Bees exposed to climate change are more sensitive to pesticides
Abstract
© 2023 The Authors. Global Change Biology published by John Wiley & Sons Ltd. This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
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Glob Change Biol. 2023;29:6248–6260.wileyonlinelib a y.com/jou nal/gcb
Recei ed: 4 May 2023
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Accep ed: 13 Augus 2023
DOI: 10.1111/gcb.16928
RESEARCH ARTICLE
Bees exposed o clima e change a e mo e sensi i e o
pes icides
Se gio Albace e1,2 | Gonzalo Sancho1,2 | Celes e Azpiazu1,3 | Anselm Rod igo1,2 |
Robe o Molowny- Ho as1,2 | Fabio Sgolas a4 | Jo di Bosch1,2
This is an open access a icle unde he e ms o he C ea i e Commons A ibu ion License, which pe mi s use, dis ibu ion and ep oduc ion in any medium,
p o ided he o iginal wo k is p ope ly ci ed.
© 2023 The Au ho s. Global Change Biology published by John Wiley & Sons L d.
1Uni e si a Au ònoma de Ba celona,
Bella e a, Spain
2Cen e o Ecological Resea ch and
Fo es y Applica ions (CREAF), Bella e a,
Spain
3Ins i u e o E olu iona y Biology (CSIC—
Uni e si a Pompeu Fab a), Ba celona,
Spain
4Dipa imen o di Scienze e Tecnologie
Ag o- Alimen a i, Alma Ma e S udio um
Uni e si à di Bologna, Bologna, I aly
Co espondence
Se gio Albace e, Uni e si a Au ònoma
de Ba celona and CREAF (Cen e o
Ecological Resea ch and Fo es y
Applica ions), 08193 Bella e a, Spain.
Email: s.albace e@c ea .uab.ca
Funding in o ma ion
Spanish Minis y o Science and
Inno a ion, G an /Awa d Numbe :
PRE2019- 090375, PRE2019- 088817,
PID2021- 128938OB- I00 and RTI2018-
098399- B- I00; Spanish Minis y o
Uni e si ies, G an /Awa d Numbe :
Ma ga i a- Salas- schola ship
Abs ac
Bee popula ions a e exposed o mul iple s esso s, including land- use change, bio-
logical in asions, clima e change, and pes icide exposu e, ha may in e ac syne gis i-
cally. We analyze he combined e ec s o clima e wa ming and suble hal insec icide
exposu e in he soli a y bee Osmia co nu a. P e ious Osmia s udies show ha wa m
win e ing empe a u es cause body weigh loss, lipid consump ion, and a body de-
ple ion. Because he a body plays a key ole in xenobio ic de oxi ica ion, we ex-
pec ed ha bees exposed o clima e wa ming scena ios would be mo e sensi i e o
pes icides. We exposed O. co nu a emales o h ee win e ing ea men s: cu en sce-
na io (2007– 2012 empe a u es), nea - u u e (2021– 2050 p ojec ed empe a u es),
and dis an - u u e (2051– 2080). Upon eme gence in sp ing, bees we e o ally exposed
o h ee suble hal doses o an insec icide (Close , a.i. sul oxa lo ; 0, 4.55 and 11.64 ng
a.i./bee). We measu ed he combined e ec s o win e ing and insec icide exposu e
on pho o ac ic esponse, sy up consump ion, and longe i y. Win e ing ea men by
i sel did no a ec win e mo ali y, bu body weigh loss inc eased wi h inc eas-
ing win e ing empe a u es. Simila ly, win e ing ea men by i sel ha dly in luenced
pho o ac ic esponse o sy up consump ion. Howe e , bees win e ed a he wa mes
empe a u es had sho e longe i y, a s ong ecundi y p edic o in Osmia. Insec icide
exposu e, especially a he high dose, impai ed he abili y o bees o espond o ligh ,
and esul ed in educed sy up consump ion and longe i y. The combina ion o he
wa mes win e and he high insec icide dose esul ed in a 70% longe i y dec ease.
Smalle bees, esul ing om smalle pollen– nec a p o isions, had sho e longe i y
sugges ing nu i ional s ess may u he comp omise ecundi y in O. co nu a. Ou
esul s show a syne gis ic in e ac ion be ween wo majo d i e s o bee declines, and
indica e ha bees will become mo e sensi i e o pes icides unde he cu en global
wa ming scena io. Ou indings ha e impo an implica ions o pes icide egula ion
and unde sco e he need o conside mul iple s esso s o unde s and bee declines.
KEYWORDS
body size, clima e change, global wa ming, longe i y, nu i ional s ess, Osmia co nu a,
pes icide exposu e, sul oxa lo , syne gis ic e ec s, oxici y
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ALBACETE e al.
1 | INTRODUCTION
Bees play a key ole in he unc ioning o e es ial ecosys ems
and p o ide essen ial pollina ion se ices o ag icul u al c ops
(Klein e al., 2007; Olle on e al., 2011). Howe e , bees ha e ex-
pe ienced signi ican declines in abundance and di e si y o e he
las cen u y (Goulson e al., 2015; Po s e al., 2010; Sánchez- Bayo
& Wyckhuys, 2019). The causes o hese declines a e a leas pa -
ially known, and include land- use change, biological in asions, cli-
ma e change, and he inc easing use o pes icides associa ed wi h
ag icul u al in ensi ica ion (Goulson e al., 2015; IPBES, 2021).
Impo an ly, hese s esso s do no ac in isola ion and some imes
in e ac syne gis ically (Cas elli e al., 2020; Goulson e al., 2015;
Si i e e al., 2021). Va ious s udies show ha he combined expo-
su e o mul iple s esso s a suble hal le els may cause le hal e ec s
(Double e al., 2015; Vanbe gen, 2021). Fo example, disease-
induced s ess may esul in inc eased sensi i i y o pes icides, and,
a he same ime, suble hal exposu e o oxican s may cause immu-
nosupp ession and inc eased ulne abili y o pa hogenic in ec ions
(Au au e e al., 2012; Double e al., 2015; G assl e al., 2018; Pe is
e al., 2012; Vidau e al., 2011). Insec icide exposu e and nu i ional
s ess may also in e ac syne gis ically, esul ing in educed he mo-
egula ion capabili y, ood consump ion, ligh abili y, and su i al
(Cas le e al., 2022; Linguadoca e al., 2021; Tong e al., 2019; Tosi
e al., 2017). These s udies unde sco e he need o add ess he com-
bined e ec s o a ious s esso s o unde s and he d i e s o bee
declines.
Like o he ec o he ms, insec s a e highly dependen on en i-
onmen al empe a u es o adequa e g ow h, de elopmen , and
ep oduc ion, which makes hem pa icula ly ulne able o global
wa ming (Deu sch e al., 2008; Po ne , 2002). In gene al, expo-
su e o wa m empe a u es inc eases me abolic ac i i y in insec s,
a ec ing de elopmen a es and o e all physiological unc ion-
ing (González- Tokman e al., 2020; Ne en, 2000). These e ec s
a e accompanied by an inc ease in ene gy expendi u e (B own
e al., 2004), esul ing in he mobiliza ion and consump ion o
s o ed me abolic esou ces (S o ey & S o ey, 2004), ul ima ely
a ec ing body size, longe i y, and ecundi y (Blanckenho n &
Hensele , 2005; Fische e al., 2014; Kie a e al., 2017; Ves e -
lund e al., 2014; Zhang e al., 2015). Se e al s udies show ha
he mal s ess enhances he deple ion o a body ese es in di -
e en insec g oups (Jean e al., 1990; Klepsa el e al., 2016; Wil-
liams e al., 2012), including bees (Bosch e al., 2010; Fliszkiewicz
e al., 2012; Sgolas a e al., 2011). Fa bodies play a c ucial ole no
only in he s o age and elease o ene gy in esponse o me abolic
demands (A ese & Soulages, 2010), bu also in he unc ioning o
key physiological p ocesses such as diapause de elopmen (Hahn
& Denlinge , 2007), ho mone egula ion, and immune esponse
(Keeley, 1985; Skow onek e al., 2021). Impo an ly, a bodies
a e also he main issue in which de oxi ica ion enzymes, such as
cy och ome P450 monooxygenases, a e p oduced and exp essed
(Da id e al., 2006; Pe e sen e al., 2001). The e o e, he al e a ion
o a bodies caused by hea s ess may also impai de oxi ica ion
p ocesses in insec s (Cos a e al., 2020; Linguadoca e al., 2021;
Lyce e al., 2006).
In his s udy we explo ed he combined e ec s o inc easingly
wa m win e ing empe a u es associa ed wi h he cu en scena io
o global wa ming and exposu e o suble hal le els o insec icide in
he soli a y bee Osmia co nu a. We expec ed exposu e o wa m em-
pe a u es o esul in inc eased sensi i i y o he insec icide. To he
bes o ou knowledge, he in e ac ion be ween pes icide exposu e
and clima e change has no been p e iously add essed in soli a y
bees. Osmia spp. a e app op ia e o ganisms o a s udy o his so
because bo h hei win e ing ecophysiology and hei sensi i i y o
insec icides ha e been s udied in some de ail. Osmia spp. o e win-
e on a ixed ene ge ic budge (Bosch e al., 2010). Adul eclosion
akes place in au umn, bu adul s emain inside hei cocoons wi hin
hei na al nes , wi hou access o ood un il nex sp ing. The e o e,
win e ing adul s ely o ally on he ene gy ese es de i ed om he
ood p o isions inges ed by he la al s age in ea ly summe . This
is in con as o bumblebees and honey bees, which o e win e as
eme ged adul s and he e o e a e able o eed be o e, and some imes
du ing, he win e . P e ious Osmia s udies ha e shown ha wa m
p e- win e ing and win e ing empe a u es enhance a body deple-
ion, lipid consump ion, and body weigh loss (Bosch e al., 2000,
2010; Bosch & Kemp, 2003, 2004; Fliszkiewicz e al., 2012; Sgolas-
a e al., 2011). Osmia spp. nes abo e g ound, and he e o e a e
mo e di ec ly exposed o ambien empe a u es han g ound nes -
ing bees (Do ian e al., 2022). O. co nu a has a s ong a ini y o
ui ee pollen (Jaumejoan e al., 2023) and, along wi h o he Osmia
species, is comme cially managed o o cha d pollina ion, esul ing
in equen exposu e o pes icides (Bosch & Kemp, 2002). In 2013,
he Eu opean Food Sa e y Au ho i y ecommended he use o O.
co nu a and O. bico nis as model species in pes icide isk assessmen
(EFSA, 2013), and in o ma ion on he e ec s o pes icides on hese
species has no ably inc eased since hen (Sgolas a e al., 2019).
The aim o his s udy is o unde s and whe he clima e wa ming
may exace ba e he sensi i i y o soli a y bees o pes icides. We ex-
posed O. co nu a emales o h ee simula ed win e ing ea men s
and hen assessed hei sensi i i y o acu e o al exposu e o he in-
sec icide Close TM® (a o mula ion o sul oxa lo ) a wo suble hal
concen a ions. We hen measu ed he combined e ec s o hese
wo s ess ac o s on he p opensi y o he bees o espond o a ligh
s imulus (pho o ac ic esponse), eeding beha io , and longe i y.
2 | MATERIALS AND METHODS
2.1 | Li e his o y o O. co nu a
O. co nu a, known as he Eu opean o cha d bee o he ho ned mason
bee, occu s in mos o cen al and sou he n Eu ope. I s popula ions
ly in la e win e and ea ly sp ing. Females a e ac i e o app oxi-
ma ely 20 days (Bosch & Vicens, 2006), du ing which ime hey build
one o mo e nes s in p e- exis ing ca i ies. Each nes consis s o a
linea se ies o cells, delimi ed by mud pa i ions, each con aining a
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ALBACETE e al.
pollen– nec a p o ision and an egg. A e consuming he p o ision,
he la a spins a cocoon and unde goes a summe diapause in he
p epupal s age (Sgolas a e al., 2012). Pupa ion occu s in mid o la e
summe , and adul eclosion in la e summe o ea ly au umn. Eclosed
adul s emain inside hei cocoons and lowe hei me abolic a es
(Bosch e al., 2010; Sgolas a e al., 2010). Adul s equi e exposu e
o cold empe a u es (win e ing) o comple e diapause and eme ge
he ollowing sp ing as empe a u es inc ease (Bosch & Kemp, 2004;
Sgolas a e al., 2010).
2.2 | Win e ing and eme gence
We used he p ogeny o an O. co nu a popula ion ha nes ed in
Feb ua y– Ma ch 2021 in an almond o cha d nea Lleida (Ca alo-
nia, Spain). In mid- Sep embe , when bees eached he adul s age,
we dissec ed a subse o nes s and collec ed 825 emale cocoons.
Cocoon sex can be eliably es ablished based on size and posi ion
wi hin he nes (Bosch, 1994). The collec ed cocoons we e indi-
idually weighed and andomly assigned o one o h ee simula ed
win e ing ea men s (n = 275 emales pe ea men ): (a) Cu en
scena io (a e age hou ly empe a u es eco ded in he a ea o o i-
gin o he popula ion du ing 2007– 2012); (b) nea - u u e scena io
(p ojec ed empe a u es o 2021– 2050); and (c) dis an - u u e sce-
na io (p ojec ed empe a u es o 2051– 2080). Fu u e win e ing
ea men s we e based on he empe a u e p ojec ions o he 8.5
Rep esen a i e Concen a ion Pa hways (RCPs) used in he IPCC
AR5 assessmen epo on clima e change (Moss e al., 2010). Ou
p ojec ions co e a 30- yea pe iod and e lec a mean empe a u e
inc ease o 0.6 and 2.9°C o he nea - u u e and dis an - u u e sce-
na ios, espec i ely, compa ed o he win e empe a u es o 2007–
2012 (Table 1). Da a o he a ea o o igin o he s udy popula ion
we e ex ac ed om he Escena ios- PNACC 2017 p ojec (h p://
escen a ios.adap ecca.es). We simula ed daily empe a u e cu es
o each ea men and mon h (Figu e S1; Suppo ing In o ma ion
Me hods). Cocoons we e indi idually placed in mul i- well pla es and
ans e ed o empe a u e- con olled chambe s on 1 Oc obe un il
eme gence he ollowing yea . Ac ual empe a u es wi hin he h ee
chambe s we e moni o ed wi h da a logge s h oughou he win e -
ing pe iod.
Bees o he clima e change ea men s we e expec ed o eme ge
be o e bees o he cu en ea men (Bosch & Blas, 1994a; Bosch &
Kemp, 2003, 2004). Cocoons we e checked daily, and when eme -
gence o a gi en ea men eached 5%, cocoons o ha ea men
we e ans e ed o an incuba ion chambe in which hey we e ex-
posed o 15°C o 24 h and subsequen ly o 20°C un il 100% eme -
gence. Be o e being ans e ed o he incuba ion chambe cocoons
we e again indi idually weighed o ob ain a measu e o weigh loss
o e he win e .
2.3 | Pes icide exposu e
Upon eme gence, bees we e indi idually kep o 24 h in anspa -
en plas ic con aine s (diame e : 11 cm; heigh : 7 cm) capped wi h
a pin- pe o a ed lid o allow hem o deposi he meconium. Bees
we e hen o ally and acu ely exposed o one o h ee insec icide
ea men s using he “pe al me hod” (Azpiazu e al., 2023). Each
bee was o e ed 20 μL o es solu ion. Only bees ha consumed
100% o he es solu ion wi hin 3 h (≥90% in all ea men s) we e
included in he analyses. Following his exposu e phase, bees we e
le in he plas ic cages and ed ad libi um wi h a 1- mL calib a ed
sy inge illed wi h a eeding solu ion (hence o h sy up; 33% w/w
suc ose– wa e ). A pe al o Eu yops spp. (As e aceae) was a ached
o he ip o he sy inge o enhance p omp loca ion by he bees
(Azpiazu e al., 2023). Du ing he expe imen , es con aine s we e
main ained a 20 ± 2°C and 50%– 70% ela i e humidi y, and e-
cei ed indi ec na u al ligh .
We wo ked wi h he comme cial o mula ion o sul oxa lo Clos-
e TM® (Sul oxa lo 11.43% SC, Co e a Ag iscience, Spain S.L.U.).
We es ed wo doses o sul oxa lo (SUL), 4.55 ng/bee (hence o h
low dose) and 11.64 ng/bee (high dose), along wi h a con ol (0 ng/
bee; 0 dose). The wo SUL doses co espond o he LD10 and LD50
a 72 h a e exposu e o emale O. bico nis (Azpiazu e al., 2021),
adjus ed o he g ea e body weigh o O. co nu a (0.149 g ± 0.0142;
Bosch & Vicens, 2002). To ob ain he es solu ions (20 μL/bee),
we p epa ed a p ima y s ock solu ion o 1.16 g/L SUL by dissol ing
Close in dis illed wa e . This solu ion was subsequen ly dilu ed and
inally mixed wi h sy up a a a io o 50 μL/mL o achie e he desi ed
doses.
TABLE 1 Mean weigh loss and % win e mo ali y in Osmia co nu a emales exposed o h ee win e ing ea men s ep esen ing
inc easingly wa m clima e change scena ios.
Win e ing ea men N
Tempe a u es (°C)
(
X
± SE) ( ange)1,2
Win e ing
du a ion
(days)1
P e- win e ing weigh
(mg) (
X
± SE)3
% Win e mo ali y
(
X
± SE)3
% Weigh loss
(
X
± SE)3
Cu en 275 9.4 ± 0.3 (2.6– 20.1) 141 224.2 ± 1.6a 2.2 ± 0.8a 3.9 ± 0.04a
Nea - u u e 275 10.0 ± 0.4 (3.2– 22.5) 134 224.0 ± 1.6a 1.8 ± 0.6a 5.8 ± 0.05b
Dis an - u u e 275 12.3 ± 0.4 (4.4– 25.3) 128 227.0 ± 1.6a 4.0 ± 1.2a 8.4 ± 0.09c
1F om 1 Oc obe un il 5% emale eme gence.
2Daily empe a u e cu es p o ided in Figu e S1.
3Values ollowed by di e en le e s a e signi ican ly di e en (Tukey HSD es , p > .05).
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ALBACETE e al.
2.4 | Pho o axis es
Two hou s a e he exposu e phase, app oxima ely 25 indi iduals o
each win e ing- pes icide ea men we e subjec ed o a pho o ac ic
es in which bees in a da k chambe we e exposed o a ligh s imu-
lus. The esponse o each bee was sco ed as ei he posi i e ( he bee
walked o he ligh sou ce wi hin 60 s) o nega i e ( he bee walked
bu did no each he ligh sou ce; see Suppo ing In o ma ion Me h-
ods o de ails).
2.5 | Sy up consump ion and su i al
Tes cages we e inspec ed daily o moni o sy up consump ion
(assessed by checking he le el o sy up in he calib a ed sy inge;
accu acy: 0.01 mL) and bee mo ali y. Th ee addi ional con ain-
e s wi hou bees we e used as con ols o measu e and accoun
o changes in sy up le els due o e apo a ion. The sy up solu ion
was enewed e e y 3– 4 days un il all he bees died. Sample sizes o
sy up consump ion and su i al we e app oxima ely 60 indi iduals
pe win e ing ea men and insec icide dose.
2.6 | Da a analysis
To es he e ec o win e ing ea men on win e mo ali y we
used a binomial gene alized linea model (GLM). To de e mine he
e ec o win e ing ea men on pe cen weigh loss, we used a be a
eg ession model, wi h indi idual p e- win e ing weigh as a co a ia e
(be a eg package; C iba i- Ne o & Zeileis, 2010).
We used GLMs o analyze he e ec s o win e ing ea men ,
insec icide exposu e and hei in e ac ion on pho o ac ic esponse
(binomial e o dis ibu ion and iden i y link unc ion), daily sy up
consump ion (ze o- in la ed Gamma e o dis ibu ion and log link
unc ion), and longe i y (Poisson e o dis ibu ion and log link
unc ion). Because body size may a ec ood consump ion (Azpiazu
e al., 2019; Sgolas a e al., 2018) and pes icide sensi i i y (Thomp-
son, 2016), p e- win e ing weigh was added as a co a ia e in he
sy up consump ion and longe i y analyses. Pai wise compa isons
we e done wi h Tukey's p- alue adjus men me hod (emmeans-
package; Len h e al., 2019).
We used Kaplan– Meie (K- M) su i al cu es o illus a e he
combined e ec s o win e ing and insec icide ea men s on pos -
exposu e su i al. Then, we an a log- ank omnibus es o ex-
plo e o e all di e ences among ea men s (su di unc ion o
he su i al R package wi h ρ = 0; The neau e al., 2020). Pai wise
compa isons be ween su i al cu es we e done wi h Holm mul i-
compa ison co ec ions and ρ = 0 (pai wise_su di unc ion o he
su mine package; Kassamba a e al., 2020).
To explo e po en ial syne gis ic e ec s be ween win e ing and
insec icide exposu e on su i al we used he Bliss d ugs' indepen-
dence c i e ion (Demidenko & Mille , 2019) o compa e he obse ed
su i al cu es o he nea - and dis an - u u e popula ions (a he
di e en insec icide doses) wi h he co esponding expec ed su -
i al p obabili y cu es, buil assuming no in e ac ion be ween he
wo ac o s. The analyses (de ails p o ided in Suppo ing In o ma-
ion Me hods) we e conduc ed wi h he Fh es cc unc ion o he
Fh es package (Olle & Langoh , 2017).
All analyses we e conduc ed in R (R Co e Team, 2020). P ima y
da a and associa ed R sc ip s a e accessible on he eposi o y D yad
(Albace e e al., 2023).
3 | RESULTS
3.1 | Win e mo ali y and weigh loss
As expec ed, bees exposed o clima e change win e ing ea men s
eme ged ea lie han bees o he cu en clima e scena io (Table 1).
Win e mo ali y was e y low and was no a ec ed by win e ing
ea men (GLM, χ2 = 2.8; d = 2; p = .2516). On he o he hand, body
weigh loss inc eased wi h win e ing empe a u e (GLM, χ2 = 2311.8;
d = 2; p < .0001). Bees o he dis an - u u e scena io los wice as
much body weigh as bees o he cu en scena io (Table 1). Re-
ga dless o he win e ing ea men , bees wi h lowe p e- win e ing
weigh los a g ea e p opo ion o body weigh (GLM, χ2 = 16.7;
d = 1; p < .0001).
3.2 | Pho o ac ic esponse
Pho o ac ic esponse was a ec ed by win e ing ea men (GLM,
χ2 = 14.7; d = 2; p = .001), insec icide dose (GLM, χ2 = 109.2; d = 2;
p < .0001), and hei in e ac ion (GLM, χ2 = 16.1; d = 4; p = .003).
The as majo i y o bees no exposed o he insec icide (0 dose)
esponded posi i ely o ligh , i espec i e o he win e ing ea men
(Figu e 1). The pe cen age o bees ha esponded posi i ely o ligh
dec eased wi h inc easing insec icide dose, and his dec ease was
especially p onounced in bees o he dis an - u u e scena io (Fig-
u e 1). In he cu en and nea - u u e scena ios, he p opo ion o
posi i ely esponding bees was ha dly a ec ed by he low insec i-
cide dose, bu d opped o ca. 50% when bees we e exposed o he
high dose. In bees o he dis an - u u e scena io, he p opo ion o
posi i ely esponding bees wen om 95.8% (0 dose) o 73.1% (low
dose) and 11.1% (high dose).
3.3 | Sy up consump ion
Daily consump ion o he eeding solu ion was no a ec ed by
win e ing ea men (GLM, χ2 = 2.5; d = 2; p = .2827) bu a ied
wi h insec icide exposu e (GLM, χ2 = 65.6; d = 2; p < .0001). The
in e ac ion be ween win e ing and pes icide exposu e was signi i-
can (GLM, χ2 = 17.7; d = 4; p = .0014) because di e ences in sy up
consump ion ac oss insec icide doses we e especially p onounced
in bees o he dis an - u u e ea men (Figu e 2A). The e ec o
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ALBACETE e al.
he high insec icide dose on sy up consump ion was e iden om
day 1 (Figu e S2). We expec ed la ge bees o consume mo e sy up
han small bees, bu he ela ionship be ween p e- win e ing body
weigh and daily sy up was no signi ican (GLM, χ2 = 1.6; d = 1;
p = .1987).
3.4 | Su i al p obabili y and longe i y
Su i al cu es di e ed signi ican ly among ea men s (log- ank
es : χ2 = 244.0; d = 8; p < .0001; Figu e 3). Fo a gi en insec icide
dose, he cu en and nea - u u e su i al cu es we e simila
(p > .05). Su i al p obabili y d opped as e in bees o he dis an -
u u e scena io han in bees o he cu en and nea - u u e scena ios
a all he insec icide doses es ed, including 0 ng/bee. Consequen ly,
longe i y di e ed signi ican ly ac oss di e en ea men s (Fig-
u e 2B). Longe i y was a ec ed by win e ing ea men (GLM,
χ2 = 262.1; d = 2; p < .0001), insec icide exposu e (GLM, χ2 = 613.3;
d = 2; p < .0001), and hei in e ac ion (GLM, χ2 = 39.6; d = 4;
p < .0001). P e- win e ing body weigh had a signi ican e ec on lon-
ge i y (GLM, χ2 = 27.7; d = 1; p < .0001), wi h la ge bees li ing longe
han small ones.
To assess po en ial syne gism be ween win e ing ea men and
insec icide exposu e on su i al p obabili y, we compa ed he ob-
se ed su i al cu es o he nea and dis an - u u e popula ions a
he wo insec icide doses wi h he expec ed su i al cu es based
on he Bliss c i e ion o d ugs independence. We ound ha he
combina ion o he dis an - u u e scena io and exposu e o he
high insec icide dose esul ed in a syne gis ic dec ease in su i al
(Figu e 4a). We also ound a signi ican an agonis ic e ec in bees
o he nea - u u e scena io exposed o he low insec icide dose
(Figu e 4b).
4 | DISCUSSION
The aim o his s udy was o es ablish whe he clima e wa ming
could a ec he abili y o adul bees o cope wi h pes icide expo-
su e. We used clima e change p ojec ions om IPCC RCP8.5 and
ealis ic concen a ions o a widely used insec icide o assess he
combined e ec s o inc easingly wa m win e ing empe a u es and
suble hal insec icide exposu e on he beha io and longe i y o a
soli a y bee. Ou esul s demons a e syne gis ic e ec s be ween
ealis ic scena ios o wo o he main d i e s o bee declines. Impo -
an ly, hese e ec s we e ob ained ollowing acu e o al exposu e o
a single insec icide. In ield condi ions bees may expe ience epea ed
and/o ch onic exposu e o a a ie y o chemicals ia di e en ex-
posu e ou es (Knapp e al., 2023; Sanchez- Bayo & Goka, 2014). A
he same ime, he empe a u es o ou mos pessimis ic clima e
scena io a e al eady occu ing in pa icula ly wa m win e s (win e
empe a u es in Eu ope in 2019– 2020 we e 3.4°C highe han he
mean o 1981– 2010; AEMET, 2021; Cope nicus, 2020). The e o e,
bo h ou pes icide and clima e scena ios may be conside ed con-
se a i e. Ou esul s unde sco e he need o s udy combina ions
o s esso s o ully unde s and he e ec s o global change on bee
popula ions (Goulson e al., 2015). Ou indings also ha e impo an
implica ions o pes icide egula ion. Pes icide isk assessmen is
based on median le hal and e ec doses (LD50 and ED50). Gi en
FIGURE 1 Model- es ima ed means and 95% con idence in e als o pe cen posi i e esponse o a pho o axis es in Osmia co nu a
emales exposed o h ee win e ing ea men s ep esen ing inc easingly wa m clima e change scena ios, and h ee o ally adminis e ed
doses o he insec icide sul oxa lo (0, 4.55 and 11.64 ng/bee). Di e en le e s deno e signi ican di e ences (Tukey HSD es , p < .05).
N = 24– 29 indi iduals pe win e ing scena io and dose.
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ALBACETE e al.
ou esul s, cu en LD50 and ED50 alues may no ep esen su i-
cien ly p o ec i e h esholds as bee popula ions a e con on ed wi h
inc easingly wa m empe a u es.
Win e ing ea men did no ha e a signi ican e ec on win-
e mo ali y, which was e y low and simila o mo ali y alues
ound in s udies in which Osmia popula ions we e win e ed unde
na u al condi ions (Bosch & Blas, 1994b; Bosch & Kemp, 2000;
Ca aDonna e al., 2018; Sgolas a e al., 2012). Simila ly, win e ing
ea men by i sel did no impai he abili y o emales o espond
o ligh . On he o he hand, win e ing ea men had an impo an
impac on weigh loss, which, in ag eemen wi h p e ious s udies,
inc eased wi h win e ing empe a u es. Because body weigh loss
du ing win e ing is accompanied by he deple ion o ene gy e-
se es in Osmia (Fliszkiewicz e al., 2012; Sgolas a e al., 2011), we
expec ed ha bees exposed o clima e wa ming would consume
mo e sy up o ebuild hei me abolic ese es (Nes el e al., 2016).
FIGURE 2 Model- es ima ed means and 95% con idence in e als o daily sy up consump ion (a) and longe i y (b) in Osmia co nu a
emales exposed o h ee win e ing ea men s ep esen ing inc easingly wa m clima e change scena ios, and h ee o ally adminis e ed
doses o he insec icide sul oxa lo (0, 4.55, and 11.64 ng/bee). Di e en le e s deno e signi ican di e ences (Tukey HSD es , p < .05).
N = 53– 65 indi iduals pe win e ing scena io and dose.
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6254
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ALBACETE e al.
Con a y o his expec a ion, win e ing ea men did no a ec
daily sy up consump ion. So a , hese indings sugges ha he
clima e change scena ios es ed would no comp omise win e
su i al, eeding success and pos - eme gence pe o mance in O.
co nu a. Howe e , e en wi h simila eeding a es, bees win e ed a
he wa mes empe a u e egime had signi ican ly educed mean
longe i y (10 days compa ed o 14– 15 days in bees o he o he
wo win e ing scena ios), a s ong p edic o o ealized ecundi y
in Osmia (Bosch & Vicens, 2006; Sgolas a e al., 2016). Longe i y
was also signi ican ly a ec ed by body size, wi h small indi iduals
ha ing sho e li e spans. Adul body size in Osmia is di ec ly de-
penden on he amoun o ood p o ision alloca ed o he la a by
he nes ing emale (Bosch & Vicens, 2002). The e o e, his o ical
declines in bee body size a ibu ed o sca ci y o lo al esou ces
in simpli ied landscapes may be u he comp omising bee longe -
i y and ealized ecundi y (Chole e al., 2019; G ab e al., 2019;
He e a e al., 2023; Oli ei a e al., 2016).
Like mos soli a y bees, Osmia spp. o e win e on a ixed bud-
ge , and expe ience a conside able deple ion o lipid ese es du ing
win e ing (Fliszkiewicz e al., 2012; Sgolas a e al., 2011). Upon
eme gence, adul s ly o nea by lowe s and ake a i s , long, nec-
a meal ha p esumably allows hem o ebuild hei ene ge ic e-
sou ces (Bosch & Kemp, 2001; Nes el e al., 2016). In ag icul u al
en i onmen s, howe e , he nec a inges ed in his i s meal may
con ain suble hal le els o pes icides (Da id e al., 2016; Di ely &
Kamel, 2012; Helle e al., 2020; Hladik e al., 2016). To mimic his
scena io, we exposed newly eme ged bees o wo suble hal doses
o Close , a widely used insec icide. The doses used co espond o
concen a ions o 0.58 and 0.23 ppm o ac i e ing edien , which
all wi hin he ange o sul oxa lo esidues ound in he nec a o
a ious c op lowe s 2– 7 days a e applica ion (USEPA, 2019). Ou
esul s show ha hese ealis ic le els o exposu e, especially he
high dose, impai ed he abili y o bees o espond o ligh esul ing
in a d as ic educ ion o pho o ac ic esponse in bees o he dis an -
u u e clima e scena io (Figu e 1). The inabili y o espond o ligh is
indica i e o an al e a ion o he sensi i i y o he unc ioning o he
isual sys em (Klein e al., 2017). Exposu e o suble hal doses o im-
idaclop id, a neonico inoid insec icide wi h a mode o ac ion simila
o sul oxa lo (Spa ks e al., 2013), inc eases he exp ession o genes
ela ed o biogenic amine ecep o s, such as se o onin, y amine,
and oc opamine, associa ed wi h a lack o pho o ac ic esponse in
D osophila (Ma elli e al., 2020). High le els o oc opamine ha e
also been linked o educed esponse o ligh in honey bees (Bloch &
Meshi, 2007; Scheine e al., 2014).
The in e ac ion be ween win e ing and pes icide exposu e was
also e iden in he a e o daily sy up consump ion. Exposu e o
he insec icide dep essed eeding a es in bees o he h ee win-
e ing ea men s, bu his dec ease was especially p onounced in
FIGURE 3 Cumula i e su i al p obabili y o Osmia co nu a emales exposed o h ee win e ing ea men s ep esen ing inc easingly
wa m clima e change scena ios, and h ee o ally adminis e ed doses o he insec icide sul oxa lo (0, 4.55, and 11.64 ng/bee). Cu es wi h
di e en le e s a e signi ican ly di e en (pai wise compa isons, log- ank es , p < .05).
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ALBACETE e al.
bees exposed o he wa mes win e (Figu e 2A). The inhibi o y e -
ec o sul oxa lo on sy up consump ion has been documen ed in
bo h soli a y and social bees (Azpiazu e al., 2022; Li e al., 2021;
Si i e e al., 2020). Longe i y was educed by ca. 50% in bees o
he cu en and nea - u u e scena ios exposed o he high insec i-
cide dose. In bees o he dis an - u u e scena io, exposu e o he low
dose led o an es ima ed 11% educ ion in longe i y and exposu e
o he high dose esul ed in a syne gis ic 70% educ ion (Figu e 3).
As men ioned, he cogni i e abili ies o he bees o he la e ea -
men we e signi ican ly impai ed, u he educing he e ec i e ime
ame a ailable o ep oduc ion (Bosch & Vicens, 2006; Sgolas a
e al., 2016). We also ound ha bees exposed o he nea - u u e
scena io and he low insec icide dose li ed longe han expec ed.
Howe e , his an agonis ic e ec did no esul in an inc ease in lon-
ge i y compa ed o bees o he nea - u u e scena io exposed o he
0 insec icide dose. An agonis ic in e ac ions a e no uncommon in
s udies add essing in e ac ions be ween s esso s (Bi d e al., 2021;
B uckne e al., 2023; Si i e e al., 2021; Za agoza- T ello e al., 2021).
The inc eased sensi i i y o Close in bees exposed o clima e
wa ming scena ios may be media ed by he e ec s o wa m win e
empe a u es on he consump ion o ene gy ese es and a body
deple ion in Osmia (Bosch e al., 2000, 2010; Bosch & Kemp, 2003,
2004; Fliszkiewicz e al., 2012; Sgolas a e al., 2011). The a body
is a dynamic, “li e - like”, issue ha ac s as an o gan o ene gy
s o age and o he me abolic unc ions in insec s (A ese & Soul-
ages, 2010). S udies on bu e lies and mosqui oes ha e ound ha
exposu e o xenobio ics inc eases he exp ession o cy och ome
P450 monooxygenases genes, in ol ed in de oxi ica ion, in he
a body (Da id e al., 2006; Pe e sen e al., 2001). In addi ion,
s udies on bumblebees ha e ound ha he exp ession o hese
genes in he a body is enhanced by a suc ose- ich die (Cos a
e al., 2020), and ha queens, which ha e signi ican ly highe a
body ese es han males and wo ke s, a e mo e esilien o pes-
icides (Linguadoca e al., 2022). In honey bees, a ack by he mi e
Va oa des uc o , ha eeds on he a body o adul s (Ramsey
e al., 2019) dis up s de oxi ica ion abili y and inc eases sensi i i y
FIGURE 4 Obse ed ( ed/yellow lines) and expec ed (black dashed lines) su i al p obabili y cu es o Osmia co nu a emales exposed
o dis an - (a) and nea - u u e (b) clima e change scena ios and o wo o ally adminis e ed doses o he insec icide sul oxa lo (4.55 and
11.64 ng/bee). In e ac ion signi icance is based on he Bliss c i e ion o d ugs independence (FH s a is ic dis ibu ion >0 indica es syne gism
be ween he wo s esso s; FH s a is ic dis ibu ion <0 indica es an agonism).
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6256
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ALBACETE e al.
o pes icides (Blanken e al., 2015; Schwa z e al., 2021; Zhu
e al., 2022). Based on his line o e idence, we sugges ha he
abili y o p oduce de oxi ica ion enzymes o con on suble hal
le els o insec icide is dep essed in soli a y bees eme ging wi h
deple ed a bodies as a esul o wa m win e empe a u es.
Ou indings indica e ha ongoing global wa ming may exace ba e
he impac o pes icides on bee heal h and comp omise bee ep o-
duc i e success, wi h po en ially impo an consequences on popu-
la ion dynamics. The magni ude o hese impac s will depend on ou
abili y o educe he dependence o ag icul u e on pes icides (Si i e
e al., 2023; Sponsle e al., 2019) and on he ex en o which bee pop-
ula ions a e able o adjus o he new clima e scena io h ough adap a-
ion and/o pheno ypic plas ici y. The dis ibu ion o O. co nu a anges
om no he n A ica o sou he n Sweden (Mülle , 2022), sugges ing
ha he species has he capaci y o adap o local clima es. Tempe a-
u e inc eases such as hose simula ed in ou s udy a e likely o ha e
a s onge impac in popula ions om al eady wa m en i onmen s,
li ing close o he he mal sa e y limi s o he species, han in no h-
e n popula ions (Ca aDonna e al., 2018). Bees may also mi iga e he
e ec s o clima e wa ming by ac i ely selec ing coole nes ing si es, as
shown in O. bico nis (Os ap- Chec e al., 2021), o h ough la i udinal o
al i udinal mig a ion o coole a eas (Ke e al., 2015). A any a e, he
ac ha empe a u e inc eases simila o hose o ou mos pessimis-
ic scena io ha e been eco ded in ecen yea s (AEMET, 2021; Cope -
nicus, 2020) sugges s ha he combined e ec s o clima e wa ming
and pes icide exposu e a e al eady a ec ing bee popula ion dynamics.
ACKNOWLEDGMENTS
The au ho s a e g a e ul o h ee anonymous e iewe s o hei
cons uc i e commen s. The au ho s a e also g a e ul o M. Ba na-
das, E. Se a osa and P. Sole o hei echnical assis ance h ough-
ou he expe imen . The s udy was unded by he Spanish Minis y
o Science and Inno a ion, h ough p ojec s RTI2018- 098399- B- I00
and PID2021- 128938OB- I00, and PhD schola ships o SA and GS
(PRE2019- 088817 and PRE2019- 090375). CA was suppo ed by a
Ma ga i a Salas pos doc o al ellowship om he Spanish Minis y
o Uni e si ies h ough he EU Nex Gene a ion p og am.
CONFLICT OF INTEREST STATEMENT
The au ho s decla e hey ha e no con lic o in e es .
DATA AVAILABILITY STATEMENT
The da a ha suppo indings o his s udy a e a ailable on D yad a
h ps://doi.o g/10.5061/d yad.dz08k ps3 .
ORCID
Se gio Albace e h ps://o cid.o g/0000-0001-7696-623X
Gonzalo Sancho h ps://o cid.o g/0000-0001-7711-846X
Celes e Azpiazu h ps://o cid.o g/0000-0001-8217-9347
Anselm Rod igo h ps://o cid.o g/0000-0001-6341-0363
Robe o Molowny- Ho as h ps://o cid.o g/0000-0003-2626-6379
Fabio Sgolas a h ps://o cid.o g/0000-0002-2845-8297
Jo di Bosch h ps://o cid.o g/0000-0002-8088-9457
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