Moringa Oleifera seeds and Chitosan as alternatives to conventional coagulation agents
Abstract
This article discusses the possibilities of using natural polymers in the water treatment process to replace conventional chemical-based reagents. Mainly part of article presented the results of a laboratory-scale research focused on the use of alternative coagulants in water treatment. Attention was particularly paid to natural cation coagulants derived from Moringa oleifera seeds and chitin. These two coagulant agents were used in laboratory research for treating real raw water. Several series of laboratory jar tests were performed to identify the effectiveness of the selected coagulants in removing turbidity from water.
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Mo inga Olei e a seeds and Chi osan as al e na i es o con en ional
coagula ion agen s
To ci e his a icle: T Kue a and L Ho mano á 2020 IOP Con . Se .: Ma e . Sci. Eng. 800 012032
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Mo inga Olei e a seeds and Chi osan as al e na i es o
con en ional coagula ion agen s
T Kuče a1*, L Ho mano á1
1B no Uni e si y o Technology, Facul y o Ci il Enginee ing, Ins i u e o Municipal
Wa e Managemen , Žižko a 17, B no, 602 00, Czech Republic.
*Email: omas.kuce a@ u .cz
Abs ac . This a icle discusses he possibili ies o using na u al polyme s in he wa e ea men
p ocess o eplace con en ional chemical-based eagen s. Mainly pa o a icle p esen ed he
esul s o a labo a o y-scale esea ch ocused on he use o al e na i e coagulan s in wa e
ea men . A en ion was pa icula ly paid o na u al ca ion coagulan s de i ed om Mo inga
olei e a seeds and chi in. These wo coagulan agen s we e used in labo a o y esea ch o
ea ing eal aw wa e . Se e al se ies o labo a o y ja es s we e pe o med o iden i y he
e ec i eness o he selec ed coagulan s in emo ing u bidi y om wa e .
1. In oduc ion
The in oduc ion o a coagula ion p ocess is o en equi ed o ea ing wa e om su ace sou ces o
dec ease u bidi y and colo , as well as he olume o pa hogenic o ganisms. The p ocess may also be
op imized o he emo al o na u al o ganic ma e (NOM) and hea y me als [6]. Va ious coagulan
agen s a e used o he p ocess and he selec ion o a sui able coagulan depends upon he ype o
subs ance emo ed, as well as he o e all wa e ea men p ocess [8]. Coagula ion may be combined
wi h o he physical, chemical o biological p ocesses.
Coagulan s a e p ima ily di ided in o he o ganic and ino ganic. Ino ganic coagulan s a e me al sal s,
o possibly in a hyd olyzed polyme o m. O ganic coagulan s a e a ailable in many ypes o subs ances
and c ea e long chains. Coagulan s may u he be di ided based on hei cha ge in o ca ion and anion
and, acco ding o hei o igin, di ided in o syn he ic o na u al.
Sal s o aluminum and i on appea o be mos comme cially success ul. Howe e , in ecen yea s,
polyme coagulan s a e also used [25], mos o en as auxilia y agen s used o inc ease he e iciency o
wa e ea men on he one hand and dec ease cos s on he o he .
Va ious coagulan s display di e ing e iciency in des abilizing indi idual pollu an s [18]. The e o e,
he p ope ies o he aw wa e mus be known in o de o es ablish he ype and olume o he necessa y
coagulan . The deg ee o concen a ion also a ec s he po ency o hei coagula ion.
Choice o coagulan s p ima ily depends upon he composi ion o he wa e ea ed, including i s pH,
empe a u e, oxida ion- educ ion po en ial, olume o subs ances suspended in he wa e , e c. The
choice o an op imal des abiliza ion agen mus always be made based on labo a o y es s, ideally by
es ing unde pa ial ope a ing condi ions. The size o loccules is he majo physical pa ame e a ec ing
he ea men p ocess. Ano he impo an p ope y is he esis ance o hese loccules o decomposi ion
in o smalle pa s. Smalle pa s dec ease he e ec i eness o he subsequen sepa a ion, as hey se le
mo e slowly han la ge pa icles o simila densi y [18].
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2. Ino ganic coagulan s, hei p ope ies and use
2.1. Me al coagulan s
Me al sal s a e p obably he mos equen ly used coagulan s in p ac ical wa e ea men . These a e
mos o en i alen compounds o aluminum and i on [8]. The e ec i eness o hei coagula ion is
a ec ed by dosage, he me hod o homogeniza ion, pH and he p ope ies o he subs ance emo ed [29].
Wa e empe a u e is also an essen ial ac o o hei unc ion [9], pa icula ly in he case o aluminum-
based coagulan s. Sa is ac o y coagula ion e ec i eness will no be achie ed a low empe a u es du ing
he colde pa o he yea , e en by inc eased doses o he agen .
Ino ganic coagulan s a e ypically dosed in highe concen a ions, esul ing in he p oduc ion o a
la ge olume o sedimen . A ce ain amoun o he me al ca ion o he espec i e sal emains in such
ea ed wa e . Me al coagulan esidues alone pose ce ain heal h and/o en i onmen al isks.
The disad an ages o ino ganic sal s, along wi h hei sensi i i y o seasonal changes in he physical
p ope ies o aw wa e (pH and empe a u e) as well as hei minimal e ec i eness in emo ing ine
pa icles, b ough a demand o di e en ypes o coagulan s. E ec i eness is imp o ed by
polyme iza ion o ino ganic coagulan s and hei use in wa e ea men [29].
Examples o me al coagulan s used in wa e ea men a e i on(III) sul a e, aluminum sul a e,
aluminum chlo ide, i on(III) chlo ide, as well as i anium disul ide and zi conyl chlo ide oc ahyd a e
[11].
2.1.1. P e-hyd olyzed me al coagulan s
To minimize he disad an ages o ino ganic coagulan s, hey may be hyd olyzed, c ea ing an ino ganic
polyme wi h imp o ed coagula ion p ope ies. Bu gene ally, we could say ha hey a e much mo e
e ec i e han he monome s o sal s om which hey a e p oduced. Among hei mos equen ly
men ioned bene i is a highe e ec i eness a lowe dosage. Because a smalle amoun o he coagulan
is used du ing he wa e ea men , a a lowe olume o sludge is p oduced [12], no do hey lea e as
many esidual ca ions in he ea ed wa e . Unlike hei monome s, hey unc ion wi hin la ge anges o
pH and a e less sensi i e o empe a u e [21]. These g oups o coagulan s include he equen ly used
polyaluminium chlo ide (PAC), as well as polyme s o i on(III) sul a e, polyaluminium silica e-chlo ide
and polyaluminium silica e sul a e.
3. O ganic polyme s as coagula ion agen s
Na u al o syn he ic mac omolecula wa e -soluble subs ances a e p ima ily used as des abilizing o
auxilia y agg ega ion agen s ( locculan s). The use o polyme s enables as e loccule sedimen a ion
( he o ma ion o loccules wi h s onge , dense s uc u e) and imp o ed il e abili y o he o med
suspension. Fu he , polyme locculan s dec ease he con en o o ganic subs ances, including u bidi y
as well as esidual coagulan , hus imp o ing he ul ima e quali y o he ea ed wa e . The use o hese
subs ances also enables a dec ease in dosage o ino ganic coagulan s.
Unlike me al coagulan s, o ganic polyme s unc ion wi hin a la ge pH ange, while ha ing no e ec
on he pH o he ea ed wa e . Thei use p oduces o ma ions ha a e la ge, compac , hick and display
good sedimen a ion p ope ies. Unlike me al coagulan s, o ganic polyme s lea e no me al ca ions in he
ea ed wa e . High e ec i eness is achie ed e en a ela i ely small doses o he coagulan agen ,
educing he p oduc ion o sludge [21]. The addi ion o an app op ia e polyme o an ino ganic coagulan
may signi ican ly imp o e i s e ec i eness in emo ing impu i ies, because i o ms la ge hicke
loccules wi h be e sedimen a ion p ope ies [4].
O ganic polyme s a e also e ec i e in emo ing small-size pa icles. They ha e a double e ec on
coagula ion – aside om cha ge neu aliza ion, hey also ha e a b idging e ec [7]. B idging is
speci ically mos no able in long molecules wi h la ge molecula weigh . Du ing he eac ion, he
polyme is bound o he pollu ing pa icle in se e al places and he loops o loose ends o he polyme
loa in space, eady o bind o ano he pa icle. Among o he ac o s, he e ec i eness o coagula ion is
de e mined by he dosage o he agen . Should he dose be oo low, a ce ain a io o impu i ies emain
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in he wa e . To he con a y, should he dose be oo high, he pollu an s a e dispe sed again and he
polyme s subsequen ly plug he il e s [3].
O ganic polyme s a e cu en ly used p ima ily as auxilia y coagula ion and loccula ion agen s [15],
al hough hey may also be used as p ima y coagulan s. Wide use o o ganic polyme s is p e en ed by
hei highe cos . Cu en ly, hey a e also a cen e o ocus ega ding possible heal h isks [30].
O ganic polyme s may p ima ily be di ided in o ei he syn he ic o na u al. Depending upon hei
o e all cha ge hey u he di ide in o ca ion, anion, and cha ge neu al. Syn he ic o ganic polyme s
(such as ca ion polyac ylamides) a e usually e y e icien coagulan s, bu unlike na u al polyme s, hey
end o be mo e cos ly, a e no biodeg adable and show ce ain dange ous p ope ies ( oxici y,
ca cinogenic p ope ies). Na u al o ganic polyme s a e somewha less e ec i e, bu a e biodeg adable,
no oxic and do no p oduce any seconda y pollu ion [21].
4. Na u al polyme s
O e ime, he e has been an e o o eplace classic coagulan s wi h na u al non- oxic and
en i onmen ally- iendly subs ances. The eason may be he high cos o limi ed a ailabili y o
commonly used coagulan s (aluminum sul a e, i on(III) sul a e, syn he ic polyme s e c.), he
equi emen o highly e ec i e doses o hese agen s, p oduc ion o an no able olume o sludge [12]
and he undesi able oxici y o he esidual coagulan s ha emain in he ea ed wa e .
The use o seeds o ce ain plan s ( o example Lens esculen a, Tama indus indica, Cyamoppsis
pso aloides) p esen s a cos -e ec i e, p ac ical and sui able solu ion o wa e ea men in de eloping
coun ies and beyond. A ce ain p epa a ion is necessa y in o de o use hese seeds, including d ying,
g inding and dilu ion wi h wa e .
4.1. Ca ion polyelec oly es
S ong ca ion polyelec oly es ha e a posi i e cha ge ega dless o he pH o he solu ion. To he
con a y, weak ca ion polyelec oly es ha e a posi i e cha ge only in an acidic en i onmen , as co e ed
[4]. Na u al coagulan s we e used long be o e chemical sal s. Bu in he end hey we e pushed o he
backg ound, as he use o sal s appea ed o be an easie and be e solu ion o ea ing d inking wa e . In
his ega d, wi h he inc easing necessi y o ea wa e in de eloping coun ies, na u al polyme s a e
e u ning o he cen e o a en ion [23]. Na u al polyme s a e easily a ailable, cos -e ec i e and easy
o handle.
Among he common na u al ca ion polyme s a e he polysaccha ides. The main ad an age o
polysaccha ides is ha hey a e biodeg adable, al hough hey a e he leas e ec i e and mus be used in
high concen a ions. A combina ion o syn he ic polyme s on o polysaccha ides o ms a b anched
polyme wi h imp o ed e ec i eness [4].
The mos equen ly used na u al ca ion polyme is chi osan. Chi osan is no wa e -soluble and mus
he e o e be dissol ed in a solu ion o a ca boxylic acid, such as ace ic acid [22].
Among o he na u al ca ion polyme s a e bo h s a ch and annins [23]. Tannins include many
seconda y me aboli es o plan o igins. They a e ound in ba k, lea es o seeds o plan s. A e y
p omising ca ion polyme among he annins is an ex ac ob ained om he seeds o he Mo inga
olei e a ee, con aining a ca ion p o ein. The main ad an age o his ex ac is ha i is no oxic o
ei he humans o animals, while se ing as a a he e ec i e coagulan . Fu he , i does no cause
p oblems wi h co osion and p oduces less sludge. Compa ed wi h aluminum o i on sal , he ex ac
shows a lesse e ec in emo ing u bidi y. T ea men o wa e wi h his ex ac inc eases he con en o
o ganic subs ances (pa icula ly o hophospha es and ni a es) in he ea ed wa e . These esidue
subs ances may wo sen he o ganolep ic p ope ies o wa e , such as colo , as e and odo [4, 16, 19].
O he op ions o wa e ea men use ex ac s om he seeds o he Eu opean ho se-ches nu
(Aesculus hippocas anum), English oak (Que cus obu ), Aus alian oak (Que cus ce is), No he n ed
oak (Que cus ub a) and swee ches nu (Cas anea sa i a). The concen a ion o he ob ained ca ion
p o eins a e app oxima ely en- imes less han in he case o Mo inga olei e a, ye , despi e his, good
coagula ion p ope ies we e con i med [5, 24].
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O ganic ca ion polyme s may be used bo h as auxilia y coagula ion- loccula ion agen s and as
p ima y coagulan s. Coagula ion p ope ies o ca ion polyme s used as p ima y coagulan s may
addi ionally be imp o ed by he addi ion o insoluble solid subs ances such as clay o me al oxides (i on,
aluminum and manganese oxides). Fo example, chi osan alone has a low e iciency in emo ing
u bidi y and colo , bu when mixed wi h ben oni e, i s e ec i eness imp o es syne gically. Solid
pa icles unc ion as so ben s o NOM and, simul aneously, as a co e o condensing a NOM-polyme
complex.
4.1.1. Mo inga olei e a ee seeds
Mo inga olei e a is an oil-p oducing ee o iginally om No he n India (Himalayas), cu en ly sp ead
ac oss opical egions wo ldwide. The plan is no able o i s high esis ance o d ough . Mo inga seeds
a e composed o app oxima ely 31% p o ein, 18% saccha ides and 37% a s. Powde om g ound seeds
con ains soluble p o eins capable o loccula ing u bidi y con ained in wa e . The solubili y o hese
p o eins is inc eased wi h he con en o sal s in wa e . Sodium chlo ide (NaCl) is hus some imes used
du ing labo a o y p epa a ions o he coagula ion agen . The coagula ion e ec o he ex ac p epa ed
wi h he use o sal shows g ea e e ec i eness han agen s p epa ed using only ap o dis illed wa e .
S udies p o e ha , in he case o Mo inga olei e a, adso p ion, cha ge neu aliza ion and o ma ion o
polyme b idges be ween pa icles a e he p edominan mechanisms o emo ing u bidi y [13, 26].
The p ocesses o p epa ing a coagula ion agen om Mo inga olei e a seeds may di e . None heless,
he polyelec oly e used o wa e ea men is in mos cases ob ained by g inding d ied seeds om he
ee and mixing hem wi h wa e . The p o eins wi h p edominan ly posi i e cha ge on hei su ace a e
hus ans e ed in o he wa e solu ion. A ypical dose o p epa a ion anges om 10 o 50 g ams o
g ound seeds pe li e o wa e . The suspension o seeds wi h wa e is shaken in ensi ely o allow he
de elopmen o molecules, ollowed by il a ion. The dosage o coagula ion agen anges om 75-200
mg·l-1 depending on he p ope ies (pa icula ly u bidi y) o ea ed wa e [16].
In case cooling o he suspension is possible, i s e ec is ex ended by up o one week. O he wise i
is necessa y o p epa e a esh suspension daily. The e ec o Mo inga olei e a ex ac in emo ing
u bidi y om wa e dec eases by ex ending he s o age pe iod o he p epa ed coagula ion agen [26].
4.1.2. Chi osan
Chi osan is a subs ance insoluble in mos o ganic sol en s. Howe e , i dissol es in bo h o ganic and
ino ganic acids (such as ace ic acid, o mic acid, e c.). This polysaccha ide is p oduced h ough an
alkaline deace yla ion o chi in, which is ound in he ou e shells o c us aceans, insec s and gas opods,
as well as wi hin he cellula walls o yeas and ce ain ungi. Chi in and chi osan may be p oduced om
he was e p oduc s o p ocessing ma ine animals [28]. Chi osan p oduced o he pu poses o wa e
ea men is ypically p epa ed using ace ic acid whe e i is a subjec o hyd olysis.
Chi osan is a ca ion polyelec oly e used o he educ ion o wa e u bidi y [20], so p ion o me al
i ons, as well as emo al o o ganic pollu ion. Des abiliza ion p ima ily akes place h ough he
mechanism o cha ge neu aliza ion. Chi osan is a biodeg adable subs ance and i s use in wa e ea men
is he e o e mo e en i onmen ally iendly han commonly used coagulan s. The equen use o chi osan
is inc easing in ecen yea s. This subs ance is used o example in No way, whe e i was selec ed as a
coagulan in se e al wa e ea men acili ies, used ei he exclusi ely o in a combina ion wi h me al-
based coagulan s [20].
Chi osan has many ad an ages in compa ison wi h adi ional coagulan s ( locculan s). Among hem
a e e ec i eness in low doses, success in he educ ion o chemical oxygen demand (COD), he abili y
o emo e me al ions, he o ma ion o la ge ( oluminous) loccules wi h highe sedimen a ion a es,
biological deg adabili y, majo e ec in he emo al o algae and suspended pa icles, an i-bac e ial
e ec s and ze o o ma ion o seconda y pollu ion [1]. Chi osan is capable o binding bo h a s and
me als, including a senic, molybdenum, cadmium, ch omium, lead and cobal [14].
Many s udies ha e been conduc ed ega ding he use o chi osan as a single coagulan o in
combina ion wi h o he agen s in emo ing u bidi y [2, 20].
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Chi osan, as a posi i ely cha ged polyme wi h long chains, is able o coagula e nega i ely cha ged
and inely dispe sed colloidal pa icles h ough adso p ion, cha ge neu aliza ion, hyd ophobic e ec
o h ough he o ma ion o polyme b idges. Conside able sa ings in e ms o he olume o agen s
used may be achie ed by using such na u al coagulan s in combina ion wi h he mo e classic o ms,
esul ing in addi ional cos educ ions o sludge emo al, as i is p oduced in smalle quan i ies [1].
A coagula ion ja es was [20] pe o med using aw wa e om he E ans Lake in Cali o nia,
compa ing he e ec s o chi osan, aluminum sul a e and i on(III) chlo ide. Upon pe o ming he
coagula ion, sedimen a ion and il a ion using il a ion pape , he esul ing alues o u bidi y educ ion
we e 98.8% (aluminum sul a e), 96.9% (chi osan) and 98.9% (i on(III) chlo ide). The emo al o
coli o m bac e ia was mos e ec i e wi h i on(III) chlo ide and leas e ec i e using chi osan (upon
op imal doses o coagulan s and pH alues). Chi osan was he mos e ec i e o all agen s used in
emo ing colo and also caused only mino wa e so ening (by 22 %). In he case o chi osan, excessi e
doses caused e-s abiliza ion o he dispe sion. Op imum pH mus be kep in mind when ea ing aw
wa e in o d inking wa e .
5. Me hods
Ou labo a o y esea ch ocused on es ablishing he e ec o selec ed na u al polyme coagulan s
o igina ing om he seeds o he Mo inga olei e a ee and chi osan. The e ec i eness o bo h hese
agen s was compa ed o a con en ional coagulan – aluminum sul a e (50% solu ion).
5.1. Raw wa e
Raw su ace wa e sampled om he S a ka Ri e was used in he labo a o y es . The esea ch used
a olume o app oxima ely 30 li e s. A he ime o es ing, he aw wa e had a empe a u e o 18.2° C,
u bidi y 8.92 (NTU) and a pH alue o 7.85. The pH alue was adjus ed using sul u ic acid o a
alue o 7.5. This alue was s ipula ed wi h ega d o p e ious es s wi h aluminum sul a e.
Ou esea ch was pe o med wi h a s anda d ja es using a blending column wi h a paddle blende .
Tu bidi y was used as he indica o o e ec i eness. Aside om u bidi y, he pa ame e s o wa e
empe a u e and pH we e also moni o ed. P ocess pa ame e s we e iden ically main ained o all h ee
agen s wi h he pa icula goal o e i ying whe he o he condi ions o an ac ual applica ion p ocess
would equi e adjus men upon changing he coagulan .
Fas blending was i s pe o med o a du a ion o 2 minu es a he a e o 150 pm, ollowed by
slow blending a 40 pm o 20 minu es. Subsequen ly, a 60-minu e undis u bed sedimen a ion
comple ed he p ocess.
5.2. Mo inga olei e a seeds
A coagulan was ob ained by p ocessing 9 pieces o Mo inga olei e a seeds and used in a se ies o
es s. The whi e ounded co es unde he peel we e pul e ized in a mo a and pes le o powde o m.
The amoun ob ained was ans e ed o a po celain bowl and weighed. The weigh o he agen
amoun ed o 1.262 g.
A coagulan was p epa ed by mixing he powde om he seeds wi h 306 ml o d inking wa e ( he
addi ional 6 ml we e added due o loss o wa e in he subsequen il a ion by being abso bed by he
clo h). The suspension was in ensi ely shaken o he du a ion o 5 minu es and subsequen ly il e ed
h ough a clean co on clo h o sepa a e la ge pa icles. A dose anging om 2.5 o 42.5 ml o he
solu ion was added o he indi idual essels, ep esen ing 20.6 o 350.9 mg o powde .
5.3. Chi osan
The e ec o chi osan in emo ing u bidi y was examined las . The agen was used in he o m o 25 g
o whi e powde – chi osan o igina ing om sh imp shells. Chi osan was dissol ed in ace ic acid (99%),
ha was subsequen ly mixed wi h 32.6 ml o d inking wa e and used in he o m o a solu ion a he
concen a ion CH3COOH 1 mol·dm-3. Subsequen ly, 0.1 g o chi osan was added o he acid solu ion.
This o med a liquid o a a he hick consis ency ha was u he dilu ed wi h d inking wa e o a 100
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ml olume. This coagulan (100 mg o chi osan in 100 ml o he agen ) was dosed o he essels in an
op imiza ion ja es .
6. Resul s
Ou esea ch ocused on he compa ison o e ec i eness in educing u bidi y a e applying h ee
coagulan s used in wa e ea men . The selec ed coagulan s we e aluminum sul a e commonly used as
a con en ional coagulan , as well as chi osan and Mo inga olei e a as al e na i es. An op imiza ion ja
es was pe o med wi h he es ed aspec being u bidi y. The esea ch was ca ied ou in he labo a o y
o ma as a se ies o ja es s.
6.1. Aluminum sul a e
Aluminum sul a e was selec ed as ep esen a i e o con en ional agen s used in wa e ea men . The
pu pose o i s use in his esea ch s udy is p ima ily as a compa ison wi h he o he wo agen s ha a e
no as equen ly used and p ac ically ne e in he Czech Republic.
The au ho s o his a icle ha e ex ensi e p e ious expe ience wi h his coagulan in ela ion o aw
wa e used in his esea ch. As is appa en om p e ious ja es s, he op imum pH o u bidi y emo al
is 7.5, he a e o he i s phase o mixing is 150 pm ( o he du a ion o 2 minu es) and he a e o
he second phase o coagula ion is 40 pm ( o 20 minu es). The same alues we e also used o he
compa ison es s wi h he o he agen s. The esul s a e appa en om Table 1 and Figu e 1.
Table 1. Tu bidi y emo al – aluminum sul a e
Sample
Dosage
Tu bidi y
Tu bidi y
emo al
Aluminum sul a e
Al
@ 60 min
[ml]
[mg]
[mg]
[NTU]
[%]
1
0.050
65.5
2.6
3.56
60.09
2
0.075
98.3
3.9
2.13
76.12
3
0.100
131.0
5.2
0.94
89.46
4
0.115
150.7
6.0
0.46
94.84
5
0.130
170.3
6.8
0.65
92.71
6
0.175
229.3
9.2
0.85
90.47
7
0.220
288.2
11.5
1.00
88.79
8
0.265
347.2
13.9
1.26
85.87
The lowes measu ed alue o u bidi y a e six y minu es o sedimen a ion was 0.46 NTU in case
o 0.115 ml dose o aluminum sul a e. The dec ease o NTU by 8.46 shows emo al o u bidi y a 94.84
%. The wo s esul was eco ded a doses o 0.050 ml – he alue o he u bidi y 3.56 ZF and u bidi y
emo al a only 60.09 %.
5 h In e na ional Con e ence on New Ad ances in Ci il Enginee ing (ICNACE 2019)
IOP Con . Se ies: Ma e ials Science and Enginee ing 800 (2020) 012032
IOP Publishing
doi:10.1088/1757-899X/800/1/012032
7
Figu e 1. Tu bidi y emo al – aluminum sul a e
A la ge numbe o disce nable loccules o med when using aluminum sul a e, e en in he ea ly s age
o as blending. The mos agg ega es we e o med in he wa e o which mos o he agen was dosed.
Upon 60 minu es o sedimen a ion he loccules se led a he bo om, whe e hey o med sludge o a
ligh b own colo . The op imal dose o aluminum sul a e 150.7 mg·l-1 managed o educe he u bidi y
by 94.84 % o a alue o 0.46 NTU.
6.2. Mo inga olei e a
The coagulan ob ained om Mo inga olei e a seeds by he me hod desc ibed abo e was used o ea
wa e o iden ical quali y as abo e and also wi hin a labo a o y-scale es . The same pa ame e s we e se
o he coagula ion es . The o ma ion o small ligh -colo ed loccules in he ea ed wa e was eco ded
as ea ly as he slow blending s age.
The amoun o hese small obse ed clus e s g ew wi h inc eased amoun s o he coagula ion agen .
Howe e , he loccules emained suspended in he olume o he essels h oughou he en i e phase
and we e only pa ly sedimen ed. Only a po ion o he loccules se led on he bo om, along wi h
sedimen . Despi e his, lowe le els o u bidi y we e measu ed han p io o wa e ea men . Resul s
a e shown in Figu e 2.
5 h In e na ional Con e ence on New Ad ances in Ci il Enginee ing (ICNACE 2019)
IOP Con . Se ies: Ma e ials Science and Enginee ing 800 (2020) 012032
IOP Publishing
doi:10.1088/1757-899X/800/1/012032
8
Figu e 2. Tu bidi y emo al – Mo inga olei e a
As is appa en om he abo e esul s, he mos e ec i e dose o Mo inga olei e a o u bidi y
emo al was 164.6 mg. The ini ial u bidi y alue was educed o 1.60 NTU, ep esen ing he emo al
o 82.04% o u bidi y. The lowes alue o u bidi y emo al was measu ed a he dose o 20.6 mg o
Mo inga olei e a. He e, he u bidi y alue only dec eased by 0.01 NTU.
When using Mo inga olei e a, he loccules o med du ing coagula ion we e o pale colo . They we e
isible o he naked eye only in he second phase o blending. The sedimen a ion o he agg ega es ook
place e y slowly. E en a e one hou o sedimen a ion, he e we e no appa en changes. The op imum
dose was 164.6 mg·l-1, which is he la ges in compa ison wi h bo h aluminum sul a e and chi osan.
Be e esul s o u bidi y emo al could appa en ly be achie ed by p olonging he sedimen a ion pe iod
o using il a ion.
6.3. Chi osan
The nex coagula ion es s we e using chi osan as an agen – also unde he same condi ions. The
o ma ion o loccules in aw wa e was isible om app oxima ely he middle o he slow blending
phase. The smallagg ega es had a ligh b own colo and se led mo e quickly han he agg ega es using
Mo inga olei e a. Al hough mos loccules se led a e 60 minu es o sedimen a ion, a po ion o he
loccules emained suspended. As ega ds u bidi y emo al, he esul ing alues a e shown in Figu e 3.