Maria Cristina Aprea

Environmental and biological monitoring in the estimation of absorbed doses of pesticides.

Exposure to pesticides affects most of the population, not only persons occupationally exposed. In a context of high variability of exposure, biological monitoring is important because of the various routes by which exposure can occur and because it assesses both occupational and non-occupational exposure. The main aim of this paper was to critically compare estimates of absorbed dose measured by environmental and biological monitoring in situations in which they could both be applied. The combination of exposure measurements and biological monitoring was found to provide extremely important information on the behaviour of employees, and on the proper use and effectiveness of personal protection equipment.

Assessment of exposure to pesticides during mixing/loading and spraying of tomatoes in the open field

ABSTRACT Some evidence of exposure-response of metolachlor and pendimethalin for lung cancer and an association of metribuzin with risk of glioma have been reported. The primary objectives in this study were to evaluate exposure and occupational risk during mixing/loading of pesticides and during their application to tomatoes cultivated in open fields. Sixteen farmers were sampled. Respiratory exposure was estimated by personal air sampling using fiberglass filters in a IOM device. Dermal exposure was assessed using skin pads and hand washing. Absorbed doses were estimated assuming 100% lung retention, and 50% or 10% skin absorption for metribuzin, and pendimethalin and metolachlor, respectively. The three pesticides were quantified by gas chromatography tandem mass spectrometry in all matrices. Metolachlor was used as a tracer of contamination of clothes and tractors unrelated to the exposure monitored. Respiratory exposure to metribuzin, used in granular form, was on average more than one order of magnitude higher than exposure to pendimethalin, used in the form of microencapsulated liquid. The actual doses were 0.067–8.08 µg/kg bw, 0.420–12.6 µg/kg bw, and 0.003–0.877 µg/kg bw for pendimethalin, metribuzin, and metolachlor, respectively. Dermal exposure was about 88% of the actual dose for metribuzin and more than 95%, for pendimethalin and metolachlor. For risk assessment, the total absorbed doses (sum of respiratory and skin absorbed doses) were compared with the AOEL for each compound. The actual and absorbed doses of the three pesticides were always lower than the acceptable operator exposure level (AOEL), which are reported to be 234 µg/kg bw, 20 µg/kg bw, and 150 µg/kg bw for pendimethalin, metribuzin, and metolachlor, respectively. In any case, personal protective equipment and spraying devices should be chosen with care to minimize exposure.

Methodology to define biological reference values in the environmental and occupational fields: the contribution of the Italian Society for Reference Values (SIVR)

BACKGROUND Biological reference values (RVs) explore the relationships between humans and their environment and habits. RVs are fundamental in the environmental field for assessing illnesses possibly associated with environmental pollution, and also in the occupational field, especially in the absence of established biological or environmental limits. OBJECTIVES The Italian Society for Reference Values (SIVR) determined to test criteria and procedures for the definition of RVs to be used in the environmental and occupational fields. METHODS The paper describes the SIVR methodology for defining RVs of xenobiotics and their metabolites. Aspects regarding the choice of population sample, the quality of analytical data, statistical analysis and control of variability factors are considered. The simultaneous interlaboratory circuits involved can be expected to increasingly improve the quality of the analytical data. RESULTS Examples of RVs produced by SIVR are presented. In particular, levels of chromium, mercury, ethylenethiourea, 3,5,6-trichloro-2-pyridinol, 2,5-hexanedione, 1-hydroxypyrene and t,t-muconic acid measured in urine and expressed in micrograms/g creatinine (μg/g creat) or micrograms/L (μg/L) are reported. CONCLUSIONS With the proposed procedure, SIVR intends to make its activities known to the scientific community in order to increase the number of laboratories involved in the definition of RVs for the Italian population. More research is needed to obtain further RVs in different biological matrices, such as hair, nails and exhaled breath. It is also necessary to update and improve the present reference values and broaden the portfolio of chemicals for which RVs are available. In the near future, SIVR intends to expand its scientific activity by using a multivariate approach for xenobiotics that may have a common origin, and to define RVs separately for children who may be exposed more than adults and be more vulnerable.

Monitoring and Control of Exposure to Buprofezin in Greenhouses

The aim of this study was to assess dermal and respiratory exposure of workers to Buprofezin during spraying and during stapling of previously treated ornamental plants in greenhouses. Eight workers were monitored. A combination of hand washing and pads placed on the skin was used to evaluate actual skin contamination. The efficacy of protective clothing was evaluated placing pads on top of outer clothing. Respiratory exposure was evaluated by personal air sampling. Respiratory dose was calculated on the basis of a lung ventilation of 15 l/min for females and 20 l/min for males. Absorbed doses were calculated assuming a skin penetration of 40% and a respiratory retention of 100%. Dislodgeable foliar residues (DFRs) were evaluated during re-entry. Buprofezin was determined by gas chromatography with selective mass detection in all matrices. Respiratory dose was 1.5-12.8% and 3.6-15.4% of the total real dose during spraying and stapling, respectively. The estimated absorbed doses, 0.05-0.57 μg/kg body weight and 0.19-1.54 μg/kg body weight during spraying and stapling, respectively, were less than the acceptable operator exposure level of 40 μg/kg body weight. During stapling, a mean dermal transfer factor of 1.13 cm2/h was estimated. During spraying, the efficacy of protective clothing depends on the spraying device used. During stapling, daily replacement of cotton gloves appears to reduce actual exposure. Since proper use of equipment and protective clothing is essential, training of workers is of fundamental importance.

Urinary levels of metal elements in the non-smoking general population in Italy: SIVR study 2012-2015

The purpose of this study of the Italian Society of Reference Values (SIVR) was to provide the reference values for metals in the urine of the Italian general population. Thirteen sampling centres situated in the north, centre and south of Italy took part in this project. Each sampling centre selected 20 adult subjects. The sample was made up of 120 male and 140 female non-smokers or smokers who had abandoned the habit at least 5 years previously, aged between 18 and 60 years. Urine samples were obtained from the same subjects in June and again in November of the same year. During collection of these two samples, we administered an ad hoc questionnaire designed to assess factors that might influence exposure and the results of the study such as personal characteristics, occupational or extra-occupational activities, dietary habits, the presence of dental fillings containing amalgam, the frequency and mode of exposure to passive smoking and exhaust gases of motor vehicles (traffic). Therefore, the urinary levels of thirteen trace elements (Be, Cd, Co, Cr, Cu, In, Mn, Ni, Pb, Pt, Sb, Tl and V) were determined by Inductively Coupled Plasma Mass Spectrometry. The concentrations obtained (95th percentile) are in μg/L: 0.034, 0.900, 2.24, 0.600, 24.0, 0.013, 1.53, 4.44, 2.64, 0.022, 0.095, 0.759 and 0.855 for Be, Cd, Co, Cr, Cu, In, Mn, Ni, Pb, Pt, Sb, Tl and V, respectively. Further studies with a larger number of subjects are needed in order to continue the biomonitoring of the Italian general population and to monitor the modified levels over time.