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Identification of Volatile and Semi-Volatile Compounds in Polymeric Coatings Used in Metal Cans by GC-MS and SPME

Abstract

Polymeric coatings are used as a protective layer to preserve food or beverage quality and protect it from corrosion and avoid a metallic taste. These types of materials can contain some chemicals that are susceptible to migrate to food and constitute a risk for consumers’ health. This study is focused on the identification of volatile and semi-volatile low molecular weight compounds present in polymeric coatings used for metal food and beverage cans. A method based on solid–liquid extraction followed by gas chromatography–mass spectrometry (GC-MS) was optimized for the semi-volatile compounds. Different solvents were tried with the aim of extracting compounds with different polarities. Furthermore, a method based on solid-phase microextraction (SPME) in headspace (HS) mode and gas chromatography coupled with mass spectrometry (HSSPME-GC-MS) was developed for the identification of potential volatile migrants in polymeric coatings. Some parameters such as extraction time, equilibrium temperature, or the type of fiber were optimized. Different compounds, including aldehydes such as octanal or nonanal, alcohols such as α-terpineol or 2-butoxyethanol, ethers, alkenes, or phthalic compounds, among others, were identified and confirmed with analytical standards both via SPME analysis as well after solvent extraction

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Identification of Volatile and Semi-Volatile Compounds in Polymeric Coatings Used in Metal Cans by GC-MS and SPME

Author: Vázquez Loureiro, Patricia; Lestido Cardama, Antía; Sendón García, Raquel; López Hernández, Julia; Paseiro Losada, Perfecto; Rodríguez Bernaldo de Quirós, Ana Isabel
Publisher: MDPI
Year: 2021
DOI: 10.3390/ma14133704
Source: https://minerva.usc.es/bitstreams/ac18c03f-500a-477d-938d-d99c467bd3cd/download
ma e ials
A icle
Iden i ica ion o Vola ile and Semi-Vola ile Compounds in
Polyme ic Coa ings Used in Me al Cans by GC-MS and SPME
Pa icia Vázquez-Lou ei o , An ía Les ido-Ca dama , Raquel Sendón , Julia López-He nández ,
Pe ec o Pasei o-Losada and Ana Rod íguez-Be naldo de Qui ós *


Ci a ion: Vázquez-Lou ei o, P.;
Les ido-Ca dama, A.; Sendón, R.;
López-He nández, J.; Pasei o-Losada,
P.; Rod íguez-Be naldo de Qui ós, A.
Iden i ica ion o Vola ile and
Semi-Vola ile Compounds in
Polyme ic Coa ings Used in Me al
Cans by GC-MS and SPME. Ma e ials
2021,14, 3704. h ps://doi.o g/
10.3390/ma14133704
Academic Edi o : Csaba Balázsi
Recei ed: 2 June 2021
Accep ed: 28 June 2021
Published: 2 July 2021
Publishe ’s No e: MDPI s ays neu al
wi h ega d o ju isdic ional claims in
published maps and ins i u ional a il-
ia ions.
Copy igh : © 2021 by he au ho s.
Licensee MDPI, Basel, Swi ze land.
This a icle is an open access a icle
dis ibu ed unde he e ms and
condi ions o he C ea i e Commons
A ibu ion (CC BY) license (h ps://
c ea i ecommons.o g/licenses/by/
4.0/).
Depa men o Analy ical Chemis y, Nu i ion and Food Science, Facul y o Pha macy, Uni e si y o San iago de
Compos ela, 15782 San iago de Compos ela, Spain; pa icia azquez.lou ei [email p o ec ed] (P.V.-L.);
[email p o ec ed] (A.L.-C.); [email p o ec ed] (R.S.); [email p o ec ed] (J.L.-H.);
[email p o ec ed] (P.P.-L.)
*Co espondence: ana. [email p o ec ed]; Tel.: +34-88-181-4965
Abs ac :
Polyme ic coa ings a e used as a p o ec i e laye o p ese e ood o be e age quali y
and p o ec i om co osion and a oid a me allic as e. These ypes o ma e ials can con ain some
chemicals ha a e suscep ible o mig a e o ood and cons i u e a isk o consume s’ heal h. This
s udy is ocused on he iden i ica ion o ola ile and semi- ola ile low molecula weigh compounds
p esen in polyme ic coa ings used o me al ood and be e age cans. A me hod based on solid–
liquid ex ac ion ollowed by gas ch oma og aphy–mass spec ome y (GC-MS) was op imized o
he semi- ola ile compounds. Di e en sol en s we e ied wi h he aim o ex ac ing compounds
wi h di e en pola i ies. Fu he mo e, a me hod based on solid-phase mic oex ac ion (SPME) in
headspace (HS) mode and gas ch oma og aphy coupled wi h mass spec ome y (HSSPME-GC-MS)
was de eloped o he iden i ica ion o po en ial ola ile mig an s in polyme ic coa ings. Some
pa ame e s such as ex ac ion ime, equilib ium empe a u e, o he ype o ibe we e op imized.
Di e en compounds, including aldehydes such as oc anal o nonanal, alcohols such as
α
- e pineol
o 2-bu oxye hanol, e he s, alkenes, o ph halic compounds, among o he s, we e iden i ied and
con i med wi h analy ical s anda ds bo h ia SPME analysis as well a e sol en ex ac ion.
Keywo ds: po en ial mig an s; polyme ic coa ings; GC-MS; SPME
1. In oduc ion
Mig a ion o componen s om ood con ac ma e ial o ood is a ma e o conce n
om he ood sa e y poin o iew. Special a en ion has been paid o low molecula weigh
compounds and pa icula ly o unknown compounds. Thei iden i ica ion is a cu en
challenge in he ood packaging ield [1].
Di e en ma e ials ha e adi ionally been used in ood packaging including glass,
me als, pape , pape boa ds, and plas ics. Ma sh e al. [
2
] epo ed some ad an ages
and disad an ages o hese ypical ma e ials used in be e age packaging, such as he
suscep ibili y o b eakages o he hea y weigh in he case o glass. Me al cans a e widely
used, and hey ha e se e al ad an ages o e o he ma e ials as hey a e able o ole a e
high empe a u e and p essu e condi ions [
3
]. Polyme ic coa ings a e used as unc ional
ba ie s be ween ood and me al cans. They p ese e he quali y o ood in e ms o la o ,
odo , and colo , as well as ex end shel -li e and help he me al can in p o ec ing ood om
ex e nal agen s such as ligh , oxygen, and mic oo ganisms, and acili a e anspo and
s o age o he canned ood.
Be e age packaging o en combines se e al ma e ials o exploi hese p ope ies.
Mul ilaye sys ems, new app oaches based on ac i e o in elligen packaging o ma e ials
wi h lowe en i onmen al impac s a e in de elopmen [2].
Be e age cans a e one o he mos used mul ilaye packaging ma e ials, made o
aluminum wi h an inne epoxy esin coa ing o p e en di ec con ac be ween ood o
Ma e ials 2021,14, 3704. h ps://doi.o g/10.3390/ma14133704 h ps://www.mdpi.com/jou nal/ma e ials
Ma e ials 2021,14, 3704 2 o 14
be e age and he aluminum su ace [
4
]. Final coa ings a e ob ained by he addi ion
o componen s such as c oss-linke s, sol en s, pigmen s, an i- oaming agen s, adhesion
p omo e s, esins, and su ac an s [
5
]. Du ing he polyme iza ion p ocess, side eac ions
can occu , and linea o cyclic byp oduc s may be o med. These unknown chemicals may
mig a e in o ood esul ing in consume exposu e [6].
Epoxy esins a e comme cially used in coa ings because o hei excep ional adhesion
due o he p esence o pola hyd oxyl and e he g oups in hei s uc u e [
7
]. Besides his
echnical ad an age, some d awbacks ega ding hei sa e y can be ound in he li e a u e;
some au ho s ha e shown he po en ial mig a ion o bisphenol A (BPA) om hese ma e ials
o ood [
8
]. Epoxy monome s such as bisphenol A-diglycidyl e he (BADGE) ha e been
ex ac ed om epoxy esins [
9
] and ound in ood simulan s a e mig a ion assays [
10
],
and o he BADGE-based de i a i es om epoxy coa ings we e also iden i ied by Schae e
e al. [11].
Commission Regula ion (EU) No. 10/2011 [
12
] es ablished speci ic ules o plas ic
ma e ials in ended o come in con ac wi h ood. Cu en ly, he e is no speci ic Eu opean
legisla ion o coa ings. Bo h in en ionally added subs ances (IAS) and non-in en ionally
added subs ances (NIAS) such as impu i ies, eac ion byp oduc s, and deg ada ion p od-
uc s can mig a e in o ood, and hey should be e alua ed.
These mig an s may also be oligome s, p epolyme s, ca alys , eac ion accele a o s,
epoxidized edible oils, es e s, waxes, lub ican s, me als, e c. [
13
,
14
]. The mig a ion o
hese chemicals om packaging o ood and be e age is one o he main conce ns o ood
sa e y au ho i ies.
Non- a ge ed me hods using LC-MS o GC-MS a e being widely employed o he
iden i ica ion o po en ial mig an s in ood packaging. Bo h echniques p o ide essen ial
and complemen a y in o ma ion necessa y o a comple e cha ac e iza ion o packaging
ma e ials. In GC-MS analysis, he use o comme cial lib a ies helps he iden i ica ion, al-
hough in he case o NIAS, hey usually a e no p esen in he da abases. B adley e al. [
15
]
ca ied ou an analysis ia headspace GC-MS and a sol en ex ac ion wi h ace oni ile
ollowed by GC-MS o de e mine ola ile compounds in epoxy phenolic can coa ings. The
au ho s de ec ed bisphenol A, used as a s a ing subs ance in he manu ac u ing o he coa -
ing. Mo e ecen ly, Ome e al. [
16
] used GC-MS wi h di e en ioniza ion sou ces, namely
elec on ioniza ion (EI) and a mosphe ic p essu e chemical ioniza ion (APCI), and di e en
mass spec ome e s, speci ically quad upole, ime-o - ligh , and o bi ap, o in es iga e
po en ial mig an s in polyes e –polyu e hane lacque s. Se e al cyclic oligoes e e ame s
we e iden i ied in he wo lacque s es ed. In ano he s udy epo ed in he li e a u e,
GC-MS and highly accu a e mass spec ome y was used o he analysis o bisphenol A al-
e na i e ood-con ac me al can coa ings. Cyclic polyes e oligome s om polyes e -based
coa ings and bisphenol- ype compounds, including e ame hyl bisphenol F, e ame hyl
bisphenol F diglycidyl e he , and bisphenol F, among o he s, we e iden i ied [3].
The aim o his wo k was o de elop a sc eening me hod o he iden i ica ion o ola ile
compounds in polyme ic coa ings o me al cans o be e age packaging. Fo ha pu pose, a
me hod based on solid–liquid ex ac ion ollowed by gas ch oma og aphy–mass spec ome y
(GC-MS) and a me hod based on solid-phase mic oex ac ion in headspace mode and gas
ch oma og aphy coupled wi h mass spec ome y (HSSPME-GC-MS) we e op imized.
2. Ma e ials and Me hods
2.1. Sample Desc ip ion and FTIR Cha ac e iza ion
A o al o en be e ages packed in me al cans we e bough in local supe ma ke s
in San iago de Compos ela (Spain). All o hem we e wo-piece cans. The in e nal su -
ace o me al cans is o en coa ed wi h a polyme ic coa ing (wi h a hickness o abou
2µm) o p ese e ood and a oid me al co osion. The hickness o he samples analyzed
(
me al + coa ing
) is p o ided in Table 1. The hickness o he packaging was measu ed
wi h a manual digi al mic ome e (Mi u oyo-Japan, Kanagawa, Japan). The polyme ic
coa ings we e analyzed by using an a enua ed o al e lec ance FTIR spec ome e and
Ma e ials 2021,14, 3704 3 o 14
we e iden i ied using he KnowI All
®
17.4.135.B IR Spec al Lib a ies o Polyme s and
Rela ed Compounds (Bio-Rad Labo a o ies, Inc., He cules, CA, USA).
Table 1. Sample desc ip ions.
Code Be e age Polyme ic Coa ing Thickness (µm)
BC01 T adi ional Bee
La . Ex .: PU
La e al: 114.5
Lid: 313.0
La . In .: Phx
Lid In .: Phx
Lid Ex .: Phx
BC02 Vodka mixed d ink
La . Ex .: PU
La e al: 109.0
Lid: 218.0
La . In .: Phx
Lid In .: Epx
Lid Ex .: Epx
BC03 Mixed lemon la ou
La . Ex .: PU
La e al: 104.0
Lid: 218.0
La . In .: Phx
Lid In .: Phx
Lid Ex .: Phx
BC04 Ene gy D ink Ze o
La . Ex .: PU
La e al: 112.0
Lid: 264.0
La . In .: Phx
Lid In .: Epx
Lid Ex .: Epx
BC05 S a Wa s Space
Punch
La . Ex .: PP
La e al: 114.0
Lid: 331.0
La . In .: Ac ylic
Lid In .: Polyes e
Lid Ex .: Phx
BC06 G een cola
La . Ex .: PU
La e al: 115.0
Lid: 234.0
La . In .: Phx
Lid In .: Phx
Lid Ex .: Phx
BC07 Tonic o iginal
La . Ex .: PU
La e al: 111.0
Lid: 258.0
La . In .: Phx
Lid In .: Epx
Lid Ex .: Epx
BC08 Tonic wa e o iginal
La . Ex .: PU
La e al: 113.0
Lid: 230.0
La . In .: Phx
Lid In .: Epx
Lid Ex .: Epx
BC09 P emium onic wa e
La . Ex .: PU
La e al: 123.0
Lid: 226.0
La . In .: Ac ylic
Lid In .: Polyes e
Lid Ex .: Phx
BC10 Na u al mine al
wa e d ink
La . Ex .: PU
La e al: 103.0
Lid: 248.0
La . In .: Phx
Lid In .: Epx
Lid Ex .: Epx
Epx: Epoxy esin; Ex .: ex e nal; In : In e nal; La : La e al; Phx: Phenoxy esin; PP: Polyp opylene;
PU: Polyu e hane.
The pH o he be e age samples anged be ween 2.56 and 6.60. A b ie o e iew o
he samples is p esen ed in Table 1; and a mo e de ailed desc ip ion o he samples used in
his s udy was desc ibed by Les ido-Ca dama e al. [17].
Ma e ials 2021,14, 3704 4 o 14
2.2. Sample T ea men
2.2.1. Sol en Ex ac ion P ocedu e
Samples we e opened, emp ied, and washed wi h wa m wa e be o e analysis. Cans
we e cu in o small pieces (app oxima ely 0.5 cm
2
), hen 0.8 g we e weigh ed in a ial
and
5 mL
o me hanol was added and a e wa d he ial was he me ically sealed. The
ex ac ion was pe o med in an o en a 70
◦
C o 24 h. One aliquo was hen emo ed wi h
a 0.22 µm poly e a luo oe hylene (PTFE)-memb ane il e and analyzed ia GC-MS.
2.2.2. SPME P ocedu e
An SPME holde o manual sampling and comme cial ibe s was pu chased om
Supelco (Belle on e, PA, USA). Fibe s wi h di e en coa ing ma e ials we e es ed: a
di inylbenzene-Ca boxen-polydime hylsiloxane (DVB/PDMS/CAR) ibe wi h 50–30
µ
m
hickness and a Ca boxen-polydime hylsiloxane (CAR-PDMS) ibe wi h 100
µ
m hickness.
P io o use hey we e condi ioned by inse ing hem in o he GC injec o acco ding o he
supplie ’s ins uc ions: o 1 h a 270 ◦C and 0.5 h a 250 ◦C, espec i ely.
Fo each expe imen , 0.8 g o each sample, p e iously cu in o small pieces (app oxi-
ma ely 0.5 cm
2
) we e weigh ed in o a 20 mL headspace ial and sealed wi h a PTFE- aced
silicone sep um (C omlab, Ba celona, Spain). The SPME ibe was pu in o he ial, and his
was hea ed a 100
◦
C o 30 min. The ibe was hen deso bed in o he GC injec o o 10 min
a 200
◦
C. The compounds abso bed by he ibe we e sepa a ed ia gas ch oma og aphic
analysis and iden i ied using he MS de ec o ope a ing in he desc ibed condi ions below.
2.3. Reagen s and Analy ical S anda ds
Ace oni ile HPLC g ade, me hanol, and hexane GC-MS g ade we e supplied by
Me ck (Da ms ad , Ge many). E hanol o analysis was supplied by Me ck (Da ms ad ,
Ge many). The 2-bu oxye hanol, spec opho ome ic g ade wi h a pu i y o
≥
99.0%, 2,2-
dime hyl-1,3-p opanediol wi h a pu i y o 99.0%, oc anal wi h a pu i y o 99%, D-Limonene,
ε
-Cap olac am; 2,6-Di- e -bu yl-1,4-benzoquinone wi h a pu i y o 98.0%, die hyl ph hala e
wi h a pu i y o 99.5%, benzophenone wi h a pu i y o
≥
99.0%, benzoic acid wi h a pu i y
o 99.5%, anillin wi h a pu i y o 99.0%, 2,4-di e bu ylphenol wi h a pu i y o 99.0%, and
α
- e pineol we e pu chased om Sigma Ald ich (S einheim, Ge many). Nonanal wi h
pu i y o 98.7% was pu chased om Supelco (Belle on e, PA, USA). The 2-phenoxye hanol
wi h pu i y o
≥
99.0% was supplied by Fluka (Seelze, Ge many). Wo king solu ions we e
p epa ed by dilu ing di e en amoun s o he s ock s anda d solu ion in me hanol.
2.4. GC-MS Condi ions o Sol en Ex ac ion Samples
A T ace 1300 gas ch oma og aph equipped wi h a p og ammed spli /spli less injec o ,
a 1310 au osample , and an ISQ LT Single Quad upole mass spec ome e (The mo Elec on
Co p., Madison, WI, USA) we e used o pe o m he GC analyses. The sepa a ion was
pe o med on a Rxi-5Sil MS (30 m
×
0.25 mm
×
0.25
µ
m) column om Res ek (Belle on e,
PA, USA). The ope a ing condi ions we e he ollowing: he injec o empe a u e was
300
◦
C and he empe a u e o he ans e line o he de ec o was 300
◦
C. The o en
empe a u e was se as ollows: ini ially he empe a u e was se a 40
◦
C o 2 min, hen
inc eased a a a e o 9
◦
C/min un il 300
◦
C and held o 12 min. Injec ion was pe o med
in spli less mode, and he injec ion olume was 1
µ
L. The ca ie gas was helium wi h a
low a e o 1 mL/min. The mass spec ome e was ope a ed in elec on impac ioniza ion
mode wi h a ull scan ange be ween 20 and 500 m/z.
Da a analysis was pe o med using Xcalibu e sion 4.1 and he NIST/EPA/NIH 11
mass spec al lib a y ( e sion 2.0) and Wiley Regis y TM 8 h edi ion da abase we e used
o iden i ica ion.
2.5. GC-MS Condi ions o SPME Analysis
A The mo Finnigan T ace GC gas ch oma og aph and a Finnigan T ace DSQ mass
selec i e de ec o (The mo Scien i ic, Wal ham, MA, USA) we e used o pe o m all GC
Ma e ials 2021,14, 3704 5 o 14
analyses. Fo SPME analyses, an Rxi-624Sil MS (30 m
×
0.25 mm
×
1.40
µ
m) column om
Res ek (Belle on e, PA, USA) was used, and he sepa a ion o compounds was pe o med
unde he ollowing ope a ing condi ions: he injec o empe a u e was se a 200
◦
C and
he ans e line empe a u e was 250
◦
C. The amp empe a u e was se om 45 o 250
◦
C.
The mass spec ome e ope a ed in ull scan mode (be ween 20 and 500 m/z).
Da a analysis was pe o med using Xcalibu e sion 2.0.7 and he NIST/EPA/NIH 11
mass spec al lib a y ( e sion 2.0) and Wiley Regis y TM 8 h edi ion da abase we e used
o de ec ion and iden i ica ion.
In o de o es ima e he oxici y o he iden i ied compounds, an in silico me hod,
namely C ame ules we e applied. Fo ha , he so wa e Tox ee was used [
18
]. Acco ding
o C ame ules, subs ances a e classi ied based on hei chemical s uc u e in o Class I (low
oxici y), Class II (in e media e oxici y) and Class III (high oxici y). Thus, Class I com-
p ises subs ances wi h simple chemical s uc u es such as common ca bohyd a es, acyclic
alipha ic hyd oca bons, and so on. Class II includes subs ances ha possess s uc u es
ha a e less innocuous han hose o Class I bu do no con ain subs ances wi h s uc u al
ea u es ha sugges oxici y like subs ances o Class III. Examples o Class II subs ances
a e common componen s o ood, subs ances con aining no unc ional g oups o he han
alcohol, aldehyde, acid, es e , e c. Class III includes subs ances wi h chemical s uc u es
ha may sugges signi ican oxici y o con ain eac i e unc ional g oups. Examples o
subs ances belonging o his Class a e ce ain benzene de i a i es, ce ain he e ocyclic
subs ances, e c. [19].
3. Resul s and Discussion
3.1. Sol en Selec ion o Can Ex ac ion
Di e en sol en s we e es ed wi h he aim o ex ac compounds wi h di e en
pola i ies p esen in he coa ing o me al cans. Samples we e ex ac ed unde di e en
condi ions, bo h me hanol and ace oni ile o 24 h a 70
◦
C, hexane o 4 h a 60
◦
C, and
a mix u e o hexane and e hanol (3:1 / ) o 24 h a 20
◦
C. In Figu e 1, ch oma og ams
ob ained a e ex ac ion wi h di e en sol en s a e shown. Me hanol was he sol en
selec ed o ex ac ion because mo e peaks we e de ec ed and iden i ied. Table 2lis s he
compounds de ec ed a e ex ac ion wi h di e en sol en s. As he analyzed samples we e
al eady in con ac wi h he d ink, some o he iden i ied compounds may ha e hei o igin
in ood. On he o he hand, i is in e es ing o no e ha la o ings a e commonly used in
hese be e ages, hus some o he de ec ed compounds in he samples a e au ho ized as
ood la o ings in he Eu opean Union [
20
]. These compounds a e indica ed in he able
wi h hei co esponding Fla is Numbe (FL No.). Some o hem a e, o example, benzoic
acid me hyl es e and cap ylic acid me hyl es e .
Ma e ials 2021, 14, x FOR PEER REVIEW 6 o 17
Figu e 1. Ch oma og ams o sample BC04 ex ac ed wi h di e en sol en s.
Table 2. Compa ison o he mos abundan de ec ed compounds in sample BC04 using di e en ex ac ion sol en s.
T /min Compound CAS Fl No. MeOH ACN Hex Hex: E OH
(3:1 / )
10.56 Benzoic acid
me hyl es e 93-58-3 09.725 x
11.01 Cap ylic acid
me hyl es e 111-11-5 09.117 x
12.97 Adipic acid
me hyl es e 627-93-0 x
17.17 Lau ic acid
me hyl es e 111-82-0 09.101 x
17.55
Unknown
compound
(m/z 129)
x
18.07 Die hyl
ph hala e * 84-66-2 x x x
19.92 Es e x
20.25
Unknown
compound
(m/z 56)
x
21.71 Thiophene x
25.07
Unknown
compound
(m/z 151)
x
25.56 Adipa e s uc-
u e x x x x
Figu e 1. Ch oma og ams o sample BC04 ex ac ed wi h di e en sol en s.

Ma e ials 2021,14, 3704 6 o 14
Table 2. Compa ison o he mos abundan de ec ed compounds in sample BC04 using di e en ex ac ion sol en s.
T /min Compound CAS Fl No. MeOH ACN Hex Hex: E OH (3:1 / )
10.56 Benzoic acid me hyl es e 93-58-3 09.725 x
11.01 Cap ylic acid me hyl es e 111-11-5 09.117 x
12.97 Adipic acid me hyl es e 627-93-0 x
17.17 Lau ic acid me hyl es e 111-82-0 09.101 x
17.55
Unknown compound (m/z129)
x
18.07 Die hyl ph hala e * 84-66-2 x x x
19.92 Es e x
20.25 Unknown compound (m/z56) x
21.71 Thiophene x
25.07
Unknown compound (m/z151)
x
25.56 Adipa e s uc u e x x x x
25.65 Adipa e s uc u e x x x x
30.43 Unknown compound x x x x
* Subs ances con i med wi h a s anda d solu ion.
Es e compounds we e mainly iden i ied in ex ac ion wi h me hanol as a sol en .
Some s udies show he mig a ion o hese ypes o compounds in cu ed a nishes used
in ood packaging [
21
]. In his wo k, samples we e ex ac ed wi h e hanol 95% ( / ).
Adipic acid has been epo ed as a chemical in e media e used in he manu ac u ing o
polyu e hane esins [22].
3.2. Op imiza ion o SPME Me hod
In he p esen wo k, a me hod based on solid-phase mic oex ac ion in headspace
mode and gas ch oma og aphy coupled wi h mass spec ome y (HSSPME-GC-MS) was
de eloped o he iden i ica ion o po en ial mig an s in polyme ic coa ings.
SPME is an easy, cheap, and clean me hod o use, al hough he e is a o need u he
op imiza ion in e ms o equilib ium o expe imen al condi ions such as hea ing empe a-
u e, ex ac ion ime, sample olume, concen a ion o ola iles, and sample ma ix [
23
].
Fo ha pu pose, some pa ame e s such as ex ac ion ime, equilib ium empe a u e, o
he ype o ibe we e op imized.
The e ec o ex ac ion empe a u e, ex ac ion ime, and deso p ion ime was e alu-
a ed using he ibe DVB-CAR-PDMS.
Fi s ly, he ex ac ion ime was op imized. Di e en imes we e es ed (10, 30, and
60 min
), keeping ex ac ion empe a u e (40, 70, and 100
◦
C), equilib a ion ime (2 min),
and deso p ion ime (10 min) ixed. Unde hese condi ions he bes esul s we e ound a
30 and 60 min o ex ac ion because mo e peaks we e iden i ied and wi h a highe in ensi y,
and he e was ha dly any di e ence be ween he wo es ed imes, he e o e,
30 min
o
ex ac ion was selec ed. Once he ime o ex ac ion was op imized, he empe a u e was
s udied anging om 40 o 100
◦
C. The di e ence in he sensi i i y and he numbe o
peaks de ec ed was ela ed wi h he inc ease o he empe a u e.
The e ec s o empe a u e and ex ac ion ime we e e iden om he ch oma og ams
ob ained unde he ollowing condi ions: 40, 70, and 100
◦
C o 10, 30, and 60 min. An
inc ease in he peak ch oma og aphic a ea was ound, especially wi h he less ola ile
compounds a highe empe a u es.
Machiels e al. [
24
] epo ed ha highly ola ile compounds we e no a ec ed by
deso p ion ime and less ola ile compounds needed mo e ime o deso b.
Ma e ials 2021,14, 3704 7 o 14
The nex pa ame e ha was op imized was he amoun o he sample used, which
was conside ed be ween 0.8 g and 2 g. Finally, he amoun 0.8 g was chosen because la ge
amoun s o sample did no lead o highe in ensi y o he ch oma og aphic peaks.
I is impo an o ge a well-balanced comp omise be ween sensi i i y and ex ac-
ion a e, pa icula ly wi h espec o he ex ac ion empe a u e, o achie e a ca e ul
op imiza ion o each pa ame e .
Bes esul s and wi h he highe peak in ensi ies we e ob ained o 30 min a 100
◦
C
wi h 2 min o equilib a ion ime and 10 min o deso p ion ime.
Selec ion o he Type o Fibe
The selec ion o he ibe and SPME ex ac ion condi ions can a ec he sensi i i y
and accu acy o SPME analysis. Pa k e al. [
25
] a i med ha using wo-phase ibe s
(Ca boxen-PDMS) seems o be mo e sui able o measu ing low molecula weigh com-
pounds, whe eas h ee-phase ibe s (DVB-Ca boxen on PDMS) appea ed o be mo e app o-
p ia e o measu ing high molecula weigh compounds. DVB-CAR-PDMS ibe has shown
he bes so p ion capaci y o some compounds such as ood packaging con aminan s in
alcoholic be e ages.
In ou s udy, a DVB/PDMS/CAR ibe wi h 50–30
µ
m hickness and a CAR-PDMS
wi h 100
µ
m hickness we e es ed. Peak a eas om decanal, 2-oxepanone and die hylph-
hala e, which we e he mos abundan peaks, we e compa ed be ween bo h ypes o ibe s,
wi h he i s one achie ing he highe esponse. This ac con i ms ha DVB/PDMS/CAR
ibe is mo e app op ia e o sepa a e ola ile compounds wi h highe molecula weigh .
3.3. Can Coa ings Analysis ia GC a e a Sol en Ex ac ion
GC-MS was used o en a i ely iden i y semi- ola ile compounds ha could po en-
ially mig a e om polyme ic coa ings. A GC-MS me hod ha co e ed a wide mass ange
( om 35 o 500 m/z) wi h a sui able g adien o empe a u es was used. Samples we e
injec ed in spli less mode. Resul s ob ained a e shown in Table 3. Only compounds wi h
app op ia e di ec ma ching ac o s (SI) and e e se sea ch ma ching (RSI) a e iden i ied in
Table 3. In gene al, alues o 900 o g ea e a e conside ed an excellen ma ch, 800–900 a
good ma ch, and 700–800 a ai ma ch. Fo hose compounds whose iden i ica ion was no
achie able, he mos abundan m/zis speci ied.
Table 3. Compounds iden i ied ia GC-MS analysis a e ex ac ion wi h MeOH as a sol en .
T /min Compound CAS Fl No. SI RSI Sample(s) TC
10.56 Benzoic acid me hyl es e 93-58-3 09.725 745 857 BC04 I
11.01 Cap ylic acid me hyl es e 111-11-5 09.117 701 789 BC04 I
11.37 2-Oxepanone 502-44-3 729 862 BC06, BC07 I
12.34 α-Te pineol * 98-55-5 02.014 902 936 9 III
12.97 Adipic acid me hyl es e 627-93-0 794 867 BC01, BC03, BC04,
BC06–BC08 I
14.2 Isobenzo u an-1,3-dione 85-44-9 841 922 BC02, BC05, BC07,
BC10 III
15.58 Unknown diol BC05
16.93 (+)-Ledene 21747-46-6 893 927 BC09 I
17.17 Lau ic acid me hyl es e 111-82-0 09.101 855 878 BC01–BC10 I
17.55 Es e s uc u e (m/z129) BC01–BC10
18.08 Die hyl ph hala e * 84-66-2 929 938 BC01–BC05, BC09,
BC10 I
18.37
Unknown compound (m/z107, 163)
BC09
19.28 Dodecalac one 2305-05-7 10.019 855 894 BC05 II
19.92 Es e s uc u e (m/z129) BC01–BC10
20.29 Unknown compound (m/z56, 111) BC08
Ma e ials 2021,14, 3704 8 o 14
Table 3. Con .
T /min Compound CAS Fl No. SI RSI Sample(s) TC
20.72 Bu yl oc yl ph hala e 84-78-6 714 758 BC02 I
20.99 Ke one s uc u e BC05, BC07
21.53 Unknown compound m/z(45, 109) BC05
21.73 2-Isobu yl-5-p opyl hiophene 4861-63-6 BC01–BC06,
BC08–BC10 III
21.99
7,9-Di- e -bu yl-1-
oxaspi o[4,5]deca-6,9-diene-2,8-
dione
82304-66-3 BC05 III
22.33 and 23.3 Unknown compound (Ph hala e
s uc u e m/z: 149) BC02, BC05, BC07
23.81 Unknown compound (m/z151) BC06–BC08, BC10
25.08 Unknown compound (m/z151) BC01, BC02, BC04,
BC08–BC10
25.56
Unknown compound (m/z129, 111)
BC01–BC10
25.65
Unknown compound (m/z129, 111)
BC01–BC010
26.53 Unknown compound (m/z163) BC08, BC10
27.19 α-Me hyl-δ-oxo-2-phenyl-1,3-
dioxolane-2-hep aneni ile 58422-90-5 782 940 BC02, BC05, BC07,
BC09, BC10 III
27.42 Hexa(me hoxyme hyl)melamine 68002-20-0 857 874 BC01- BC03, BC05,
BC08, BC10 III
27.87
Unknown compound (m/z143, 111)
BC08
28.4 Unknown compound (Ph hala e
s uc u e m/z149)
BC02, BC05, BC07,
BC09, BC10
29.96 Unknown compound (m/z301) BC02, BC05,
BC09, BC10
30.46 Unknown compound (m/z69, 81) BC08
32.45 Unknown compound (m/z345) BC02, 5 BC0,
BC09, BC10
35.36 Unknown compound (Ph hala e
s uc u e m/z: 149) BC02, BC05, BC010
35.95 Unknown compound (m/z389) BC02, BC05, BC09
* Subs ances con i med wi h a s anda d solu ion.
Vola ile compounds coming om he be e age we e de ec ed. Thus, di e en es-
e s (e.g., benzoic acid me hyl es e , lau ic acid me hyl es e , e c.) we e iden i ied. Es-
e s we e epo ed by D agone e al. [
26
] in alcoholic dis illed be e ages, which con-
ibu e o he g ea es p opo ion o he o al a oma. The analysis was pe o med using
dichlo ome hane as an ex ac ion sol en and he compounds we e sepa a ed on a CP-Wax
52 CB (
50 m ×0.25 mm
i.d., 0.2
µ
m ilm hickness, Ch ompack). Ledene, a sesqui e pene
hyd oca bon, has also been ound in na u al p oduc s [
27
].
α
-Me hyl-
δ
-oxo-2-phenyl-1,3-
dioxolane-2-hep aneni ile has been epo ed as a p ecu so o hymol and a ca ac ol
and eugenol in e media y [
28
]. Mo eo e , la o ings au ho ized in he EU [
20
], such as
α
- e pineol and dodecalac one, we e iden i ied in di e en samples. These subs ances
belong o Class III and Class II, acco ding o C ame ules, espec i ely.
Wi h espec o compounds coming om he packaging ma e ials, se e al plas icize s,
including ph hala es (e.g., die hyl ph hala e, bu yl oc yl ph hala e), we e iden i ied in
almos all samples. Chemicals o ph hala e es e s (PAEs) can ac as endoc ine dis up-
o s and lead o ad e se e ec s on o ganisms e en in a low concen a ion [
29
]. They
can also induce a ious e iological diseases o humans, such as diso de s o he male
ep oduc i e ac , b eas and es icula cance s, and dys unc ion o he neu oendoc ine
sys em [
30
]. Isobenzo u an-1,3-dione, also called ph halic anhyd ide, was iden i ied in
samples BC02, BC05, BC07, and BC10. The mos impo an de i a i es o his compound
Ma e ials 2021,14, 3704 9 o 14
a e plas icize s and also polyes e esins and dyes [
31
]. This compound has been clas-
si ied as high oxici y (Class III), acco ding o C ame ules. Besides, i can be pa o
a cu ing agen sys em used du ing he manu ac u ing o an epoxy esin [
32
]. O he
compounds iden i ied include 2-oxepanone and hexa(me hoxyme hyl)melamine. The
lac one has been epo ed as a deg ada ion p oduc o polyu e hanes and in his s udy
he analysis was ca ied ou by py olysis-gas-ch oma og aphy/mass spec ome y [
33
],
and hexa(me hoxyme hyl)melamine is widely employed as a c oss-linking agen in coa -
ings [
34
]. This compound belongs o Class III, acco ding o C ame ules. A NIAS com-
pound, speci ically 7,9-di- e -bu yl-1-oxaspi o[4,5]deca-6,9-diene-2,8-dione (Figu e 2), was
iden i ied in sample BC05 and i p esen s high oxici y (Class III). This compound has been
epo ed as a deg ada ion p oduc o he an ioxidan I ganox 1010 and has been ound in
se e al samples o bo h plas ic and pape packaging and in polyu e hane adhesi es [
35
,
36
].
In plas ic ma e ials he analy e was de e mined in aqueous ex ac s using he pu ge and
ap me hod combined wi h GC-MS [36].
Ma e ials 2021, 14, x FOR PEER REVIEW 11 o 17
Figu e 2. Chemical s uc u e o 7,9-di- e -bu yl-1-oxaspi o[4,5]deca-6,9-diene-2,8-dione.
Fo some compounds, despi e hei high abundance, iden i ica ion was no possible
wi h he spec al lib a ies a ailable, such as he compounds a 28.4 min (m/z 149, which is
he cha ac e is ic mass o ph hala es compounds), 29.97 min (m/z 301), 32.45 min (m/z 345),
35.37 min (m/z 149), and 35.95 min (m/z 389). De ailed in o ma ion abou he mass spec a
o he uniden i ied compounds is a ailable in he elec onic Supplemen a y Ma e ial.
3.4. Can Coa ings Analysis ia SPME
The compounds de ec ed a e he ex ac ion wi h SPME a e summa ized in Table 4.
Only compounds wi h app op ia e di ec ma ching ac o s (SI) and e e se sea ch ma ch-
ing (RSI) a e included. Fo hose compounds whose iden i ica ion was no achie able, he
mos abundan m/z is speci ied.
Table 4. Compounds iden i ied ia SPME GC-MS analysis.
T
/
min Compound CAS Fl No. SI RSI Sample(s) TC
9.61 P opylene gly-
col 57-55-6 571 818 BC04 I
13.72 2-Bu oxy-
e hanol * 111-76-2 02.242 866 925 BC01–BC10 I
15.37 α-Te pinene 99-86-5 01.019 586 754 BC09 I
15.61 Benzaldehyde 100-52-7 05.013 631 865 BC01, BC05 I
15.85
2,2-Dime hyl-
1,3-P opane-
diol *
126-30-7 821 892
BC01, BC02,
BC03, BC04,
BC08
I
16.11 Oc anal * 124-13-0 05.009 505 701 BC04 I
16.28
1,2,3,4-Te a-
me hyl ben-
zene
488-23-3 849 879 BC09 I
16.43 Limonene * 5989-27-5 01.045 916 924 BC02, BC03,
BC05–BC08 I
16.5 p-Cymene 99-87-6 01.002 909 926
BC02, BC03,
BC06, BC09 I
16.69 1-Hexanol-2-
e hyl 104-76-7 02.082 809 913
BC05, BC06,
BC08 I
17.05 g-Te pinene 99-85-4 01.020 882 894 BC02, BC09 I
17.68 Te pinolene 586-62-9 01.005 795 864 BC02 I
18.07 Benzene s uc-
u e
BC02, BC05,
BC07, BC09
Figu e 2. Chemical s uc u e o 7,9-di- e -bu yl-1-oxaspi o[4,5]deca-6,9-diene-2,8-dione.
Fo some compounds, despi e hei high abundance, iden i ica ion was no possible
wi h he spec al lib a ies a ailable, such as he compounds a 28.4 min (m/z149, which is
he cha ac e is ic mass o ph hala es compounds), 29.97 min (m/z301), 32.45 min (m/z345),
35.37 min (m/z149), and 35.95 min (m/z389). De ailed in o ma ion abou he mass spec a
o he uniden i ied compounds is a ailable in he elec onic Supplemen a y Ma e ial.
3.4. Can Coa ings Analysis ia SPME
The compounds de ec ed a e he ex ac ion wi h SPME a e summa ized in Table 4.
Only compounds wi h app op ia e di ec ma ching ac o s (SI) and e e se sea ch ma ching
(RSI) a e included. Fo hose compounds whose iden i ica ion was no achie able, he mos
abundan m/zis speci ied.
Table 4. Compounds iden i ied ia SPME GC-MS analysis.
T /min Compound CAS Fl No. SI RSI Sample(s) TC
9.61 P opylene glycol 57-55-6 571 818 BC04 I
13.72 2-Bu oxye hanol * 111-76-2 02.242 866 925 BC01–BC10 I
15.37 α-Te pinene 99-86-5 01.019 586 754 BC09 I
15.61 Benzaldehyde 100-52-7 05.013 631 865 BC01, BC05 I
15.85 2,2-Dime hyl-1,3-P opanediol * 126-30-7 821 892 BC01, BC02, BC03,
BC04, BC08 I
16.11 Oc anal * 124-13-0 05.009 505 701 BC04 I
16.28 1,2,3,4-Te ame hyl benzene 488-23-3 849 879 BC09 I
16.43 Limonene * 5989-27-5 01.045 916 924 BC02, BC03,
BC05–BC08 I