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Cytotoxic plant extracts towards insect cells: bioactivity and nanoencapsulation studies for application as biopesticides

Abstract

The potential of plant extracts as bioinsecticides has been described as a promising field of agricultural development. In this work, the extracts of Punica granatum (pomegranate), Phytolacca americana (American pokeweed), Glandora prostrata (shrubby gromwell), Ulex europaeus (gorce), Tagetes patula (French marigold), Camellia japonica red (camellia), Ruta graveolens (rue or herb-of-grace) were obtained, purified, and their activity against Spodoptera frugiperda (Sf9) insect cells was investigated. From the pool of over twenty extracts obtained, comprising different polarities and vegetable materials, less polar samples were shown to be more toxic towards the insect cell line Sf9. Among these, a dichloromethane extract of R. graveolens was capable of causing a loss of viability of over 50%, exceeding the effect of the commercial insecticide chlorpyrifos. This extract elicited chromatin condensation and the fragmentation in treated cells. Nanoencapsulation assays of the cytotoxic plant extracts in soybean liposomes and chitosan nanostructures were carried out. The nanosystems exhibited sizes lower or around 200 nm, low polydispersity, and generally high encapsulation efficiencies. Release assays showed that chitosan nanoemulsions provide a fast and total extract release, while liposome-based systems are suitable for a more delayed release. These results represent a proof-of-concept for the future development of bioinsecticide nanoformulations based on the cytotoxic plant extracts.

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Cytotoxic plant extracts towards insect cells: bioactivity and nanoencapsulation studies for application as biopesticides

Author: Lopes, Ana I. F.; Monteiro, Mariana; Araújo, Ana Rita L.; Rodrigues, Ana Rita Oliveira; Castanheira, Elisabete M. S.; Pereira, David M.; Olim, Pedro; Fortes, A. Gil; Gonçalves, M. Sameiro T.
Publisher: MDPI
Year: 2020
DOI: 10.3390/molecules25245855
Source: https://repositorium.uminho.pt/bitstreams/f32891d9-dee8-4e44-969f-67ecc51b6920/download
molecules
A icle
Cy o oxic Plan Ex ac s owa ds Insec Cells:
Bioac i i y and Nanoencapsula ion S udies o
Applica ion as Biopes icides
Ana I. F. Lopes 1,2, Ma iana Mon ei o 1,2, Ana R. L. A aújo 1, Ana Ri a O. Rod igues 2,
Elisabe e M. S. Cas anhei a 2, Da id M. Pe ei a 3, Ped o Olim 3, A. Gil Fo es 1
and M. Samei o T. Gonçal es 1,*
1Cen e o Chemis y, Depa men o Chemis y, Campus o Gual a , Uni e si y o Minho,
4710-057 B aga, Po ugal; [email p o ec ed] (A.I.F.L.); [email p o ec ed] (M.M.);
[email p o ec ed] (A.R.L.A.); [email p o ec ed] (A.G.F.)
2Cen e o Physics, Depa men o Physics, Campus o Gual a , Uni e si y o Minho,
4710-057 B aga, Po ugal; [email p o ec ed] (A.R.O.R.); [email p o ec ed] (E.M.S.C.)
3REQUIMTE/LAQV, Labo a o y o Pha macognosy, Depa men o Chemis y, Facul y o Pha macy,
Uni e si y o Po o, R. Jo ge Vi e bo Fe ei a, 228, 4050-313 Po o, Po ugal; dpe ei a@ .up.p (D.M.P.);
up201706671@ .up.p (P.O.)
*Co espondence: [email p o ec ed]; Tel.: +351253604372
Recei ed: 12 No embe 2020; Accep ed: 8 Decembe 2020; Published: 11 Decembe 2020


Abs ac :
The po en ial o plan ex ac s as bioinsec icides has been desc ibed as a p omising
ield o ag icul u al de elopmen . In his wo k, he ex ac s o Punica g ana um (pomeg ana e),
Phy olacca ame icana (Ame ican pokeweed), Glando a p os a a (sh ubby g omwell), Ulex eu opaeus
(go ce), Tage es pa ula (F ench ma igold), Camellia japonica ed (camellia), Ru a g a eolens ( ue o
he b-o -g ace) we e ob ained, pu i ied, and hei ac i i y agains Spodop e a ugipe da (S 9) insec cells
was in es iga ed. F om he pool o o e wen y ex ac s ob ained, comp ising di e en pola i ies
and ege able ma e ials, less pola samples we e shown o be mo e oxic owa ds he insec cell
line S 9. Among hese, a dichlo ome hane ex ac o R. g a eolens was capable o causing a loss o
iabili y o o e 50%, exceeding he e ec o he comme cial insec icide chlo py i os. This ex ac
elici ed ch oma in condensa ion and he agmen a ion in ea ed cells. Nanoencapsula ion assays
o he cy o oxic plan ex ac s in soybean liposomes and chi osan nanos uc u es we e ca ied ou .
The nanosys ems exhibi ed sizes lowe o a ound 200 nm, low polydispe si y, and gene ally high
encapsula ion e iciencies. Release assays showed ha chi osan nanoemulsions p o ide a as and o al
ex ac elease, while liposome-based sys ems a e sui able o a mo e delayed elease. These esul s
ep esen a p oo -o -concep o he u u e de elopmen o bioinsec icide nano o mula ions based on
he cy o oxic plan ex ac s.
Keywo ds: biopes icides; bioinsec icides; Ru a g a eolens; chlo py i os; nanoencapsula ion
1. In oduc ion
Many syn he ic chemicals ha e been used in plan p o ec ion agains ag oindus ial and medicinal
pes s o he las 60 yea s [
1
–
3
]. This has caused a s ong nega i e impac a di e en le els, and he e
a e se ious conce ns abou hei side e ec s, such as he p esence o esidues on ood and d inking
wa e , oxici y o humans as well as o o he non- a ge o ganisms, and high pe sis ence, leading o
an eme gence o pes esis ance. These ac s ha e demanded o a d as ic dec ease in he use o
chemical pes icides and opening up space o new and sa e al e na i e s a egies [
1
]. The use o
na u al compounds o con ol weeds has long been accep ed as an en i onmen iendly s a egy,
Molecules 2020,25, 5855; doi:10.3390/molecules25245855 www.mdpi.com/jou nal/molecules
Molecules 2020,25, 5855 2 o 14
bu a me s ha e mos ly elied on oxic syn he ic ag ochemicals. New ools in pes managemen a e
based on biopes icides, which include semiochemicals and plan -inco po a ed p o ec an s, bo anical
and mic obial de i ed chemicals, and also new syn he ic analogues [
1
]. The majo p oblems in o ganic
ag icul u e aced by a me s a e weed managemen , c op diseases and insec con olling ools. Due o
he di e si y o chemicals p esen , na u al p oduc s ha e become impo an sou ces o mos biological
ac i i y op imiza ion, also playing also an impo an ole in d ug disco e y [
4
]. In ecen yea s,
esea ch has been ocused on he pes icidal e iciency o many phy ocompounds, om essen ial oils
o mo e complex mix u es ex ac ed om di e en plan s [
5
,
6
]. Compa ed o syn he ic pes icides,
phy ochemical biopes icides p esen lowe oxici y, a e less pe sis en , and biodeg adable [
1
,
7
].
Phy ochemical biopes icides, such as nico ine, o enone, py e h ins and sabadilla alkaloids, a e some
examples o he i s se ies o bo anical pes icides used. Howe e , due o ei he hei s abili y o
oxici y and ad e se e ec s on human heal h, hei use has been es ic ed, and despi e an inc easing
applica ion, hese emain less han 5% o he o al pes icide use [8].
Phy ochemical biopes icides comp ise a se ies o seconda y me aboli es ha ac in a syne gis ic
way, which s ongly educes he chances o insec pes s o de elop esis ance. Li e a u e has co e ed
in de ail many plan species and hei use as biopes icides.
Punica g ana um L. 1753, Phy olacca ame icana L. 1753, Glando a p os a a Loisel, 1844, Ulex eu opaeus
L. 1753, Tage es pa ula L. 1753, Camellia japonica L. 1753 and Ru a g a eolens L. 1753 displayed a huge ange
o biological ac i i ies [
3
,
9
–
19
], including an ibac e ial (e.g., P. g ana um) [
9
], an i i al (e.g., P. g ana um,
C. japonica) [
10
,
11
], an i ungal (e.g., P. g ana um,T. pa ula,C. japonica) [
12
], nema icide (T. pa ula) [
13
],
he bicide (U. eu opaeus) and insec icide (e.g., T. pa ula and R. g a eolens) [14–19].
The chemical composi ion and bioac i i y o R. g a eolens lea es we e s udied and es ed agains
he maize wee il. The insec icidal and epellen p ope ies o R. g a eolens we e analyzed and e alua ed
in con ac and apo o ms, wi h a o al o 45 compounds de ec ed by ch oma og aphic echniques,
mos o which we e 2-ke ones. The esea ch ca ied ou o da e suppo s he e idence ha R. g a eolens
lea es con ain bioac i e seconda y plan me aboli es, which jus i y i s use agains S.zeamais in s o age
pes managemen p og ams [
20
]. Lee e al. isola ed essen ial oils om he lowe s and lea es o
R. g a eolens, which we e e alua ed using umigan and con ac oxici y bioassays agains s o e ood
pes s, suppo ing he eco-po en ial o using R. g a eolens essen ial oil and i s majo cons i uen s in he
managemen o s o ed pes s [21,22].
Despi e he epo ed ac i i y agains pes s, se e al plan compounds exhibi ed some limi a ions in
hei applica ion, due o hei easy deg ada ion and high ola ili y. Nanoencapsula ion echniques a ise
as sui able s a egies o allow o he p ese a ion and con olled elease o plan componen s [
23
,
24
].
Speci ically, lipid-based nanosys ems ha e been widely used as ehicles o bioac i es in cosme ic and
pha maceu ical indus ies [
25
,
26
], as well as o he encapsula ion o plan ex ac s wi h insec icidal
ac i i y [
27
,
28
], being a p omising ou e o a sa e applica ion o pes icides [
29
]. Plan ex ac s ha e also
been encapsula ed in cyclodex ins [
24
] and polyme ic nanopa icles, he la e including algina e [
30
],
gum a abic/mal odex in [
31
], gela in [
32
], poly inylalcohol (PVA) [
33
], poly(dl-lac ide-co-glycolide)
(PLGA) [34] and chi osan nanos uc u es [35,36].
In his wo k, ex ac s om se en plan species, P. g ana um (pomeg ana e), P. ame icana
(Ame ican pokeweed), G. p os a a (sh ubby g omwell), U. eu opaeus (go ce), T. pa ula (F ench ma igold),
C. japonica (camellia) and R. g a eolens ( ue o he b-o -g ace), we e isola ed using wa e /e hanol and
dichlo ome hane as sol en s. The ob ained ex ac s we e e alua ed as po en ial insec icides, h ough he
assessmen o hei biological ac i i y agains S 9 insec cell lines, compa ed wi h a comme cial syn he ic
pes icide. Conside ing he insec icidal ac i i y exhibi ed by he R. g a eolens dichlo ome hane ex ac ,
encapsula ion assays in chi osan nanoemulsions and lipid nanosys ems we e ca ied ou , o he u u e
de elopmen o g een insec icide nano o mula ions.
Molecules 2020,25, 5855 3 o 14
2. Resul s and Discussion
2.1. Plan Ex ac s
A se ies o se en plan species we e selec ed, aking in o accoun hei p oduc ion in he coun y,
endemic cha ac e is ics, he in o ma ion o li e a u e, as well as hei unexploi ed po en ial in he ield
o bioinsec icides. A e he ha es , he pa s o plan s/ ui s ha we e in ended o be s udied we e
sepa a ed, namely ui peel in he case o P. g ana um (pomeg ana e); be ies in he case o P. ame icana
(Ame icanpokeweed); lowe sandlea esin hecaseo G.p os a a(sh ubbyg omwell),U.eu opaeus(go ce),
R. g a eolens ( ue o he b-o -g ace), and T. pa ula (F ench ma igold)—in he o me , lowe s (sepa a ed om
he ecep acle) and lea es we e ex ac ed sepa a ely—and lea es in he case o C. japonica.
The p epa a ion o he plan ma e ial included d ying unde sunligh (20–25
◦
C, 45 days) (peel o
P. G ana um), he lyophiliza ion (be ies o P. ame icana, lea es and lowe s o T. pa ula), o d ying
in an o en (40–45
◦
C, 3 days), ollowed in bo h cases by g ounding wi h a sh edde o ob ain he
co esponding powde , which was passed h ough a sie e un il a pa icle size
≤900 µm
was ob ained.
Fu he mo e, hese ma e ials we e subjec ed o Soxhle ex ac ion wi h sol en sys ems o di e en
pola i ies, namely in a pola sys em, using a wa e /e hanol solu ion (1:1), and in a less pola one,
using dichlo ome hane, o 9 o 4 h, espec i ely. The sol en s we e emo ed by e apo a ion unde
educed p essu e (dichlo ome hane ex ac s) ollowed by lyophiliza ion (aqueous e hanolic ex ac s).
In o de o emo e he chlo ophyll con en , dichlo ome hane ex ac s we e passed h ough a Ch omabond
C18 column, using me hanol as eluen , ollowed by sol en e apo a ion. The 22 ex ac s hus ob ained
(11 in wa e /e hanol and 11 in dichlo ome hane, Table 1) we e submi ed o assays o cell iabili y using
he insec cell line Spodop e a ugipe da (S 9), o assess hei capaci y as po en ial bioinsec icides.
Table 1.
Ex ac s o a ious species ob ained using wo di e en sol en sys ems and s udied agains S 9.
En y Specie Pa o he Plan Sol en Code
1Phy olacca ame icana Lea es DCM A1
2Phy olacca ame icana Be ies DCM A2
3Phy olacca ame icana Be ies Wa e /E OH (1:1) D2
4Phy olacca ame icana Lea es Wa e /E OH (1:1) D3
5Tage es pa ula ( ed lowe s) Lea es DCM (F.1-3) A3
6Tage es pa ula (yellow lowe s) Lea es DCM (F.1-4) A4
7Tage es pa ula (o ange lowe s) Lea es DCM (F.1-3) A5
8Tage es pa ula ( ed lowe s) Flowe s DCM A6
9Tage es pa ula ( ed lowe s) Lea es Wa e /E OH (1:1) B6
10 Tage es pa ula Flowe s ( ed) Wa e /E OH (1:1) C1
11 Tage es pa ula (yellow lowe s) Lea es Wa e /E OH (1:1) C2
12 Tage es pa ula (o ange lowe s) Lea es Wa e /E OH (1:1) C3
13 Ru a g a eolens Lea es DCM B1
14 Ru a g a eolens Lea es Wa e /E OH (1:1) D4
15 Ulex eu opaeus
Lea es and lowe s
DCM B2
16 Ulex eu opaeus
Lea es and lowe s
Wa e /E OH (1:1) C5
17 Glando a p os a a
Lea es and lowe s
DCM B3
18 Glando a p os a a
Lea es and lowe s
Wa e /E OH (1:1) D1
19 Punica g ana um F ui peel DCM B4
20 Punica g ana um F ui peel Wa e /E OH (1:1) C4
21 Camellia japonica Lea es DCM B5
22 Camellia japonica Lea es Wa e /E OH (1:1) C6
2.2. E alua ion o he Ac i i y Agains S 9 Cells
Gi en he high numbe o samples unde s udy (22), we we e in e es ed in knowing which samples
we e he mos oxic owa ds he S 9 cell line. To his end, all ex ac s we e e alua ed a he same
concen a ion (100
µ
g/mL) o hei impac in he iabili y o hese cells a e 24 h o incuba ion. Fo a
clea e unde s anding, a hea map o all esul s can be ound in Figu e 1(le ). Conside ing he esul s,
Molecules 2020,25, 5855 4 o 14
he e was a clea clus e o a g oup o samples ha we e ac i e ( ed) and hose ha we e mos ly inac i e
(blue). The mos ac i e samples we e, in ac , hose a ising om he use o non-pola sol en s, as i
can be seen in clea e de ail in Figu e 1( igh ), when plo ing he esul s om iabili y assays agains
he pola i y o he ex ac s. This esul can be explained by he ac ha he use o nonpola sol en s
allows he ex ac ion o classes o na u al p oduc s ha a e usually no ex ac able wi h highly pola
sol en s, such as wa e . As so, while pola sol en s will ex ac molecules such as suga s, polyphenols
and hei glycosyla ed de i a i es, he use o non-pola sol en s widens he chemical di e si y o he
a ge molecules o include classes such as alkaloids, e penes, couma ins, among o he s.
Molecules 2020, 25, x FOR PEER REVIEW 4 o 15
same concen a ion (100 μg/mL) o hei impac in he iabili y o hese cells a e 24 h o incuba ion.
Fo a clea e unde s anding, a hea map o all esul s can be ound in Figu e 1 (le ). Conside ing he
esul s, he e was a clea clus e o a g oup o samples ha we e ac i e ( ed) and hose ha we e
mos ly inac i e (blue). The mos ac i e samples we e, in ac , hose a ising om he use o non-pola
sol en s, as i can be seen in clea e de ail in Figu e 1 ( igh ), when plo ing he esul s om iabili y
assays agains he pola i y o he ex ac s. This esul can be explained by he ac ha he use o
nonpola sol en s allows he ex ac ion o classes o na u al p oduc s ha a e usually no ex ac able
wi h highly pola sol en s, such as wa e . As so, while pola sol en s will ex ac molecules such as
suga s, polyphenols and hei glycosyla ed de i a i es, he use o non-pola sol en s widens he
chemical di e si y o he a ge molecules o include classes such as alkaloids, e penes, couma ins,
among o he s.
Figu e 1. (Le ): Resul s o he iabili y (%) o insec cells a e ea men wi h he indica ed samples.
(Righ ): Compa ison o he iabili y o cells ea ed wi h non-pola (A1–B5) s. pola (B6–C4) ex ac s.
Ha ing educed he numbe o samples unde s udy, we we e in e es ed in knowing which
species we e igge ing highe le els o oxici y. As seen in Figu e 2, mos samples educed cell
iabili y o he 50–75% ange; howe e , he R. g a eolens dichlo ome hane ex ac (B1, Table 1) was
able o educe he iabili y below 50%. Fo benchma king pu poses, we addi ionally es ed he
iabili y o S 9 cells a e exposu e o he comme cial syn he ic insec icide chlo py i os. As shown in
Figu e 2, his molecule elici ed ca. 50% o iabili y loss, hus being less po en han B1. Fo his eason,
he la e was selec ed o subsequen s udies.
Ex ac
Viabili y (%)
Pola
Apola
0
50
100
Figu e 1.
(
Le
): Resul s o he iabili y (%) o insec cells a e ea men wi h he indica ed samples.
(
Righ
): Compa ison o he iabili y o cells ea ed wi h non-pola (
A1
–
B5
) s. pola (
B6
–
C4
) ex ac s.
Ha ing educed he numbe o samples unde s udy, we we e in e es ed in knowing which species
we e igge ing highe le els o oxici y. As seen in Figu e 2, mos samples educed cell iabili y o he
50–75% ange; howe e , heR. g a eolens dichlo ome haneex ac (
B1
,Table 1) wasable o educe he iabili y
below 50%. Fo benchma king pu poses, we addi ionally es ed he iabili y o S 9 cells a e exposu e o
he comme cial syn he ic insec icide chlo py i os. As shown in Figu e 2, his molecule elici ed ca. 50% o
iabili y loss, hus being less po en han
B1
. Fo his eason, he la e was selec ed o subsequen s udies.
Molecules 2020, 25, x FOR PEER REVIEW 5 o 15
Figu e 2. Viabili y o S 9 cells a e exposu e o he indica ed samples a 100 μg/mL, o 24 h. CHPY =
chlo py i os. *** p < 0.001. Iden i y o samples (A1–A6 and B1–B5) as in Table 1.
The UHPLC ESI-Q-TOF-MME analysis o R. g a eolens ex ac e ealed he p esence o en
compounds, some o which show a molecula mass compa ible wi h quinolin, benzopy an, and
ac idone de i a i es (Table 2). A ch oma og am o he ex ac is shown in he Suppo ing
In o ma ion, Figu e S1.
Table 2. Mass spec ome y da a and pu a i e iden i ica ion o he R. g a eolens ex ac . The peak
men ioned is he ch oma og am peak numbe shown in he Suppo ing In o ma ion, Figu e S2.
Peak RT M+ Compound Re e ence
10 19.477 279
G a eoline
[37]
11 20.455 259
Skimmianin
[37]
11 20.455 261
4,6,7-T ime hoxy- u o[2,3-b]quinoline
[38]
Figu e 2.
Viabili y o S 9 cells a e exposu e o he indica ed samples a 100
µ
g/mL, o 24 h.
CHPY =chlo py i os. *** p<0.001. Iden i y o samples (A1–A6 and B1–B5) as in Table 1.
Molecules 2020,25, 5855 5 o 14
The UHPLC ESI-Q-TOF-MME analysis o R. g a eolens ex ac e ealed he p esence o en
compounds, some o which showa molecula mass compa iblewi h quinolin, benzopy an, andac idone
de i a i es (Table 2). A ch oma og am o he ex ac is shown in he Suppo ing In o ma ion, Figu e S1.
Table 2.
Mass spec ome y da a and pu a i e iden i ica ion o he R. g a eolens ex ac . The peak
men ioned is he ch oma og am peak numbe shown in he Suppo ing In o ma ion, Figu e S2.
Peak RT M+Compound Re e ence
10 19.477 279
Molecules 2020, 25, x FOR PEER REVIEW 5 o 15
Figu e 2. Viabili y o S 9 cells a e exposu e o he indica ed samples a 100 μg/mL, o 24 h. CHPY =
chlo py i os. *** p < 0.001. Iden i y o samples (A1–A6 and B1–B5) as in Table 1.
The UHPLC ESI-Q-TOF-MME analysis o R. g a eolens ex ac e ealed he p esence o en
compounds, some o which show a molecula mass compa ible wi h quinolin, benzopy an, and
ac idone de i a i es (Table 2). A ch oma og am o he ex ac is shown in he Suppo ing
In o ma ion, Figu e S1.
Table 2. Mass spec ome y da a and pu a i e iden i ica ion o he R. g a eolens ex ac . The peak
men ioned is he ch oma og am peak numbe shown in he Suppo ing In o ma ion, Figu e S2.
Peak RT M+ Compound Re e ence
10 19.477 279
G a eoline
[37]
11 20.455 259
Skimmianin
[37]
11 20.455 261
4,6,7-T ime hoxy- u o[2,3-b]quinoline
[38]
G a eoline
[37]
11 20.455 259
Molecules 2020, 25, x FOR PEER REVIEW 5 o 15
Figu e 2. Viabili y o S 9 cells a e exposu e o he indica ed samples a 100 μg/mL, o 24 h. CHPY =
chlo py i os. *** p < 0.001. Iden i y o samples (A1–A6 and B1–B5) as in Table 1.
The UHPLC ESI-Q-TOF-MME analysis o R. g a eolens ex ac e ealed he p esence o en
compounds, some o which show a molecula mass compa ible wi h quinolin, benzopy an, and
ac idone de i a i es (Table 2). A ch oma og am o he ex ac is shown in he Suppo ing
In o ma ion, Figu e S1.
Table 2. Mass spec ome y da a and pu a i e iden i ica ion o he R. g a eolens ex ac . The peak
men ioned is he ch oma og am peak numbe shown in he Suppo ing In o ma ion, Figu e S2.
Peak RT M+ Compound Re e ence
10 19.477 279
G a eoline
[37]
11 20.455 259
Skimmianin
[37]
11 20.455 261
4,6,7-T ime hoxy- u o[2,3-b]quinoline
[38]
Skimmianin
[37]
11 20.455 261
Molecules 2020, 25, x FOR PEER REVIEW 5 o 15
Figu e 2. Viabili y o S 9 cells a e exposu e o he indica ed samples a 100 μg/mL, o 24 h. CHPY =
chlo py i os. *** p < 0.001. Iden i y o samples (A1–A6 and B1–B5) as in Table 1.
The UHPLC ESI-Q-TOF-MME analysis o R. g a eolens ex ac e ealed he p esence o en
compounds, some o which show a molecula mass compa ible wi h quinolin, benzopy an, and
ac idone de i a i es (Table 2). A ch oma og am o he ex ac is shown in he Suppo ing
In o ma ion, Figu e S1.
Table 2. Mass spec ome y da a and pu a i e iden i ica ion o he R. g a eolens ex ac . The peak
men ioned is he ch oma og am peak numbe shown in he Suppo ing In o ma ion, Figu e S2.
Peak RT M+ Compound Re e ence
10 19.477 279
G a eoline
[37]
11 20.455 259
Skimmianin
[37]
11 20.455 261
4,6,7-T ime hoxy- u o[2,3-b]quinoline
[38]
4,6,7-T ime hoxy- u o[2,3-b]quinoline
[38]
16 23.932 216
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
P eleine
[37]
18 33.006 314
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
Chalepin
[37]
21 38.681 356
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
Ru ama in
[37]
20 37.305 271
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
Molecules 2020, 25, x FOR PEER REVIEW 6 o 15
16 23.932 216
8-Me hoxypso alen 5-Me hoxypso alen
[39]
17 24.082 229
P eleine
[37]
18 33.006 314
Chalepin
[37]
21 38.681 356
Ru ama in
[37]
20 37.305 271
2-N-Nonyl-4-quinolone
[38]
21 38.681 357
G a ac idone iol
[37]
2.3. Mo phological Assessmen
In ligh o he p onounced impac o B1 in S 9 cell iabili y, we we e in e es ed in unde s anding
he unde lying e ec o he ex ac . To his end, he con ol and B1- ea ed cells ha e been imaged in
o de o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1 elici s a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion
(yellow a ows), al hough o e all cell in eg i y is main ained. This esul sugges s ha B1 may be
elici ing he loss o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which
mo phological ai s a e compa ible o hose desc ibed he e.
G a ac idone iol
[37]

Molecules 2020,25, 5855 6 o 14
2.3. Mo phological Assessmen
In ligh o he p onounced impac o
B1
in S 9 cell iabili y, we we e in e es ed in unde s anding he
unde lying e ec o he ex ac . To his end, he con ol and
B1
- ea ed cells ha e been imaged in o de
o assess pu a i e di e ences in o e all cell mo phology and ch oma in. As shown in Figu e 3,
B1
elici s
a signi ican deg ee o ch oma in condensa ion (blue a ows) and e en agmen a ion (yellow a ows),
al hough o e all cell in eg i y is main ained. This esul sugges s ha
B1
may be elici ing he loss
o cell iabili y by igge ing an o ganized p ocess o cell dea h, in which mo phological ai s a e
compa ible o hose desc ibed he e.
Molecules 2020, 25, x FOR PEER REVIEW 7 o 15
Figu e 3. S 9 cells exposed o B1 (100 μg/mL) o 24 h (S Plan Fluo ELWD 40 × DIC N1 objec i e). Cell
mo phology was e alua ed using 4′,6-diamidino-2-phenylindole (DAPI, ch oma in) and phalloidin (ac in).
Yellow a ow: ch oma in agmen a ion; Blue a ow: ch oma in condensa ion. (C)—con ol. Colo blind-
iendly image in Suppo ing In o ma ion Figu e S2.
2.4. Nanoencapsula ion S udies
The size and size dis ibu ion o he chosen nanoencapsula ion sys ems was de e mined by
dynamic ligh sca e ing (DLS), Table 3. The liposomes p epa ed by he e hanolic injec ion me hod
ha e a smalle size han he ones p epa ed by hin ilm hyd a ion bu exhibi a sligh ly highe
polydispe si y. The chi osan nanos uc u es (p epa ed by ionic gela ion) a e he encapsula ion
sys ems wi h he lowes hyd odynamic diame e . The sizes we e main ained cons an o wo weeks,
wi h no signi ican change in polydispe si y, p o ing he s abili y o he p epa ed nanosys ems.
Table 3. Size (hyd odynamic diame e ) and he polydispe si y o soybean liposomes and chi osan
nanos uc u es de e mined by dynamic ligh sca e ing (DLS) (SD: s anda d de ia ion om i e
independen measu emen s).
Sys em Size ± SD (nm) PDI ± SD
Liposomes (e hanolic injec ion) 121 ± 28 0.256 ± 0.08
Liposomes ( hin ilm hyd a ion) 203 ± 17 0.185 ± 0.05
Chi osan nanos uc u es 118 ± 23 0.203 ± 0.02
Liposomes ha e been desc ibed as ideal bioac i e deli e y sys ems, due o hei biocompa ibili y
and hei abili y o ca y bo h hyd ophilic (in he aqueous lumen) and hyd ophobic (in he lipid
bilaye ) payloads [40]. The esul s in Table 3 a e in acco dance wi h he ones epo ed in he li e a u e
o leci hin-based liposomal sys ems p epa ed by e hanolic injec ion [41,42] and hin ilm hyd a ion
[43,44], he la e being sligh ly la ge . Chi osan nanos uc u es ha e also been desc ibed as
ad an ageous o he encapsula ion o pes icides and na u al ex ac s [45–48]. The hyd odynamic
diame e and polydispe si y ob ained o chi osan nanocapsules (Table 3) a e also in acco dance wi h
he epo ed esul s o a simila p epa a ion me hod [45].
The encapsula ion e iciencies o he ex ac wi h he bes insec icidal ac i i y B1 in soybean
liposomes and chi osan nanoemulsions a e p esen ed in Table 4.
Figu e 3.
S 9 cells exposed o
B1
(100
µ
g/mL) o 24 h (S Plan Fluo ELWD 40
×
DIC N1 objec i e).
Cell mo phology was e alua ed using 4
0
,6-diamidino-2-phenylindole (DAPI, ch oma in) and phalloidin
(ac in). Yellow a ow: ch oma in agmen a ion; Blue a ow: ch oma in condensa ion. (
C
)—con ol.
Colo blind- iendly image in Suppo ing In o ma ion Figu e S2.
2.4. Nanoencapsula ion S udies
The size and size dis ibu ion o he chosen nanoencapsula ion sys ems was de e mined by
dynamic ligh sca e ing (DLS), Table 3. The liposomes p epa ed by he e hanolic injec ion me hod ha e
a smalle size han he ones p epa ed by hin ilm hyd a ion bu exhibi a sligh ly highe polydispe si y.
The chi osan nanos uc u es (p epa ed by ionic gela ion) a e he encapsula ion sys ems wi h he lowes
hyd odynamic diame e . The sizes we e main ained cons an o wo weeks, wi h no signi ican change
in polydispe si y, p o ing he s abili y o he p epa ed nanosys ems.
Table 3.
Size (hyd odynamic diame e ) and he polydispe si y o soybean liposomes and chi osan
nanos uc u es de e mined by dynamic ligh sca e ing (DLS) (SD: s anda d de ia ion om i e
independen measu emen s).
Sys em Size ±SD (nm) PDI ±SD
Liposomes (e hanolic injec ion) 121 ±28 0.256 ±0.08
Liposomes ( hin ilm hyd a ion) 203 ±17 0.185 ±0.05
Chi osan nanos uc u es 118 ±23 0.203 ±0.02
Molecules 2020,25, 5855 7 o 14
Liposomes ha e been desc ibed as ideal bioac i e deli e y sys ems, due o hei biocompa ibili y
and hei abili y o ca y bo h hyd ophilic (in he aqueous lumen) and hyd ophobic (in he lipid bilaye )
payloads [
40
]. The esul s in Table 3a e in acco dance wi h he ones epo ed in he li e a u e o
leci hin-based liposomal sys ems p epa ed by e hanolic injec ion [
41
,
42
] and hin ilm hyd a ion [
43
,
44
],
he la e being sligh ly la ge . Chi osan nanos uc u es ha e also been desc ibed as ad an ageous
o he encapsula ion o pes icides and na u al ex ac s [
45
–
48
]. The hyd odynamic diame e and
polydispe si y ob ained o chi osan nanocapsules (Table 3) a e also in acco dance wi h he epo ed
esul s o a simila p epa a ion me hod [45].
The encapsula ion e iciencies o he ex ac wi h he bes insec icidal ac i i y
B1
in soybean
liposomes and chi osan nanoemulsions a e p esen ed in Table 4.
Table 4.
Encapsula ion e iciencies (EE%
±
SD) o he ex ac wi h he bes insec icidal ac i i y in
liposomes and chi osan nanoemulsions (SD: s anda d de ia ion o h ee independen measu emen s).
Sys em Sample B1
Liposomes (e hanolic injec ion) 93.3 ±6
Liposomes ( hin ilm hyd a ion) 73.0 ±9
Chi osan nanoemulsions 94.0 ±2
The encapsula ion e iciencies we e gene ally high (abo e 70%), especially in liposomes p epa ed
by he e hanolic injec ion me hod and in chi osan nanos uc u es.
The elease o he encapsula ed ex ac was ollowed o 24 h a oom empe a u e (25
◦
C) owa ds
phospha e bu e , pH =7.3 (Figu e 4). The esul s e idence ha chi osan nanos uc u es a e sui able
o a as e and comple e elease, while liposomes allow a delayed elease. The di e ence in he elease
p o iles ob ained om liposomes p epa ed by he wo echniques ( hin ilm hyd a ion and e hanolic
injec ion) may be ela ed wi h he hyd ophobic cha ac e o his ex ac , as e hanolic injec ion is mo e
ad an ageous o his ype o bioac i es [41].
Molecules 2020, 25, x FOR PEER REVIEW 8 o 15
Table 4. Encapsula ion e iciencies (EE% ± SD) o he ex ac wi h he bes insec icidal ac i i y in
liposomes and chi osan nanoemulsions (SD: s anda d de ia ion o h ee independen measu emen s).
Sys em Sample B1
Liposomes (e hanolic injec ion) 93.3 ± 6
Liposomes ( hin ilm hyd a ion) 73.0 ±9
Chi osan nanoemulsions 94.0 ± 2
The encapsula ion e iciencies we e gene ally high (abo e 70%), especially in liposomes
p epa ed by he e hanolic injec ion me hod and in chi osan nanos uc u es.
The elease o he encapsula ed ex ac was ollowed o 24 h a oom empe a u e (25 °C)
owa ds phospha e bu e , pH = 7.3 (Figu e 4). The esul s e idence ha chi osan nanos uc u es a e
sui able o a as e and comple e elease, while liposomes allow a delayed elease. The di e ence in
he elease p o iles ob ained om liposomes p epa ed by he wo echniques ( hin ilm hyd a ion and
e hanolic injec ion) may be ela ed wi h he hyd ophobic cha ac e o his ex ac , as e hanolic
injec ion is mo e ad an ageous o his ype o bioac i es [41].
The expe imen al elease p o iles we e analyzed by a modi ied Ko smeye –Peppas model [49] and
he esul s a e summa ized in Table 5 ( he i ings a e shown in Suppo ing In o ma ion Figu e S3).
Figu e 4. Release p o iles o sample B1 om he liposomes and chi osan nanos uc u es.
Table 5. Release pa ame e s o he Ko smeye –Peppas model i ed o he elease p o iles (R is he
coe icien o de e mina ion).
Nanosys em Ks n l

Liposomes ( hin ilm hyd a ion) 0.07 0.50 0.9 0.98
Liposomes (e hanolic injec ion)
Liposomes (e hanolic injec ion) *
0.01 1.39 0 0.98
0.0045 1.74 0 0.99
Chi osan nanos uc u es
Chi osan nanos uc u es *
0.04 1.07 2.13 0.98
0.0314 1.21 2.11 0.99
Conside ing ha he nanoencapsula ion sys ems a e sphe ical, he n alue in he ange 0.43 < n
< 0.85 sugges s ha he elease p o iles om liposomes p epa ed by hin ilm hyd a ion can be mainly
asc ibed o di usion and swelling, i.e., bo h con ibu ions ha e compa able a es [49]. The samples
ma ked wi h * in Table 5 we e subjec ed o a di e en analysis, o which he elease is ini ially
assumed o be associa ed wi h he supe case-ii anspo mechanism, whe e e osion, elaxa ion and
di usion a e esponsible o ex ac elease. Despi e he easonable i ing o he model o he
Figu e 4. Release p o iles o sample B1 om he liposomes and chi osan nanos uc u es.
The expe imen al elease p o iles we e analyzed by a modi ied Ko smeye –Peppas model [
49
]
and he esul s a e summa ized in Table 5( he i ings a e shown in Suppo ing In o ma ion Figu e S3).
Molecules 2020,25, 5855 8 o 14
Table 5.
Release pa ame e s o he Ko smeye –Peppas model i ed o he elease p o iles (Ris he
coe icien o de e mina ion).
Nanosys em Ksn l R2
Liposomes ( hin ilm hyd a ion)
0.07 0.50 0.9 0.98
Liposomes (e hanolic injec ion)
Liposomes (e hanolic injec ion) *
0.01 1.39 0 0.98
0.0045 1.74 0 0.99
Chi osan nanos uc u es
Chi osan nanos uc u es *
0.04 1.07 2.13 0.98
0.0314 1.21 2.11 0.99
Conside ing ha he nanoencapsula ion sys ems a e sphe ical, he n alue in he ange
0.43 <n<0.85
sugges s ha he elease p o iles om liposomes p epa ed by hin ilm hyd a ion can be mainly asc ibed
o di usion and swelling, i.e., bo h con ibu ions ha e compa able a es [
49
]. The samples ma ked wi h *
in Table 5we e subjec ed o a di e en analysis, o which he elease is ini ially assumed o be associa ed
wi h he supe case-ii anspo mechanism, whe e e osion, elaxa ion and di usion a e esponsible o
ex ac elease. Despi e he easonable i ing o he model o he expe imen al da a ob ained in liposomes
p epa ed by injec ion and chi osan nanos uc u es (as implied by he coe icien s o de e mina ion), i does
no p ope ly explain he da a om a quali a i e poin o iew. The e o e, he elease p o iles we e also
i ed o he Gompe z empi ical unc ion (Table 6), de ined as
X =Xmaxe−aeblog10
whe e
X
and
Xmax
a e he dissol ed ac ion pe cen ages a ime and i s maximum,
a
is a shape
pa ame e and
b
is he dissolu ion a e pe uni o ime [
50
]. The i ings o his model a e also
gene ally good (see Suppo ing In o ma ion Figu e S4). Al hough he model does no p o ide
mechanis ic in o ma ion, he la ge b alues o he samples in chi osan indica e as e elease kine ics,
while liposomes ob ained by hyd a ion seem o be mo e e ec i e in ensu ing a slowe elease.
Table 6. Release pa ame e s ob ained om he i ing o he Gompe z model o he elease p o iles.
Nanosys em Xmax a B R2
Liposomes ( hin ilm hyd a ion)
49.38 3.61 1.55 0.99
Liposomes (e hanolic injec ion) 100 680.48 5.99 0.99
Chi osan nanos uc u es 100 163.23 5.34 0.97
The esul s ob ained he ein indica e ha lipid-based and chi osan nanoencapsula ion sys ems allow
high encapsula ion e iciencies o he ex ac s wi h insec icidal ac i i y and p o ide di e en elease
a es. This ep esen s a p oo -o -concep o u u e de elopmen s o bioinsec icide nano o mula ions
using he mos ac i e ex ac s.
3. Expe imen al Sec ion
3.1. Chemicals and Reagen s
E hanol, me hanol, dichlo ome hane, isop opanol, DMSO, ace ic acid and e ahyd o u an we e
pu chased om Me ck KGaA (Da ms ad , Ge many). Ch omabond C18 column was pu chased om
Sigma-Ald ich (S . Louis, MO, USA). T ypan blue and 3-(4,5-dime hyl hiazolyl-2)-2,5-diphenyl e azolium
b omide (MTT) we e ob ained om Sigma-Ald ich (S . Louis, MO, USA). Dulbecco’s modi ied eagle
medium (DMEM), Hank’s balanced sal solu ion (HBSS), e al bo ine se um (FBS), penicillin–s ep omycin
solu ion (penicillin 5000 uni s/mL and s ep omycin 5000
µ
g/mL) and 0.25% ypsin-EDTA we e ob ained
om GIBCO, In i ogen™(G and Island, NY, USA).
Molecules 2020,25, 5855 9 o 14
3.2. Plan Ma e ial
The se en species o plan s we e ha es ed in he No h o Po ugal, namely in Melgaço (42.1144
◦
N,
8.2580
◦
W) (P. g ana um,P. ame icana,G. p os a a,U. eu opaeus,T. pa ula,C. japonica ed) and Guima
ã
es
(41.4425
◦
N, 8.2918
◦
W) (R. g a eolens), a he lowe ing s age in he case o G. p os a a,U. eu opaeus and
T. pa ula in Ma ch 2019 (G. p os a a,U. eu opaeus) o Oc obe 2019 o he emaining plan s. The plan
ma e ial included ui peel (P. g ana um), be ies (P. ame icana), lowe s and lea es (G. p os a a,
U. eu opaeus, and T. pa ula), as well as only lea es (C. japonica and R. g a eolens). In he case o T. pa ula,
he lea es and yellow, o ange and ed lowe s (sepa a ed om he ecep acle) we e used in sepa a e
expe imen s. A leas h ee specimens o each species we e collec ed.
The pomeg ana e peel (P. g ana um) was d ied unde sunligh a 20–25
◦
C du ing 45 days.
The be ies o P. ame icana, as well as he lea es and lowe s o T. pa ula, we e ozen a
−
20
◦
C un il
lyophiliza ion in an Alpha 1-4 ld Plus–Ch is eeze d ye (Ma in Ch is Ge ie ocknungsanlagen
GmbH, Os e ode am Ha z, Ge many). The lea es and lowe s o he emaining species we e d ied in
an o en a 40–45 ◦C du ing 3 days.
A e d ying o lyophiliza ion, he ege able ma e was g ound wi h a sh edde , and he esul ing
powde passed h ough a sie e un il a pa icle size
≤
900
µ
m was ob ained. The ma e ial was s o ed
unde acuum o u he use.
3.3. Plan Ma e ials Ex ac ion
The d ied o lyophilized plan ma e ials o P. g ana um,P. ame icana,G. p os a a,U. eu opaeus,
T. pa ula,C.japonica,R. g a eolens (8 g) we e subjec ed o Soxhle ex ac ion wi h wa e /e hanol (1:1)
(50 mL) o dichlo ome hane (50 mL) o 9 o 4 h, espec i ely.
The o ganic sol en s we e emo ed by e apo a ion unde educed p essu e a 40
◦
C (Ro a apo
®
R-210, BÜCHI Labo echnik AG, Flawil, Swi ze land), ollowed by lyophiliza ion (Alpha 1-4 ld
Plus–Ch is eeze d ye , Ma in Ch is Ge ie ocknungsanlagen GmbH, Os e ode am Ha z, Ge many)
in he case o ex ac ions wi h wa e /e hanol (1:1). The esul ing lyophilized ex ac s we e s o ed
unde acuum o u he use. The e apo a ed ex ac s o dichlo ome hane we e passed h ough a
Ch omabond C18 column, using me hanol as eluen , o he emo al o chlo ophylls. A e he sol en
e apo a ion unde acuum a 35 ◦C, he esul ing ex ac s we e s o ed a −20 ◦C o u he use.
3.4. Cell Cul u e
S 9 (Spodop e a ugipe da)cells we e omATCC/LGC S anda ds(Spain)main ained as asuspension
cul u e and cul i a ed in G ace’s medium wi h 10% FBS and an ibio ics a 28
◦
C. Cells we e used
in he expe imen s while in he exponen ial phase o g ow h. HaCaT (human ke a inocy es) cells
we e cul u ed in DMEM supplemen ed wi h 10% FBS and 1% penicillin/s ep omycin a 37
◦
C, in a
humidi ied a mosphe e o 5% CO2.
3.5. Assessmen o Viabili y
Fo he assessmen o iabili y, a esazu in-based me hod was used, as p e iously desc ibed [
51
].
S 9 cells we e pla ed a a densi y o 3
×
10
4
cells/well, incuba ed o 24 h and hen exposed o he
molecules unde s udy o 24 h. A e his pe iod, a comme cial solu ion o esazu in was added (1:10)
and he kine ic eac ion o luo escence inc ease was moni o ed. An incuba ion ime o 30 min was used.
3.6. Mo phological Assessmen
Fo mo phological s udies, he cells we e cul u ed in 96-well pla es, as desc ibed abo e o iabili y
expe imen s, in he p esence o he samples unde s udy. A e incuba ion, he cells we e washed wi h
HBSS and ixed in 10% o malin solu ion o 30 min, a oom empe a u e. DAPI (0.25
µ
g/mL) and
CF543 (5 U/mL) we e added and he cells we e s ained o 25 min a oom empe a u e and washed
wi h HBSS, as desc ibed be o e [52,53].