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The composition and relationships between trace element levels in inhalable atmospheric particles (PM10) and in leaves of Nerium oleander L. and Lantana camara L.

Abstract

In order to evaluate the composition of inhalable atmospheric particles and to study the relationship between trace element levels in PM10 and in leaves of two plant species, the amount of Ba, Cu, Fe, Mn, Pb, Ti and V were analysed in PM10 and in Nerium oleander L. and Lantana camara L. leaves from two sites in the city of Seville and one remote control site. In PM10, the Cu and Fe content was significantly lower (p < 0.05) in the control site than in the other sites. No correlations between leaf content and air content were found for the elements in L. camara. On the contrary, positive and significant correlations (p < 0.05) were found between leaf content of N. oleander and PM10 content for Cu and Fe. The data suggest that N. oleander can be used in atmospheric biomonitoring studies, because it is especially useful for Cu and Fe, N. oleander being a better indicator than L. camara.

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The composition and relationships between trace element levels in inhalable atmospheric particles (PM10) and in leaves of Nerium oleander L. and Lantana camara L.

Author: Fernández Espinosa, Antonio José; Rossini Oliva, Sabina
Publisher: Elsevier
Year: 2006
DOI: 10.1016/j.chemosphere.2005.06.038
Source: https://idus.us.es/bitstreams/be03edc6-aedd-4e4e-b88c-c85971485c8a/download
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“This is an Accep ed Manusc ip o an a icle published by Else ie in:
CHEMOSPHERE on 2006, a ailable a :
h ps://doi.o g/10.1016/j.chemosphe e.2005.06.038”
The composi ion and ela ionships be ween ace elemen le els
in inhalable a mosphe ic pa icles (PM10) and in lea es o Ne ium oleande L. and
Lan ana cama a L.
1A.J. Fe nández Espinosa, 2S. Rossini Oli a*
1 Depa men o Analy ical Chemis y, Uni e si y o Se ille, C. P o eso Ga cía González
s/n, E-41012, Se ille, Spain E.mail: [email p o ec ed]
2Depa men o Plan Biology and Ecology, Uni e si y o Se ille, A . Reina Me cedes s/n,
Apdo. 1095, 41080 Se ille, Spain, Tel.: +34954557056; Fax: +34954557059
*Co esponding au ho : e-mail: [email p o ec ed]
ABSTRACT
In o de o e alua e he in luence o ai pollu an in lux on inhalable a mosphe ic pa icles
(PM10) me al composi ion and s udy he ela ionship be ween ace elemen le els in PM10
and in lea es o wo plan species, he concen a ion o Ba, Cu, Fe, Mn, Pb, Ti and V we e
analysed in PM10 and in Ne ium oleande L. and Lan ana cama a L. lea es om 3 si es o
he ci y o Se ille. In he PM10, Cu, Fe and Mn con en was signi ican ly lowe (p0.05) in
he con ol si e han in he o he si es. A mosphe ic pollu ion le el o he ci y o Se ille can
be gene ally conside ed no dange ous o human heal h. No co ela ion be ween lea con en
and ai con en was ound o none elemen s in L. cama a. By con as posi i e and
signi ican co ela ions (p0.05) we e ound be ween lea con en o N. oleande and PM10
con en o Cu and Fe. The da a sugges ha N. oleande can be used in a mosphe ic
biomoni o ing s udies, being especially use ul o Cu and Fe and much indica e han L.
cama a.
Keywo ds: Biomoni o ing; Lea ; Pa icles; T ace elemen s
INTRODUCTION
In e es on he e ec o a mosphe ic pa icles and especially in he inhalable ac ion
(PM10) inc eased du ing he las yea s. PM10 a e conside ed o be ha m ul o human heal h
since hey can cause espi a o y and ca dio ascula disease. Associa ion be ween as hma
a acks and coughs wi h pa icula es ha e also been epo ed (F ee -Smi h e al., 1997). In
la ge u ban a eas, he conside able amoun o pa icula e ma e in he ai is a e y c ucial
p oblem. The p ima y sou ce o ai bo ne pa icula e ma e is ag icul u al p ac ises, ehicle
a ic, indus ial p ocesses and ossil uel s a ions (Becke e al., 1998). On he o he hand,
plan s a e known o cap u e ace elemen s and can be used in biomoni o ing s udies
(Ma ke , 1996; Rossini Oli a and Valdés, 2003). Se e al s udies ha e been done on he
con amina ion by pa icula e ma e in he ci y (Janssen e al., 1997; Monaci e al., 2000;
Fe nández e al., 2001), and on he use ul o plan species as biomoni o s (Ba ghigiani e al.,
1991; Sawidis e al., 1995; Aksoy and Öz ü k, 1997; Ba gagli e al., 2003; Rossini Oli a and
Valdés, 2003, 2004, Rossini Oli a & Rau io, 2004). Ne e heless, whe he a ela ion be ween
PM10 composi ion and ace elemen s in plan s exis s was insu icien ly s udied. An a emp
o s udy he ela ion be ween Hg con en in osema y and b oom lea es, Abies alba needles
and pine needles in ela ion o hose in a mosphe e was done in I aly (Ba ghigiani e al.,
1991; Ba ghigiani and Bauleo, 1992; Ba ghigiani and Ris o i, 1995).
Se ille is he mos densely popula ed ci y o Sou he n Spain, wi h 716.937
inhabi an s, si ua ed only 10 m abo e he sea le el on an ex ensi e plain c ossed by he
Guadalqui i Ri e . The ci y has a Medi e anean clima e wi h an annual a e age
empe a u e o 19 °C and ain all o 580 mm. T a ic ep esen s he mos impo an pollu ion
sou ce since indus ies a e a he sca ce and me allu gic p oduc s ep esen only 15% o his
indus ies. Impo an con ibu ions o c us al pa icles in Se ille and in he sou h o Spain a e
well known by he local scien i ic communi y and he Spanish and he egional go e nmen s.
The aim o his s udy was o compa e ace elemen le els be ween he con en in
PM10 and lea es o Ne ium oleande L. (oleande ) and Lan ana cama a L. (lan ana) o
e alua e i a di ec co espondence be ween he me al con en o pollu an s in ai and in plan
exis s. These species we e chosen because hey a e widesp ead in he ci y o Se ille (S o
Spain), bo h a e pe ennial and Oleande is know o be an use ul biomoni o (Sawidis e al.,
1991; Aksoy and Öz ü k, 1997; Rossini Oli a and Valdés, 2003). In addi ion, he
composi ion o inhalable a mosphe ic pa icles was s udied o es ablish he a mosphe ic
con amina ion le el o Se ille.
MATERIALS AND METHODS
Samples o pa icles smalle han 10 µm (PM10) and adul lea es o N. oleande and
L. cama a we e collec ed simul aneously in h ee sampling si es om au umn 2003 o sp ing
o 2004. A o al o 22 samples o PM10 we e collec ed oge he wi h he samples o bo h
species o plan s a he same day. Samples we e usually aken on di e en days o he week,
ob aining samples o e e y day o he week, he e o e, in di e en me eo ological and
en i onmen al condi ions. Sampling pe iods o ai bo ne pa icles we e om 0:00 a.m. o 23:59
p.m. Acco ding o he local au ho i ies in o ma ion, one o he sampling si e ep esen s he a ea
o Se ille a ec ed by he highes ehicula emissions (To neo, TRN) and he o he is a less
con amina ed a eas wi h low a ic densi y (Po eni , POR). The hi d sampling si e (BLK),
was chosen as a con ol si e; i is loca ed a abou 40 Km a om Se ille, in Sie a Mo ena,
away om any a ic emissions bu wi h simila clima ic cha ac e is ics.
Se e al b anches om h ee heal hy-looking plan s we e cu o om sides o he
canopy a 1.5 m o N. oleande and a 0.5 m o L. cama a. Once in he lab, abou 300 g o
esh ma u e lea es (including he pe ioles) we e mixed o p o ide a unique sample. Samples
we e d ied o e nigh a 70 °C, g ound o a ine powde .
A mosphe ic pa icula e ma e was collec ed wi h a s anda d high- olume sample MCV,
model CAV-A/HF equipped wi h a PM10 inle (MCV, model PM10/CAV). PM10 inle was
used o collec all pa icles less han 10 mic ome e s (aed) and he MCV ma k was in e -
compa ed wi h he e e ence PM10 inle o he EN 12341 Eu opean No m. The sampling
sys em was se a a low a e o 68 m-3h-1, acco ding manu ac u ing speci ica ions. Glass ib e
il e s we e used as collec ion media (Wha man GF/A, 24.5 x 20.3 cm). Be o e he analysis
o ai bo ne samples, il e s used o pa icle collec ion we e d ied, be o e and a e weighing,
in a high- olume desicca o unde 3% R.H. o a 48-h pe iod. Ope a ions o conse a ion,
d ying and weighing ook place in a da k oom a 505 % R.H, a empe a u e o 201 ºC was
con olled by a hea ing-cooling sys em. Ca e was aken in handling he sampled il e s and
plan s in o de o a oid con amina ion p oblems using a e ical lamina ai low cabine wi h
a HEPA il e INDELAB, model IDL-48V, he eby ensu ing ai cleanliness s anda ds o class
100 acco ding o he US-Fede al S anda d 209E (FED.STD-209E, 1988).
Fil e s and plan s we e placed in closed e lon essels wi h 15 ml o HNO3-HClO4
/ (3:1) and diges ed in a mic owa e o en Milles one, model E hos 900 wi h a speci ic
diges ion p og amme. A e diges ion and cooling, sample solu ions we e ans e ed in o
s e ile ubes.
Since indi iduals blanks we e no a ailable o each il e used o sampling, a se o
unexposed il e s o each ype o il e was analysed as blanks using he same p ocedu e used

o samples. The mean unexposed il e s alue we e de e mined and sub ac ed om each
sample o ob ain he bes es ima e o each elemen in he pa icula e ma e .
The accu acy o he de e mina ions we e p e iously checked by analysis o a NIST e e ence
ma e ial (SRM 1648) o ai bo ne pa icles and a GBW 07604 (popla lea es) e e ence
ma e ial o plan s. A gold solu ion was used as in e nal s anda d o spike samples, blanks
and e e ence ma e ial and o check he co ec quan i ica ion o he elemen s. P e iously, i
was s udied ha gold was no p esen ed in u ban ai and plan s and i s p esence wi hin he
e lon essel had no in luence on analy ical de e mina ions o he o he me als. All ul apu e
eagen s and s anda ds we e supplied by Me ck and dis illed wa e was o Milli-Q g ade
ob ained om a Wa e s-Millipo e appa a us, model Plus. The concen a ion o Ba, Cu, Fe,
Pb, Mn, Ni, Ti and V ha e been de e mined simul aneously by induc i ely coupled plasma
a omic emission spec ome y (ICP-AES), using a Fisons-ARL 3410 sequen ial mul i-
elemen ins umen . The s anda d ope a ional condi ion o his ins umen a e summa ised as
ollows: he ca ie gas, coolan gas, and plasma gas is a gon a 80 psi o p essu e, he ca ie
gas and plasma gas low a e a e 0.8 l min-1, he coolan gas low a e is 7.5 l min-1 and he
in eg a ion ime is 1 s. One mini- o ch consumes a gon gas a a adio equency powe o 650
W. Consequen ly, i is capable o consuming a ew millili es o sample a a low a e o 2.3
ml min –1. In o de o a oid e o s in esul s due o he e ec p oduced by he di e en
iscosi y and densi y o he acid ma ix o samples on he ICP nebulisa ion, calib a ion cu es
ha e been made wi h he same acid ma ix.
S a is ical analyses we e ca ied ou using he CSS:STATISTICA (S a So ) so wa e
package. Summa y s a is ics we e used o calcula e he mean alues and s anda d de ia ion
and, one-way analysis o a iance (ANOVA) o de ec signi ican di e ences o mean
con en be ween si es and species (p0.05). Rela ionship be ween me al concen a ion in
pa icles and in bo h species was es ed by he Pea son co ela ion coe icien s ( ). The
in e p e a ion o he co ela ion esul s consis in assigning a common sou ce o he me al
ac ions co ela ed, in ela ion o he main sou ces o his ci y, such as he a ic, he land
pa icles and he indus ial ac i i ies. In ou case, when one me al inc eases hei
concen a ion in he ai , pa allelly o o he me al h ough di e en sampling si es and
di e en days, one can conside ha hese me als come om he same emission sou ce.
Because a high co ela ion coe icien does no necessa ily imply linea i y, linea i y was
e i ied by g aphical examina ion. Any non-linea case was disca ded.
RESULTS AND DISCUSSION
The s udied elemen s mean concen a ions ound in PM10 and in plan s in di e en
si es a e epo ed in Table 1. The alues o pa icles me al concen a ion o all sampling si es
can be conside no dange ous o human heal h, since hei alues showed lowe
concen a ions han hose indica ed by he Uni Risk (UR) alues on cance o he WHO
(Wo ld Heal h O ganiza ion). Only o Ni, he mean alue was close o he UR limi (2.5 ng
m-3), indica ing he po en ial isk o ha m ul o his elemen . The esul o Cu and Pb is also
acco ding o Ross (1994) c i e ia, since he concen a ion o hese wo elemen s in bo h
s udied species did no exceed he uppe limi o alues conside ed oxic o p esen in
con amina ed plan s.
The ANOVA esul s showed ha he ai pollu an concen a ions we e no
signi ican ly di e en be ween he a ious sampling si es, excep o Mn, Cu and Fe. The Mn
concen a ion was signi ican ly low in he con ol si es espec o POR and TRN and, his
was also he case o Cu and Fe only compa ing o TRN. The TRN si e ep esen s he zone o
he ci y mo e in luenced by he ehicula a ic as i was abo e men ioned, sugges ing ha
a mosphe ic pollu ion by bo h elemen s is highe due o he a ic o soil e-suspension
(Fe nández e al., 2004).
In ela ion o he plan s, in bo h species he mean concen a ion o Pb, Ni, Mn, Cu
(excep o lan ana en POR), Fe (excep o lan ana in POR) and Ba we e below han he
e e ence alues gi en by Ma ke (1996). On he o he hand he V and, mainly he Ti mean
alues in bo h species we e always highe han he e e ence alues, including he samples
om he con ol si e, sugges ing ha hey come mainly om he soil.
Lea es o oleande showed a mean concen a ion o Cu, Pb, Fe and Ni lowe han ha
epo ed by Rossini Oli a and Valdés (2003) in Pale mo. Sawidis e al. (1995) ound highe
alues o Cu and Pb in con ol si e and in ci y oads o Tessaloniki han hose ound in Se ille
and he same esul s we e epo ed by Aksoy and Öz ü k (1997) in An alya (Tu key),
con i ming he da a o PM10 abo e discussed.
In he case o N. oleande , di e ences o Pb, Ni and V concen a ion in he con ol
si e wi h espec o he o he si es we e no ind, whils a lowe Cu, Fe and Mn concen a ion
we e ound in he con ol si e. Fo L. cama a pollu an concen a ions we e signi ican ly
di e en be ween he a ious sampling si es, excep o Ni. The Pb, Ba, Cu, Fe and V
concen a ions we e signi ican ly lowe in he con ol si es only wi h espec o POR and, Mn
concen a ion in he con ol si e was signi ican ly highe han in bo h si es; signi ican ly
highe Ba and V concen a ions in he con ol si e wi h espec o TRN we e also ound. In
addi ion, he Ti concen a ion in he con ol si e was signi ican ly highe han in he o he
si es. This means ha lan ana is no use ul as biomoni o since i does no e lec s he
pollu ion en i onmen al condi ions.
Co ela ion be ween con en in PM10 and plan s was only ound in one species, N.
oleande and only o Cu and Fe (Fig. 1), indica ing ha oleande can be a mo e use ul
biomoni o s o hese wo elemen s han L. cama a. This is in acco dance wi h Jones e al.
(1985) s a ing ha high posi i e associa ions be ween he pollu an concen a ions in plan s
and hei en i onmen sugges he po en ial use o pollu ion moni o ing in gene al and o
he examined me als in pa icula . Ba ghigiani and Ris o i (1995) did no ound any
ela ionship be ween Hg concen a ion in osema y and b oom lea es and in ai , indica ing
ha one o he easons could be he low Hg ai concen a ion. Since a mosphe ic pollu ion in
he sampling si es can be conside ed low, his can be he eason because he absence o
ela ionship in lan ana, indica ing he e o e ha i is less sensible han oleande o de ec
a mosphe ic pollu ion a ia ions by Cu and Fe.
Al hough lan ana has a oughe lea su ace han oleande , ha i is known ha his
cha ac e is ic inc eases he dus deposi ion, his s udy shows ha his p ope y look likes han
does no a ec s he capaci y o e ain and ap mo e pollu an s, since he ANOVA esul s
showed ha signi ican di e ences (p0.05) be ween he wo species only exis s o Cu and
Fe con en s, in addi ion oleande lea es accumula es mo e Ba han lan ana. On he o he hand
like Fa me epo ed (1993) ha his cha ac e is ic is impo an o pa icle g ea e han 10
m, he e o e his can be he eason because he null co ela ions ound in lan ana.
CONCLUSIONS
The a mosphe ic pollu ion by me als o he Se ille Ci y can be conside ed low and gene ally
no dange ous o human heal h excep o Ni. I on and Cu we e specially di e en ia ing
be ween he con ol si e and he u ban si es. These wo me als we e he only co ela ed
be ween pa icles and oleande lea concen a ions, indica ing ha his species is mo e use ul