uni so wa e. Flux was calcula ed by he ollowing equa ion
(Eq. (1)):
J=QP
AM
(1)
Whe e J is he pe mea e lux (m⋅s
−1
), Q
P
is he pe mea e low (m
3
⋅s
−1
),
and A
M
is he memb ane su ace a ea (m
2
).
In addi ion, samples o he pe mea e and e en a e we e collec ed
pe iodically and kep a 4 ◦C o u he analysis.
D. Nú˜
nez e al.
Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
3
A e he il a ions, he ouled memb ane was insed wi h dis illed
wa e un il a cons an lux was ob ained, and i s pe meabili y was
measu ed o u he ouling modelling.
2.2.3. Fouling modelling
Resis ance-in-se ies, He mia’s, and Men ha’s ouling models we e
employed o cha ac e ise bo h he e e sibili y and main mechanism o
memb ane ouling occu ed du ing he di e en il a ion expe imen s.
Resis ance-in-se ies model exp esses he o al hyd aulic esis ance o
he memb ane (R
T
, m
−1
) as he sum o di e en esis ances caused by
e e sible ouling (R
e
, m
−1
), i e e sible ouling (R
i e
, m
−1
), o by he
memb ane i sel (R
m
, m
−1
) (Eq. (2)). Hyd aulic esis ance can be
calcula ed as shown in Eq. (3):
RT=Rm+R e +Ri e (2)
R=TMP
μ
J(3)
Whe e
μ
is he dynamic iscosi y o he WAS a 50 ◦C (kg⋅m⋅s
−1
). By
adding o sub ac ing he esis ances ob ained wi h he clean, ouled, o
insed memb ane luxes, R
m
, R
e
, and R
i e
can be easily calcula ed. A
mo e de ailed explana ion o hese calcula ions can be ound in he
Appendix o [31]).
The main ouling mechanism occu ed on each memb ane du ing
ul a il a ion was de e mined h ough He mia’s model [32] (Eq. (4)):
dJ
d = − Kj⋅(J−J0)⋅J2−n(4)
Whe e is ime (min), K
j
is he model cons an ha depends on he
ouling phenomenon, J
0
is he limi ing lux (m⋅s
−1
), and n is a cons an
ha a ies o he ouling mechanism: comple e po e blocking (CPB) (n
=2, K
b
in min
−1
), whe e he ac i e memb ane a ea is blocked by pa -
icles la ge han he po e size; in e nal po e blocking (IPB) (n =1.5, K
i
in m
−1
), whe e memb ane po es a e blinded by ei he adso p ion o
deposi ion o pa icles smalle han he po e size; pa icle po e blocking
(PPB) (n =1, K
p
in m
−1
), whe e pa icles migh seal a po e o e ime, o
b idge i and no block i comple ely; and cake il a ion (CF) (n =0, K
c
in min⋅m
−2
), whe e a cake o pa icles ha does no en e he po es is
o med on he memb ane su ace [33].
The K
j
o he ou models we e calcula ed by minimizing he di -
e ence be ween he p edic ed alues and he expe imen al da a,
calcula ed as he sum o squa ed esiduals (SSR). The model wi h he
lowes SSR was chosen as he mos sui able one o each se o expe i-
men al da a.
In addi ion, lux was also modelled using he Meh a’s model [34],
which akes in o accoun he wo lux decline domains ha ake place
du ing memb ane il a ion: domain 1, whe e a apid lux decline occu s
du ing he ea ly s age o il a ion; and domain 2, whe e he lux decline
dec eases un il he lux emains quasi-s able [35]. I can be exp essed as
ollows (Eq. (5)):
J=J0−J∞1⋅exp−
α
+ (J∞1 −J∞2)⋅exp−β +J∞2 (5)
Whe e J∞1 is he lux a he end o domain 1 (m⋅s
−1
); J∞2 is he lux a
he end o domain 2 (i.e., a he end o he expe imen ) (m⋅s
−1
); and
α
(min −1)and β(min −1)a e wo cons an s de e mined expe imen ally
ha desc ibe he a e o lux decline associa ed wi h he memb ane
ouling and he concen a ion pola iza ion and gel laye o ma ion,
espec i ely.
2.3. A omic o ce mic oscopy
The oughness o he ouled and clean memb anes was analysed by
a omic o ce mic oscopy (AFM). All AFM measu emen s we e pe o med
a oom empe a u e (20 ◦C) using a Nanoscale scanning unnelling
mic oscope (Nano ec Ce an es FullMode SPM), wo king in con ac
mode in ai medium wi h gold coa ed silicon ni ide ips. Memb ane
samples we e ixed o he sample holde o he mic oscope wi h high-
acuum silicone g ease. Roughness pa ame e s we e de e mined om
he collec ed da a using he WSxM 5.0 so wa e [36]. Memb ane
oughness was compa ed in e ms o mean oughness (R
a
[nm/
μ
m]),
oo mean squa e oughness ( ms), peak- o-peak dis ance (nm/
μ
m), and
su ace skewness and ku osis. R
a
is he mean alue o he su ace
ela i e o he cen e plane; ms is he s anda d de ia ion o he heigh s
o all he pixels in he image om he a i hme ic mean [37]; and
skewness and ku osis desc ibe he shape o a p obabili y dis ibu ion,
e lec ing he obliqui y and he la ness o he cu e, espec i ely [38].
2.4. In a ed spec oscopy
In a ed spec a (FTIR) o he clean and ouled memb anes we e
aken in he ange om 600 o 4000 cm
−1
using Va ian 670-IR FTIR
spec ome e equipped wi h a Golden Ga e ho izon al a enua ed o al
e lec ance (ATR) accesso y. Expe imen al condi ions we e 32 scans, 4
cm
−1
esolu ion and ape u e open.
2.5. Analy ical me hods
P o eins, humic acids, ca bohyd a es, colou numbe (CN) and
chemical oxygen demand (COD) we e measu ed by colo ime ic
me hods. P o eins and humic acids we e measu ed ollowing he
modi ied Low y me hod desc ibed by F ølund e al. [39], using bo ine
se um albumin and comme cial humic acid as s anda ds. Ca bohyd a es
we e measu ed acco ding o he Dubois me hod [40] using D-glucose as
s anda d. Spec al abso bance coe icien s (SAC [cm
−1
]) we e measu ed
a 436, 525 and 620 nm and used o calcula e he CN alue (cm-1) ac-
co ding o Eq. (6):
CN =SAC2
436 +SAC2
525 +SAC2
620
SAC436 +SAC525 +SAC620
(6)
The abso bances o p o eins, humic acids, ca bohyd a es and SAC
we e measu ed wi h a Helios Alpha UV–Vis spec opho ome e (The mo
Scien i ic, USA).
Densi y was measu ed a 50 ◦C and 1 a m wi h a pycnome e . Ki-
nema ic iscosi y was measu ed a 50 ◦C and 1 a m wi h a Cannon-
Fenske in e sed- low iscome e (P o on, UK). Dynamic iscosi y was
calcula ed by mul iplying he kinema ic iscosi y by he densi y. pH was
measu ed wi h a Basic 20 pH me e (C ison, Spain). COD alues we e
de e mined by he po assium dich oma e me hod [41], and he abso -
bance a 600 nm was measu ed wi h a HACH DR/2500 spec opho-
ome e (Hach Company, USA). To al o ganic ca bon (TOC) was
de e mined wi h a Shimadzu TOC-V
CSH
TOC analyse (Shimadzu,
Japan).
Rejec ion coe icien s (RC
i
) we e calcula ed acco ding o he Eq. (7):
RCi=1−CPm,i
CR ,i
(7)
Whe e CPm,i and CR ,i he concen a ion o he compound “i” in he
pe mea e and he e en a e (g⋅L
−1
), espec i ely. All analy ical mea-
su emen s we e conduc ed a leas h ee imes.
3. Resul s and discussion
3.1. Oxidised was e ac i a ed sludge
The oxidised WAS was sligh ly acid and p esen ed a deep b own
colou . I s main physical-chemical cha ac e is ics a e shown in Table 1.
D. Nú˜
nez e al.
Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
4
3.2. Memb ane ma e ial sc eening
3.2.1. Con ac angle measu emen s
Measu ed con ac angles o wa e on he polyme ic memb anes used
in he ul a il a ion o he oxidised WAS a e shown in Table 2. A se-
lec ion o he pic u es o he sessile d ops, om which he con ac angles
we e calcula ed, can be ound in Fig. A1.
A su ace is conside ed hyd ophilic i he con ac angle is lowe han
90◦[42]. Thus, PES50 could be conside ed hyd ophobic, while PESH50
and PAN50 we e ound o be hyd ophilic. This was in acco dance wi h
he esul s ob ained by o he au ho s ela ed o ouling esis ance o
ul a il a ion memb anes [43]. A e il e ing he oxidised WAS, he
ouled PES50 and PESH50 u ned mo e hyd ophilic han he p is ine
ones, while PAN50 became less hyd ophilic a e being ouled, which
showed he di e en na u e o he oulan -memb ane in e ac ions
depending on he memb ane ma e ial: i seems ha PES50 and PESH50
we e coa ed wi h mo e hyd ophilic oulan s, while PAN50 in e ac ed
wi h oulan s less hyd ophilic han i sel .
3.2.2. Pe meabili y es s
The luxes ob ained wi h PES50, PESH50 and PAN50 a e shown in
Fig. 1.
Final luxes app oxima ely 3 imes highe we e ob ained wi h
PESH50 (67.2 ±0.9 LMH) and PAN50 (74 ±3 LMH) compa ed o he
one achie ed by PES50 (25 ±2 LMH), due o hei hyd ophilic cha -
ac e . In his sense, memb ane hyd ophilici y p e en ed ouling, in
acco dance o wha was epo ed by o he au ho s [44,45]. The
esis ance-in-se ies models (Fig. 2) con i med he a o emen ioned abou
hyd ophobici y and i s highe endency o ouling. In his sense, all he
esis ances (memb ane, e e sible and i e e sible) measu ed o
PES50, which added up a o al hyd aulic esis ance o 1.07⋅10
14
m
−1
,
we e highe han hose o PESH50 (13.3, 2.5 and 1.1 imes highe ,
espec i ely) and PAN50 (3.4, 2.4 and 6.3 imes highe , espec i ely).
On he o he hand, he di e en beha iou be ween luxes in PESH50
and PAN50 can be explained based on he alues o i e e sible ouling
o each memb ane. Thus, he esis ance-in-se ies modelling showed
ha he highe endency o ouling obse ed in PESH50 is due o i e-
e sible ouling, since i s R
i e
accoun ed o he 49.6 % o i s o al
hyd aulic esis ance, while R
i e
obse ed in PAN50 only ep esen ed
12.4 % o he o al hyd aulic esis ance. The o al R
i e
also seemed o be
co ela ed wi h he hyd ophobici y o he memb ane, as PES50 showed
he highes R
i e
([2.8 ±0.4]⋅10
13
m
−1
), ollowed by PESH50 ([2.45 ±
0.01]⋅10
13
m
−1
) and PAN50 ([4.3 ±0.6]⋅10
12
m
−1
).
Besides, e e sible ouling was ound o be he main ouling in PES50
and PAN50 memb anes, co esponding o a 53.4 % and o a 68.9 % o
he o al ouling o PES50 and PAN50, espec i ely.
The luxes ob ained in his s udy we e in he same o de o magni-
ude han hose ob ained by o he au ho s when PES memb anes we e
used du ing he il a ion o milk [46], e ine y and pe ochemical
was ewa e [47] and oil-in-wa e emulsion [48,49]; and wi h PAN
memb anes when ap wa e [50] and oil-in-wa e emulsion [49] we e
il e ed. Besides, lowe ini ial luxes we e ob ained when PESH mem-
b anes we e employed o he il a ion o molasses [51], while simila
luxes we e a ained o oli e oil washing was ewa e [52].
I should be no ed ha he highe luxes ob ained wi h PESH50 and
PAN50 come along wi h lowe ejec ion coe icien s and lowe selec-
i i ies be ween p o eins and humic acids (Table 3). In pa icula , he
lowes ejec ion coe icien s o CN, TOC, and he h ee measu ed bio-
compounds we e hose co esponding o PESH50. On he o he hand,
he highes ejec ions we e ob ained wi h PES50, also achie ing he
highes ejec ion di e ences be ween p o eins and humic acids (22 %
di e ence s 7 % di e ence ob ained wi h PAN50, and 10 % di e ence
ob ained wi h PESH50); and be ween ca bohyd a es and humic acids
(23 % di e ence s 13 % ob ained wi h PAN50 and 17 % di e ence
ob ained wi h PESH50).
These highe e en ions may be due o he o ma ion o a hicke cake
laye on op o he memb ane, which would ac as a seconda y il a ion
mesh, inc easing he selec i i y o he memb ane [53]. The o ma ion o
his hicke ouling cake could be obse ed h ough he esis ance-in-
se ies model (Fig. 2), whe e he R
e
, mainly associa ed wi h he o -
ma ion o he ouling cake [54], was mo e han wo- old highe a e
il e ing wi h PES50 ([5.7 ±0.8]⋅10
13
m
−1
) han wi h PESH50 ([2.3 ±
0.2]⋅10
13
m
−1
) o PAN50 ([2.41 ±0.07]⋅10
13
m
−1
). Rejec ion di e -
ences be ween PESH50 and PAN50 a e cohe en wi h his explana ion,
as he R
e
o PESH50 is sligh ly lowe han ha o PAN50.
As bo h highe ejec ion coe icien s and highe ejec ion di e ences
be ween humic acids and he o he biomolecules (p o eins and ca bo-
hyd a es) we e achie ed wi h PES50, he ac iona ion es s wi h
memb anes o di e en MWCO (MWCO sc eening expe imen s) was
ca ied ou wi h PES memb anes.
3.2.3. Flux modelling
As i can be seen in Fig. 3 and Table 4 (SSR), CF was he bes - i ing
He mia’s model in all h ee cases, al hough he i ings indica ed ha
none o he He mia’s models ully explain he ouling mechanism, hus
indica ing se e al ouling mechanisms may ha e occu ed h oughou
he il a ion. Indeed, he ac ha di e en ouling mechanisms occu a
di e en s ages o he il a ion is well documen ed in he li e a u e
[55,56] and i was aken in o accoun by Meh a’s model [34]. Thus, CF
was he main ouling mechanism o e all, al hough i e e sible po e
blocking also occu ed; especially du ing he il a ion wi h PESH50,
whe e he IPB model showed be e i ing han in he il a ions wi h
PES50 and PAN50, e lec ing he abo e-men ioned mo e i e e sible
na u e o he PESH50 ouling. Besides, CF has also been desc ibed by
o he au ho s as he main ouling mechanism o na u al o ganic ma e
du ing ul a il a ion wi h PES memb anes [57,58].
Howe e , i should be no ed ha he bes i ing o he expe imen al
da a was achie ed wi h Meh a’s model, which p o ides in o ma ion
abou he e ec o memb ane ouling (pa ame e
α
) and concen a ion
pola iza ion and gel laye o ma ion (pa ame e β) on he lux decline.
The op imised alues o hese wo cons an s a e shown in Table 4.
Highe
α
and β alues ep esen as e ini ial memb ane ouling and
as e s abilisa ion o he lux by he es ablishmen o he concen a ion
pola iza ion g adien and gel laye o ma ion, espec i ely. The
α
alues
ob ained o he il a ions wi h PESH50 and PAN50 we e 10- old highe
han hose o PES50 (3.88), while he β alues we e 4- old lowe han
hose ob ained o PES50 (5.20⋅10
−2
). This indica es ha a s ong ini ial
memb ane ouling occu ed a e s a ing he il a ion o he oxidised
Table 1
Main physical-chemical cha ac e is ics o he oxidised was e
ac i a ed sludge.
Pa ame e Value
pH 5.04 ±0.03
COD
a
(g O
2
L
−1
) 20.5 ±0.5
TOC
a
(g L
−1
) 8.00 ±0.01
CN
a
(cm
−1
) 3.9 ±0.2
P o eins (g L
−1
) 3.4 ±0.3
Humic acids (g L
−1
) 8.4 ±0.2
Ca bohyd a es (g L
−1
) 2.75 ±0.03
a
COD: chemical oxygen demand; TOC: o al o ganic ca -
bon; CN: colou numbe .
Table 2
Wa e su ace con ac angles on he s udied memb anes.
Memb ane size Memb ane ma e ial Memb ane s a e Con ac angle
50 kDa PES Clean 90 ±3
Fouled 70 ±2
PESH Clean 72 ±1
Fouled 54 ±11
PAN Clean 39 ±4
Fouled 57 ±10
D. Nú˜
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Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
5
WAS wi h PESH50 and PAN50, causing a apid dec ease in he lux.
A e his ini ial d op, he s abilisa ion o he lux by concen a ion po-
la iza ion occu ed mo e slowly. Rega ding he beha iou du ing he
il a ion wi h PES50, i was opposi e o ha o he o he polyme ic
memb anes: he ini ial d op caused by memb ane ouling was less
d as ic, and he equilib ium in concen a ion pola iza ion was eached
as e .
This esul is in acco dance wi h he li e a u e, and can be explained
conside ing he pola iza ion sie ing model [59], based on he di e -
ences o hyd ophilici y be ween he memb anes:
Thus, in hyd ophilic memb anes, an ini ial i e e sible adso p ion
laye is o med, ega dless o he solu e concen a ion, and subsequen
0
200
400
600
800
1000
1200
1400
1600
0
0.2
0.4
0.6
0.8
1
1 1.2 1.4 1.6 1.8 2 2.2 2.4 2.6
J (LMH)
J/J0
VCR
b)
0
20
40
60
80
100
0
0.2
0.4
0.6
0.8
1
1 1.2 1.4 1.6 1.8 2 2.2 2.4 2.6
J (LMH)
J/J0
VCR
0
60
120
180
240
300
360
420
0
0.2
0.4
0.6
0.8
1
1 1.2 1.4 1.6 1.8 2 2.2 2.4 2.6
J (LMH)
J/J0
VCR
c)
a)
Fig. 1. No malised lux a ia ion o e VCR o he oxidised WAS il a ion wi h (a) PES50 (J
0
=102.4 ±0.2 L/m
2
h), (b) PESH50 (J
0
=1590 ±40 L/m
2
h) and (c)
PAN50 (J
0
=420 ±40 L/m
2
h).
Fig. 2. R
m
(
), R
e
(
) and R
i e
(
) a e il a ion wi h PES50, PESH50 and PAN50.
D. Nú˜
nez e al.

Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
6
ouling will appea in he o m o a gel-pola iza ion laye . On he o he
hand, in hyd ophobic memb anes, he size o he i e e sible adso p ion
laye inc eases un il i s hickness p o ec s he hyd ophobic su ace om
he adso bed molecules, which gene a es highe alues o i e e sible
ouling han in hyd ophilic su aces, and only a e his limi is eached,
he gel-pola iza ion laye s a s o o m [59]. Acco ding o his, he
beha iou o PES50 can be explained by i s hyd ophobic cha ac e , since
mo e ime was equi ed o he ini ial memb ane ouling o be ully
occu , and he inal concen a ion pola iza ion laye needed less ime o
s abilise, hus s a ing o o m a highe eed concen a ions.
3.2.4. A omic o ce mic oscopy
AFM images we e aken om clean and ouled memb anes in o de
o analyse he su ace mo phology (Fig. 4). The e ical p o ile o he
memb ane su ace was ep esen ed by he colou in ensi y, wi h ligh e
colou s indica ing highe egions, and da ke colou s indica ing
dep essions.
The su ace o all he h ee clean memb anes was clea ly a anged in
a “c es and alley” o “nodule and alley” pa e n, o igina ed by he
andom o ien a ion and o e lapping o he ib e s uc u e [60]. This
su ace a angemen has also been obse ed by o he au ho s when PES,
PAN and polyamide memb anes wi h la -shee , ubula and hollow-
ib e geome ies we e used in ul a il a ion and nano il a ion p o-
cesses [60–63]. The p esence o alley-like o ma ions is highly ela ed
o ouling, as oulan pa icles end o deposi in hese o ma ions [64].
This ac was suppo ed by he images o ouled memb anes, whe e
c es -like o ma ions could no longe be seen, indica ing ha he alley-
like egions had been clogged by oulan s.
In addi ion o AFM imaging, memb ane oughness was compa ed in
e ms o mean oughness (R
a
[nm/
μ
m]), oo mean squa e oughness
( ms), peak- o-peak dis ance (nm/
μ
m), and su ace skewness and
Table 3
Rejec ion coe icien s (RC) ob ained wi h he 50 kDa polyme ic memb anes.
PES50* PESH50* PAN50*
RC
CN*
0.80 ±0.02 0.69 ±0.03 0.73 ±0.04
RC
TOC*
0.47 ±0.03 0.34 ±0.04 0.38 ±0.05
RC
COD*
0.48 ±0.08 0.41 ±0.03 0.4 ±0.1
RC
CH*
0.70 ±0.02 0.57 ±0.07 0.60 ±0.06
RC
P o *
0.69 ±0.06 0.50 ±0.05 0.54 ±0.09
RC
HA*
0.47 ±0.04 0.40 ±0.03 0.47 ±0.03
*CN: colou numbe ; TOC: o al o ganic ca bon; COD: chemical oxygen demand;
CH: ca bohyd a es; PROT: p o eins; HA: humic acids; PES50: poly-
e he sulphone, 50 kDa; PESH50: pe manen ly hyd ophilic polye he sulphone,
50 kDa; PAN: polyac yloni ile, 50 kDa.
0
20
40
60
80
100
120
140
0 5 10 15 20 25 30 35 40
J (LMH)
(min)
0
200
400
600
800
1000
1200
1400
1600
1800
0 5 10 15 20 25 30 35 40
J (LMH)
(min)
0
50
100
150
200
250
300
350
400
450
0 5 10 15 20 25 30 35 40
J (LMH)
(min)
a)
b)
c)
Fig. 3. He mia’s (comple e po e blocking [ ], in e media e po e blocking [ ], pa ial po e blocking [ ] and cake o ma ion
[]) and Meh a’s ( ) lux models o PES50 (a), PESH50 (b) and PAN50 (c) expe imen al luxes (●).
Table 4
Fi ing pa ame e s o he adjus ed models.
PES50 PESH50 PAN50
He mia’s models
CPB K
b
(min
−1
) 3.31⋅10
−2
5.29 9.43⋅10
−2
SSR 172,041.83 617,253.55 628,747.63
IPB K
i
(m
−1
) 4.58⋅10
−3
1.37⋅10
−1
7.31⋅10
−3
SSR 116,241.52 590,551.29 431,129.86
PPB K
p
(m
−1
) 6.54⋅10
−4
1.40⋅10
−3
5.97⋅10
−4
SSR 77,545.23 852,391.39 286,513.46
CF K
c
(min⋅m
−2
) 1.45⋅10
−5
4.42⋅10
−6
3.86⋅10
−6
SSR 32,776.51 255,336.20 129,005.00
Meh a’s model
J∞1 (LMH) 46.05 114.16 116.08
α
(min −1)3.88 30.70 30.70
β(min −1)5.20⋅10
−2
1.33⋅10
−2
1.26⋅10
−2
SSR 700.38 1401.89 783.73
D. Nú˜
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Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
7
ku osis in o de o analyse i s ela ionship wi h ouling (Table 5).
The loss o no malised lux was in e sely ela ed o R
a
and ms
alues. In his sense, PES50, whose no malised lux dec eased he leas
(77 %) du ing he ul a il a ion o he oxidised WAS, also showed he
lowes R
a
, ms and peak- o-peak dis ance alues. Fu he mo e, he
highes alues we e ob ained wi h PESH50, which los he highes
p opo ion o no malised lux (96 %). The di e ence be ween no mal-
ised luxes o PES50 and PAN50 was less ma ked han he oughness
alues may sugges , which could be explained based on hei di e en
hyd ophilic p ope ies ( ouling allegedly inc eases wi h hyd ophobici y
[61]). The ela ionship be ween loss o no malised lux and R
a
and ms
alues is in acco dance wi h he exis ing li e a u e, indica ing ha su -
ace oughness plays a key ole in lux loss [61,64–66]. As i was p e-
iously commen ed, in he ini ial s ages o il a ion, he pa icles end o
deposi in he “ alley-like” o ma ions o he memb anes, clogging hese
dep essed egions. Memb anes wi h lowe su ace oughness p esen
ewe “ alley-like” o ma ions on hei su ace, so he a achmen o
solu e molecules is es ic ed [64]. The e ec o his ewe p esence o
alley-like egions can be a ended con as ing he oughness alues
om Table 5 wi h he images in Fig. 4: alley o ma ions we e mo e
e iden in PAN50 and PESH50 han in PES50, and he dep h o he
alleys was lowe in he la e memb ane, as i can be con i med by he
peak- o-peak dis ance.
As p o ed by he pe meabili y es s and he AFM measu emen s, lux
loss is a complex phenomenon, which depends on se e al ac o s, among
which, he na u e o he memb ane su ace (hyd ophilic su aces p e-
en ouling) and i s ugosi y ( he highe he ugosi y, he mo e space
he solu e molecules ha e o deposi ing) can be conside ed
de e minan .
3.3. Memb ane molecula weigh cu -o sc eening
3.3.1. Pe meabili y es s
As PES was selec ed as he mos sui able ma e ial o WAS ac-
ioning (Sec ion 3.2.2), he MWCO sc eening expe imen s we e ca ied
ou wi h memb anes made o his polyme ic ma e ial (PES10 and PES3).
The lux ob ained wi h PES3 was ex emely low (a ound 0.5 LMH on
a e age), making his il a ion un easible, and hus no da a om his
expe imen a e depic ed. The luxes ob ained wi h PES10, PES50-10 and
PES50-3 a e shown in Fig. 5.
The highes lux ob ained du ing he MWCO sc eening was achie ed
wi h PES50-10. Howe e , he low ejec ion coe icien s obse ed made
his op ion un easible (Table 6). The highes ejec ions in e ms o CN,
TOC and COD we e achie ed wi h PES50-3. Ne e heless, in he case o
he biomolecules, sligh ly di e ences we e obse ed in ejec ions and
ejec ion di e ences be ween PES10 and PES50-3.
Based on he ejec ion coe icien s and he obse ed dec ease in lux
du ing he ul a il a ion o he oxidised WAS using PES10, as well as he
pe mea es ob ained om PES50 wi h PES10 and PES3, i can be
concluded ha he majo i y o molecules e ained by he PES10 mem-
b ane can also be e ained by he PES50 memb ane. The e o e, coupling
hese wo memb anes would be edundan and unnecessa y. This
beha iou was in acco dance wi h he wo k by U ea e al. [67], whe e
he e ec o WO on he di e en molecula weigh ac ions o WAS was
s udied. They epo ed ha , a e a WO ea men a 190 ◦C and 90 min,
he molecula weigh o he majo i y o he p esen molecules was
comp ised in he anges be ween 0 and 35 kDa ( e e ed by U ea e al.
as low molecula weigh molecules) and 35–150 kDa (medium molec-
ula weigh molecules). Mo eo e , hyd ophobic molecules we e also
p esen due o he in e ac ions wi h size-exclusion column. Acco ding o
he esul s a ained in his s udy, he sizes o he majo i y o he low
molecula weigh molecules we e comp ised be ween 0 and 10 kDa, and
Fig. 4. AFM images o clean and ouled PES50 (A and B), PESH50 (C and D) and PAN50 (E and F) o memb ane su ace mo phology analysis.
Table 5
Memb ane su ace oughness pa ame e s.
Clean Fouled
PES50 PESH50 PAN50 PES50 PESH50 PAN50
R
a
[nm/
μ
m] 23.0 ±
0.6
74 ±5 67 ±8 56 ±
15
164 ±
37
92 ±6
ms 30.4 ±
0.9
94 ±7 89 ±5 41 ±
12
212 ±
47
119 ±7
peak- o-
peak
dis ance
[nm/
μ
m]
142 ±
5
391 ±
32
365 ±
16
255 ±
59
918 ±
208
487 ±
26
Skewness −0.23
±0.04
– −0.08
±0.03
– – −0.05
±0.03
Ku osis 3.35 ±
0.03
2.72 ±
0.05
2.8 ±
0.3
3.4 ±
0.4
2.89 ±
0.01
2.7 ±
0.1
D. Nú˜
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Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
8
he ones o he medium molecula weigh molecules we e abo e 50 kDa.
The esis ance-in-se ies model (Fig. 6) showed ha app oxima ely
hal o he memb ane ouling du ing he il a ion wi h bo h PES10 and
PES50-3 was i e e sible, which con as o he esul s ob ained wi h
PES50, whe e only 33 % o he ouling esis ance was a ibu able o
i e e sible ouling. Mo eo e , a compa ison be ween he alues o he
R
e
and he R
i e
ob ained when il e ing wi h PES50 and PES10 shows
ha no signi ican di e ences could be ound be ween he alues o
e e sible ouling, whe eas he i e e sible one o he PES10 memb ane
was a ound 2.5 imes highe han ha o he PES50 memb ane. Thus,
he addi ional lux decay obse ed be ween he il a ion wi h PES10
and PES50 was exclusi ely due o an inc ease in i e e sible ouling. I
has been epo ed ha i e e sible ouling du ing he il a ion o na -
u al o ganic ma e is p ima ily caused by he hyd ophilic ac ion o
his o ganic ma e [68–70]. The e o e, he addi ional i e e sible
ouling obse ed in his s udy is likely a ibu ed o hyd ophilic sub-
s ances, p esumably oxidised HA, since hei ejec ion coe icien s we e
lowe han hose o he o he biomolecules, which sugges s a lowe
a e age size. In his sense, se e al au ho s ha e epo ed ha he
oxida ion o HA inc eased hei hyd ophilici y [71–74] by oxidizing
benzene g oups in o di e en aldehydes and ca boxylic acids [72,74].
A e a subsequen educ ion o he memb ane MWCO o 3 kDa, he
ouling p o ile emained simila (sligh ly mo e i e e sible han
e e sible ouling), p o ing ha he molecules e ained by he PES50
memb ane mainly caused e e sible ouling. In his sense, Taniguchi
e al. [57] compa ed he ouling o PES memb anes wi h MWCOs om
10 o 1000 kDa du ing he UF o na u al o ganic ma e , and epo ed
ha memb anes wi h lowe MWCO (10 and 30 kDa) showed highe
i e e sible ouling, al hough ouling was mos ly e e sible in all cases.
3.3.2. Fouling modelling
The i ing o he s udied ouling models o he expe imen al da a
co esponding o he il a ions wi h PES10, PES50-10 and PES50-3 is
shown in Fig. 7.
Simila ly o he il a ion wi h he 50 kDa memb anes, he bes i ing
He mia’s model was CF in he h ee il a ions. This esul s we e in
acco dance o hose epo ed by Pee a e al. [75] ela ed o he ul a-
il a ion o humic acid solu ions wi h PES memb anes. Howe e , as i
was discussed in he p e ious sec ion, he i ing showed ha his model
alone could no adequa ely explain he obse ed ouling endency. In
Fig. 5. Flux a ia ion o e VCR o he oxidised WAS il a ion wi h PES10 (a) (J
0
=101.5 ±0.9 L/m
2
h), PES50-10 (b) (J
0
=102 ±3 L/m
2
h) and PES50-3 (c) (J
0
=
13.72 ±0.01 L/m
2
h).
Table 6
Rejec ion coe icien s ob ained wi h PES10, PES50-10 and PES50-3.
PES10 PES50-10 PES50-3
RC
CN
0.90 ±0.01 0.35 ±0.01 0.9942 ±0.0009
RC
TOC
0.70 ±0.16 0.17 ±0.09 0.88 ±0.01
RC
COD
0.60 ±0.04 0.09 ±0.04 0.66 ±0.04
RC
CH*
0.79 ±0.05 0.14 ±0.05 0.83 ±0.05
RC
P o *
0.84 ±0.09 0.21 ±0.08 0.87 ±0.06
RC
HA*
0.63 ±0.05 0.15 ±0.06 0.67 ±0.06
*CH: ca bohyd a es; PROT: p o eins; HA: humic acids.
D. Nú˜
nez e al.
Jou nal o Wa e P ocess Enginee ing 55 (2023) 104086
9
his case, he ul a il a ion o bo h he oxidised WAS wi h PES10 and
he pe mea es ob ained om PES50 wi h PES10 and PES3 su e ed a
p opo iona ely highe i e e sible ouling compa ed wi h he ul a il-
a ion o oxidised WAS wi h he PES50 memb ane, which in all cases
could be mainly a ibu ed o PPB, as i was he second-bes i ing
He mia’s model (Table 7). The ac ha PPB emained he main i e-
e sible ouling mechanism in memb anes wi h lowe MWCO is in
acco dance wi h he li e a u e. Thus, i has been epo ed ha , when
Fig. 6. R
m
(
), R
e
(
) and R
i e
(
) a e il a ion wi h PES10 and PES50-3 memb anes.
Fig. 7. He mia’s (comple e po e blocking [ ], in e media e po e blocking [ ], pa ial po e blocking [ ] and cake o ma ion
[]) and Meh a’s ( ) lux models o PES10 (a), PES50-10 (b) and PES50-3 (c) expe imen al luxes (●).
D. Nú˜
nez e al.