R. Chester et al., DEFINING THE CHEMICAL CHARACTER OF AEROSOLS FROM THE ATMOSPHERE OF THE MEDITERRANEAN-SEA AND SURROUNDING REGIONS, Oceanologica acta, 16(3), 1993, pp. 231-246
Atmospherically-transported trace metals can play an important role in
biogeochemical cycles in the Mediterranean Sea. However, although the
magnitude of trace metal air to sea fluxes is initially dependent on
the metal concentrations in the air, it is the ''chemical character''
of the aerosol which constrains the fate of the metals in sea water; f
or example, the solubility of trace metals is considerably greater fro
m anthropogenic than from crustal components. To a first approximation
the chemical composition of the Mediterranean particulate aerosol is
controlled by the extent to which an anthropogenic-rich ''background''
material, having a mainly European origin, is perturbed by mixing wit
h crustal components having a desert origin. These perturbations offer
an environmentally meaningful index which can be used to define the '
'chemical character'' of the Mediterranean particulate aerosol in term
s of the manner in which trace metals are partitioned between the anth
ropogenic and crustal components. This ''chemical character'' concept
was assessed using: a) a total of 83 particulate aerosols collected on
a W --> E transect across the Mediterranean Sea and surrounding regio
ns; and b) particulate aerosol populations from a number of adjacent c
oastal seas. The crustal component in the samples was assumed to have
the composition of the average crust and trace metals in excess of the
ir crustal metal:Al ratios were assigned to a European aerosol ''backg
round'' component (EABC). It was found that the average Zn:Cu, Zn:Ni,
Zn:Cr and Zn:Mn ratios in the EABC indicate that it has a composition
which is generally similar to the average anthropogenic background emi
ssions of trace metals over Europe. The extent to which the EABC is af
fected by mixing with crustal material in the particulate aerosols was
estimated using enrichment factors in which Al is employed as the sou
rce indicator; thus, EF(crst) = (C(xp)/C(Alp))/(C(XC)/C(Alc)), in whic
h C(XP) and C(Alp) are the concentrations of an element x and Al, resp
ectively, in the aerosol, and C(XC)c and C(Alc) are their concentratio
ns in average crustal material. Elements which have EF(crust) values <
10 in a particulate aerosol are assumed to have a significant crustal
source and are termed non-enriched elements (NEEs), and those which h
ave EF(crust) > 10 are assumed to have a significant non-crustal sourc
e and are termed anomalously enriched elements (AEEs). For a particula
te aerosol composed of crustal and anthropogenic components the EF(cru
st) values of the AEEs will be reduced as the proportions of crustal m
aterial increase. When this is expressed in the form of an EF diagram,
in which the EF(crust) values of a trace metal in a particulate aeros
ol population are plotted against the concentrations of Al, the partic
ulate aerosols from the atmosphere of the Mediterranean Sea and surrou
nding regions can be described in terms of the extent to which the EAB
C is mixed with, and diluted by, crust-rich components. Under certain
conditions the ''mixing relationship'' is distorted by relatively larg
e inputs of either: a) crust-rich components, or b) urban-rich materia
l having a local origin. However, the overall ''chemical character'' o
f the aerosols can be assessed on the basis of the EF(crust) values of
the AEEs Cd, Pb, Zn, Cu, Ni and Cr.