[Use of illicit substances in the workplace]. / Consommation de substances illicites en milieu professionnel.

The development of addictive behaviors is a source of worry and concern for workplace and occupational physicians. To estimate the prevalence of behaviors, two types of surveys can be carried out: self-assessment surveys and biological testing in the workplace. For the latter, when a settlement is within the company, the prevalence is often lower compared to those enterprises that have not adapted this policy. Very few investigations have been published in France to date. Data published by the United Nations Office against Drugs and Crime (UNODC) shows a stable consumption of illicit substances in recent years. They reported consumption in the world among the general population (all subjects aged 15 to 64). For France, were described a prevalence estimated in 2005 to 8.6%, 0.6% and 0.2% for cannabis, cocaine and amphetamine derivatives, respectively, and in 2007 to 4.6% for opiates. Some prevalence in the workplace have been reported in Europe in chemical, petrochemical, metallurgical, automotive, in the transport sector and in medical and military fields. However, it appears that few surveys in the workplace have been published in France, this lack may be explained by a desire for anonymity on the subject at the level of company management and doctors work that focus on individual support with the problem of addiction. Screening for illicit substances is necessary because these psychotropic substances affect alertness and pose risks in the workplace, especially such that the association cannabis-alcohol further increases the risk. Knowledge of consumption is, moreover, an important factor in job security. It may be acquired if reliable methods, inexpensive to allow routine screening. Publication of results will reveal the extent of the problem and implement more effective campaigns of information and prevention in the workplace.

Glycol ethers and semen quality: a cross-sectional study among male workers in the Paris Municipality.

OBJECTIVES: Apparent increases in human male reproductive disorders, including low sperm production, may have occurred because of increased chemical exposure. Various glycol ether-based solvents have pronounced adverse effects on sperm production and male fertility in laboratory animals. The authors investigated the effects of past and current exposure to glycol ether-containing products on semen quality and reproductive hormones among men employed by the Paris Municipality. METHODS: Between 2000 and 2001 the authors recruited 109 men who gave semen, blood and urine samples and underwent an andrological examination. Information on lifestyle, occupation, exposure and medical history was obtained by interview. According to their job and chemical products used during the period 1990-2000, men were classified as either occupationally exposed or non-exposed. Current exposure levels to glycol ethers at the time of the study were evaluated by biological monitoring of six urinary metabolites. RESULTS: Previous exposure to glycol ethers was associated with an increased risk for sperm concentration, for rapid progressive motility and for morphologically normal sperm below the World Health Organization semen reference values. No effect of previous glycol ether exposure on hormones levels was observed. By contrast, current glycol ether exposure levels were low and not correlated with either seminal quality or hormone levels. CONCLUSIONS: This study suggests that most glycol ethers currently used do not impact on human semen characteristics. Those that were more prevalent from the 1960s until recently may have long lasting negative effects on human semen quality.

Environmental lead exposure and its relationship to traffic density among Senegalese children: a cross-sectional study.

Leaded-gasoline is probably the primary source of lead (Pb) exposure in Dakar (Senegal). The present cross-sectional study was undertaken to investigate the levels of Pb in Senegalese children and to present helpful data on the relationship between Pb levels and changes in biological markers of heme biosynthesis and oxidative stress. A total of 330 children, living since birth either in rural or urban areas (ie, Khombole (n = 162) and Dakar (n = 168), respectively) were included. During this cross-sectional study, the mean blood (B)-Pb level in all children was 7.32 +/- 5.33 microg/dL, and was influenced by the area of residence and gender. In rural children, 27 subjects (16.7%), 18 boys (19.6%) and nine girls (12.9%), had a B-Pb level > 10 microg Pb/dL, whereas 99 urban children (58.9%), respectively, 66 boys (71.8%) and 33 girls (43.4%), had alarmingly high B-Pb levels. Accordingly, urine delta-aminolevulinic acid levels were higher in children living in the urban area than in the rural areas (P < 0.001), and closely correlated with the B-Pb levels (P < 0.01). Moreover, glutathione peroxidase (GPx) activity, selenium (Se) level, glutathione reductase (GR) activity, and glutathione status were significantly influenced by area of residence and/or by gender. GPx activity and Se level were not only negatively correlated with B-Pb levels, but also positively correlated together (P < 0.01). Taken together, the present results allow us to conclude that urban children have higher B-Pb levels than rural children, and that of these children, boys have higher B-Pb levels than girls, leading thereby to alterations of heme biosynthesis and pro-oxidant/antioxidant balance. We also suggest that exposure to Pb and the Pb-induced adverse effects merits attention and that the development of preventive actions are of increasing importance in Senegal.

Exposure to glycol ethers in a population of French men evaluated by measurement of urinary alkoxycarboxylic acids.

OBJECTIVES: Glycol ethers are solvents that are present in a large number of products used commercially and domestically. During recent years, ethylene glycol ether derivatives, in particular ethylene glycol methyl ether and ethylene glycol ethyl ether, have been progressively replaced by propylene glycol ether derivatives, which are less toxic. The aim of this study was to estimate the level of exposure to glycol ethers in a sample population of French men employed by the Paris Municipality by measuring the amount of alkoxycarboxylic acid metabolites in their urine. METHODS: Urine samples were collected at the end of two different working weeks from 109 men, 54 of whom were judged to be occupationally exposed to glycol ether-containing products. Five alkoxyacetic acids (methoxyacetic, ethoxyacetic, n-propoxyacetic, phenoxyacetic, butoxyacetic acids) from ethylene glycol derivatives, and one alkoxypropionic acid (2-methoxypropionic) from a propylene glycol derivative, were simultaneously analysed by gas chromatography coupled to electron-capture detection. RESULTS: 2-Methoxypropionic was the most frequently found alkoxycarboxylic acid. The concentration of this metabolite reached 5.6 mmol/mol creatinine. The second most common alkoxycarboxylic acid was phenoxyacetic (up to 2.3 mmol/mol creatinine). The concentrations of the other alkoxycarboxylic acids were less than 1 mmol/mol creatinine. Although the concentration of alkoxycarboxylic acids was higher among men occupationally exposed to glycol ether-containing products than among unexposed men, the difference was significant only for butoxyacetic acid. CONCLUSIONS: Our data suggest that the use and exposure levels of glycol ethers have qualitatively and quantitatively changed dramatically over recent years. Particular attention should be paid in the future to alkoxypropionic acids derived from minor isomers of propylene glycol ether derivatives.

Environmental lead exposure and its relationship to traffic density among Senegalese children: a pilot study.

In Senegal, as in many developing countries, traffic density is increasing in urban areas; in Dakar more than 50% of vehicles use gasoline. Yet the extent and real magnitude of the problem has neither been recognized nor assessed in these countries. Systemic data assessment of lead pollution and people's exposure are not well known in Senegal. This study was also designed to determine the impregnation levels of the lead released by the exhaust of cars and the changes of some early biological markers in Senegalese children. Blood lead (BPb) levels showed that all the children enrolled were exposed. However, lead exposure levels (from 34.7 to 145.8 microg/L) were less important for children living in rural areas (60.9+/-18.3 microg/L) than for those living in urban areas (106.7+/-16.9 microg/L). These changes could be correlated to the difference in the automobile traffic between both these regions (P < 0.001). BPb mean levels found in boys were higher than those in girls (P < 0.05). Despite elevated BPb levels, all values for blood zinc protoporphyrin and urine delta-aminolevulinic acid were within physiological ranges. In addition, variations in some biological markers of oxidative stress and renal disorders were seen; however, they must be confirmed by a future epidemiological study.

Urinary homovanillic acid and serum prolactin levels in children with low environmental exposure to lead.

Current evidence suggests that the neurotoxic effects of lead may partially be mediated through interference with the dopaminergic system. The aim of this study was to assess the levels of two peripheral dopaminergic markers--serum prolactin (Pro-S) and urinary homovanillic acid (HVA-U)--in children living around two lead smelters, who are presumed to be exposed to high environmental lead pollution (n = 200), and compare their results with 200 age- and sex-matched controls living in an area unpolluted by heavy metals, giving a total of 400 children (200 boys and 200 girls). The influence of lead exposure on HVA-U and Pro-S was assessed by stepwise multiple regression, testing lead concentrations in blood (Pb-B), age, sex and area of residence as predictors. Though lead levels were significantly higher in boys and in the lead-polluted environment, mean Pb-B values were relatively low, indicating a low uptake of lead in the contaminated environment (39.5 micrograms l-1, range 4.6-165 micrograms l-1, n = 200), and no significant correlation could be found with either Pro-S or HVA-U. However, when the subgroup of 121 children with Pb-B levels above 50 micrograms l-1 were considered, a weak positive correlation was found between Pb-B and HVA-U (r2 = 0.04, p = 0.03), whilst in the even smaller subgroup of 15 children with Pb-B levels above 100 micrograms l-1, Pro-S appeared to be positively correlated with Pb-B, though the numbers of children were too small for the correlation to reach statistical significance (p = 0.095). These weak associations, probably not important in biological terms, indicate that Pro-S and HVA-U are not useful biomarkers at present exposure levels to lead in the environment. Nevertheless, the finding of subtle biochemical alterations in the dopaminergic system at Pb-B levels of around 100 micrograms l-1 supports the recommended setting of the action level at this value.

[Home environment and acute propylene glycol intoxication in a two-year old. An unusual case report]. / Environnement domestique et intoxication aiguë au propylène glycol chez un nourrisson de deux ans. A propos d'une observation inhabituelle.

BACKGROUND: Acute propylene glycol intoxication in a two-year-old toddler underlines the potentially serious toxicity in children of this chemical agent present as a diluent in many drugs and environmental products such as cosmetics, diapers, cleansing towels, despite a common consideration of safety and lack of toxicity. CASE REPORT: A two-years-old boy previously healthy was found in the morning by his parents in his cradle, lethargic, responsive only to sharp pain. On admission, vital signs were: temperature 38.5 degrees C, lethargy, polypnea; propylene glycol intoxication through disposable cleansing towels chewing was ascertained by anamnesis and blood urine analyses which revealed metabolic acidosis and serum propylene glycol peak. CONCLUSION: Environmental acute propylene glycol intoxication must be considered and searched for in front of a metabolic acidosis case of unknown origin in children.

Personal exposure of workers to atmospheric PAHs on gasworks sites--The SOLEX study.

The aim of the SOLEX study was to estimate the personal exposure of workers to atmospheric polycyclic aromatic hydrocarbons (PAHs) on former gasworks sites in the Paris metropolitan area. Devices to sample gas and particulate phases for 9 PAHs were carried during one working day of a study week in November 1997 by 24 workers and in June 1998 by 19 workers with contrasted job profiles involving different opportunities for contact with the soil; among these volunteers, some were active in the process of contaminated soil remediation during the November study period. PAH concentrations were measured by high-performance liquid chromatography. Subjects working on the site under remediation were clearly more exposed (684.1 ng/m3 for total PAHs in November 1997) than workers, without close contact with soil, whose PAH exposure was similar to that measured by fixed monitors in the ambient air in Paris. The contrasts were weaker in June 1998, when soil remediation had nearly been completed. Only subjects involved in activities with close contact with the ground were found with exposures exceeding background levels. Further investigations are needed to improve our understanding of the influence of the pollutants present in the soil.

Environmental exposure to lead in a population of adults living in northern France: lead burden levels and their determinants.

As part of the assessment of a site in northern France polluted by metals from two smelters (in particular, lead, cadmium and mercury), a cross-sectional study was carried out which intended to estimate the levels of the lead burden of the adult population living on the site and the factors associated with these levels. The exposed zone included 10 municipalities in the Nord-Pas de Calais region, located in the vicinity of two non-ferrous metal smelters. The soils in these municipalities contained between 100 and 1700 ppm of lead. The non-polluted zone contained 20 municipalities from the same region, drawn randomly from those in the region of comparable size but free from any industrial lead exposure. The adult study population (301 men and 300 women) was stratified according to age, sex, employment status and exposure level. The inclusion criteria required subjects who were aged between 20 and 50 years and had been living in the exposed zone for at least 8 years; the exclusion criteria were pregnancy, cancer, kidney disease and diabetes. No more than 10% of the subjects participating could work at one of the two smelters. Data collection took place at home; visiting nurses interviewed subjects to complete a questionnaire and also took blood samples. The lead assay was performed by atomic absorption spectrometry. The geometric mean of the blood-lead levels was 74 microg/l, 95% CI = 69-80 among men and 49 microg/l, 95% CI = 46-53 among women. Blood-lead levels exceeding 100 microg/l were found among 30% of men and 12% of women. Several factors were associated with variation of the mean blood-lead level: the blood-lead level was significantly higher among the men for subjects living less than 1 km from the smelters (geometric mean x 1.3, 95% CI = 1.1-1.6), for those who drink alcoholic beverages (x 1.1, 95% CI = 1.0-1.2 for consumption of 30 g/day), those who smoke (x 1.2, 95% CI = 1.0-1.3 for 20 cigarettes/day), and for subjects with occupational exposure; among the women, for subjects living less than 1 km from the smelters (geometric mean x 1.5, 95% CI = 1.2-1.7), for those who drink alcohol (x 1.1, 95% CI = 1.1-1.2 for a daily consumption of 10 g), and for women living in a building constructed before 1948 (x 1.2, 95% CI = 1.0-1.4).

Occupational and environmental risk factors of the myelodysplastic syndromes in the North of France.

Aetiological factors of the myelodysplastic syndromes (MDS) are largely unknown, with the exception of alkylating agents, ionizing radiation and benzene. Some other risk factors have been suggested by the few epidemiological studies reported (solvents, ammonia, exhaust gases, metals, pesticides, alcohol). We performed a case-control study to assess the relationship between occupational or environmental factors and MDS. Two hundred and four patients with newly diagnosed MDS, and 204 sex- and age-matched controls were included. Medical history, demographic data, lifetime exposure and hobbies were obtained. Qualitative and quantitative exposure to chemical and physical hazards were evaluated with the patients and reviewed by a group of experts in occupational exposure. The median age was 70 years and 62% of the patients were men. In univariate analyses, we found relationships between MDS and smoking habits, gardening, occupations such as health professionals, technical and sale representatives, machine operators, agricultural workers, textile workers, qualitative occupational exposures (exposed/non-exposed) to oil, solvents, ammonia, pesticides, fertilizers, cereal dusts, contact with poultry or livestock and infective risk, and lifetime cumulative exposure to solvents, oil, textile dust and infective risk. The main risk factors of MDS determined by multivariate analyses (conditional logistic regression) were, being an agricultural worker [odds ratio (OR) = 3.66; 95% confidence interval (CI) 1.9-7.0], textile operator (OR = 3.66; 95% CI 1.9-7.9), health professional (OR = 10.0; 95% CI 2.1-48.7), commercial and technical sale representative (OR = 4.45; 95% CI 1.4-14.6), machine operator (OR = 2.69; 95% CI 1.2-6.0), living next to an industrial plant (OR = 2.45; 95% CI 1.5-4.1), smoking (OR = 1.74; 95% CI 1.1-2.7) and lifetime cumulative exposure to oil (OR = 1.1; 95% CI 1.0-1.2). Further studies should be performed to assess specific exposures more precisely and it would be of interest to develop a map of haematological malignancies according to industrial background.

Determinants of cadmium burden levels in a population of children living in the vicinity of nonferrous smelters.

This report covers part of the assessment of a site in northern France polluted by industrial metal emissions. Our objectives were to assess the cadmium burden in children aged 8 to 11 years and look for factors that affected it. A cross-sectional population-based study took place in 1996-1997 and included 400 children (200 in the metal-polluted area). The geometric mean of the blood cadmium (CdB) levels of children living on the polluted site was 0.51 microg/L (95% CI=[0.49-0.53]); that of the nonexposed children was 0.47 microg/L (95% CI=[0.45-0.49]) (P<0.01). The geometric mean of the urinary cadmium (CdU) levels of children living on the polluted site was 1.16 microg/g creatinine (95% CI=[1.01-1.34]); that of the nonexposed children was 0.99 microg/g creatinine (95% CI=[0.86-1.14]) (P=0.10). Mean CdB was higher among children within 4 km of a zinc smelter and consuming > or =500 ml of tap water daily (x1.34; 95% CI=[1.14-1.51]) compared with children living more than 4 km away and consuming <500 ml of tap water daily. Independently of this association, consumption of fish and shellfish (> or =once a week vs. or =once daily vs.

Acute respiratory effects of exposure to stainless steel and mild steel welding fumes.

Over the past few years, many studies, including one on our previous work, have examined the chronic effects of fumes from stainless steel (SS) welding on the health of welders. These chronic effects have been related to concentrations of chromium and nickel in SS welding fumes. The present study examined the acute respiratory effects of welding fumes in the workplace by measuring the across-shift changes in a population of 144 SS and mild steel (MS) welders and 223 controls. Manual Metal Arc, Metal Inert Gas, and Tungsten Inert Gas welding processes were studied. Pulmonary function tests were performed at the start (ante, or A) and at the end (post, or P) of the work shift. The study of sensitization to harmful respiratory effects of welding was based on the study of the (P-A)/A ratio (%) of the spirometric variations during the shift. The means of these ratios in the control subjects were used to account for the circadian effect. In SS welders we observed a significant decrease in forced vital capacity (FVC) during the shift. Significant across-shift decrements in forced expiratory volume in 1 second (FEV1) and FVC were related to the SS welding exposure compared with MS welding. Moreover, the across-shift decreases in FEV1, FVC, and peak expiratory flow (PEF) were significantly related to the Manual Metal Arc welding process, compared with Metal Inert Gas techniques (respectively, PEF = -2.7% of baseline values [SD, 11.9] vs 2.0% of baseline values [SD, 7.7] P = 0.04; FVC = -1.5% of baseline values [SD, 4.8] vs 0.2% of baseline values [SD, 4.5] P = 0.05). We also demonstrated the influence of duration of SS welding exposure on the course of lung function during the work shift. After 20 years of SS welding activity, SS welders had more significant across-shift decreases than MS welders with a similar MS exposure duration (respectively, FEV1 = -2.7% of baseline values [SD, 5.9] vs 0.7% of baseline values [SD, 4.2] P = 0.008; PEF = -3.8% of baseline values [SD, 9.6] vs 2.3% of baseline values [SD, 6.5] P = 0.04). We concluded that welding-related lung function responses are seen in SS compared with MS welders and in those with a longer lifetime welding history.

Modification of the proteinase/anti-proteinase balance in the respiratory tract of Sprague-Dawley rats after single intratracheal instillation of benzo[A]pyrene-coated onto Fe(2)O(3) particles.

Available data suggest that repeated concurrent exposure to haematite (Fe(2)O(3)) and benzo[A]pyrene (B[A]P) results in a decreased latency and an increased incidence of lung tumours in rodents compared to exposure to B[A]P alone. Moreover, the reactive oxygen species (ROS) formed by the lung cells themselves and/or by activated inflammatory cells may possibly contribute to the development of pulmonary disorders such as cancer formation. In order to investigate the precise role of iron in the injury induced by B[A]P-coated onto Fe(2)O(3) particles, we tend to address the hypothesis that Fe(2)O(3) and B[A]P, alone or in association, can induce oxidative stress conditions (malondialdehyde) and/or inflammatory reactions (interleukin-6) and thereby disrupt the proteinase/anti-proteinase balance (cathepsins B and L, polynuclear neutrophil (PNN) elastase, alpha-1 proteinase inhibitor (alpha(1)PI) and its inhibitory capacity) in the rat respiratory tract. Thus, Fe(2)O(3) or B[A]P-coated onto Fe(2)O(3) particles produce oxidative stress conditions through not only iron-catalysed oxidative reactions but also inflammatory processes. However, B[A]P initiates only inflammatory responses. These pollutants generate increased levels of proteases and decrease the concentrations of free alpha(1)PI. There is also a clear relationship between the partial inactivation of alpha(1)PI and the occurrence of ROS after exposure to Fe(2)O(3), alone or as a carrier of B[A]P. Hence, the proteinase/anti-proteinase balance might be more disrupted by Fe(2)O(3) or B[A]P-coated onto Fe(2)O(3) particles than by B[A]P alone. These results suggest a mechanism that can explain why B[A]P-coated onto Fe(2)O(3) particles are more injurious than B[A]P alone.

Environmental lead exposure in a population of children in northern France: factors affecting lead burden.

BACKGROUND: This study is part of the assessment of a site in northern France polluted by lead from industrial emissions. Our objectives were to look for the factors that influence lead burden in children aged 8-11 years. METHODS: A cross-sectional population-based study took place in 1996-97 and included 400 children (200 of whom lived on the metal-polluted site). RESULTS: The geometric mean of the blood-lead levels of children living on the polluted site was 39.5 microg/l (95% CI = 36.3-43.1); that of the non-exposed children was 30.6 microg/l (95% CI = 27.8-33.6) (P < 0.0001). Analysis of the variations in the mean blood-lead levels showed associations with: distance from the smelting plants (mean blood-lead level fell by a factor of 1/1.3 (95% CI = 1/1.2-1/1.4) for each km from the smelter over the range of 1-3 km and was constant thereafter) and consumption of tap water (when the water pipes were made of lead, the mean blood-lead level of children who drank tap water was twice as high (95% CI = 1.2-3.4) as that of children who did not). CONCLUSIONS: The children's blood-lead levels were essentially linked to two factors: proximity to the smelters and drinking tap rather than bottled water.

Urinary 1-hydroxypyrene as a biomarker of polycyclic aromatic hydrocarbons exposure of workers on a contaminated site: influence of exposure conditions.

The aim of the study was to determine the exposure levels of workers to polycyclic aromatic hydrocarbons on gasworks sites by the measurement of urinary 1-hydroxypyrene. Start-shift and end-shift urine samples were taken every day during an entire week (Monday to Friday), once in November and a second time in June. Four groups of workers were selected according to their activity. Increased exposure was only found among volunteers involved in the remediation of a site, 0.16 to 2.31 mumol/mol creatinine in non-smokers. The median of the non-smoker referent group was 0.02 mumol/mol creatinine (95% confidence interval, 0.01 to 0.04). Smokers had greater exposure levels than non-smokers in every group. Within and between variability was around 200%. Assessment of the exposure of persons on contaminated soil is possible, with the condition that the exposed subjects come in direct contact with the soil.

Feasibility of assessing dermal exposure to PAHs of workers on gaswork sites--the SOLEX study.

Population exposure to pollutants in soil is an important public health concern. Difficult to measure, it is usually estimated using multimedia models. Modeling data predict that the skin surface is a predominant exposure route in roughly 15% of the US Superfund sites. Nonetheless, no study has confirmed these predictions. The SOLEX study was an opportunity to study the feasibility of estimating the cutaneous polycyclic aromatic hydrocarbons (PAHs: all 16 of the United States Environmental Protection Agency list) load of workers at three former manufactured gas sites, one of those being under remediation. Over two measurement periods (November 1997 and June 1998), 30 and 28 volunteers, respectively, were equipped for a single day work with five pads that collected soil particles and were placed at the neck, shoulder, wrist, groin, and ankle. Pad contamination was observed for six of the nine workers on the site being remediated but not on other sites. The wrist pad was most often affected, followed by the neck pad, these are, the exposed regions of the body. The PAHs most frequently identified were anthracene, fluoranthene, naphthalene, phenanthrene, and pyrene, at concentrations relatively high. In conclusion, this study showed that estimating skin exposure to soil pollutants is feasible. Secondly, it suggested that only subjects in close contact with the soil had a detectable exposure to PAHs. Extension of this approach to other exposure settings is warranted, especially among children playing in polluted public or private gardens, because their games lead to frequent contact with the soil.

Respiratory symptoms and pulmonary function among stainless steel welders.

In the last few years, many studies have been carried out concerning the effects of fumes from stainless steel (SS) welding on the health of welders. The respiratory effects of exposure to SS welding fumes have already been studied, but the results of lung function investigations have not been consistent. However, the main factor of risk for the welders' health seems to be related to the great concentration of chromium and nickel contained in fumes coming from SS welding. The aim of this study was to detect the chronic effects of SS welding exposure on pulmonary symptoms and ventilatory function tests. Respiratory symptoms and lung function tests were studied in 134 SS welders and 252 controls (C). Welders and controls were of similar average age, height, and duration in employment. The smoking habits of the groups were also similar. The medical questionnaire on respiratory symptoms was a version of the Medical Research Council questionnaire, modified by the British Occupational Hygiene Society. The flow-volume curves were performed with a calibrated pneumotachograph spirometer before each subject started working. After adjustment for tobacco habits, the SS welders presented a higher prevalence of bronchial irritative symptoms such as cough (P = 0.01) or sputum production (P = 0.02) than the controls. On the other hand, chronic bronchitis appeared to be significantly linked to tobacco consumption. The pulmonary function analysis underscored no significant difference between stainless steel welders and controls (forced expiratory volume in one second, observed/predicted: SS = 0.99 vs C = 0.98; maximal midexpiratory flow, observed/predicted: SS = 0.90 vs C = 0.92; maximal expiratory flow at 50 % of the forced vital capacity, observed/predicted: SS = 0.95 vs C = 0.95). On the other hand, by the mean of the two-ways analysis, a significant tobacco effect was found, without exposure or interaction of tobacco-exposure effects. There was no influence of the specific welding processes on the spirographic parameters, but a decrease in spirographic values after 25 years of welding activity was evident. The results of multiple regression indicated that age was not a confounding factor.

Peripheral markers (Clara cell protein and alpha-glutathione S-transferase) and lipidoperoxidation (malondialdehyde) assessment in Sprague-Dawley rats instilled with haematite and benzo[a]pyrene.

The literature suggests that the concomitant exposure to polycyclic aromatic hydrocarbons (PAH) and ferric oxide particles could enhance lung cancer incidence in environmental and occupational settings. High levels of tracheobronchial tumours were obtained in hamsters exposed to benzo[a]pyrene (B[a]P) adsorbed onto ferric oxide carrier particles. Therefore, we have assessed the toxic effects of exposure to haematite (Fe2O3) and B[a]P in male Sprague-Dawley rats. Animals were instilled with the chemicals alone (3 mg of Fe2O3 or B[a]P) or in combination (3 mg Fe2O3 + 3 mg B[a]P). Bronchoalveolar lavages (BAL) and biological samples (serum and urine) were collected 48 h after the intoxication. Clara cell protein (CC16) and alpha-glutathione S-transferase (alpha-GST), as peripheral markers of both tracheobronchial epithelial cell integrity and renal dysfunction, were determined in BAL fluid, serum and urine. Malondialdehyde (MDA), a marker of lipid peroxidation, was measured in BAL fluid and serum. We observed a significant increase of CC16 concentrations in BAL fluid after Fe2O3 + B[a]P instillation (p < 0.05) in serum after Fe2O3 and Fe2O3 + B[a]P exposure (p < 0.01) and in urine after B[a]P administration (p < 0.01). Instillation of Fe2O3 + B[a]P produced an increased amount of alpha-GST in BAL fluid (p < 0.01), whereas B[a]P alone caused a significant elevation of alpha-GST in serum and urine (p < 0.01). Moreover, Fe2O3 or Fe2O3 + B[a]P instillation induced a significant increase in MDA levels in BAL fluid (p < 0.01 and p < 0.05). In conclusion, Fe2O3 may have a low pulmonary toxicity. However, B[a]P manifested a rapid and high toxicity in the respiratory tract and kidneys. When B[a]P was adsorbed on haematite particles, both its retention in the respiratory tract and pulmonary toxicity increased.

Development and evaluation of immunochromatographic rapid tests for screening of cannabinoids, cocaine, and opiates in urine.

The test principle and the optimization of the reactive ingredients are described for the one-step dip and-read immunochromatographic FRONTLINE rapid tests for drugs-of-abuse testing in urine samples. In a multicenter evaluation the rapid tests were compared with FPIA and EMIT immunoassays. Discrepant results were further analyzed by gas chromatography-mass spectrometry methods. In the comparison of the cannabinoids rapid tests versus both immunoassays using clinical and forensic urine samples (399 versus FPIA and 755 versus EMIT), sensitivities and specificities were 97% or better for both comparisons. For cocaine, a sensitivity of 100% versus both routine technologies was obtained, whereas the specificity was reduced somewhat to 91% because of some cross-reactivity with metabolites of methadone and of clozapine. Specificity was very high for the cocaine rapid tests (98-100%) when applied to urine samples of persons not in a methadone maintenance program. Sensitivities and specificities for the opiates rapid tests were 99% or better at all sites when compared with the routine methods. In the screening of about 1200 clinical urine samples for cannabinoids, cocaine or opiates misuse only six samples would have stayed undetected by rapid test analyzes. These results show the FRONTLINE assays allow a reliable and immediate screening for drugs of abuse.

Assessment of biological chromium among stainless steel and mild steel welders in relation to welding processes.

Air and biological monitoring were used for assessing external and internal chromium exposure among 116 stainless steel welders (SS welders) using manual metal arc (MMA), metal inert gas (MIG) and tungsten inert gas (TIG) welding processes (MMA: n = 57; MIG: n = 37; TIG: n = 22) and 30 mild steel welders (MS welders) using MMA and MIG welding processes (MMA: n = 14; MIG: n = 16). The levels of atmospheric total chromium were evaluated after personal air monitoring. The mean values for the different groups of SS welders were 201 micrograms/m3 (MMA) and 185 micrograms/m3 (MIG), 52 micrograms/m3 (TIG) and for MS welders 8.1 micrograms/m3 (MMA) and 7.3 micrograms/m3 (MIG). The curve of cumulative frequency distribution from biological monitoring among SS welders showed chromium geometric mean concentrations in whole blood of 3.6 micrograms/l (95th percentile = 19.9), in plasma of 3.3 micrograms/l (95th percentile = 21.0) and in urine samples of 6.2 micrograms/l (95th percentile = 58.0). Among MS welders, mean values in whole blood and plasma were rather more scattered (1.8 micrograms/l, 95th percentile = 9.3 and 1.3 micrograms/l, 95th percentile = 8.4, respectively) and in urine the value was 2.4 micrograms/l (95th percentile = 13.3). The analysis of variance of chromium concentrations in plasma previously showed a metal effect (F = 29.7, P < 0.001), a process effect (F = 22.2, P < 0.0001) but no metal-process interaction (F = 1.3, P = 0.25). Concerning urinary chromium concentration, the analysis of variance also showed a metal effect (F = 30, P < 0.0001), a process effect (F = 72, P < 0.0001) as well as a metal-process interaction (F = 13.2, P = 0.0004). Throughout the study we noted any significant differences between smokers and non-smokers among welders. Taking in account the relationships between chromium concentrations in whole, plasma or urine and the different welding process. MMA-SS is definitely different from other processes because the biological values are clearly higher. These higher levels are due to the very significant concentrations of total soluble chromium, mainly hexavalent chromium, in welding fumes.