New reference value and the background exposure for the PAH metabolites 1-hydroxypyrene and 1- and 2-naphthol in urine of the general population in Germany: basis for validation of human biomonitoring data in environmental medicine

Reference values for environmental pollutants in the German population are established continuously by the Human Biomonitoring Commission of the German Federal Environment Agency. The reference value for 1-hydroxypyrene in urine was derived from the representative adult population data collection of the 1998 German Environmental Survey (GerES III) and the representative data collection for children of the German Environmental Survey on Children, 2003/06 (GerES IV). For the non-smoking general population (aged 3-69 years) the commission derived a reference value of 0.5 microg/l (corresponding to 0.3 microg/g creatinine) for 1-hydroxypyrene in urine. For 1- and 2-naphthol levels in urine the amount of data is small and not representative of the German population. Therefore, the commission recommends the following upper margins of background exposures for adult non-smokers: 1-naphthol less than 30 microg/l, 2-naphthol less than 20 microg/l.     

Urinary biomarkers of occupational jet fuel exposure among Air Force personnel

There is a potential for widespread occupational exposure to jet fuel among military and civilian personnel. Urinary metabolites of naphthalene have been suggested for use as short-term biomarkers of exposure to jet fuel (jet propulsion fuel 8 (JP8)). In this study, urinary biomarkers of JP8 were evaluated among US Air Force personnel. Personnel (n=24) were divided a priori into high, moderate, and low exposure groups. Pre- and post-shift urine samples were collected from each worker over three workdays and analyzed for metabolites of naphthalene (1- and 2-naphthol). Questionnaires and breathing-zone naphthalene samples were collected from each worker during the same workdays. Linear mixed-effects models were used to evaluate the exposure data. Post-shift levels of 1- and 2-naphthol varied significantly by a priori exposure group (levels in high group>moderate group>low group), and breathing-zone naphthalene was a significant predictor of post-shift levels of 1- and 2-naphthol, indicating that for every unit increase in breathing-zone naphthalene, there was an increase in naphthol levels. These results indicate that post-shift levels of urinary 1- and 2-naphthol reflect JP8 exposure during the work-shift and may be useful surrogates of JP8 exposure. Among the high exposed workers, significant job-related predictors of post-shift levels of 1- and 2-naphthol included entering the fuel tank, repairing leaks, direct skin contact with JP8, and not wearing gloves during the work-shift. The job-related predictors of 1- and 2-naphthol emphasize the importance of reducing inhalation and dermal exposure through the use of personal protective equipment while working in an environment with JP8.     

Blood and urine levels of Pb, Cd and Hg in the general population of the Czech Republic and proposed reference values

The Human Biological Monitoring (HBM) project was launched in the Czech Republic in 1994 as a part of the nation-wide Environmental Health Monitoring System to assess the exposure of the Czech general population to a broad spectrum of environmental contaminants. Over the years 2001-2003, the concentrations of lead (Pb), cadmium (Cd), and mercury (Hg) were determined in whole blood of 1188 adults (blood donors) and 333 children and in urine of 657 adults and 619 children. In adults, the median blood lead (B-Pb) level was 33microg/l. Men had higher B-Pb levels than women (medians 37microg/l vs. 25microg/l). Significantly higher B-Pb levels were observed in smokers compared to non-smokers (36microg/l vs. 31microg/l). In children, no sex-dependent differences were observed (median 31microg/l). In total, the median blood Cd level (B-Cd) in adults was 0.5microg/l. Smokers showed a median B-Cd level about 3 times as high as non-smokers (1.3microg/l vs. 0.40microg/l). Neither sex- nor age-related differences were observed in B-Cd levels. In 65% of children, B-Cd levels were below the limit of detection (LOD). The overall median urinary cadmium level (U-Cd) in adults was 0.31microg/g creatinine. Significantly higher U-Cd levels were found in women (median 0.39microg/g creatinine) compared to men (0.29microg/g creatinine). No significant differences were found between smokers and non-smokers. In more than 50% of children, the U-Cd level was below the LOD (=0.2microg/l). The median blood mercury (B-Hg) level in adults was 0.89microg/l. Significant differences were found between smokers (0.80microg/l) and non-smokers (0.92microg/l), and between men and women (0.86microg/l vs. 0.94microg/l). The median B-Hg level in children was 0.42microg/l and no sex-related differences were observed. The median urinary mercury (U-Hg) levels were 0.63microg/g creatinine in adults and 0.37microg/g creatinine in children. Significantly higher U-Hg levels were obtained in women and non-smokers compared to men and smokers, respectively. The B-Pb, B-Hg, U-Cd, and U-Hg levels significantly correlated with age. The following reference values were recommended for the period 2001-2003: 80, 65 and 55microg/l for B-Pb and 3.1, 4.0 and 1.5microg/l for B-Hg in men, women and children, respectively; 1.1microg/l and 1.2microg/g creatinine for B-Cd and U-Cd, respectively, in adult non-smokers; 5.4 and 12.0microg/g creatinine for U-Hg in men and women, respectively, and 3.7 and 5.5microg/g creatinine for U-Hg in boys and girls, respectively. The previous reference values for B-Pb and B-Cd needed revision and were reduced.     

Internal exposure of nursery-school children and their parents and teachers to di(2-ethylhexyl)phthalate (DEHP)

Di(2-ethylhexyl)phthalate (DEHP) is the main plasticizer for polyvinyl chloride (PVC) products. It has become widely spread in our environment and among people. DEHP is suspected to be responsible for endocrine-disruptor-like effects in mankind. Children are probably most susceptible to these endocrine effects. In this study we determined the internal exposure of nursery school children (aged 2-6 years) to DEHP and compared it to their parents' and teachers' exposure. The DEHP-metabolites mono(2-ethyl-5-hydroxyhexyl)phthalate (5OH-MEHP), mono(2-ethyl-5-oxo-hexyl)phthalate (5oxo-MEHP) and mono(2-ethylhexyl)phthalate (MEHP) were determined in first morning urine. The sum of the three DEHP metabolites in children's and in adults' urine was 90.0 and 59.1 micrograms/l respectively (median values; p = 0.074). Concentrations of the secondary metabolites 5OH-MEHP (median: 49.6 vs. 32.1 micrograms/l; p = 0.038) and 5oxo-MEHP (median: 33.8 vs. 19.6 micrograms/l; p = 0.015) were significantly higher in children than in adults. MEHP concentrations were low both in adults and children (median: 6.6 micrograms/l vs. 9.0 micrograms/l). Creatinine adjusted values should more accurately reflect the dose taken up with respect to body weight when comparing children with adults. Total creatinine adjusted DEHP metabolites in urine were significantly higher in children than in adults (median values: 98.8 vs. 50.9 micrograms/g creatinine; p < 0.0001). This also applied to the concentrations of both secondary metabolites 5OH-MEHP (55.8 vs. 28.1 micrograms/g creatinine; p < 0.0001) and 5oxo-MEHP (38.3 vs. 17.2 micrograms/g creatinine; p < 0.0001). Creatinine corrected concentrations for the monoester MEHP in children and adults were very similar (8.7 vs. 8.6 micrograms/g creatinine; p = 0.908). Based on the sum of the three determined metabolites we estimated the DEHP dose (in microgram/kg body-weight) taken up by children to be about twice as high as the dose taken up by adults. Routes of the ubiquitous exposure to DEHP remain indistinct. In children's urine the mean relative ratios of MEHP to 5OH-MEHP to 5oxo-MEHP were 1 to 7.1 to 4.9, in adults they were 1 to 3.4 to 2.1. This might indicate an enhanced oxidative metabolism in children. To date no information on the biological activity and toxicity of oxidative metabolites of DEHP is available. Since these are the major metabolites of DEHP toxicological data on these metabolites is urgently needed.     

Perchlorate exposure of the US Population, 2001-2002

Perchlorate is commonly found in the environment and can impair thyroid function at pharmacological doses. As a result of the potential for widespread human exposure to this biologically active chemical, we assessed perchlorate exposure in a nationally representative population of 2,820 US residents, ages 6 years and older, during 2001 and 2002 as part of the National Health and Nutrition Examination Survey (NHANES). We found detectable levels of perchlorate (>0.05 microg/l) in all 2,820 urine samples tested, indicating widespread human exposure to perchlorate. Urinary perchlorate levels were distributed in a log normal fashion with a median of 3.6 microg/l (3.38 microg/g creatinine) and a 95th percentile of 14 microg/l (12.7 microg/g creatinine). When geometric means of urinary perchlorate levels were adjusted for age, fasting, sex and race-ethnicity, we found significantly higher levels of urinary perchlorate in children compared with adolescents and adults. We estimated total daily perchlorate dose for each adult (ages 20 years and older), based on urinary perchlorate, urinary creatinine concentration and physiological parameters predictive of creatinine excretion rate. The 95th percentile of the distribution of estimated daily perchlorate doses in the adult population was 0.234 microg/kg-day [CI 0.202-0.268 microg/kg-day] and is below the EPA reference dose (0.7 microg/kg-day), a dose estimated to be without appreciable risk of adverse effects during a lifetime of exposure. These data provide the first population-based assessment of the magnitude and prevalence of perchlorate exposure in the US.     

Assessing transferable residues from intermittent exposure to flea control collars containing the organophosphate insecticide chlorpyrifos

Children can be exposed to pesticides from numerous residential sources such as carpet, house dust, toys and clothing from treated homes, and flea control remedies on pets. In the present studies, 48 pet dogs (24 in each of two studies) of different breeds and weights were treated with over-the-counter flea collars containing chlorpyrifos (CP), an organophosphorus insecticide. Transferable insecticide residues were quantified on cotton gloves used to rub the dogs for 5 min and on cotton tee shirts worn by a child (Study 2 only). First morning urine samples were also obtained from adults and children in both studies for metabolite (3,5,6-trichloro-2-pyridinol) quantification. Blood samples were obtained from treated dogs in Study 1 and plasma cholinesterase (ChE) activity was monitored. Transferable residues on gloves for all compounds were highest near the neck of the dogs and were lowest in areas most distant from the neck. Rubbing samples (over the collar) at two weeks post-collar application contained 447+/-57 microg CP/glove while samples from the fur of the back contained 8+/-2 microg CP/glove. In Study 2, cotton tee shirts worn by children at 15 days post-collar application for 4 h showed CP levels of 134+/-66 ng/g shirt. There were significant differences between adults and children in the levels of urinary metabolites with children generally having higher urinary levels of metabolites than adults (grand mean+/-SE; 11.6+/-1.1 and 7.9+/-0.74 ng/mg creatinine for children and adults, respectively, compared to 9.4+/-0.8 and 6.9+/-0.5 ng/mg creatinine before collar placement). Therefore, there was little evidence that the use of this flea collar contributed to enhanced CP exposure of either children or adults.     

Cadmium in urine of children and adults from industrial areas

Various human activities result in the release of significant quantity of cadmium to the environment. The study population included adults (230) and children (100) residing near the tobacco plant and a control group, unexposed to elevated cadmium concentrations, living in unpolluted area in the same city. Biomonitoring methods were used to assess the effects of contaminated air on the health of the public (urine samples). Ambient air samples were collected near the cadmium-related plant and in unpolluted area during the last ten years. Values of cadmium concentrations in urine found in polluted area were in range of 0.05-0.42 microg/g creatinine for children and 0.15-1.96 microg/g creatinine for adults. The results indicated statistical significant age-dependent differences in urine cadmium concentration between polluted and unpolluted area for adults. Boys and men had significantly higher urine cadmium levels than girls and women, but in children there were no significant gender-dependent differences in cadmium excretion found out. In conclusion, the results from the present study indicate that cadmium urine concentration in polluted area are very high, particularly in children.     

Scalp hair and urine mercury content of children in the Northeast United States: the New England Children's Amalgam Trial

Children may be at particular risk from toxic effects of mercury (Hg). Previous studies of hair (organic) and urine (inorganic) Hg levels in US children were unable to assess Hg levels while accounting for exposure to amalgam dental restorations. This analysis describes, over a 5-year period, levels and correlates/predictors of scalp hair (H-Hg) and urinary (U-Hg) mercury in 534 New England Children's Amalgam Trial (NECAT) participants, aged 6-10 years and without exposure to dental amalgam at baseline. RESULTS: Mean H-Hg levels were between 0.3 and 0.4 microg/g over 5 years. 17-29% of children had H-Hg levels > or = 0.5 microg/g, and 5.0 to 8.5% of children had levels > or = 1 microg/g, in any given study year. In adjusted models, fish consumption frequency was the most robust predictor of high H-Hg. U-Hg mean levels were between 0.7 and 0.9 microg/g creatinine over two years. The percentage of those with U-Hg > or 2.3 microg/g creatinine ranged from 4% to 6%. Number of amalgam restorations had a significant dose-response relationship with U-Hg level. Daily gum chewing in the presence of amalgam was associated with high U-Hg.     

Lead and cadmium exposure from contaminated soil among residents of a farm area near an industrial site

In this study, the authors determined the degree of lead and cadmium exposure in a population that resided in an area with contaminated soil. The extent of exposure from soil pollution was also assessed. Lead and cadmium concentrations in blood of children and adults who resided in the contaminated area were measured, and cadmium concentration in urine of adults was also determined. An adult control group was recruited from a nonpolluted area. The mean blood lead level in adults who resided in the polluted area was 9.8 microg/dl, compared with a mean level of 6.8 microg/dl in controls (p = .004). Urinary cadmium levels were well below the level associated with onset of symptoms, but the differences between levels in residents of the contaminated area (0.54 microg/gm creatinine) and levels in the controls (0.37 microg/gm creatinine) indicated that life-long cadmium exposure had been higher among the residents of the contaminated area (p = .086). The mean blood lead level and mean blood cadmium level in children were 5.2 microg/dl (maximum = 7.90 microg/dl) and 0.10 microg/l, respectively. Lead in soil accounted in large part for the differences in blood lead levels in children; however, blood cadmium levels were not associated with soil cadmium levels, but, rather, with consumption of home-grown vegetables.     

Effects of the exposure to polycyclic aromatic hydrocarbons or toluene on thiobarbituric acid reactive substance level in elementary school children and the elderly in a rural area]

OBJECTIVES: Polycyclic aromatic hydrocarbons (PAH) and toluene have been reported to induce reactive oxygen species and oxidative stress. This study was performed to investigate the effects of low level exposure to PAHs or toluene on the lipid peroxidation level in elementary school children and the elderly in a rural area. METHODS: Forty seven elementary school children and 40 elderly people who were living in a rural area and not occupationally exposed to PAH or toluene were the subjects of this study. Information about active or passive smoking and diet was obtained using a self-administered questionnaire. The urinary 1-hydroxypyrene (1-OHP), 2-naphthol, hippuric acid and thiobarbituric acid reactive substance (TBARS) concentrations were measured, and these values were corrected with the urinary creatinine concentration. RESULTS: In school children, the geometric means of the urinary 1-OHP, 2-naphthol, hippuric acid and TBARS levels were 0.02 micromol/mol creatinine, 0.47 micromol/mol creatinine, 0.14 g/g creatinine and 0.95 micromol/g creatinine, respectively. Those values for the elderly were 0.07 micromol/mol creatinine, 1.87 micromol/mol creatinine, 0.11 g/g creatinine and 1.18 micro mol/g creatinine, respectively. The mean levels of urinary 1-OHP, 2-naphthol and TBARS were significantly higher in the elderly subjects than in the children. The urinary TBARS level was not correlated with the urinary 1-OHP, 2-naphthol and hippuric acid, but they were correlated with the age of the subjects. CONCLUSIONS: These results suggest that low level inhalation exposure to PAH or toluene does not markedly increase lipid peroxidation, and age is a significant determinant of lipid peroxidation.     

Mercury concentrations in urine,scalp hair,and saliva in children from Germany

Mercury levels measured in urine, hair, and saliva of 245 German children (8-10 years old) are reported. Mercury concentrations in urine ranged between <0.1 and 5.3 microg/l [geometric mean (GM) 0.26 microg/l or 0.25 microg/g creatinine; median for both, 0.22 in microg/l and microg/g, respectively]. Using multiple linear regression analysis, two predictors have been found accounting for 25.3% of the variance of mercury levels in urine: the number of teeth with amalgam fillings (23.2%) and the number of defective amalgam fillings (2.1%). The mercury content in hair ranged from <0.06 to 1.7 microg/g (GM 0.18 microg/g; median 0.18 microg/g). The frequency of fish consumption, the smoking habits of the parents, and the age of the children accounted for 20.4% of the variance of mercury levels in hair. The correlation between the hair mercury content and urine mercury concentration was low (r=0.297). Mercury levels in saliva ranged between <0.32 and 4.5 microg/l (median 0.16 microg/l). The mercury concentration in saliva was below the limit of quantification of 0.32 microg/l in more than 70% of the samples. Mercury analysis in urine is suitable to estimate mercury exposure due to amalgam fillings, whereas hair mercury better reflects mercury intake by fish consumption. Up to now, saliva does not seem to be a suitable tool to monitor the mercury burden, at least not at low exposure levels.     

Variability of phthalate monoester levels in daily first-morning urine from adult women: a pilot study

Phthalate exposure is ubiquitous and may affect child and adolescent health through both in utero exposure and direct exposure during childhood. Variability in exposure within women is not well documented. We analyzed 90 first-morning urine samples collected by ten reproductive-age women for phthalate metabolites and creatinine. Monoethyl [122 ng/mL (geometric mean concentration = 139 microg/g creatinine)], monobutyl [85.4 ng/mL (97.0 microg/g creatinine)], monobenzyl [37.2 ng/mL (42.2 microg/g creatinine)], and mono-2-ethylhexyl phthalate [9.4 ng/mL (10.7 microg/g creatinine)] were detected in most (94.4%) samples. The concentrations ranged from 23.8-1090 ng/mL, 43-437 ng/mL, 12.4-186 ng/mL, and 1.3-31.1 ng/mL, respectively. We observed considerable variation in phthalate concentrations by day for individual women. The intraclass correlation coefficient, indicating the proportion of variance explained by differences between subjects, ranged from 0.40 (monobutyl) to 0.68 (monoethyl). Monobenzyl and monoethyl phthalates showed higher levels on weekends as compared with weekdays (p = .01 for both). We found no significant difference between monoester levels from different menstrual cycles. Phthalate concentrations vary considerably for an individual and may require multiple samples for accurate assessment     

An assessment of occupational exposure to polycyclic aromatic hydrocarbons in the UK

A cross-industry occupational hygiene survey was commissioned by the Health and Safety Executive (HSE) to determine the levels of polycyclic aromatic hydrocarbon (PAH) exposure in UK industry and to determine if one or more target analytes were suitable as markers for assessing total exposure to PAHs. There were no broadly applicable UK exposure standards for assessing total exposure to PAHs. Until 1993 a guidance value for assessing exposure in coke ovens only, where PAH exposure is known to be the highest, was based on gravimetric analysis of cyclohexane-soluble material. Biological monitoring based on urinary 1-hydroxypyrene (1-OHP) is widely reported to be an effective indicator of exposure by both dermal and inhalation routes but there was no UK guidance value. The survey involved an occupational hygiene study of 25 sites using both airborne monitoring of a total of 17 individual PAHs and biological monitoring. The results showed 8 h TWA levels of total PAH in air ranged from 0.4 to 1912.6 microg m(-3) with a GM of 15.8 microg m(-3). The profile of PAHs was dominated by naphthalene, the most volatile 2-ring PAH. Airborne benzo(a)pyrene (BaP) correlated well (r(2) = 0.971) with levels of carcinogenic 4-6 ring PAHs and was an effective marker of exposure for all industries where significant particle bound PAH levels were found and, in particular, for CTPV exposure. The 8 h TWA levels of BaP ranged from <0.01 to 6.21 microg m(-3) with a GM of 0.036 microg m(-3); 90% were <0.75 microg m(-3) and 95% were <2.0 microg m(-3). Two hundred and eighteen urine samples collected from different workers at the end of shift and 213 samples collected pre-shift next day were analysed for 1-OHP. Levels of 1-OHP in end-of-shift samples were generally higher than those in pre-shift-next-day samples and showed a good correlation (r(2) = 0.768) to airborne BaP levels if samples from workers using respiratory protection or with significant dermal exposure were excluded. Urinary 1-OHP in end-of-shift samples ranged from the limit of detection (0.5 micromol mol(-1) creatinine) to 60 micromol mol(-1) creatinine with a mean of 2.49 micromol mol(-1) and a 90th percentile value of 6.7 micromol mol(-1) creatinine. The highest 1-OHP levels were found in samples from workers impregnating timber with creosote where exposure was dominated by naphthalene. If the 11 samples from these workers were excluded from the dataset, the 90% value for end-of-shift urine samples was 4 micromol mol(-1) creatinine (n = 207) and this value has since been adopted by the HSE as a biological monitoring benchmark value.     

The effects of environmental cadmium exposure on kidney function: the possible influence of age

The study aimed to assess the possible influence of long-term environmental exposure to cadmium and age at the time of exposure on renal function. The study was a follow-up of the 1991-1994 project concerning 2000 inhabitants of a cadmium-contaminated area in the vicinity of a zinc smelter. Since the smelter was built in the late 1950s but was not operated until 1968, some of the inhabitants were not exposed to cadmium during childhood. For the follow-up, 308 persons who in 1993 presented with Cd-U levels > or = 0.5 microg/L adjusted for specific gravity (1.020) were selected in 2000. The study population included 136 people who were exposed to cadmium in childhood (former children) and 172 adults (unexposed adults) with no such exposure. These two groups were divided into subgroups according to Cd-U levels: < or =1 (group 1), 1-2 (group 2), and > or =2 microg/g creatinine (group 3). Urinary and blood cadmium and the markers of renal tubular dysfunction (beta2 M-U, RBP-U, NAG, NAG-A, NAG-B) and glomerular dysfunction (Alb-U and beta2 M-S) were measured. Persons with a history of occupational exposure to cadmium were excluded from this project. In group 3 of the unexposed adults, concentrations of RPB-U, NAG, NAG-B, and Alb-U were significantly higher than those in group 1. In former children, this could be observed only for RPB-U and Alb-U. Urine concentrations of these markers were higher in all of the subgroups of former children than in the groups of unexposed adults (except for NAG and its two forms). However, these differences were significant only for RBP-U in group 3. The findings indicate that early renal effects in the general population may occur at Cd-U concentrations above 2 microg/g creatinine and at lower levels for NAG-B. Moreover, cadmium exposure in childhood may have a stronger impact the renal function, particularly tubular reabsorption, than the exposure of a mature organism.     

Urinary biomarkers of exposure to jet fuel (JP-8)

Benzene, naphthalene, and 1- and 2-naphthol were measured in urine samples obtained from 322 U.S. Air Force personnel categorized a priori as likely to have low, moderate, or high exposure to jet fuel [jet propulsion fuel-8 (JP-8)]. In postexposure samples, levels of these analytes in the high-exposure group were 3- to 29-fold greater than in the low-exposure group and 2- to 12-fold greater than in the moderate-exposure group. Heavy exposure to JP-8 contributed roughly the same amount of benzene and more than three times the amount of naphthalene compared with cigarette smoking. Strong correlations were observed among postexposure levels of naphthalene-based biomarkers in urine and naphthalene in air and breath. We conclude that urinary naphthalene and the naphthols can serve as biomarkers of exposure to jet fuel. Of these, the naphthols are probably more useful because of their greater abundance and slower elimination kinetics.     

Ambient and biological monitoring of coke plant workers – determination of exposure to polycyclic aromatic hydrocarbons

OBJECTIVES: The aims of this study were to determine external and internal polycyclic aromatic hydrocarbon (PAH) exposure in a coke plant and to contribute to the evaluation of biological limit values. METHODS: Personal air sampling was carried out on a study population of 24 coke plant workers. In detail, 16 PAHs were determined, among them phenanthrene, pyrene and benzo[ a]pyrene. For the determination of internal exposure, post-shift urine samples from the workers were examined for hydroxylated metabolites of pyrene (1-hydroxypyrene, 1-OHP) and phenanthrene (1-, 2+9-, 3-, 4-hydroxyphenanthrene, 1-, 2+9-, 3-, 4-OHPhe). In both cases, approved HPLC methods were used. RESULTS: The workers were classified into three groups. The group most exposed was that on the top side of the coke oven, with a mean value of 491.2 microg/m(3) for the sum of all sixteen PAHs. The mean value at the bench side was 26.61 microg/m(3), while it was 76.18 microg/m(3) in the group of workers with no dedicated location (=complete area). Both the excretion of 1-OHP and the sum of hydroxyphenanthrenes had the highest mean levels in the top side group of workers (mean: 19.70 microg/g creatinine (crea.) and 39.18 microg/g crea.), followed by the bench-side workers (mean: 7.01 microg/g crea. and 12.95 microg/g crea.) and the whole-area workers (mean: 3.57 microg/g crea. and 8.70 micorg/g crea.). The concentrations of all urinary metabolites correlated significantly with benzo[ a]pyrene (BaP) in the air. CONCLUSIONS: According to these correlations, urinary concentrations of 8 and 11 microg 1-OHP/g crea., respectively 16 and 23 microg/g crea. for the sum of hydroxyphenanthrenes, correspond to BaP concentrations in air of 2 and 5 micorg/m(3), the German technical guiding concentration (TRK value). Our results are in line with others reported in the literature. That means that it should be possible today to define a standard of occupational hygiene and medicine in coke plants using the elimination of hydroxyphenanthrenes and hydroxypyrene in urine as markers for internal PAH exposure.     

Possible adverse effect of chromium in occupational exposure of tannery workers

Our aim was to investigate the adverse effects of occupational exposure to trivalent chromium. We measured chromium and iron levels in serum and urine and hemoglobin levels in tannery workers and unexposed persons. We studied three groups of subjects. Group 1 included 15 non-smoking male tannery workers highly exposed to chromium from tanning and retanning departments. Group 2 included 14 non-smoking male tannery workers with moderate chromium exposure from dying, drying and finishing departments. Group 3 included 11 healthy, non-smoking male subjects without direct chromium exposure. Higher serum chromium levels were observed in groups 1 and 2 with respect to group 3 (mean values respectively: 0.43; 0.25 and 0.13 microg x l(-1)). Urine chromium levels in group 1 were higher than those in controls (mean values: 1.78 and 1.35 microg x l(-1)). In group 1 an inverse association was found between serum chromium and urine iron (-0.524), urine chromium and hemoglobin (-0.594) and between the urine chromium to iron ratio and hemoglobin (-0.693, p<0.05). The results suggest a chromium adverse effect on iron metabolism, possibly associated with excessive body chromium accumulation. In conclusion, chromium urine test could be recommended for diagnosis of chromium adverse effect on iron metabolism. Further studies are needed to quantify the relationship between urine chromium and hemoglobin metabolism.     

尿中萘及其代谢产物作为焦炉工生物监测指标的研究

目的　探讨尿中萘及其代谢产物作为焦炉工生物监测指标的可行性。方法　在某焦化厂随机选取 2 8名焦炉工人和 2 2名对照个体 ,统一收集工作周末班后 2h尿 ,并使用调查表收集一般情况。采用顶空固相微提取结合气相色谱 -质谱联机方法 ,同时测定尿中萘和芘的水平 ,采用酶水解结合气相色谱 -质谱联机方法 ,同时测定样品中 1-萘酚、 2 -萘酚和 1-羟基芘的水平。使用多元线性回归分析不同工种和吸烟量对尿中这 5种多环芳烃生物标志物浓度的影响。结果　尿中萘、 1-萘酚、 2 -萘酚和 1-羟基芘的浓度呈炉顶工 >炉侧和炉底工 >对照个体的趋势 ,其中尿中 1-萘酚和 1-羟基芘的水平受工种的影响大于2 -萘酚 ;不同暴露水平组中 ,吸烟个体尿中 1-萘酚、 2 -萘酚和 1-羟基芘的浓度均大于不吸烟者 ,但吸烟对 2 -萘酚的影响最大。结论　尿中 1-萘酚和 2 -萘酚浓度均能够有效地反映个体短期多环芳烃暴露的内剂量水平 ,可用于焦炉工的生物监测。     

A longitudinal investigation of selected pesticide metabolites in urine.

As part of a longitudinal investigation of environmental exposures to selected chemical contaminants, concentrations of the pesticide metabolites 1-naphthol (INAP), 3,5,6-trichloro-2-pyridinol (TCPY), malathion dicarboxylic acid (MDA), and atrazine mercapturate (AM) were measured in repeated samples obtained from 80 individuals in Maryland during 1995-1996. Up to six urine samples were collected from each individual at intervals of approximately 8 weeks over a 1-year period (i.e., one sample per participant in each of six cycles). INAP (median=4.2 microg/l and 3.3 microg/g creatinine) and TCPY (median=5.3 microg/l and 4.6. microg/g creatinine) were present in over 80% of the samples, while MDA and AM were detected infrequently (6.6% and <1% of samples, respectively). Geometric mean (GM) concentrations of INAP in urine did not vary significantly among sampling cycles. In contrast, GM concentrations of TCPY were significantly greater in samples collected during the spring and summer of 1996 than in the preceding fall and winter. Repeated measurements of INAP and TCPY from the same individual over time were highly variable. The average range of INAP and TCPY concentrations from the same individual were approximately 200% and 50% greater than the respective population mean levels. Geometric mean (GM) TCPY concentrations differed significantly between Caucasian (n=42, GM=5.7 microg/g creatinine) and African-American (n=11, GM=4.0 microg/g) participants and among education levels, but were not significantly different among groups classified by gender, age, or household income. In future research, environmental measurements of the parent compounds and questionnaire data collected concurrently with the biomarker data will be used to characterize the determinants of variability in the urinary pesticide metabolite levels.     

Environmental and biological monitoring of exposure to polycyclic aromatic hydrocarbons in workers of an electric steel foundry

AIMS: To assess and classify exposure to Polycyclic Aromatic Hydrocarbons (PAHs) in some specific working areas of a steel foundry operating with a continuous casting process and evaluate biomonitoring data in different job tasks. METHODS: Exposure to dusts and six PAHs classified as carcinogenic by EU directives was studied in a cohort of 35 male foundry workers (aged 41.1 +/- 6.9 years), who were examined both prior to and at the end of the work-shift (06:00 a.m.-02:00 p.m.) in two different periods. The urinary excretion of 1-hydroxypyrene (1-OH-P) was measured as a biomarker of exposure to pyrene. RESULTS: PAHs concentrations ranged from 461.8 to 935.6 ng/m3 near the continuous casting area, whereas lower values were measured near the ladle furnace. End of shift 1-OH-P values were higher in 11 non-smoking workers involved in continuous casting process as compared to those employed in mantenance and furnace areas (median of the second determination: 5.70 microg/g creatinine--range: 1.24-21.24 vs 1.17 microg/g creatinine--range: 0.23-4.49; p< 0.001). 1-OH-P excretion was significantly correlated with both the sum of six carcinogenic PAHs and pyrene airborne concentrations. In two biomonitoring sessions, 9.1% and 34.3% of the workers respectively showed end-of-shift 1-OH-P values exceeding the occupational exposure limit (OEL) (4.4 microg/g creatinine or 2.3 micromol/mol(-1) creatinine) recommended for coke-oven workers. CONCLUSIONS: 1-OH-P is a useful biomarker in assessing PAH exposure and is associated with job category at a Steelplant. Due to exposure variability, to assess risk associated with PAHs exposure, biological monitoring should be carried out periodically.