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Implementation and optimization of a sequential injection analysis ( SIA ) system by UV - Visible spectroscopy

Abstract

Due to the increasing environmental awareness of society and administration, a great number of regulations became effective over the last years in order to preserve natural resources restricting and limiting industrial waste, especially when spills affect aqueous systems. This fact has contributed to the development of a large amount of research programs to come across new methods and processes to monitor and reduce contaminants present in wastewater. Among the variety of contaminants present in industrial effluents, heavy metals are the most hazardous as this compounds are biomagnified and can reach human organism. One of the methods developed for reducing heavy metal concentration in wastewater is biosorption. Biosorption process monitoring has led to the development of sensor arrays or electronic tongues. These kinds of sensors require exhaustive training through the analysis of huge sets of standards, which is time, effort and reagent consumptive. This project is addressed on the optimization of a Sequential Injection Analysis (SIA) prototype built to prepare automatically random generated known training standards and monitor bioprocess absorption to model sensor’s response. In this phase of optimization a miniature spectrometer is assembled to the SIA tubing to monitor flow response in real time of a colorant solution. Spectroscopic analysis also allows monitoring traces of reagent remaining on the system. Calibration and cleaning routines will be designed to ensure reproducibility. Moreover, automatic preparation of standards will be discussed.

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Implementation and optimization of a sequential injection analysis ( SIA ) system by UV - Visible spectroscopy

Author: Solís García, Carlos
Publisher: Universitat Politècnica de Catalunya
Year: 2016
Source: https://upcommons.upc.edu/bitstream/2117/98505/1/Carlos_Solis_Memoria_TFG_DEFINITIVO.pdf
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 1
Abs ac
Due o he inc easing en i onmen al awa eness o socie y and adminis a ion, a g ea
numbe o egula ions became e ec i e o e he las yea s in o de o p ese e na u al
esou ces es ic ing and limi ing indus ial was e, especially when spills a ec aqueous
sys ems. This ac has con ibu ed o he de elopmen o a la ge amoun o esea ch
p og ams o come ac oss new me hods and p ocesses o moni o and educe con aminan s
p esen in was ewa e .
Among he a ie y o con aminan s p esen in indus ial e luen s, hea y me als a e he mos
haza dous as his compounds a e biomagni ied and can each human o ganism. One o he
me hods de eloped o educing hea y me al concen a ion in was ewa e is bioso p ion.
Bioso p ion p ocess moni o ing has led o he de elopmen o senso a ays o elec onic
ongues. These kinds o senso s equi e exhaus i e aining h ough he analysis o huge
se s o s anda ds, which is ime, e o and eagen consump i e.
This p ojec is add essed on he op imiza ion o a Sequen ial Injec ion Analysis (SIA)
p o o ype buil o p epa e au oma ically andom gene a ed known aining s anda ds and
moni o biop ocess abso p ion o model senso ’s esponse.
In his phase o op imiza ion a minia u e spec ome e is assembled o he SIA ubing o
moni o low esponse in eal ime o a colo an solu ion. Spec oscopic analysis also allows
moni o ing aces o eagen emaining on he sys em.
Calib a ion and cleaning ou ines will be designed o ensu e ep oducibili y. Mo eo e ,
au oma ic p epa a ion o s anda ds will be discussed.
p. 2 Repo
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 3
Table o con en s
ABSTRACT ___________________________________________________ 1
TABLE OF CONTENTS _________________________________________ 3
1. GLOSSARY ______________________________________________ 7
2. PREFACE ________________________________________________ 9
2.1. P ojec backg ound ........................................................................................ 9
2.2. Incen i e ......................................................................................................... 9
3. INTRODUCTION __________________________________________ 10
3.1. Objec i es ..................................................................................................... 10
3.2. P ojec Scope ............................................................................................... 10
4. FLOW ANALYSIS _________________________________________ 11
4.1. Wha is low analysis? .................................................................................. 11
4.2. Analy ical p ocedu e au oma ion .................................................................. 11
4.3. Flow Injec ion Analysis (FIA) ........................................................................ 12
4.4. Sequen ial injec ion analysis (SIA) ............................................................... 13
5. ULTRAVIOLET-VISIBLE SPECTROSCOPY ____________________ 15
5.1. An o e iew on spec oscopy ....................................................................... 15
5.1.1. Elec omagne ic adia ion ................................................................................ 15
5.1.2. Radia ion In e ac ion wi h ma e ..................................................................... 16
5.2. Bee – Lambe – Bougue Law ................................................................... 16
5.2.1. Basic de ini ions .............................................................................................. 16
5.2.2. Bee ’s Law ...................................................................................................... 17
5.2.3. Limi a ions o Bee ’s Law ................................................................................ 18
5.3. Spec oscopic de ec o s ............................................................................... 18
5.4. Sample Cells ................................................................................................ 20
6. SEQUENTIAL INJECTION ANALYSIS (SIA) PROTOTYPE ________ 21
6.1. Mul iBu e e 2S ............................................................................................. 22
6.2. Main Mani old ............................................................................................... 23
6.2.1. Holding Coil ..................................................................................................... 23
6.2.2. Mul i al e ........................................................................................................ 23
6.2.3. 3-way al es ................................................................................................... 24
6.2.4. Mixing Cell ...................................................................................................... 25
6.2.5. Debubble ....................................................................................................... 25
p. 4 Repo
6.3. In e ace: LabVIEW ...................................................................................... 25
6.3.1. Sc ip s and expe imen s................................................................................... 26
6.3.2. P og amming sc ip s ........................................................................................ 26
6.3.3. Execu ing sc ip s and expe imen s................................................................... 28
7. FLAME S SPECTROMETER ________________________________ 30
7.1. Componen s................................................................................................. 30
7.1.1. De ec o ........................................................................................................... 30
7.1.2. Sample cell ...................................................................................................... 31
7.1.3. Ligh sou ce ..................................................................................................... 31
7.1.4. Op ic ib e connec o s ...................................................................................... 32
7.2. OceanView so wa e .................................................................................... 32
7.2.1. S a ing OceanView ......................................................................................... 32
7.2.2. Acquisi ion pa ame e s..................................................................................... 33
7.2.3. Re e ence and da k spec um .......................................................................... 34
7.2.4. Wa eleng h selec ion ............................................................................ 35
7.2.5. S o ing da a ............................................................................................ 36
8. EXPERIMENTAL PROCEDURE _____________________________ 37
8.1. Reagen s ...................................................................................................... 37
8.2. Calib a ion Me hod ....................................................................................... 38
8.2.1. Ex e nal Calib a ion .......................................................................................... 39
8.2.2. In e nal Calib a ion ........................................................................................... 39
8.3. S anda ds p epa a ion ................................................................................. 39
8.3.1. Phenol ed s ock solu ion ................................................................................. 39
8.3.2. Sodium hyd oxide solu ion 0.1 M ..................................................................... 40
8.3.3. Sodium hyd oxide ca ie solu ion .................................................................... 40
8.3.4. S anda d solu ions ........................................................................................... 40
8.4. De ec ion sys ems cha ac e iza ion pa ame e s .......................................... 40
8.4.1. Limi o de ec ion (LOD) ................................................................................... 40
8.4.2. Limi o quan iza ion (LOQ) .............................................................................. 41
8.5. Dispe sion coe icien ................................................................................... 41
9. RESULTS AND DISCUSSION _______________________________ 43
9.1. Phenol ed cha ac e iza ion ......................................................................... 43
9.1.1. P elimina y es s .............................................................................................. 43
9.1.2. Spec ome e compa ison ................................................................................ 45
9.1.3. Sample deg ada ion ......................................................................................... 46
9.1.4. Selec ing he se o s anda ds .......................................................................... 47
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 5
9.2. Ex e nal calib a ion ....................................................................................... 48
9.2.1. Sui able low a es ........................................................................................... 48
9.2.2. SIA and Mul i al e p iming .............................................................................. 48
9.2.3. De e mina ion o minimum olume .................................................................. 49
9.2.4. Calib a ion cu es ........................................................................................... 51
9.2.5. Limi o De ec ion and Limi o Quan i ica ion .................................................. 53
9.2.6. Peak Cu es ................................................................................................... 54
9.2.7. Hyd aulic hys e esis ........................................................................................ 54
9.2.8. Cleaning he sys em........................................................................................ 55
9.3. In e nal calib a ion ........................................................................................ 55
9.3.1. Mixing cell p elimina y es s ............................................................................ 55
9.3.2. Calib a ing om 20 ppm s anda d ................................................................... 57
9.3.3. Calib a ing om s ock solu ion ........................................................................ 57
9.3.4. Calib a ing h ough successi e dilu ions ......................................................... 58
9.3.5. Cleaning he mixing cell .................................................................................. 59
10. BUDGET ________________________________________________ 61
11. ENVIRONMENTAL CONSIDERATIONS _______________________ 64
CONCLUSIONS ______________________________________________ 65
FUTURE RECOMMENDATIONS _________________________________ 66
ACKNOWLEDGEMENTS _______________________________________ 67
BIBLIOGRAPHY ______________________________________________ 68
Bibliog aphic e e ences ........................................................................................ 68
Addi ional bibliog aphic e e ences ........................................................................ 69
TABLE OF FIGURES __________________________________________ 71
TABLE OF EQUATIONS _______________________________________ 74
TABLE INDEX _______________________________________________ 75

Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 7
1. Glossa y
A g: A e age
C: Closed
DQA: Da a Acquisi ion Sys em
FIA: Flow Injec ion Analysis
LOD: Limi o De ec ion
LOQ: Limi o Quan iza ion
NO: No mally open
NC: No mally closed
O: Open
PR: Phenol Red
S/N: Signal o noise a io
SIA: Sequen ial Injec ion Analysis
UV: Ul a iole
UV-Vis: Ul a iole Visible
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 9
2. P e ace
2.1. P ojec backg ound
The p esen Deg ee Final P ojec is a con ibu ion o he esea ch p ojec : “Desa ollo de
Tecnología a Escala Pilo o pa a Depu ación de Aguas Con aminadas con Iones Me álicos
median e Residuos Ag oalimen a ios (TECMET)” unded by Minis e io de de Economía y
Compe i i idad, Mad id, 2013-2015. P ojec CTM2012-37215-C02-02 and o he esea ch
p ojec “SINTESIS VERDE DE NANOPARTICULAS METALICAS A PARTIR DE AGUAS
ACIDAS DE MINA Y EXTRACTOS DE RESIDUOS AGROALIMENTARIOS” unded by
Minis e io de Economía y Compe i i idad, Mad id and FEDER unds, EU, 2016-2018. P ojec
CTM2015-68859-C2-2-R (MINECO/FEDER).
2.2. Incen i e
This p ojec ’s incen i e is se ing he ope a ion condi ions and ob aining ep oducible ou ines
o elabo a e au oma ically s anda ds au oma ically by using a s i e cell implemen ed in he
SIA p o o ype.
The e o e, low UV-Visible spec oscopy will be u ilised o moni o colo an eagen s eams,
in o de o op imize he SIA pa ame e s.
Pág. 16 Repo
magni ude. I is common o di ide he elec omagne ic spec um in o di e en egions as
shown in Figu e 5-2
Figu e 5-2 Elec omagne ic spec um (Ha ey 2009)
The impo an egions o UV- isible spec oscopy a e ul a iole and isible spec ums.
5.1.2. Radia ion In e ac ion wi h ma e
Acco ding o (Ha ey 2009), he phenomena o abso p ion is p oduced because o he
a enua ion o a adia ion’s in ensi y a selec ed wa eleng hs when a beam goes h ough a
sample. Thus, some o he pho ons a e abso bed by a sample and hei ene gy is ans e ed
o elec ons, p omo ing hem o a highe ene gy exci ed s a e. Fo molecules, he ene gy
equi ed o elec onic exci a ion lies in he isible and UV anges. Molecules possess se e al
possible o a ional and ib a ional s a es, so he abso p ion is p oduced o e a wide ange o
wa eleng hs, which is called an abso p ion band.
Spec oscopic measu emen is possible only i he pho ons in e ac ion leads o a change in
one o mo e o he cha ac e is ic p ope ies o elec omagne ic adia ion: ene gy, eloci y,
ampli ude, equency among o he s.
5.2. Bee – Lambe – Bougue Law
5.2.1. Basic de ini ions
(Robinson e al. 2005) de ine he adian powe P o a beam o ligh as he ene gy o he
beam pe second pe uni a ea. A ela ed quan i y is he in ensi y I which is he powe pe uni
solid angle. Bo h powe and in ensi y a e ela ed o he squa e o he ampli ude o he ligh
wa e, and he abso p ion laws can be w i en in e ms o ei he powe o in ensi y.

Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 17
When ligh passes h ough an abso bing sample, he in ensi y o he ligh eme ging om he
sample is dec eased. Calling I0 he in ensi y o he beam be o e en e ing he sample, and I
he in ensi y a e passing h ough, he ansmi ance T is de ined as he a io o I o I0.
T ansmi ance is he ac ion o he o iginal ligh ha passes h ough he sample. To s udy he
quan i a i e abso p ion o adia ion is use ul o de ine ano he quan i y, he abso bance A
whe e
Equa ion 5-2
When no ligh is abso bed, I = I0 and A = 0.
5.2.2. Bee ’s Law
Following a simila app oach o (Ha ey 2009), when elec omagne ic adia ion passes
h ough an in ini esimally hin laye o sample o hickness dx, i expe iences a dec ease in i s
in ensi y o dI, as shown in Figu e 5-1
Figu e 5-3 Bee - Lambe law ac o s modi ied om (Ha ey 2009)
The ac ional dec ease in in ensi y is p opo ional o he sample’s hickness and he analy e
concen a ion C. Acco ding o (Robinson e al. 2005), he p opo ional ela ionship be ween
sample hickness ( he pa hleng h) and abso bance a cons an concen a ion was disco e ed
by P. Bougue in 1729 and J. Lambe in 1760.
The e o e, he in ensi y d op can be exp essed as
Equa ion 5-3
Whe e α is a p opo ionali y cons an . In eg a ing he le side o Equa ion 5-1 o e he en i e
sample
Pág. 18 Repo
Con e ing om ln o log, and subs i u ing in Equa ion 5-2 esul s in
Equa ion 5-4
Whe e b is he pa hleng h, usually in cm, and ε is he mola abso p i i y coe icien , which has
uni s o cm-1 M-1. The mola abso p i i y is p opo ional o he p obabili y ha he analy e
abso bs a pho on o a gi en ene gy. As a esul , ε depends on he wa eleng h o he
abso bed pho on.
Equa ion 5-4 es ablishes he linea ela ionship be ween abso bance and concen a ion, and
is mo e commonly known as he Bee -Lambe law, o Bee ’s law.
5.2.3. Limi a ions o Bee ’s Law
Bee ’s law wo ks bes when he concen a ion is less han abou 0.01 M. A high
concen a ions o analy e, i s indi idual pa icles no longe beha e independen ly o each
o he and s a in e ac ing be ween hemsel es. In his case in e ac ions may change
analy e’s abso p i i y.
Ano he impo an ac o is ha abso p i i y depends on he samples’s e ac i e index, which
a ies wi h he analy e’s concen a ion. The e o e in low sys ems, i is signi ican choosing
he igh ca ie solu ion and eagen medium o a oid adding u he e o .
Some ins umen a ion limi a ions also induce de ia ion om Bee ’s law as (Ha ey 2009)
sugges ed. The i s limi a ion is ha Bee ’s law assumes ha he adia ion eaching he
sample is o a single wa eleng h. Howe e , wa eleng h selec o s pass adia ion wi h a small
e ec i e bandwid h.
The second con ibu ion is due o impe ec ions in he wa eleng h selec o ha allows ligh o
en e he ins umen and each he de ec o wi hou passing h ough he sample. This
phenomenon is called S ay Radia ion. Inside his de ini ion i can also be included he
adia ion no being isola ed p ope ly om he de ec o . S ay adia ion minimisa ion will be
discussed la e on.
5.3. Spec oscopic de ec o s
In his sec ion a small o e iew on spec oscopic de ec o s will be explained. Speci ic
in o ma ion abou he equipmen u ilised on his p ojec will be gi en in he nex sec ion.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 19
Equipmen minia u isa ion has led o a new e a o modula spec ome e s.(Ha ey 2009)
classi ies hese spec ome e s as Diode A ay Spec ome e s.
Con en ional ins umen s ha e a single de ec o , so only a wa eleng h a a ime can be
moni o ed. The use o many pho odiodes ins ead o a single pho omul iplie esul s in an
a ay o de ec o s ha can eco d an en i e spec um in less han a second.
Figu e 5-4 Flame-S de ec o o e iew (A e 2015)
Figu e 5-4 is an o e iew o he de ec o u ilised in his p ojec . As shown in (A e 2015), ligh
a i ing om he sample e lec s om a mi o as a collima ed beam owa d he g a ing,
whe e i is dispe sed. Radia ion is hen again e lec ed o m a ocusing mi o , which di ec s
adia ion one wa eleng h apa o he de ec o a ay.
One o he ad an ages (Ha ey 2009) epo s o diode a ay spec ome e s is he speed o
da a acquisi ion, which allows o collec se e al spec a o a single sample. Indi idual
spec a a e added and a e aged o ob ain he inal spec um. This signal a e aging imp o es
a spec um’s signal- o-noise a io, smoo hing he da a. Figu e 5-5 shows he e ec s o signal
a e aging.
Figu e 5-5 Le : Non a e aged spec a. Righ : 15 scans a e aged
The signal- o-noise a io (S/N) a e n scans is desc ibed by ¡E o ! No se encuen a el
o igen de la e e encia., whe e Sx/Nx is he signal- o-noise a io o a single scan.
Pág. 20 Repo
Equa ion 5-5
Howe e , he p incipal disad an age (Ha ey 2009) has ound o hese spec ome e s is ha
he e ec i e bandwid h pe diode, on a pho odiode a ay, is nea ly an o de o magni ude
la ge han ha o a high quali y monoch oma o .
5.4. Sample Cells
Samples a e usually in he liquid o solu ion s a e, and a e placed in cells cons uc ed wi h
UV-Visible anspa en ma e ials. A sample cell mus achie e wo majo equi emen s.
I ’s i ial o assume ha cell’s ma e ial mus le all he adia ion o each he sample and
pass h ough i . Despi e his condi ion, no all ma e ials beha e he same way. Fo adia ion
in he isible ange (400-700 nm wa eleng h), ma e ials such as qua z, glass and plas ic a e
app op ia e. When wo king a sho e han 300 nm wa eleng hs qua z o used-silica cells
mus be used. O he ma e ials show a signi ican abso p ion in his ange and in e e e in
measu emen s.
The o he equi emen he cell mus accomplish is chemical compa ibili y. Ma e ial o he cell
mus be chosen o esis he chemical a ack o he u ilised sol en s and samples. (FIAlab
2015) p o ides a able o compa ibili y o SMA-Z-Cells.
When Bee ’s law was de ined in 5.2.2, Equa ion 5-4¡E o ! No se encuen a el o igen
de la e e encia. in oduced he a iable pa hleng h b. Pa hleng h is di ec ly p opo ional o
he analy e’s abso bance, hence inc easing he pa hleng h will yield o highe abso bance,
which is use ul when analyzing dilu ed solu ions o gas samples.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 21
6. Sequen ial injec ion analysis (SIA) p o o ype
The p o o ype consis s in h ee pa s: he au obu e e, he main mani old and a compu e . A
schema ic iew o he whole sys em is ep esen ed in Figu e 6-1.
Figu e 6-1 SIA schema ic modi ied om (Núñez 2016)
A compu e is equi ed o command bo h he au obu e e and he elemen s on he main
assembly h ough he u iliza ion o he p og am called LabVIEW (Na ional Ins umen s). Da a
acquisi ion (DQA) om he senso a ay can also be con olled wi h his so wa e. Howe e ,
DQA and senso s will no be discussed in his p ojec .
Al hough he spec ome e is ex e nal o he p o o ype, i has been added o he schema ic. I
is also con olled by he compu e bu uses i s own so wa e de ailed in 7.2.
Figu e 6-2 displays he comple e assembly in he labo a o y.

Pág. 22 Repo
Figu e 6-2 SIA assembly
6.1. Mul iBu e e 2S
C ison Mul ibu e e 2S is he pumping de ice o he p o o ype. I can ope a e wo sy inges
simul aneously, hough only one has been used in his p ojec ( o al olume o 5 ml).
Ope a ion condi ions o he sys em will be explained la e on in sec ion 8.
The u ilisa ion o a mul ibu e e accomplishes one o he mos ele an SIA sys ems
equi emen s. SIA sys ems mus be able o gua an ee bidi ec ional low mo emen . The
bu e e has a 40000 s eps mo o ha mo es a pis on up o down. Tha means he minimum
olume i can mo e is 1/40000 o he sy inge o al olume.
When u ning on he bu e e he mo o ac i a es lowe ing he pis on o he bo om o he
sy inge, illing i , which is why i is ecommended o always ensu e he e’s wa e o a oid
in oducing ai in o he sys em.
Figu e 6-3 Mul iBu e e 2S
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 23
In igu e Figu e 6-3 he cu en display o he bu e e is shown. On he igh side, he 5 ml
sy inge u ilised o he pa ame e iza ion o he sys em. (Núñez 2016) ound ha lesse
olume sy inges we e mo e accu a e. Each sy inge has wo inpu /ou pu al es. The igh
one is connec ed o a dis illed wa e ank and he le one, o he holding coil. Commonly, he
igh en y is named Ou and he le en y is named In.
6.2. Main Mani old
6.2.1. Holding Coil
I s unc ion is o a oid ha any eagen a i es o mul ibu e e’s sy inges ha could
con amina e he SIA sys em. When a eagen mus be inse ed in o he sys em he bu e e
has o lowe he plunge , aspi a ing liquid om he coil and allowing he en y o eagen s
om he mul i al e po s.
The holding coil is made om 1 mm in e nal diame e PTFE ube coiled o a solid plas ic od
in o de o keep a secu i y and con en ion olume o s o e eagen s and p o ec he pumping
de ice.
(de Lamo 2014) de e mines coil’s olume om he ollowing exp essions:
Equa ion 6-1
Equa ion 6-2
Equa ion 6-3
The cu en holding coil has a o al olume o 6 ml and a ube leng h o 7.64 m. Ano he
holding coil wi h 12 ml and 15 m is also p epa ed in he case o using he 10 ml sy inge.
6.2.2. Mul i al e
The nex componen ollowing he holding coil is he mul i al e. The mul i al e eplaces he
usual o a o al e in SIA sys ems, educing imes swi ching al e channels because o a o
al es only ha e one o a ion di ec ion.
Mul i al e has i e low al es connec ed o a single cen al channel. En ances 1-4 a e
des ined o he inse ion o ca ie solu ion, eagen s and calib a ion s anda ds. Numbe 5 is
connec ed o a 3-way al e whe e he bioso p ion column will be connec ed o, so samples
can be moni o ed punc ually
Pág. 24 Repo
can be moni o ed punc ually.
6.2.3. 3-way al es
The assembly con ains h ee 3-way al es ha allow he low o ake di e en pa hs h ough
he o he componen s. Figu e 6-4 displays he loca ion and nume a ion o he al es, he
holding coil and he mixing cell.
A i s al e, labelled 0, is placed o e he mul i al e and i s cen al po is connec ed o he
po 5. The bioso p ion column is connec ed o ano he po and a was e line on he
emaining. This al e allows in oducing samples in o he sys em o be analized.
Figu e 6-4 SIA on iew
The second al e, 6, is connec ed o he exi o he mul i al e and o he hi d al e. The
emaining po is cu en ly unused hough i was planned as a was e line.
Finally, he hi d al e, 7, connec s o he mixing cell and o he debubble . Ac i a ing he
al e ia so wa e he s eam goes owa ds one o hese componen s, blocking i s way o he
o he . As shown in Figu e 6-5, al es 0, 6 and 7 ha e an open en ance, a no mally closed
en ance and a no mally open one.
Figu e 6-5 Val e posi ions ( on iew)
The cen al po is always open. Upon ac i a ing he al es, he en ances swi ch o he ON
s a us, opening he no mally closed po and closing he no mally open. This way low pa hs
a e de e mined h ough he SIA sys em. NC and NO po s a e placed as in Figu e 6-5 o
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 25
al es 6 and 7. Fo al e 0, he en ances a e in e ed, so he le one is he NO and he igh
one is he NC.
6.2.4. Mixing Cell
A s i e cell was designed o eplace he eac ion coil. The cell is made o PMMA and has a
olume o 15 ml. Mixing is p oduced ac i a ing he mo o wi h a neodymium iman loca ed on
he bo om compa men , ha induces mo emen o he s i ing ba on he cell. Mo o powe
can be modi ied mo ing he knob nex o he cell.
Figu e 6-6 Mixing Cell
Reagen s and ca ie solu ion mus be pumped om he holding cell o he s i e cell. A e
he pumping, he agi a ion is ac i a ed by he compu e un il he mix u e is comple ed, and
hen mus be aspi a ed back o he holding coil in o de o be sen o he sample low cell
a e wa ds.
6.2.5. Debubble
A memb ane debubble is placed be ween al e 7 and he de ec ion sys em in o de o
elimina e he maximum amoun o bubbles con ained in he low s eam and a oid
in e e ences on signal measu ing.
6.3. In e ace: LabVIEW
A use - iendly in e ace has been designed in LabVIEW o ease he unde s anding o he
commands p og ammed as well as p o iding a isual display in o ming he s a us o he
execu ion. The c ea ed in e ace also allows con olling and eading g aphically he da a
ob ained ia he senso a ay. Howe e , his unc ion will no be discussed in his p ojec .
Pág. 32 Repo
Figu e 7-4 DH-mini UV-VIS-NIR Ligh sou ce
7.1.4. Op ic ib e connec o s
Two op ic ib e QP450-1-XSR connec o s a e u ilized o ansmi ligh om he sou ce o he
cell and om he cell o he de ec o .
7.2. OceanView so wa e
OceanView is a Ja a-based spec oscopy so wa e by Ocean Op ics, and is capable o
con olling any Ocean Op ics USB spec ome e . The p ocedu e o ob ain spec oscopy
abso bance measu emen s will be de ailed in his sec ion.
7.2.1. S a ing OceanView
Be o e execu ing he p og am, make su e he spec ome e is connec ed o he compu e . I
no , he so wa e will simula e a de ice based on he selec ed wo king op ion. Upon
launching he p og am, he spec oscopy applica ion wiza d sc een will igge showing a g id
o nine wo king modes, as can be seen in Figu e 7-5.
Figu e 7-5 Spec oscopy applica ion wiza d

Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 33
Selec ing Abso bance (concen a ion) UV-Vis abso p ion measu emen s can be execu ed.
The o he op ions a e no explo ed o his applica ion. When Abso bance (concen a ion) is
selec ed, Concen a ion Choice sc een pops ou o e ing h ee op ions as shown in
Figu e 7-6 Concen a ion Choice
“Abso bance only” mode only displays and s o es abso bance da a. “Bee -Lambe law”
mode allows calcula ing concen a ion a a ixed wa eleng h once all coe icien s in Bee ’s
law a e known. “Calib a e om solu ions o known concen a ion” allows s o ing abso bance-
concen a ion da a pai s and c ea e a calib a ion cu e. Abso bance only mode is selec ed as
i allows a be e moni o ing o spec al da a o calib a ion han calib a ion mode. Howe e ,
he las was used b ie ly du ing he p elimina y es s.
7.2.2. Acquisi ion pa ame e s
Choosing he wo king me hod will led o he Se Acquisi ion Pa ame e s sc een, shown in
Figu e 7-7. In his sc een he use de ines he pa ame e s u ilised o ob aining spec al da a.
On he igh side o his sc een, he use can obse e he cu en spec oscopic lec u e.
“In eg a ion ime” de ines he amoun o ime u ilised o calcula e a single spec a, i s de aul
alue is 100 ms. Clicking in au oma ic, Ocean View will calcula e in eg a ion ime se ing i o
he 85% o he spec ome e ’s dynamic ange.
“Scans o a e age” se s he amoun o scans aken o a e aging in o de o inc ease he
S/N, de ined in sec ion 5.3. In eg a ion ime and he numbe o scans o al p ocessing ime is
se o sum less han 1.5 seconds, as acquisi ion s a s o delay conside ably o e his
amoun o ime.
Pág. 34 Repo
Figu e 7-7 Se Aquisi ion Pa ame e s
7.2.3. Re e ence and da k spec um
Figu e 7-8 S o e Re e ence and Backg ound spec um
Once acquisi ion pa ame e s a e de e mined, e e ence and da k spec ums mus be s o ed
in o de o be sub ac ed om he sample’s spec um in o de o ob ain only analy e’s
esponse. Sc eens om Figu e 7-8 appea in o de o s o e spec ums. Re e ence spec um
is selec ed p essing he yellow ligh bulb when he p ope lamp has been selec ed. Da k
spec um is cap u ed closing he shu e on he ligh sou ce while he lamp is on.
When he spec ums a e s o ed, a new window appea s on sc een showing he esul an
calcula ed spec um. This spec um is ob ained h ough Equa ion 7-1.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 35
Equa ion 7-1
Whe e Aλ is he simple in ensi y a wa eleng h λ, Dλ is he da k o backg ound in ensi y a
wa eleng h λ and Rλ, he e e ence in ensi y a wa eleng h λ.
7.2.4. Wa eleng h selec ion
When wo king in abso bance only mode, o ob ain all measu emen s du ing a pe iod o ime
a a ixed wa eleng h is in e es ing o wo k in s ip cha mode. This allows isola ing he
signal o he desi ed wa eleng h and plo s a g aphic wi h all acquisi ion da a poin s.
Figu e 7-9 Wa eleng h selec ion
Figu e 7-9 shows he selec ion wa eleng h sc een whe e he desi ed wa eleng h is selec ed.
Wa eleng h selec ion will be discussed in 9.1.
Pág. 36 Repo
7.2.5. S o ing da a
Figu e 7-10 Da a sa ing con igu a ion sc een
Da a sa ing wiza d, displayed in Figu e 7-10, pe mi s con igu ing he ile o ma o he sa ed
da a, he a ge di ec o y whe e iles will be alloca ed, he ile name and an au oma ic su ix
gene a o o mul iple iles o he same expe imen . In o de o sa e all spec al da a inside
he same ile, Time Se ies (column da a) o ma will be selec ed. Sa ed da a will appea
abula ed in h ee columns: acquisi ion ime, ac i e pixels and abso bance alue.
Each ow will con ain a single acquisi ion ime and he measu ed abso bance a ha ime.
O he ile o ma s gene a e mul iple iles o each measu emen , which is useless o long
unning expe imen s as a la ge amoun o iles has o be p ocessed.
This sc een also allows con igu ing he equency da a is w i en on a ile, and p og amming
he du a ion o ile w i ing.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 37
8. Expe imen al P ocedu e
In his sec ion, he expe imen al p ocedu e u ilised will be de ailed. In o de o be capable o
moni o ing low mo ing h ough he SIA p o o ype’s ubing, a colou ed eagen solu ion will
be analysed by UV-Visible spec oscopy.
8.1. Reagen s
A colo an solu ion o Phenol ed will be employed as he op ic eagen . I s use o dispe sion
analysis in low sys ems has been desc ibed in (del Ma 2004).
Phenol ed is a weak o ganic acid and a e e sible pH-sensi i e dye. As can be seen in
Figu e 8-1, Phenol ed colou changes when i s p edominan s a e is in acidic o m o in
conjuga e base o m.
Figu e 8-1 Phenol ed in: Le : basic medium Righ : acid medium
Fo his p ojec , phenol ed will be used in i s basic o m whe e i s maximum abso p ion is
inside he 550 nm and 560 nm ange. (del Ma 2004) se s measu emen s a 550 nm while
(Sochacka 2015) wo ks a 559 nm. (Sochacka 2015) se s he wa eleng h a e analyzing
phenol ed ull abso bance spec um o bo h basic and acidic o ms in di e en medium as
shown in Figu e 8-2. As a pa o he expe imen al p ocedu e, phenol ed solu ions will be
cha ac e ized o selec he app op ia e wa eleng h.
To p ese e phenol ed in basic o m, al solu ions will con ain sodium hyd oxide 0.1 M as
sol en , and sodium hyd oxide 10-5 M will be he ca ie solu ion.

Pág. 38 Repo
Figu e 8-2 Phenol ed abso p ion spec um (Sochacka 2015)
8.2. Calib a ion Me hod
(Robinson e al. 2005) de ine calib a ion as he p ocess o es ablishing he ela ionship
be ween he measu ed signal and known concen a ions o analy e. A e es ablishing his
ela ionship, he concen a ion o he analy e in an unknown sample can be calcula ed
measu ing i s esponse.
Figu e 8-3 Reagen aspi a ion p ocedu e modi ied om (Núñez 2016)
Figu e 8-3 displays a gene al p ocedu e o in oduce samples on he sys em. Fi s , he
bu e e is loaded wi h dis illed wa e om he dis illed wa e ank and is dispensed h ough
he mul i al e, cleaning he ubing om p e iously u ilised solu ions. Nex , a olume o ca ie
is aspi a ed h ough mul i al e po 4. Then, samples a e aspi a ed ia one o he en ies 1-3
o he mul i al e, as shown in Figu e 8-4 , mo e ca ie solu ion is injec ed a e wa ds.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 39
Figu e 8-4 S anda d en ies
The aspi a ed olume is s o ed in he holding coil. Reagen s a e in oduced be ween wo
olumes o ca ie o p e en high deg ees o dispe sion. Finally, i is dispensed o he
de ec ion sys em o he s i ing cell, depending on he kind o de e mina ion.
8.2.1. Ex e nal Calib a ion
S anda ds a e injec ed in o he sys em u ilizing po s 1-3 o he mul i al e, while he ca ie
solu ion is aspi a ed om po 4. Each s anda d is in oduced sepa a ely, ha is, he nex
solu ion is no in oduced in o he sys em un il he las has been sen o he de ec o .
8.2.2. In e nal Calib a ion
A concen a ed s anda d will be injec ed and hen dilu ed o he same concen a ion as he
s anda ds u ilised in 8.2.1. Following a simila p ocedu e o Figu e 8-3 ca ie is aspi a ed
om 4 and samples om 1-3. Reagen s a e dispensed in o he mixing cell and hen he es
o he needed olume o he dilu ion is added om ca ie solu ion, o p ese e basic
medium.
8.3. S anda ds p epa a ion
Calcula ions o each solu ion can be ound in Annex A.
8.3.1. Phenol ed s ock solu ion
Following he p ocedu e desc ibed by (del Ma 2004) and (Vinde oghel 2005), a s ock
solu ion o phenol ed 400 ppm in NaOH 0.1 M was p epa ed.
0.100 g o phenol ed is weighed and added o a olume ic lask o 250 ml. Then 1.00 g o
sodium hyd oxide pelle s is weighed and dissol ed in Milli-Q wa e , and hen added o he
olume ic lask. Make up o he ma k wi h Milli-Q wa e .
Pág. 40 Repo
8.3.2. Sodium hyd oxide solu ion 0.1 M
4 g o sodium hyd oxide a e weighed on a beake and hen dissol ed in Milli-Q wa e . Then i
is added o a olume ic lask o 1000 ml. Then i is made up o he ma k wi h Milli-Q wa e .
8.3.3. Sodium hyd oxide ca ie solu ion
25 μl om he 0.1 M NaOH solu ion a e pu on a 250 ml olume ic lask. Then Milli-Q wa e
is added o he ma k.
8.3.4. S anda d solu ions
S anda d solu ions a e p epa ed aking aliquo s om he Phenol Red s ock solu ion and
sol ing hem in sodium hyd oxide 0.1 M in 100 ml olume ic lasks. This da a is dispalyed in
Table 8-1. Howe e , a di e en se o solu ions was made o cha ac e ize phenol ed
abso p ion spec um. O iginally a se o solu ions we e a ailable om an olde 4000 ppm
s ock solu ion and we e u ilized as es s o s a designing he i s p ocedu es.
S anda d
Concen a ion
(ppm)
Aliquo olume
(ml)
NaOH olume
(ml)
1
0.25
99.75
2
0.5
99.5
4
1
99
8
2
98
12
3
97
16
4
96
20
5
95
Table 8-1 S anda d solu ions
8.4. De ec ion sys ems cha ac e iza ion pa ame e s
8.4.1. Limi o de ec ion (LOD)
De ec ion limi is de ined by he In e na ional Union o Pu e and Applied Chemis y (IUPAC)
in (Nič e al. 2009), as he smalles concen a ion o analy e ha has a signi ican ly la ge
signal han he signal om a sui able blank.
The LOD in mos ins umen al me hods can be ansla ed in o he ollowing exp ession:
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 41
Equa ion 8-1
In Equa ion 8-1, SDL is he analy e’s de ec ion limi , Sb is he a e age signal o blank, σb he
blank’s s anda d de ia ion and z is an in ege .
8.4.2. Limi o quan iza ion (LOQ)
(MacDougall and C umme 1980) es ablish as a minimum c i e ion ha he egion o
quan iza ion should be clea ly abo e he limi o de ec ion. Equa ion 8-1 also desc ibes he
loca ion o he LOQ.
Figu e 8-5 Regions o de ec ion and quan iza ion (MacDougall and C umme 1980)
Howe e , a dis inc ion on z should be made in o de o obey LOD’s and LOQ’s de ini ions.
Figu e 8-5 shows his di e ence: he bo de o he egion o de ec ion is a a dis ance 3σb
om he blank a e age epo ed signal, and he e o e, all alues ha all below should be
epo ed as non-de ec ed. Values o e 10σb a e conside ed on he egion o quan iza ion.
8.5. Dispe sion coe icien
Dispe sion in low sys ems was explained in sec ion 4.3. In his segmen , dispe sion
quan i ica ion will be add essed.
In bo h FIA and SIA echniques, zone sequencing and mu ual dispe sion o he zones a e he
key ope a ions, as (Gubeli e al. 1991) s a e. Fo eagen -based chemis ies, being op ical
me hods amongs hem, a mix be ween sample and eagen zones mus be done in a
sui able p opo ion and hus a medium dispe sion has o be achie ed. On he o he hand,
conduc i i y measu emen equi es limi ed dispe sion.
The dispe sion coe icien D is de ined in (Gubeli e al. 1991) as he a io o he concen a ion
o he sample ma e ial be o e (C0) and a e (C) he dispe sion p ocess has aken place,
Pág. 48 Repo
I is isible ha abso bance spec um o s anda ds 30 and 40 ppm is e y noisy. Bee ’s law
wo ks bes o dilu ed solu ions whe e a linea co ela ion be ween abso bance and
concen a ion can be es ablished. Commonly, abso bance alues supe io o 1.5-2 a e
conside ed ou side he linea ange, so bo h s anda ds we e disca ded. The calib a ion cu e
p esen ed in Figu e 9-9 shows how linea i y s a s o d op.
Figu e 9-9 O iginal s anda ds’ calib a ion cu e
Howe e i was decided o keep he 20 ppm s anda d and in oduce wo new poin s
co esponding o 1 ppm and 16 ppm in o de o ex end he s udy ange.
9.2. Ex e nal calib a ion
All expe imen s de ailed in his segmen a e pe o med u ilizing he SIA p o o ype. Sc ip s
u ilised o each de e mina ion will be named and he me hodology will be explained.
Howe e sc ip iles will be p esen ed in Annex 1. Spec ome e acquisi ion pa ame e s will
also be de ailed o each de e mina ion.
9.2.1. Sui able low a es
Usually, FIA and SIA sys ems wo k wi h low a es om 1 ml/min o 5 ml/min. (Núñez 2016)
s udied he a ailable and ecommended ange o eloci ies ha could be se on he
au obu e e, and measu ed and abula ed he mos sui able wo king low a es o bo h 10 ml
and 5 ml sy inges. One o he ecommended low a es he es ablished included in his
in e al was 1.2 ml/min. This alue has been selec ed as he low a e o aspi a ion as well
as dispensa ion in all de e mina ions.
9.2.2. SIA and Mul i al e p iming
Be o e unning any expe imen s on he SIA p o o ype, gene al p iming o all al es and
ubes mus be ca ied on. Sys emP iming. x will load he sy inge wi h dis illed wa e and

Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 49
dispensa ions au oma ically opening all al es ensu ing low a e se all componen s.
Addi ionally, a olume is loaded in o he mixing cell and discha ged a e wa ds.
When p og amming bu e e o de s o load solu ions h ough he mul i al e po s i is
p esupposed ha i s ubing is comple ely illed o solu ion. Mul i al eP iming. x discha ges
he sy inge in o he dis illed wa e ank (as he holding coil p e en s any compound om
eaching he bu e e). Nex , a qua e o he sy inge’s o al olume is aspi a ed om each po
o en ies 1-4. Las , dis illed wa e dispensa ions h ough he mainline discha ge he holding
coil un il abso bance d ops o he baseline.
The p ocess spec um is ep esen ed in Figu e 9-10.
Figu e 9-10 Mul i al e p iming
9.2.3. De e mina ion o minimum olume
This expe imen was designed o de e mine he minimum olume ha mus be injec ed in o
he sys em o ob ain he maximum signal in abso bance a he same ime ensu ing ha
dispe sion coe icien ends o he uni , as de ined in sec ion 8.5.
A se o injec ions o he 16 ppm phenol ed solu ion will be analyzed. Injec ed olume s a s
a 25 μl and is pumped di ec ly o he de ec ion sys em. Se e al samples a e injec ed
inc easing by 25 μl he aspi a ed olume un il a inal olume o 1100 μl. The abso bance o
each injec ion will be measu ed o de e mine he minimum olume needed o achie e
maximum abso bance.
To ensu e peaks do no o e lap and all colo an is ca ied ou o he sampling cell addi ional
3.75 ml o dis illed wa e a e dispensed be ween each injec ion. This has been p og ammed
in MinVolumeTes . x .
Fo he spec ome e pa ame e s, in eg a ion ime was se au oma ically o 236.91 ms and
he amoun o scans o a e age was 6. Rep esen ing abso bance, ob ained as he peak
Pág. 50 Repo
heigh o each injec ion, e sus he injec ed olume he cu e in Figu e 9-11.
Figu e 9-11 Abso bance o di e en injec ed olume
Applying Equa ion 8-3 o he poin s ob ained, and de ining A0 as he maximum abso bance
measu ed in Figu e 9-11, he dispe sion coe icien and he a io o abso bance e olu ion can
be s udied o inc easing olumes. Bo h pa ame e s a e plo ed in Figu e 9-12
Figu e 9-12 Abso bance a io and dispe sion coe icien
In o de o de e mine he minimum olume ha shall be injec ed in he SIA p o o ype o
ob ain accep able esponse bo h, dispe sion coe icien and abso bance a io, mus end o 1.
I is obse ed in Figu e 9-12 ha dispe sion coe icien eaches i s limi signi ican ly as e
han abso p ion a io. Fo olumes la ge han 925 μl bo h cu es a e inside a 5%
disc epancy ega ding he heo e ical limi . In u he de e mina ions, sample olumes will be
se o 1 ml.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 51
9.2.4. Calib a ion cu es
Calib a ion cu es a e d awn plo ing he peak heigh o he abso bance o each o he
s anda d solu ions. S anda ds a e sequen ially injec ed and he nex is no in oduced in he
sys em be o e i s p eceden has no been ca ied ou .
All he calib a ion cu es p esen ed in his sec ion a e ex e nal calib a ions. S anda ds a e
in oduced in o he SIA and hen a e sen di ec ly o he de ec o sys em. Po 4 o he
mul i al e has always been ese ed o ca ie solu ion. All calib a ion sequences we e
made om he same sc ip which has been e ol ing h ough he analysis o he spec al
cu es.
A olume o 0.5 ml o ca ie is injec ed p io o he colo an aspi a ion in o de o minimize
dispe sion inside he holding coil. Addi ionally, 50 μl o ca ie a e also aspi a ed a e he
colo an injec ion. Dis illed wa e is injec ed a e wa ds o push he solu ions h ough he SIA
mainline. Calib a ion sequence is ound in Calib a ionP ocedu e. x . An addi ional sc ip ,
Calib a ionP ocedu eDualPeak. x was u ilised o a ew de e mina ions ha will be de ailed
la e on in 9.2.7.
Figu e 9-13 Calib a ion cu es Le : 1-20 ppm Righ : 1-16 ppm
One o he undamen al concep s in calib a ion is es ablishing he linea i y ange so he
esul an cu e can be desc ibed by Bee ’s Law. Two calib a ion cu es a e p esen ed in
Figu e 9-13. I can be obse ed ha eg ession coe icien s imp o e excluding he 20 ppm
s anda d in calib a ion as i s a s o d i ou side linea i y. Thus he linea i y ange will be
de ined be ween 1 ppm and 16 ppm.
Pág. 52 Repo
Figu e 9-14 Calib a ion 2016-6-1
Al hough Bee ’s law cu es in e cep (0,0), eg ession i s displayed in Figu e 9-13 and
Figu e 9-14 p esen a y-axis in e cep de ia ion. This de ia ion on he eg ession models is
due o he elec onic noise p oduced du ing he usual ope a ion o he spec ome e .
Baseline oscilla ion will be de ailed in 9.2.5.
Ga he ing all he calib a ion esul s du ing he p ojec , a gene al abso p i i y coe icien can
be calcula ed. Fo a 95% con idence in e al:
Ne e heless, as s udied in 9.1.3, s anda ds decay o e ime, hus abso p i i y coe icien
can be s udied g ouping calib a ions by he amoun o days passed since hei p epa a ion.
Nume ical da a can be ound in Table 9-1 and he in e als plo ed in Figu e 9-15.
Day
Mean
Con idence In e al
1
0.1313
(0.1145, 0.1481)
2
0.1160
(0.1014, 0.1306)
3
0.1226
(0.1161, 0.1292)
4
0.1069
(0.0955, 0.1182)
5
0.1051
(0.0881, 0.1220)
Table 9-1 Abso p i i y con idence in e als
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 53
Figu e 9-15 Con idence in e als o abso p i i y o e ime
I can be obse ed in Figu e 9-15 ha he mos signi ican d op in abso bance is p oduced
be ween he i s and second days. U ilizing ANOVA me hods o compa e he means o each
g oup, wi h a alue o α = 0.05, i is ob ained ha popula ion means di e wi h a p- alue o
0.015. When compa ing he o he g oups excluding day 1 g oup, o a p- alue o 0.052
means can be conside ed s a is ically equal.
9.2.5. Limi o De ec ion and Limi o Quan i ica ion
A se o blank measu emen s we e egis e ed be ween 15:53 pm o 15:57 pm, s o ing 157
acquisi ions. In eg a ion ime was se au oma ically o 158.64 ms and 8 scans we e
a e aged. Due o he la ge numbe o da a, i is assumable ha he sample’s a iance (s)
app oaches o he s anda d de ia ion o he blanks (σ). Blank’s mean and σ, LOD and LOQ
a e calcula ed in Table 9-2.
Mean
0.0107
S anda d De ia ion
0.0015
LOD
0.0151
LOQ
0.0255
Table 9-2 Blank cha ac e iza ion
54321
0,15
0,14
0,13
0,12
0,11
0,10
0,09
0,08
Day
Abso p i i y coe icien
In e al Plo o Abso p i i y coe icien
95% CI o he Mean
Indi idual s anda d de ia ions we e used o calcula e he in e als.

Pág. 54 Repo
9.2.6. Peak Cu es
When ep esen ing all da a poin s acqui ed du ing a calib a ion in on o ime, peak cu es
a e d awn. Analyzing peak o ms in hese cu es allows con olling i eagen s a e being
adso bed on he ubing walls, and he posi ion o he samples inside he sys em can be
in e ed by peak o m.
Figu e 9-16 Peak cu es compa ison
In he Figu e 9-16, a compa ison o he peak cu es o a calib a ion u ilizing s anda ds 1-4
ppm is shown. I was obse ed in he le cu e ha baseline was ising o e ime, and when
he nex peak a i ed, a alley was gene a ed and hen abso bance s a ed o inc ease. This
phenomenon was due o he samples no being comple ely expulsed om he sample cell.
One o he ails emained in he op ical pa h. In he cu e on he le , 500 μl dis illed wa e
we e dispensed a e he solu ion (cu e on he igh ), In o de o co ec his p oblem 2050 μl
wa e we e dispensed.
9.2.7. Hyd aulic hys e esis
In his sec ion low e ec s will be s udied. I was obse ed ha when au obu e e inished he
pis on mo emen s, low was s ill a ec ed by p essu e and mo ed back when any al e was
pe mu ing. One solu ion o his phenomenon was o pu wai ing imes a e dispensa ions
and aspi a ions. Coding 2 seconds educed conside ably he phenomena.
On he o he hand, ano he s udy was ealized e e ed o calib a ion mechanics. Calib a ions
peaks we e duplica ed and he s anda ds o de was e e sed (downwa ds) o see i he e
was any in luence o i he less concen a ed solu ions p esen ed aces o he highe
s anda ds.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 55
Figu e 9-17 Upwa ds and downwa ds calib a ions
Figu e 9-17 shows he calib a ion cu es o an upwa ds calib a ion (s a ing a 1 ppm) and a
downwa ds calib a ion (s a ing a 16 ppm). No di e ences we e obse ed be ween peak
heigh s ei he be ween same concen a ion, same calib a ion and same concen a ion
e e se calib a ion. I is concluded hen, ha bo h calib a ion di ec ions a e independen ly
eliable.
9.2.8. Cleaning he sys em
De i ed om analyzing peak o ms like in 9.2.6, i was ound ha dispensing dis illed wa e
h ough mainline all eagen s can be ca ied ou o he sys em. The same sc ip o p iming
he sys em can be u ilised as a cleaning ou ine. Howe e , passing a 0.1 M HNO3 solu ion
and hen insing is ecommended once a week.
Acid cleaning is ecommended a e long expe imen s o p e en eagen p ecipi a ion,
especially i he low is s a ic o se e al hou s. O he wise, ubing o al es can be obs uc ed
gene a ing p essu e necks when p opelling low, o acuum bubbles in he sy inge when
aspi ing, which can cause al e mal unc ioning and he sy inge glass o b eak.
9.3. In e nal calib a ion
In e nal calib a ion me hods u ilize he mixing cell o dilu e a concen a ed s anda d o he
ex e nal calib a ion s anda ds in o de o being able o compa e magni udes.
9.3.1. Mixing cell p elimina y es s
A se o expe imen s was designed o check he wo king condi ions o he mixing cell. The
20 ppm s anda d was dilu ed o 50% dissol ing i in NaOH ca ie solu ion o a o al olume
o 4 ml. Du ing he i s g oup o ials, i was obse ed ha when dispensing he same
amoun o aspi a ed luid, ail aces emained in he holding coil. Agi a ion was se o 5
seconds. The me hod can be ound in Dilu ion50%M1M4. x , Dilu ion50%M2M4. x ,
Dilu ion50%M3M4. x .
Pág. 56 Repo
(Escudé 2015) designed he ubing o he sys em. Be ween he mul i al e and he mixing cell
he e a e 435 mm o Te lon ubing 0.8 in e nal diame e , a olume o 874.6 μl olume.
(Núñez 2016) s a ed ha al es could be conside ed s agnan so he olume displacemen
inside can be negligible compa ed o he ubing olume. Howe e , ha is only ue when
al es ha e been p imed. Cleaning he mixing cell equi es emo ing all he luid e ained
inside pa h om al e 7 o he mixing cell. An addi ional olume o 1000 μl was decided o be
dispensed o compensa e hese olumes. Howe e , hal o ha olume is dispensed a e he
phenol ed solu ion and he es a e he ca ie solu ion, allowing ca ie solu ion o push
colo an inside he cell.
Po s 1-3 o he mul i al e we e ed wi h he 20 ppm s anda d and en y 4 was ese ed o
NaOH ca ie solu ion. Ten eplicas o each po we e made s a ing po 1 o po 3 and
ano he en eplicas e e sing he o de . Dilu ion esul s a e ep esen ed in Figu e 9-18 and
nume ical da a in Table 9-3.
Figu e 9-18 Ex e nal calib a ion and 50 % dilu ions Mul i al e po s a e labelled M1, M2, and
M3 Le : Ascending o de Righ : Descending o de
Ascending
Descending
Concen a ion
mean (ppm)
S De
Concen a ion
mean (ppm)
S De
M1
9.62
0.14
8.91
0.10
M2
9.72
0.02
9.00
0.11
M3
9.77
0.13
9.09
0.12
Table 9-3 Concen a ions ob ained o 50% dilu ions
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 57
Be ween bo h se ies o calib a ions, no di e ences a e ound be ween M1, M2 and M3
se ies, as hei means in each calib a ion a e s a is ically equal. Thus he e is no p e e ence
in injec ing samples h ough a de e mined po . The d op in concen a ion is due o he decay
o he s anda ds wo days a e he ascending calib a ion.
9.3.2. Calib a ing om 20 ppm s anda d
Unde he same wo king condi ions, and modi ying he sc ip s u ilised in sec ion 9.3.1, a se
o sc ip s is p og ammed o dilu e he 20 ppm s anda d o he s anda ds u ilised o ex e nal
calib a ion. These sc ip s a e 20 o1. x , 20 o2. x , 20 o4. x , 20 o8. x , 20 o12. x and
20 o16. x .
Two eplicas o wo in e nal calib a ions we e made as o he i s calib a ion ca ie solu ion
addi ion be o e colo an aspi a ion was no added. The calib a ions a e hen ep esen ed wi h
an ex e nal calib a ion in o de o obse e he de ia ions. Cu es a e p esen ed in Figu e
9-19.
Figu e 9-19 In e nal calib a ions using 20 ppm as s ock solu ion
Fo he second calib a ion, he eplicas we e a e aged and compa ed wi h a new calib a ion
made he nex day, as he expe imen las ed all nigh . The e o e, calib a ion 1 app oxima es
mo e accu a ely o 2016-6-7 calib a ion. I can be obse ed also in Figu e 9-19 ha small
de ia ions appea o he leas and mos concen a ed dilu ions. Fo small olumes, colo an
solu ion is mo e a ec ed by dispe sion as abso bance alues all below he ex e nal
calib a ion while o concen a ed samples, abso bance alues a e abo e he cu e.
9.3.3. Calib a ing om s ock solu ion
Simila ly o segmen 9.3.2, he same p ocedu e is applied u ilizing he 400 ppm s ock di ec ly
ins ead o make he dilu ions. Sc ip s u ilised ollow he same ins uc ions changing he
olumes o main ain he dilu ion ac o . These sc ip s a e 400 o1. x , 400 o2. x , 400 o4. x ,
400 o8. x , 400 o12. x and 400 o16. x .
Pág. 64 Repo
11. En i onmen al conside a ions
In his p ojec se e al en i onmen al conside a ions ha e been aken accoun as he
School’s di ec i es indica e o Deg ee Final P ojec s.
Sequen ial injec ion analysis sys ems educe he en i onmen al impac because he use o
eagen s is minimized as he p ocess is au oma ed and con olled elec onically, he e o e,
mo e accu a e.
Elec onic ongues, hough equi ing aining wi h a a ie y o s anda d se s, a e less
agg essi e echniques han a omic abso p ion o o he classical analy ic me hods.
Howe e , du ing he expe imen a ion o he p ojec a la ge olume o esiduals has been
gene a ed due o he deg ada ion o he s anda ds: a se o new solu ions had o be p epa ed
each week. A e ha ing de eloped he p ojec o wen y weeks, an app oxima e olume o
62 li e s o aqueous esidue has been gene a ed. Residual solu ions we e labeled unde he
ca ego y o O ganic Colo an Reagen s.
On he o he hand, he inal applica ion o he p o o ype o moni o ing bioso p ion p ocesses
will a ou he op imiza ion o his echnique in long e m, hus elimina ing and eco e ing
g ea e yields o hea y me als. Bioso p ion p ocesses addi ionally eu ilize ag a ian esidual
o cap u e hese me als.
Consequen ly, he bene i s epo ed in op imizing bioso p ion p ocesses as well as elec onic
ongues ou come he ini ial impac du ing he i s phases o he design and implemen a ion.
The e o e, elimina ing hea y me als h ough bioso p ion educes he isk o biomagni ica ion
and u al esidual a e eu ilised.

Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 65
Conclusions
I was analyzed he in luence o luo escen ligh ning on he measu emen s by co e ing and
unco e ing he sample cell. Spec oscopic da a de e mined ha p ese ing he sample cell
om luo escen ligh ing is equi ed.
Flame S Spec ome e eliabili y was con as ed compa ing calib a ion cu es wi h a
con en ional spec ome e (UV-Mini 1240).
I was de e mined ha expe imen al maximum abso bance wa eleng h was 560 nm and i
was wi hin an accep able 5% e o ma gin om he li e a u e alues.
Phenol ed s anda d solu ion deg ada ion was measu ed h ough he e olu ion o i s
abso bance o e a pe iod o ime. I was obse ed ha concen a ed solu ions decayed
as e .
A minimum olume o sample o 925 μl was de e mined o minimize dispe sion e ec s in o
he ca ie solu ion and he wash solu ion (dis illed wa e ), while limi ing abso bance loss in
less han he 5% o he maximum alue.
1 ppm o 16 ppm linea i y ange was es ablished analyzing he noise le els in spec al da a
and plo ing calib a ion cu es.
Rep oducibili y o ex e nal calib a ions has been p o ed al e ing he o de samples a e
injec ed.
The addi ional olume o compensa e pa h leng h be ween mul i al e and mixing cell was
se in 1000 μl. Mo eo e , ep oducibili y has been es ed, o di e en con igu a ions.
The e o e, I was ound ha injec ing solu ions was independen o he mul i al e po he
sample is loca ed.
In e nal calib a ion dilu ing a 20 ppm s anda d was se and i s eliabili y has been con i med
when compa ing da a o he ex e nal calib a ion.
Sc ip s o s anda d ope a ions including p iming he sys em, calib a ing and cleaning we e
p og ammed and e i ied ob aining peak cu es usual in low sys ems.
Howe e , p og amming in e nal calib a ions using he 400 ppm was no accomplished.
Pág. 66 Repo
Fu u e ecommenda ions
Implemen ing LabVIEW and Ocean View unde he same so wa e in e ace would allow
pe o ming spec oscopic and elec ochemical analysis wi h he senso a ay simul aneously
on he SIA sys em.
Val e 6 is connec ed in a sub op imal way: he no mally open po has a lid o p e en ing
luid escaping. Fo long wo k sessions some luid leakage is p oduced. Addi ionally,
connec ing he mul i al e o he no mally closed equi es ac i a ing he al e o all
ope a ions which inc eases ope a ion imes.
In e nal calib a ion dilu ing concen a ed solu ions should be s udied u he on. Pe haps
es ing on inc easing concen a ions om 20 ppm o 400 ppm can de e mine he maximum
concen a ion in e nal calib a ion wo ks up o.
S i e op imiza ion could be s udied mo e in de ail i he knob ha con ols he mo o had a
e e ence sys em o know he pm.
Addi ionally, a g adua ed scale o olume in he mixing cell would help e i ying
dispensa ions and aspi a ions in he cell.
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 67
Acknowledgemen s
Fi s o all, I would like o exp ess my g a i ude owa ds An onio Flo ido o p o iding me he
oppo uni y o handling ano he p ojec unde his guidance, and owa ds his cons an
supe ision as well as o p o iding necessa y in o ma ion ega ding he p ojec and all he
pa ience shown especially on he i s weeks p epa ing Phenol Red s anda ds and allowing
me o u ilize addi ional equipmen om academic labo a o ies.
I would also like o show g a i ude o Sa a, my pa en s and my b o he s o suppo ing me
du ing hese yea s s udying Deg ee in Chemical Enginee ing and encou aging me o
con inue ad ancing.
Las , bu no leas , hanks o E ic, Ad ián, José Luis, Anabel, Eli and C is ina o sha ing
expe iences in he labo a o y.
p. 68 Repo
Bibliog aphy
Bibliog aphic e e ences
AVE, D., 2015. Flame Minia u e Spec ome e Use Manual
BAXTER, P.J. and G.D. CHRISTIAN, 1996. Sequen ial Injec ion Analysis: A Ve sa ile
Technique o Biop ocess Moni o ing. Accoun s o Chemical Resea ch [online], 29(11),
515–521 A ailable om: h p://pubs.acs.o g/doi/abs/10.1021/a 950214z
CHRISTIAN, G.D., 2003. Flow analysis and i s ole and impo ance in he analy ical
sciences. Analy ica Chimica Ac a, 499(1-2), 5–8
ESCUDÉ, B., 2015. (SIA), Op imi zació d’un sis ema de moni o i zació de p ocessos basa
en anàlisi pe injecció seqüencial
FIALAB, 2015. Fibe Op ic SMA Z-Flow Cell Manual Design
GUBELI, T., G.D. CHRISTIAN and J. RUZICKA, 1991. Fundamen als o Sinusoidal Flow
Sequen ial Injec ion Spec opho ome y. Analy ical Chemis y, 63, 2407–2413
HARVEY, D., 2009. Analy ical Chemis y 2.0, 810
KIKAS, T., 2014. In oduc ion o Flow Injec ion Analysis ( FIA ) De e mina ion o Chlo ide Ion
Concen a ion [online] [ iewed 6 Oc 2016]. A ailable om:
ww2.chemis y.ga ech.edu/class/analy / ia.pd
DE LAMO, D., 2014. Diseño y cons ucción del p o o ipo de un sis ema de Análisis de
Inyección Secuencial pa a la moni o ización de p ocesos median e lenguas
elec ónicas
LARSEN, D. and D. HARVEY, 2013. Flow Injec ion Analysis [online] [ iewed 6 Dec 2016].
A ailable om:
h p://chemwiki.ucda is.edu/Co e/Analy ical_Chemis y/Analy ical_Chemis y_2.0/13_Ki
ne ic_Me hods/13.4:_Flow_Injec ion_Analysis
MACDOUGALL, D. and W.B. CRUMMETT, 1980. Guidelines o Da a Acquisi ion and Da a
Quali y E alua ion in En i onmen al Chemis y. Analy ical Chemis y [online], 52(14),
2242–2249 A ailable om: <Go o ISI>://WOS:A1980KT61200006
DEL MAR, B. i L.M., 2004. Nue as Es a egias Pa a La Ges ión de Fluidos En Sis emas
Au oma izados de Análisis. Uni e si a Au ònoma de Ba celona. Uni e si a Au ònoma
de Ba celona
NIČ, M. e al., eds., 2009. IUPAC Compendium o Chemical Te minology [online]. Resea ch
T iagle Pa k, NC: IUPAC [ iewed 2 Jun 2016]. A ailable om: h p://goldbook.iupac.o g
NÚÑEZ, J.L., 2016. Es udio de la luidica asociada a la op imización de un sis ema de
análisis po inyección secuencial (SIA)
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 69
NUÑEZ, L. e al., 2013. De elopmen and applica ion o an elec onic ongue o de ec ion
and moni o ing o ni a e, ni i e and ammonium le els in wa e s. Mic ochemical Jou nal
[online], 110, 273–279 A ailable om: h p://dx.doi.o g/10.1016/j.mic oc.2013.04.018
PASEKOVA, H., M. POLASEK and P. SOLICH, 1999. Sequen ial injec ion analysis.
Chemické lis y, 93(6), 354–359
PINTO, P.C.A.G. e al., 2011. Sequen ial Injec ion Analysis Hyphena ed wi h O he Flow
Techniques: A Re iew. Analy ical Le e s, 44(1-3), 374–397
ROBINSON, J.W., E.M. SKELLY FRAME and G.M. FRAME II, 2005. Unde g adua e
Ins umen al analysis, 1, 1079
SOCHACKA, J., 2015. Applica ion o phenol ed as a ma ke ligand o bili ubin binding si e
a subdomain IIA on human se um albumin. Jou nal o pho ochemis y and
pho obiology. B, Biology [online], 151, 89–99 A ailable om:
h p://www.ncbi.nlm.nih.go /pubmed/26231934
VINDEVOGHEL, W., 2005. Modi ica ion o a SIA-sys em by addi ion o a s i e de ice
(mixing low cell)
Addi ional bibliog aphic e e ences
AVE, D., 2015. Flame Minia u e Spec ome e Use Manual
BAXTER, P.J. and G.D. CHRISTIAN, 1996. Sequen ial Injec ion Analysis: A Ve sa ile
Technique o Biop ocess Moni o ing. Accoun s o Chemical Resea ch [online], 29(11),
515–521 A ailable om: h p://pubs.acs.o g/doi/abs/10.1021/a 950214z
CHRISTIAN, G.D., 2003. Flow analysis and i s ole and impo ance in he analy ical
sciences. Analy ica Chimica Ac a, 499(1-2), 5–8
ESCUDÉ, B., 2015. (SIA), Op imi zació d’un sis ema de moni o i zació de p ocessos basa
en anàlisi pe injecció seqüencial
FIALAB, 2015. Fibe Op ic SMA Z-Flow Cell Manual Design
GUBELI, T., G.D. CHRISTIAN and J. RUZICKA, 1991. Fundamen als o Sinusoidal Flow
Sequen ial Injec ion Spec opho ome y. Analy ical Chemis y, 63, 2407–2413
HARVEY, D., 2009. Analy ical Chemis y 2.0, 810
KIKAS, T., 2014. In oduc ion o Flow Injec ion Analysis ( FIA ) De e mina ion o Chlo ide Ion
Concen a ion [online] [ iewed 6 Oc 2016]. A ailable om:
ww2.chemis y.ga ech.edu/class/analy / ia.pd
DE LAMO, D., 2014. Diseño y cons ucción del p o o ipo de un sis ema de Análisis de
Inyección Secuencial pa a la moni o ización de p ocesos median e lenguas
elec ónicas
LARSEN, D. and D. HARVEY, 2013. Flow Injec ion Analysis [online] [ iewed 6 Dec 2016].

p. 70 Repo
A ailable om:
h p://chemwiki.ucda is.edu/Co e/Analy ical_Chemis y/Analy ical_Chemis y_2.0/13_Ki
ne ic_Me hods/13.4:_Flow_Injec ion_Analysis
MACDOUGALL, D. and W.B. CRUMMETT, 1980. Guidelines o Da a Acquisi ion and Da a
Quali y E alua ion in En i onmen al Chemis y. Analy ical Chemis y [online], 52(14),
2242–2249 A ailable om: <Go o ISI>://WOS:A1980KT61200006
DEL MAR, B. i L.M., 2004. Nue as Es a egias Pa a La Ges ión de Fluidos En Sis emas
Au oma izados de Análisis. Uni e si a Au ònoma de Ba celona. Uni e si a Au ònoma
de Ba celona
NIČ, M. e al., eds., 2009. IUPAC Compendium o Chemical Te minology [online]. Resea ch
T iagle Pa k, NC: IUPAC [ iewed 2 Jun 2016]. A ailable om: h p://goldbook.iupac.o g
NÚÑEZ, J.L., 2016. Es udio de la luidica asociada a la op imización de un sis ema de
análisis po inyección secuencial (SIA)
NUÑEZ, L. e al., 2013. De elopmen and applica ion o an elec onic ongue o de ec ion
and moni o ing o ni a e, ni i e and ammonium le els in wa e s. Mic ochemical Jou nal
[online], 110, 273–279 A ailable om: h p://dx.doi.o g/10.1016/j.mic oc.2013.04.018
PASEKOVA, H., M. POLASEK and P. SOLICH, 1999. Sequen ial injec ion analysis.
Chemické lis y, 93(6), 354–359
PINTO, P.C.A.G. e al., 2011. Sequen ial Injec ion Analysis Hyphena ed wi h O he Flow
Techniques: A Re iew. Analy ical Le e s, 44(1-3), 374–397
ROBINSON, J.W., E.M. SKELLY FRAME and G.M. FRAME II, 2005. Unde g adua e
Ins umen al analysis, 1, 1079
SOCHACKA, J., 2015. Applica ion o phenol ed as a ma ke ligand o bili ubin binding si e
a subdomain IIA on human se um albumin. Jou nal o pho ochemis y and
pho obiology. B, Biology [online], 151, 89–99 A ailable om:
h p://www.ncbi.nlm.nih.go /pubmed/26231934
VINDEVOGHEL, W., 2005. Modi ica ion o a SIA-sys em by addi ion o a s i e de ice
(mixing low cell)
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 71
Table o igu es
Figu e 4-1 Fou phases o Flow Injec ion (Kikas 2014) ........................................................ 12
Figu e 4-2 S eam di usion .................................................................................................. 13
Figu e 4-3 Basic FIA mani old (La sen and Ha ey 2013) .................................................... 13
Figu e 4-4 Con igu a ion o a basic SIA sys em. C: ca ie , PP: pumping de ice; SV: selec ion
al e; HC: holding coil; RC: eac ion coil; D: de ec o ; W: was e; R: eagen ; S: sample (Pin o
e al. 2011) ........................................................................................................................... 14
Figu e 5-1 Elec omagne ic Wa e o m (Ha ey 2009) ......................................................... 15
Figu e 5-2 Elec omagne ic spec um (Ha ey 2009) ........................................................... 16
Figu e 5-3 Bee - Lambe law ac o s modi ied om (Ha ey 2009) .................................... 17
Figu e 5-4 Flame-S de ec o o e iew (A e 2015) ............................................................... 19
Figu e 5-5 Le : Non a e aged spec a. Righ : 15 scans a e aged ....................................... 19
Figu e 6-1 SIA schema ic modi ied om (Núñez 2016) ........................................................ 21
Figu e 6-2 SIA assembly ...................................................................................................... 22
Figu e 6-3 Mul iBu e e 2S .................................................................................................... 22
Figu e 6-4 SIA on iew ...................................................................................................... 24
Figu e 6-5 Val e posi ions ( on iew) ................................................................................. 24
Figu e 6-6 Mixing Cell........................................................................................................... 25
Figu e 6-7 Sc ip File B owse .............................................................................................. 28
Figu e 6-8 Sc ip execu ion ................................................................................................... 29
Figu e 7-1 Spec oscopy sys em .......................................................................................... 30
Figu e 7-2 Flame S Spec ome e ........................................................................................ 30
Figu e 7-3 SMA-Z-10-UL ...................................................................................................... 31
Figu e 7-4 DH-mini UV-VIS-NIR Ligh sou ce ....................................................................... 32
p. 72 Repo
Figu e 7-5 Spec oscopy applica ion wiza d ......................................................................... 32
Figu e 7-6 Concen a ion Choice .......................................................................................... 33
Figu e 7-7 Se Aquisi ion Pa ame e s ................................................................................... 34
Figu e 7-8 S o e Re e ence and Backg ound spec um ....................................................... 34
Figu e 7-9 Wa eleng h selec ion .......................................................................................... 35
Figu e 7-10 Da a sa ing con igu a ion sc een ...................................................................... 36
Figu e 8-1 Phenol ed in: Le : basic medium Righ : acid medium ........................................ 37
Figu e 8-2 Phenol ed abso p ion spec um (Sochacka 2015) ............................................. 38
Figu e 8-3 Reagen aspi a ion p ocedu e modi ied om (Núñez 2016) ................................ 38
Figu e 8-4 S anda d en ies .................................................................................................. 39
Figu e 8-5 Regions o de ec ion and quan iza ion (MacDougall and C umme 1980) .......... 41
Figu e 8-6 Theo e ical cu es o Dispe sion coe icien s olume(Gubeli e al. 1991) ........ 42
Figu e 9-1 Phenol ed p elimina y abso p ion spec um ....................................................... 43
Figu e 9-2 Le : co e ed cell. Cen e : Unco e ed cell, ligh s o . Righ : Unco e ed cell ........ 44
Figu e 9-3 Re e ence and backg ound spec ums: Top: Unco e ed cell. Bo om: co e ed cell
............................................................................................................................................. 44
Figu e 9-4 Abso p ion peaks when he simple cell is unco e ed .......................................... 45
Figu e 9-5 Phenol ed spec um o 2, 10, 40 ppm ............................................................... 46
Figu e 9-6 Le : Calib a ion cu e o Flame spec ome e a 550 and 560 nm. Righ :
Calib a ion a ixed wa eleng h (560 nm) wi h Flame and UV-Mini 1240 spec ome e s ...... 46
Figu e 9-7 Sample decay o e ime ...................................................................................... 47
Figu e 9-8 S anda ds' abso bance spec um ........................................................................ 47
Figu e 9-9 O iginal s anda ds’ calib a ion cu e ................................................................... 48
Figu e 9-10 Mul i al e p iming ............................................................................................. 49
Implemen a ion and op imiza ion o a sequen ial injec ion analysis (SIA) sys em by UV-Visible spec oscopy p. 73
Figu e 9-11 Abso bance o di e en injec ed olume .......................................................... 50
Figu e 9-12 Abso bance a io and dispe sion coe icien ...................................................... 50
Figu e 9-13 Calib a ion cu es Le : 1-20 ppm Righ : 1-16 ppm ........................................... 51
Figu e 9-14 Calib a ion 2016-6-1 .......................................................................................... 52
Figu e 9-15 Con idence in e als o abso p i i y o e ime .................................................. 53
Figu e 9-16 Peak cu es compa ison ................................................................................... 54
Figu e 9-17 Upwa ds and downwa ds calib a ions ............................................................... 55
Figu e 9-18 Ex e nal calib a ion and 50 % dilu ions Mul i al e po s a e labelled M1, M2, and
M3 Le : Ascending o de Righ : Descending o de .............................................................. 56
Figu e 9-19 In e nal calib a ions using 20 ppm as s ock solu ion .......................................... 57
Figu e 9-20 Calib a ion om s ock solu ion .......................................................................... 58
Figu e 9-21 Successi e dilu ion cu es ................................................................................ 59
Figu e 9-22 Cleaning spec al da a....................................................................................... 60