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                                                 ARTICLE IN PRESS



                                                 Environmental Research 107 (2008) 371– 379

                                              Contents lists available at ScienceDirect

                                             Environmental Research


                                       journal homepage: www.elsevier.com/locate/envres




         Absorption of polycyclic aromatic hydrocarbons by Pinus bark: Analytical
         method and use for environmental pollution monitoring in the palermo area
         (Sicily, Italy)


         Santino Orecchio , Antonio Gianguzza, Loredana Culotta
         Dipartimento di Chimica Inorganica e Analitica, Universita ` di Palermo, Parco d’Orleans 2, 90128 Palermo, Italy


         article i n f o                  abstract
         Article history:                 In the light of using biomaterial as pollutants sorbents for the environmental biomonitoring, we report
         Received 16 October 2007         here the results of the absorption of polycyclic aromatic hydrocarbons (PAHs) by pine bark. Quantitative
         Received in revised form         analysis of 19 different polycyclic aromatic compounds was performed, after Soxhlet extraction in
         20 February 2008                 dichloromethane, by means GC–MS technique. Pinus was chosen due to its wide distribution in the
         Accepted 21 February 2008        Mediterranean area. The passive absorption of PAH by pine bark in the metropolitan areas allowed us to
          Available online 15 April 2008
                                          evaluate the air quality of Palermo. The obtained results showed a very high range of PAHs
         Keywords:                        concentrations, from 33 mg/kg (bark dry weight), as SPAHs, at the control site to 1015 mg/kg along a
         PAH                              road with high traffic flow.
         Bark
         Pinus                                                                        & 2008 Elsevier Inc. All rights reserved.
         Bioaccumulator
         GC/MS
         Air quality
         Palermo



         1. Introduction                                          The health effect of concern associated with PAH exposure is
                                                               cancer (de Meagd and Vethaak, 1998). According to the Interna-
            Polycyclic aromatic hydrocarbons (PAHs) may enter the atmo-  tional Agency for Research on Cancer (IARC, 1991), benzo[a]an-
         sphere from both natural and anthropogenic sources, the latter  thracene and benzo[a]pyrene are probable human carcinogens,
         prevailing in industrialized and urban areas. The primary natural  and benzo[b]fluoranthene, benzo[j]fluoranthene, benzo[k]fluor-
         sources of airborne PAHs are forest fires and volcanoes (Kim et al.,  anthene, and indeno[1,2,3,-c,d]pyrene are possible human carci-
         2003). Natural sources of PAHs also include biosynthesis by  nogens (IARC, 1991). Some researchers have suggested that 1–10%
         microbes and plants under anaerobic conditions (Neff, 1979). The  of the incidence of lung cancer is caused by air pollution.
         commercial production of PAHs is not a significant source of these  Toxicological investigations showed different cancerogenic
         compounds in the environment (Law and Biscaya, 1994; Howsam  potency for various PAH mixtures, individual PAH and different
         and Jones, 1998). PAHs are a class of chemicals that result from the  application paths (oral, dermal and inhalative) which at present
         incomplete combustion of fuels. In rural areas the residential  cannot be predicted quantitatively (Schneider et al., 2002). Of all
         burning of wood and the agricultural activities (combustion of  EPA–PAH analysed in this content of some PAHs—especially the
         grass, crop residues, etc.) represent the main source of atmo-  slightly volatile ones—are not regarded cancerogenic. Within the
         spheric PAHs, which result from inefficient combustion and  remaining PAHs there are substantial differences of potency of
         uncontrolled emissions. Other important stationary anthropo-  several orders of magnitude—the most potent possibly is
         genic sources include industrial power generation, incineration,  benzo(a)pyrene BaP. Through several different studies it became
         production of coal tar, coke, and asphalt and petroleum catalytic  evident that it is possible to specify the cancerogenic effect of
         cracking (Neff, 1979; Kim et al., 2003). The anthropogenic mobile  individual PAH compared with BaP and to weigh it by means of a
         sources are represented especially by vehicular traffic in large  conversion factor. These factors are called toxicity equivalence
         urban areas (Nielsen, 1996; Caricchia and Chiavarini Pezza, 1999;  factors (TEF, Table 1)(Larsen and Larsen, 1998; Nisbet and La Goy,
         Dumbar et al, 2001).                                  1992; Malcom and Dobson, 1994; Schneider et al., 2002).
                                                                  There are numerous references in the literature concerning the
                                                               PAHs concentration in the atmosphere of large urban areas and of
                                                              zones particularly exposed to this type of emissions (Nielsen,
            Corresponding author. Fax: +39 91427584.
            E-mail address: orecchio@unipa.it (S. Orecchio).   1996; Caricchia and Chiavarini Pezza, 1999; Dumbar et al., 2001).
         0013-9351/$ - see front matter & 2008 Elsevier Inc. All rights reserved.
         doi:10.1016/j.envres.2008.02.010
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