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  • Biological monitoring  (19)
  • Internal exposure  (3)
  • 1
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 48 (1981), S. 137-146 
    ISSN: 1432-1246
    Keywords: Limit values ; Internal exposure ; External exposure ; MAK value ; Toluene blood level ; Grenzwerte ; innere Belastung ; äußere Belastung ; MAK-Wert ; Toluol-Blutspiegel
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Description / Table of Contents: Zusammenfassung Am Beispiel einer Toluolexposition am Arbeitsplatz wird ein Verfahren zur Diskussion gestellt, Grenzwerte für Parameter der inneren Belastung zu evaluieren. Es beruht auf der Berechnung eines quantitativen Zusammenhangs zwischen der inneren und der äußeren Exposition. Ein Grenzwert für den Toluol-Blutspiegel ergäbe sich zu 2,6 mg/l. Das Verfahren sollte sich sinngemäß auf eine Reihe von gefährlichen Arbeitsstoffen anwenden lassen.
    Notes: Summary A method is proposed to evaluate limit values for parameters of internal exposure, e.g., for the toluene blood level of exposed workers. A relation between internal and external exposure is calculated. A limit value for the toluene blood level is estimated to be 2.6 mg/1. This method of evaluating limit values for biological parameters should be suited for many other hazardous substances.
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  • 2
    ISSN: 1432-1246
    Keywords: Key words Polycyclic aromatic hydrocarbons (PAH) ; 1-Hydroxypyrene ; Hydroxyphenanthrene ; Biological monitoring ; Action level
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract  Objective. The objective of this study was to assess external and internal exposure to polycyclic aromatic hydrocarbons (PAHs) of workers who are employed in a graphite-electrode producing plant. Additionally we wanted to contribute to the question of biological limit values in order to reduce exposure to tolerable levels. Methods. At five different working places 12 stationary and 16 personal air measurements were carried out to determine the concentrations of phenanthrene, fluoranthene, pyrene, benz[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[a]pyrene and dibenz[a, h]anthracene in air. In addition, we investigated the excretion of 1-, 2+9-, 3- and 4-hydroxyphenanthrene and of 1-hydroxypyrene in the urine of 67 workers by a very sensitive and practical high-performance liquid chromatographic (HPLC) method with fluorescence detection; 2- and 9-hydroxyphenanthrene could not be separated with our analytical method. Results. During the production of graphite electrodes significantly higher PAH exposures were found in the baking and impregnation area than in the crushing, graphitisation and conditioning area. The results of personal air measurements (mean values of the sum of eight PAHs) are: 29.3 (baking), 23.4 (impregnation), 5.2 (crushing), 1.3 (graphitisation) and 0.4 μg/m3 (conditioning). Stationary air measurements yielded similar concentrations. Workers employed in the baking and impregnation areas excreted the highest amount of PAH metabolites in urine. The 1-hydroxypyrene concentrations (median) were: 23.4 (baking), 22.0 (impregnation), 9.6 (crushing), 1.8 (graph itisation) and 2.3 μg/g creatinine (conditioning). The corresponding concentrations of the sum of monohydroxylated phenanthrene metabolites (median) were: 23.1, 36.0, 10.4, 4.6 and 7.6 μg/g creatinine. Within the monohydroxylated phenanthrene metabolites 3-hydroxyphenanthrene predominates with a percentage of 43%. Our results showed that a benzo[a]pyrene concentration in air of 2 μg/m3 would lead to 1-hydroxypyrene concentrations in urine of 20–74 μg/g creatinine. That means that corresponding values in the literature which lie between 4.4 and 6.2 μg/g creatinine are due to other conditions of exposure and cannot be applied to graphite-electrode producing plants. Conclusions. Although to date there are no obligatory biological exposure limits for metabolites of PAHs in urine, it must be concluded that the internal PAH exposure is too high at some work places in this plant, as is generally the case in graphite-electrode producing plants. This is probably caused by skin absorption of PAHs. So for the prevention of health hazards by PAH, internal exposure must be measured using biological monitoring. Although it has not been possible to establish biological exposure limits for PAHs until now, we suggest a reduction in skin contact with these substances and thereafter use of the 90th percentile of the results of biological monitoring as “action levels” for corrective measures.
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  • 3
    ISSN: 1432-1246
    Keywords: Key words Organochlorine compounds ; Biological monitoring ; Environmental exposure ; German population ; Refugees
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract  The aim of the study was to investigate the concentration of organochlorine compounds of environmental-medical relevance in biological materials from refugees with regard to their countries of origin and to compare these concentrations with the internal exposure of the German general population. Methods: During medical examination after entry to Germany specimens could be taken from the refugees to determine the following parameters of biological monitoring: 1,1-dichloro-2,2-bis(-chlorophenyl)-ethylene (DDE-P), polychlorinated biphenyls (PCB-P), pentachlorophenol (PCP-P) and the beta- and gamma-hexachlorocyclohexanes (β-HCH-P, γ-HCH-P) in plasma and the excretion of chlorophenols (4-MCP-U, 2,4-DCP-U, 2,5-DCP-U, 2,4,5-TCP-U, 2,4,6-TCP-U, 2,3,4,5-TeCP-U, 2,3,5,6-TeCP-U) in urine. One hundred and three men (13 from former Yugoslavia, 29 from the former USSR, 33 Africans and 28 Asians) ranging from 16 to 53 years of age (median 27 years) were investigated. Thirty four male Germans without occupational exposure to these substances and a similar age structure (age 25–36 years; median 26 years) served as a control group. Results: A much higher level of internal exposure was found for the DDT meta bolite, DDE, for those persons from Asia, the former USSR and Africa compared with the German controls (medians: 16.9 μg/l, 11.9 μg/l, 10.9 μg/l and 1.1 μg/l). The levels of PCB in plasma were below the detection limit in the majority of refugees. In the control group, however, the PCB levels were higher (ΣPCB: median: 2.1 μg/l, maximum: 13.3 μg/l). The highest β-HCH concentrations, up to a maximum of 15.5 μg/l, were detected in the persons from the former USSR and Asia. The five groups do not differ with regard to internal exposure to PCP and γ-HCH. Renal excretion of 4-MCP, 2,4-DCP and TeCP did not differ between the five groups. The concentrations of 2,5-DCP in urine, however, were significantly lower in the Germans than the refugees from the four regions investigated. The median for the Germans was 3.0 μg/l and for the refugees between 10.8 and 14.7 μg/l. Also the levels of 2,4,5-TCP and 2,4,6-TCP in urine were lower in the German controls than in the men from the former USSR, Africa and Asia. Conclusions: Organochlorine compounds exist worldwide due to their extensive use. There are, however, regional differences for the various substance groups, which during biological monitoring are seen in the different background exposures of the general population. Particularly characteristic are markedly higher levels of DDE in plasma from the refugees compared with the German population.
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  • 4
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 50 (1982), S. 341-349 
    ISSN: 1432-1246
    Keywords: Methanol ; Biological monitoring ; Formic acid
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Summary Twenty persons occupationally exposed to methanol were examined according to their methanol levels in blood and urine and their formic acid excretion. An 8-h exposure to a methanol concentration of 93 ml/m3 (geometric mean) in the air at the working area caused average methanol levels in blood and urine of (8.9 ± 14.7) mg/l and (21.8 ± 20.0) mg/l, respectively, and a mean formic acid excretion of (29.9 ± 28.6) mg/l. These average concentrations for the exposed group showed statistically significant increases compared to those of a control group. For the methanol workers we succeeded in] correlating their methanol levels in blood and urine. When considering the possible application of these parameters for biological monitoring, difficulties were encountered, especially for the individual case from the overlapping range in the concentrations of exposed and unexposed persons for each of the applied parameters. This range is minimum for the methanol concentration in urine. About 80% of the urinary levels from the methanol workers lies above the upper limit within the control group range. Based on our results a rough estimate shows the corresponding methanol content in urine to be about 40 mg/l for an 8-h exposure at 200 ml/m3 (German MAK value).
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  • 5
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 64 (1992), S. 261-264 
    ISSN: 1432-1246
    Keywords: 1-Methoxypropan-2-ol ; Internal exposure ; Blood ; Urine ; Half-lives ; Biological tolerance value
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Summary Twenty-two persons (20 men and 2 women) were examined for their external and internal exposure to the glycol ether 1-methoxypropan-2-ol (PGME) during the production, leak testing and mounting of brake-hoses. For the measurement of external exposure, personal air monitoring was the method of choice. Average concentrations of PGME of 82.2 mg/m3 (22.3 ppm), 68.6 mg/m3 (18.6 ppm) and 11.3 mg/m3 (3.1 ppm) were found in the air of the brakehose production, leak test and mounting areas, respectively. For the estimation of internal exposure to PGME, this glycol ether was measured in both urine and blood. The biological samples were taken post-shift. The highest internal exposure levels were found in the brakehose production section and in the leak test area. The average post-shift concentrations for PGME in workers in the brakehose production section were 4.6 mg/l in urine and 13.5 mg/l in blood; the corresponding figures for workers in the leak test area were 4.2 mg/l in urine and 11.0 mg/l in blood. In blood and urine samples of workers engaged in the mounting area, PGME levels were below the detection limits. The elimination kinetics of PGME were also studied in three highly exposed persons, and mean excretion half-lives of PGME of approximately 4.4 h were found. On the basis of our results we made a rough calculation of a future biological tolerance value: we would except that concentrations of 38-109 mg per litre of blood and 10–31 mg per litre of urine would correspond to the German MAK value for PGME (375 mg/m3).
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  • 6
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 62 (1990), S. 123-126 
    ISSN: 1432-1246
    Keywords: Glycolethers ; Occupational exposure ; Biological monitoring ; Metabolism ; Limit values
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Summary Seventeen persons (2 women and 15 men), who were exposed to glycolethers in a varnish production plant, were examined according to their external and internal solvent exposure. The workers in the production plant (n =12) were exposed to average concentrations of ethoxyethanol, ethoxyethyl acetate, butoxyethanol, 1-methoxypropanol-2, 2-methoxypropyl-1-acetate and xylene of 2.8; 2.7; 1.1; 7.0; 2.8 and 1.7 ppm. In the air of the store (n = 3) and in the laboratory (n = 2) only minor concentrations of xylene respectively xylene and ethoxyethyl acetate could be measured. Internal exposure was estimated by measuring butoxyethanol (BE) in blood as well as ethoxyacetic acid (EAA) and butoxyacetic acid (BAA) in urine samples. Urine samples were taken pre- and post-shift. As expected, the highest values were found in the varnish production. The average post shift concentrations of BE, EAA and BAA were 121.3 μg/l; 167.8 and 10.5 mg/l. The relatively high concentrations of EAA and BAA in pre-shift samples can be explained by the long half-lives of these metabolites. According to our findings most of the glycolethers were taken up through the skin. Comparing our results with those reported in the literature we think that a future tolerable limit value for the concentration of ethoxyacetic acid in urine should be in the order of 100 to 200 mg/l.
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  • 7
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 69 (1996), S. 91-96 
    ISSN: 1432-1246
    Keywords: Key words Toluene ; o-Cresol ; Hippuric acid ; Biological monitoring ; BAT value
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract  Object Ambient air and biological monitoring of an occupational toluene exposure was carried out on a group of 33 workers. Method The biological monitoring of the workers was based on determination of the concentration of toluene in blood and on quantification of the urinary metabolites o-cresol and hippuric acid. All blood and urine samples were collected post-shift. Results The average toluene concentration in the workplace air was 65 ppm, ranging from 13 to 151 ppm. An average concentration of toluene in blood of 911 μg/l was found, corresponding to an average urinary concentration of 2.9 mg/l (2.3 mg/g creatinine) o-cresol and 2.4 g/l (1.9 g/g creatinine) hippuric acid. Both urinary metabolites can be correlated with the concentration of toluene in ambient air and blood, respectively. Conclusions The results of our study indicate that the determination of the urinary o-cresol excretion represents a diagnostically specific and sensitive parameter for the estimation of an individual toluene uptake. In contrast, monitoring of the concentration of hippuric acid in urine cannot be recommended for assessment of individual exposure. To set up a biological tolerance value (BAT) for o-cresol, a urinary concentration of 3 mg/l o-cresol should be in accordance with the current MAK value of 50 ppm toluene.
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  • 8
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 68 (1996), S. 13-21 
    ISSN: 1432-1246
    Keywords: Industrial waste incinerator ; Combustion process ; Biological monitoring ; Organic substances ; Metals
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract One hundred and twenty-two persons employed in an industrial waste incineration plant were examined with respect to organic and inorganic substances which may be produced during the combustion of different waste. The employees were divided into three groups: persons with contact with the incinerator (WI workers,n = 45), periphery workers (n = 54) and management (n = 23). For the evaluation of internal exposure, the levels of lead, cadmium, mercury, benzene, toluene, ethylbenzene andm-xylene in blood, chromium in the erythrocytes, polychlorinated biphenyls, hexachlorobenzene and pentachlorophenol in plasma, and arsenic, chromium, nickel, vanadium, chlorophenols and hydroxypyrene in urine were determined. The internal exposures of the three groups were tested against each other and were compared with the reference values of the general population. Differences between the groups investigated were tested using theU test according to Wilcoxon, Mann and Whitney (P 〈 0.05). The biological exposure limits valid in Germany (BAT values) were not exceeded in any cases. Compared with the background levels of the German population, certain parameters were exceeded in several employees. Significantly higher levels of the WI workers in comparison to both periphery workers and management were found for toluene in blood (median: 1.1 vs 0.9 vs 0.6 μg/l). For the lead and cadmium levels in blood and for the urinary excretion of arsenic, 2,4-dichlorophenol and tetrachlorophenols, statistical differences were found only between WI workers and one of the other groups. However, in all cases the elevations were very small and of interest more from the environmental than from the occupational point of view. It must be stressed that this waste incineration plant is very modern in terms of worker health and safety. At older plants without corresponding health and safety measures, higher internal exposure of the employees to hazardous substances may exist.
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  • 9
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 71 (1998), S. 14-18 
    ISSN: 1432-1246
    Keywords: Key words Ambient monitoring ; Biological monitoring ; Biochemical effect monitoring ; Protein adducts ; Ethylene oxide ; N-Alkyl-Edman method ; N-2-Hydroxyethylvaline ; Sterilization
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract Objectives: Ethylene oxide is an alkylating agent known to be a directly acting mutagen and carcinogen. This study describes the relationship between workplace ambient air concentrations of ethylene oxide and the concentration of N-2-hydroxyethylvaline in the globin of exposed workers. Methods: During the sterilization of medical equipment, 12 workers were occupationally exposed to ethylene oxide. Personal and stationary ambient air measurements were carried out to monitor the external exposure. The determination of the protein adducts was based on the N-alkyl-Edman method, introducing a new commercially available dipeptide standard for calibration purposes. Results: Ethylene oxide concentrations ranging from 0.2 to 8.5 ppm were found in the workplace air. The adduct concentrations ranged from 5,219 to 32,738 pmol N-2-hydroxyethylvaline/g globin in the case of regularly exposed workers (n = 9) and from 518 to 3,321 pmol N-2-hydroxyethylvaline/g globin for three persons with occasional contact with ethylene oxide. Conclusions: The Deutsche Forschungsgemeinschaft established in 1993 a relationship between the ethylene oxide concentration in ambient air and the amount of N-2-hydroxyethylvaline in human globin. By extrapolation, constant exposure to 1 ppm ethylene oxide should yield approximately 4,000 pmol N-2-hydroxyethylvaline/g globin. The ambient air concentrations of ethylene oxide and the amount of N-2-hydroxyethylvaline determined within the present study confirm this extrapolation in practice. In addition, the determination of adducts based on the use of commercially available dipeptide standards for calibration purposes turned out to be an advantageous alternative to the commonly used protein standards.
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  • 10
    Electronic Resource
    Electronic Resource
    Springer
    International archives of occupational and environmental health 71 (1998), S. 309-316 
    ISSN: 1432-1246
    Keywords: Key words Dimethylformamide ; Occupational exposure ; Ambient monitoring ; Biological monitoring ; Dermal absorption ; Occupational health and safety
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract Objectives: This study examined the external and internal exposure to the solvent N,N-dimethylformamide (DMF) of 126 workers from a factory producing synthetic fibers. Methods: Air measurements were carried out using personal air samplers with diffusion tubes (Dräger, ORSA 5). For the purpose of biological monitoring the levels of N-methylformamide (NMF) in urine were measured in preshift and postshift samples. Determinations were carried out using gas chromatography. Anamnestic data were collected with standardized questionnaires, including personal data, working history and current working conditions, and former and current illness with regard to the effects of DMF. Skin diseases were documented by a dermatologist. Results: DMF concentrations measured in the air ranged between 〈0.1 and 37.9 ppm (median 1.2 ppm). Concentrations of NMF varied from 0.05 to 22.0 mg/l (preshift values) and from 0.9 to 100.0 mg/l (postshift values). The creatinine-related values (0.02–44.6 mg/g preshift; 0.4–62.3 postshift) were subject to less variation and therefore represented the level of exposure better than the values related to volume. Additional investigation of a subcollective (n = 31) over a period of 4 days showed that NMF did not accumulate in the organism. The positive but relatively weak association observed between the DMF concentrations measured in the workplace air and the values recorded for internal exposure in this study can be explained by influencing factors such as dermal absorption or protective clothing. Interindividual differences in internal exposure were found for the specific work areas. The German BAT value (15 mg NMF/l urine) was exceeded in 36 persons (29%) despite the use of breathing protection and protective gloves, without increased values being measured in the air. Increased absorption without higher-level exposure could particularly also be observed in employees with eczema. Conclusions: From the point of view of the prevention of disease, biological monitoring is the best instrument for exposure assessment of workers exposed to DMF.
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