Franco Merli

The temporal variability of the profile of carcinogenic polycyclic aromatic hydrocarbons in urban air: a study in a medium traffic area in Rome, 1993–1998

Abstract The constancy, both temporal and spatial, of the profile of polycyclic aromatic hydrocarbons (PAHs) relative to benzo[a]pyrene (BaP) is a prerequisite to using the BaP-indicator approach in the carcinogenic risk assessment for PAHs. The principal aim of this study was to provide a contribution to validate this approach, by studying the variability of the profile at a typical urban site through a multi-year data set and by comparing the profiles available for different cities. Seven carcinogenic PAHs (benz[a]anthracene, benzo[b+j+k]fluoranthenes, BaP, indeno[1,2,3-cd]pyrene, dibenz[a,h]anthracene) were determined in PM10 24-h samples collected every third day at a road site; moreover, benzo[e]pyrene was determined as a reference PAH due to its stability. The profile was found stable from year to year. Besides, it was similar to those recently found in other European cities (observed differences within a factor of four) and to those elaborated from earlier (1970s–1980s) investigations. The substantial similarity of profiles, both temporal (on an annual basis) and spatial, supports the validity of the BaP-indicator approach. Large PAH-to-PAH differences were, however, found in the seasonal pattern of profile: they were explained by the different atmospheric degradability of PAHs, whose effect is enhanced under the meteoclimatic conditions typical of the European Mediterranean countries. PAH annual means showed a slight declining trend since 1994. In the last sampling year, mean concentration of BaP was 1.2 ng m−3. Within-year differences among monthly averaged PAH concentrations were observed, as large as up to 44-fold for BaP, underlining the need for whole-year monitoring.

Polycyclic aromatic hydrocarbons in olive oils on the Italian market

The six olive oils and seven virgin olive oils which are most consumed in Italy were analysed for 28 polycyclic aromatic hydrocarbons (PAHs). The aim was to evaluate whether a carcinogenic hazard for the general population can derive from the dietary intake of this food, which is consumed particularly highly in the Mediterranean area. The analytical method involved extraction by liquid-liquid partition, filtration on silica gel, clean-up by thin-layer chromatography on silica gel, and analysis by high-resolution gas chromatography with a flame ionization detector. The 3- and 4-ring PAHs which are most abundant in the environment were found in all samples, at individual levels up to ca. 40 micrograms/kg (for phenanthrene); no important difference was observed between olive oils and virgin olive oils. PAHs which are most suspected of being carcinogenic for humans were not detected (limit of detection, ca. 3 micrograms/kg). The average yearly intake of the detected PAHs through this food was estimated at ca. 0.56 mg per capita.

Artificial-turf playing fields: contents of metals, PAHs, PCBs, PCDDs and PCDFs, inhalation exposure to PAHs and related preliminary risk assessment.

The artificial-turf granulates made from recycled rubber waste are of health concern due the possible exposure of users to dangerous substances present in the rubber, and especially to PAHs. In this work, we determined the contents of PAHs, metals, non-dioxin-like PCBs (NDL-PCBs), PCDDs and PCDFs in granulates, and PAH concentrations in air during the use of the field. The purposes were to identify some potential chemical risks and to roughly assess the risk associated with inhalation exposure to PAHs. Rubber granulates were collected from 13 Italian fields and analysed for 25 metals and nine PAHs. One further granulate was analysed for NDL-PCBs, PCDDs, PCDFs and 13 PAHs. Air samples were collected on filter at two fields, using respectively a high volume static sampler close to the athletes and personal samplers worn by the athletes, and at background locations outside the fields. In the absence of specific quality standards, we evaluated the measured contents with respect to the Italian standards for soils to be reclaimed as green areas. Zn concentrations (1 to 19 g/kg) and BaP concentrations (0.02 to 11 mg/kg) in granulates largely exceeded the pertinent standards, up to two orders of magnitude. No association between the origin of the recycled rubber and the contents of PAHs and metals was observed. The sums of NDL-PCBs and WHO-TE PCDDs+PCDFs were, respectively, 0.18 and 0.67×10(-5) mg/kg. The increased BaP concentrations in air, due to the use of the field, varied approximately from <0.01 to 0.4 ng/m(3), the latter referring to worst-case conditions as to the release of particle-bound PAHs. Based on the 0.4 ng/m(3) concentration, an excess lifetime cancer risk of 1×10(-6) was calculated for an intense 30-year activity.

The influence of soil particle adsorption on 2,3,7,8-tetrachlorodibenzo-p-dioxin biological uptake in the rabbit.

A comparative study on the biological uptake in the rabbit of 2,3,7,8-tetrachloridibenzo-p-dioxin (TCDD) in different formulations, including accident-contaminated Seveso soil, was attempted. On the whole, these results indicated that soil-borne TCDD had a bioavailability lower than that of free (solvent-borne) TCDD.

Analytical procedures to detect 2,3,7,8-TCDD at Seveso after the industrial accident of July 10, 1976

The analytical procedures used at Seveso (Milan, Italy) for the determination of 2,3,7,8-TCDD, and some isomers, in biological and environmental samples are reviewed in this paper. During the emergency period, up until the first 10 days of August, the extracts, mostly from soil or vegetation samples, were evaporated to dryness and then mixed with less than or equal to 10-ml solvent. Of these solutions, aliquots up to 10 microliter were injected into a low-resolution gas chromatograph (GC) combined with a low-resolution mass spectrometer (MS). Analytical sensitivity for vegetation and soil was less than 10 ppb and approximately 100 ppt, respectively--sufficient for the early mapping of the most heavily contaminated territory. After the emergency period, the greatest improvement in environmental sample analysis was the introduction of cleanup procedure which greatly reduced the presence of unwanted material in samples. Cleanup was followed by the complete removal of the solvent. Dry samples could be taken up with rather small volumes (greater than or equal to 0.1 ml) of solvent, of which an aliquot was used for GC-MS analysis. The instrumental setup was kept as above. For animal samples, extraction entailed preliminary alkaline digestion followed by a number of cleanup steps. The final dry sample was taken to desired volume by adding solvent (greater than or equal to 0.1 ml), of which a few microliters were injected in GC-MS apparatuses. Detection thresholds improved markedly and were less than 10 ppt for agricultural soil and sediment, less than or equal to 0.05 ppt for water, in the range of 60 to 200 ppt for air dust, less than 10 ng/m2 and 10 ppt for wipe and scrape tests, respectively, less than 50 ppt for vegetation, and 250 ppt for biological substrata. Major later improvements in TCDD assay were the use of high-resolution gas chromatography (hrGC-MS), in some cases combined with high-resolution mass spectrometry (hrGC-hrMS). This provided greater specificity, sometimes accompanied by a very marked increase in detection sensitivity.

Dibenzopyrenes, other PAHs with molecular weight 302, and selected carcinogenic PAHs seldom determined: identification and one-year quantification in urban air

The unambiguous identification in environmental samples of the potent carcinogen dibenzo[a,l]pyrene (DBalP) and the other DBPs (DBaeP, DBaiP, DBahP), whose evidence of carcinogenicity was recently re-evaluated by the International Agency for Research on Cancer (IARC), is an analytical challenge. This is attributed to their low concentrations in the environment and to the co-presence of several 302 MW isomers. In this study the four DBPs were identified in air, together with further four isomers with MW 302, based on an overall evaluation of five acceptance criteria. Their annual mean concentrations were quantified, for the first time to our knowledge. Thirteen other isomers were tentatively identified by comparison with previously published gas chromatographic profiles. The determinations were performed on PM10 samples collected every sixth day at a site in Rome, solvent extracted and analysed using GC/LRMS. The primary objective was to determine the mean DBP concentrations the population may be exposed to, and their consequent carcinogenic risks relative to benzo[a]pyrene (BaP) taken as a reference polycyclic aromatic hydrocarbon (PAH). The mean concentrations of DBalP, DBaeP, DBaiP and DBahP were, respectively, 0.014, 0.07, 0.02 and 0.01 ng m−3 (BaP: 0.65 ng m−3). Based on the available toxicity equivalence factors, DBalP contributed the carcinogenic risk of the PAH mixture by a factor of 2 relative to the risk attributable to BaP. DBaeP, DBahP and DBaiP contributed by, respectively, 11%, 1% and 0.3% of BaP. The instrumental conditions used to determine the 302 MW isomers allowed to unambiguously identify and to quantify other PAHs, ‘possibly carcinogenic’ to humans according to IARC, whose atmospheric concentrations reported in literature are scarce or missing: benzo[c]phenanthrene, 5-methylchrysene and benzo[j]fluoranthene (the latter being baseline resolved from isomers b and k). Finally, for completeness of information on PAHs recently upgraded by IARC to ‘possibly carcinogenic’, the concentrations of cyclopenta[cd]pyrene are reported.

ATMOSPHERIC BULK DEPOSITION OF CARCINOGENIC PAHS IN A RURAL AREA IN SOUTHERN ITALY

The bulk depositions of seven carcinogenic PAHs were investigated by collecting two monthly samples at seven sites. Deposition rates of individual PAHs ranged 2–89 ng/m2/d (BaP, 2–7 ng/m2/d), in agreement with the few available rates previously measured at background European sites. On six days, air samples were also collected at three sites and resulted in mean particle-bound BaP ranging 0.01–0.04 ng/m3. The ratios between the concentrations of each PAH and BaP in the deposition samples were significantly higher than those in the air samples. To investigate if an on-sampler BaP degradation during a 1-month sampling period could generate a measurable artefact, a test was carried out by two co-located samplers collecting, respectively, one continuous 5-week sample and five weekly samples. No difference in PAH profiles was found among the samples collected by the two samplers. The occurrence of PAH profiles different from those commonly found in air may affect the validity of the BaP-marker approach in risk assessment for deposition samples.