External and internal antimony exposure in starter battery production

In the production of lead batteries two antimony compounds occur: in the casting of grids antimony trioxide (Sb₂O₃), and in the formation of lead plates stibine (SbH₃). Seven workers from the gridcasting area and 14 workers from the formation area were examined with regard to the antimony concentration in blood (Sb-B) and urine (Sb-U). Antimony air concentrations (Sb-A) were measured by means of personal air samplers. Urine samples were collected at the end of the working week, at the beginning (U1) and the end (U2) of the shift, and at the beginning of work following a weekend without Sb exposure (U3). At U2 among the casters the median Sb-A exposure was 4.5 (1.18–6.6) g Sb/m³ and among the formation workers, 12.4 (0.6–41.5) g Sb/m³. The exposure in both groups is more than 10 times lower than the present threshold limit values. The median Sb-B concentrations in the preshift samples was 2.6 (0.5–3.4) g Sb/l for the casters and 10.1 (0.5–17.9) g Sb/l for the formation workers. The average Sb-U values (U2) were 3.9 (2.8–5.6) g Sb/g creatinine in the casting area and 15.2 (3.5 23.4) g Sb/g creatinine in the forming area. Our investigation indicates that the two antimony compounds show virtually equal pulmonary absorption and renal elimination. The statistically significant correlations between Sb-A/Sb-B and Sb-A/Sb-U form the basis for proposals regarding appropriate biological exposure limits for occupational antimony exposure.Dedicated in constant gratitude to our highly honoured mentor, Prof. Dr. med. H. Valentin, on the occasion of his 75th birthday     

Biological monitoring of styrene in the reinforced plastics industry in Emilia Romagna,Italy

Summary Biological monitoring of styrene exposure among workers in the reinforced plastics industry is widely implemented in the region of Emilia Romagna, Italy. More than 18000 urine samples measurements of the main metabolites of styrene, mandelic (MA) and phenylglyoxylic acid, were retrieved for the period 1978–1990, and 4689 values of MA in postshift urine samples were analyzed for various variables thought to influence styrene exposure. The job performed was found to be the most important predictor of styrene exposure. Hand laminators had the highest exposure (mean MA 682 mg/g creatinine); spray laminators showed lower values (404 mg/g), while levels in semiautomatic process operators(243 mg/g) were only slightly higher than in nonprocess workers (186 mg/g). The use of ventilation resulted in lower exposure, but differences in average values were not particularly wide. Exposure decreased weakly during the study period in all work categories, but the percentage of measurements exceeding the current biological limit value (900 mg/g creatinine, 1300 mg/1 corrected for density) is still very high (20% of measurements among hand laminators in 1990). These results indicate that the control measures implemented are only partially effective for the prevention of styrene exposure.The work was done at the International Agency for Research on Cancer (Lyon, France) and at the Documentation and Information Center on Occupational and Environmental Health and Safety (Bologna, Italy)     

Biological assessment of exposure in factories with second degree usage of cadmium compounds

Summary Biological assessment of occupational exposure to cadmium in five different factories with low-level second degree usage of Cd-compounds has been carried out. In 124 exposed and control male workers the following measurements were performed: cadmium in blood (CdB) and urine (CdU), B₂-microglobulin (B2M), creatinin in urine (Great), hemoglobin (Hb) and hematocrit (Ht). Analysis of 34 pairs of workers matched according to age, smoking habits, ethnic origin and factory, established a significant difference only in CdU, the geometric means being 0.67 g/g Creat in the exposed group and 0.48 g/g Creat in the control group. Significant correlation was found between CdU x age and CdB x smoking habits. Multiple regression analysis showed that for each year increase in age CdU increased 3%, for each percent increase of CdB CdU increased 0.28%; for each cigarette smoked per day CdB increased 1.6%. It is concluded that in this type of work the low external cadmium exposure does not express itself in different CdB-levels, but only in different CdU-levels, indicating an increased body burden due to long term low level occupational cadmium exposure. In biological assessment of exposure to Cd, it is essential to take age and smoking habits fully into account.This study was supported by a grant from the Dutch Prevention Fund and the Ministry of Health and Environmental Protection     

Biological monitoring of workers exposed to N,N-dimethylformamide in the synthetic fibre industry

Objectives: Monitoring of workplace air and biological monitoring of 23 workers exposed to N,N-dimethylformamide (DMF) in the polyacrylic fibre industry was carried out on 4 consecutive days. The main focus of the investigation was to study the relationship between external and internal exposure, the suitability of the metabolites of DMF for biological monitoring and their toxicokinetic behaviour in humans.Methods: Air samples were collected using personal air samplers. The limit of detection (LOD) for DMF using an analytical method recommended by the Deutsche Forschungsgemeinschaft (DFG) was 0.1 ppm. The urinary metabolites, N-hydroxymethyl-N-methylformamide (HMMF), N-methylformamide (NMF), and N-acetyl-S-(N-methylcarbamoyl)-cysteine (AMCC), were determined in one analytical run by gas chromatography with thermionic sensitive detection (GC/TSD). The total sum of HMMF and NMF was determined in the form of NMF. The LOD was 1.0 mg/l for NMF and 0.5 mg/l for AMCC. Results and conclusions: The external exposure to DMF vapour varied greatly depending on the workplace (median 1.74 ppm, range <0.1–159.77 ppm). Urinary NMF concentrations were highest in post-shift samples. They also covered a wide range (<1.0–108.7 mg/l). This variation was probably the result of different concentrations of DMF in the air at different workplaces, dermal absorption and differences in the protective measures implemented by each individual (gloves, gas masks etc.). The urinary NMF concentrations had decreased almost to zero by the beginning of the next shift. The median half-time for NMF was determined to be 5.1 h. The concentrations of AMCC in urine were determined to be in the range from <0.5 to 204.9 mg/l. Unlike the concentrations of NMF, the AMCC concentrations did not decrease during the intervals between the shifts. For the exposure situation investigated in our study, a steady state was found between the external exposure to DMF and the levels of AMCC excreted in urine about 2  days after the beginning of exposure. AMCC is therefore excreted more slowly than NMF. The half-time for AMCC is more than 16 h. Linear regression analysis for external exposure and urinary excretion of metabolites was carried out for a sub-group of 12 workers. External exposure to 10 ppm DMF in air (the current German MAK value) corresponds to an average NMF concentration of about 27.9 mg/l in post-shift urine from the same day and an average AMCC concentration of 69.2 mg/l in pre-shift urine from the following day. NMF in urine samples therefore represents an index of daily exposure to DMF, while AMCC represents an index of the average exposure over the preceding working days. AMCC is considered to be better suited for biomonitoring purposes because (1) it has a longer half-time than NMF and (2) its formation in humans is more closely related to DMF toxicity. Received: 25 June 1999 / Accepted: 2 October 1999     

Biological monitoring of environmental and occupational exposure to mercury

Summary Biological monitoring was used to assess mercury exposure from occupational and environmental sources in a group of chloralkali workers (n = 89) and in a control group (n = 75). In the control group, the median value for blood mercury (B-Hg) was 15 nmol/l, that for serum mercury (S-Hg) was 4 nmol/l and that for urinary mercury (U-Hg) was 1.1 nmol/mmol creatinine. Corresponding levels in the chloralkali group were 55 nmol/l, 45 nmol/l and 14.3 nmol/mmol creatinine, respectively. In the control group, there were statistically significant relationships between fish consumption and both B-Hg and S-Hg values (P < 0.001), whereas U-Hg correlated best with the individual amalgam burden (P < 0.01). In the chloralkali group, the mercury levels in blood and urine were significantly related to the type of work (P < 0.001) but not to the length of employment, to fish consumption or to the quantity of dental amalgam fillings. In both groups there were poor correlations between smoking or alcohol intake and the mercury levels in blood and urine. The results strongly suggest that fish is an important source of methylmercury exposure and that amalgam fillings are probably the most important source of inorganic mercury exposure among occupationally unexposed individuals. In the chloralkali group, mercury exposure from fish and amalgam was overshadowed by occupational exposure to inorganic mercury.     

Biological exposure limit for occupational exposure to coal tar pitch volatiles at cokeovens

Summary Biological monitoring is an efficient tool in the evaluation of exposure to chemical agents. However, the dose-response of adverse health effects using biological exposure indices and biological limit values are rarely available. This paper presents an estimation of the occupational exposure limit value of 1-hydroxypyrene in urine, a biological exposure indicator of polycyclic aromatic hydrocarbons (PAH). A large-scale study of the exposure of cokeoven workers to PAH, in wich both air sampling (benzene soluble matter and individual PAH including benzo()pyrene) and biological monitoring (1-hydroxypyrene in urine) were applied, made it possible to establish an empirical mathematical relationship between the air sampling data and biological monitoring data. It was calculated that cokeoven workers with a urinary concentration of 1-hydroxypyrene of 2.3 mol/mol creatinine after a 3-day working period equals the airborne threshold limit value (TLV) of coal tar pitch volatiles (CTPV). Epidemiological studies have quantified the relative risk of lung cancer for topside and non-topside cokeoven workers. The published environmental exposure data of topside and non-topside cokeoven workers were used to determine the time-average exposure. The data of 1-hydroxypyrene in the urine of cokeoven workers and data of epidemiological studies from different coke plants were combined according to the concentrations of PAH in the air. Thus, it was possible to establish an indirect relationship between lung cancer mortality risk and the biological exposure indicator for cokeoven workers. Exposure at the level of the suggested tentative biological exposure limit (BEL) of 2.3 mol/ mol creatinine is estimated to be equal to a relative risk of lung cancer of approximately 1.3.     

铅暴露水平与主要生物监测指标的剂量-反应关系

目的分析2012年度无锡市14家铅蓄电池生产企业1134名铅作业人员的职业健康检查结果,了解铅暴露水平与主要生物监测指标的剂量-反应关系。方法健康监护结果按照血铅浓度不同分组,采用SPSS15．0统计软件分析不同浓度下血、尿常规主要生物指标与铅水平的剂量-反应关系。结果调查铅作业工人1134人,其中男性573人,女性561人;年龄19—66（38．2±8．87）岁,工龄1个月-35a。血铅浓度范围0．01—7．60μmol／L,以血铅浓度作为内暴露剂量分析不同暴露水平对主要生物监测指标的影响,结果显示,不同暴露水平组间血红蛋白减少异常率、红细胞减少异常率、血小板减少异常率、尿胆红素阳性率差异有统计学意义（P〈0．01）,不同暴露水平组间白细胞减少异常率、尿酮体阳性率、尿蛋白阳性率、尿胆原阳性率差异无统计学意义（P〉0．05）。结论铅作业工人体内铅水平的增高可导致血液系统、消化系统损伤的加重,导致血红蛋白、红细胞、血小板减少,尿胆红素阳性率增高。     

Biological monitoring of occupational exposure to toluene diisocyanate

Summary The study validated the use of urinary toluene diamine (TDA) in postshift samples as an indicator of preceding 8-h exposure to toluene diisocyanate (TDI). Nine workers exposed in TDI-based polyurethane foam production were studied. Their exposure levels varied in 8-h time-averaged samples from 9.5 to 94 g/m³. The urinary TDA concentrations varied from 6.5 to 31.7g/g creatinine and they were linearly related to the atmospheric TDI levels. Approximately 20% of TDI is metabolized to diamines but their specificity is remarkable to the extent that by analysis for the 2,4- and 2,6-diamino isomers an idea of the percutaneous absorption may be had.     

Biological monitoring for exposure assessment of volatile organic compounds by Korean firefighters at the fire site

The VOCs and metabolites in urine for exposed VOCs were evaluated for firefighters who participated in the actual fire fighting to determine whether firefighters were exposed to hazardous chemicals, which is the basic data on cancer risk of firefighters. When the fire extinguishing time is long, the concentration of benzene, PHEMA, and toluene among VOCs and metabolites in the case of fire suppression, rescue, and fire investigation work, which is estimated that the exposure of hazardous substances generated from the fire site at the time of fire suppression was large, significantly increased. In the case where the number of urination is 2 or less, the concentration of TZCA, toluene, and benzene among VOCs and metabolites was significantly increased compared to the number of urinating more than 2 times. In the concentration of VOCs and metabolites in urine corrected with creatinine, the concentrations of toluene and PHEMA in urine were significantly higher. The concentration of PHEMA in urine was higher in the group who participated in the fire suppression for more than 11 hours (long time) than the group who participated in the fire suppression for a short time.     

Biological monitoring and exposure to mercury

Occupational health professionals' interest in controlling mercury (Hg) exposure, and the use of biological monitoring in this context, has been ongoing for a number of years. Evidence from urinary Hg results in a number of UK firms who have undertaken some form of biological monitoring or occupational health surveillance suggest that exposure has decreased over the last 10-15 years. This decrease precedes the establishment in the UK of an advisory biological monitoring guidance value (HGV) for urinary Hg and the production of updated medical guidance from the Health & Safety Executive on Hg exposure (MS12 1996). This latter document recommends a urinary sampling interval for urinary Hg of between 1 and 3 months, which is consistent with the reported toxicokinetics of Hg excretion, but we highlight that urinary Hg represents integrated exposure over many previous months. Mercury is a recognized nephrotoxin and MS12 1996 mentions the use of regular dipstick protein estimations. We review our experience of investigating proteinuria and enzymuria in a large-scale cross-sectional occupational study. The incidence of Hg-induced renal disease is probably very rare at current exposure levels. Therefore acceptance of a high false-positive rate of proteinuria not related to Hg exposure needs to be considered in any urinary protein testing regime of Hg workers. The establishment of an HGV for urinary Hg has raised questions about the uncertainty associated with a urinary Hg result, including factors such as diurnal variation, whether urine correction by creatinine or specific gravity is preferable and the possibility of non-occupational sources of Hg contributing significantly towards breaching the HGV. Correction of urinary Hg results by creatinine or specific gravity and the use of a fixed sampling time, such as the beginning or end of the day, substantially reduce the uncertainty in a urinary Hg measurement. But even with good laboratory precision, an individual with a true urinary Hg excretion of 20 nmol/mmol creatinine could supply urine samples of between 14 and 26 nmol/mmol creatinine. The influence of dietary sources in the UK contributing to urinary Hg values approaching or exceeding the HGV is unlikely. The use of tribal or ethnic cosmetics and remedies needs to be considered if a urinary Hg result looks inappropriately high, as some such preparations have been found to contain Hg and can be absorbed through the skin. The ability of excessive chewers or teeth grinders who have a large number of dental amalgam fillings to breach the urinary HGV in the absence of substantial occupational Hg exposure has been reported in a few Scandanavian studies. We report here a likely case of this phenomenon. Since the establishment of the HGV, our biological monitoring Hg data from a number of industry sectors using inorganic or metallic Hg have suggested that a minority of samples (13%) are still greater than the HGV.     

Lead exposure in starter battery production: investigation of the correlation between air lead and blood lead levels

The threshold limit value (TLV) for lead (in Germany, the MAK value) is based on a certain blood lead concentration (in Germany BAT value = biological tolerance value for working materials) that is not to be exceeded; thereby a statistically significant association between air lead (PbA) and blood lead (PbB) is assumed. On the basis of a 10-year period of (1982–1991) biological and ambient monitoring of 134 battery factory staff and their workplaces, a PbA/PbB correlation with the regression equation PbB = 62.183 + 21.242 × Log 10 (PbA) (n = 1089, r = 0.274, P < 0.001) was calculated. These results are in line with those of several other investigations. The shape of the regression curve and the wide scattering of values led to the assumption that PbA values above the MAK value (0.1 mg/m³) do not necessarily result in increased PbB values. Similarly, PbA values lower than the MAK value do not guarantee PbB levels below the BAT value in every case. These observations are influenced by numerous confounders and intervening variables. It is concluded that lowering MAK values as a consequence of lowering BAT values is not mandatory.     

Application of biological monitoring to the quantitative exposure assessment for neuropsychological effect by chronic exposure to organic solvents

Objective: Quantitative exposure assessment became more common as a result of attempts to reduce nondifferential exposure misclassification and to observe a steeper exposure-response relationship. Several exposure variables were compared in a demonstration of the exposure-response relationship between neuropsychological abnormality and long-term exposure to organic solvents in workers at one shipyard. Method: Environmental monitoring and biological monitoring were performed to evaluate the exposure of the workers to organic solvents. Cumulative exposure (CE) and lifetime-weighted average exposure variables were developed with both environmental and biological monitoring data. A neuropsychological questionnaire and a function test for confirmation of a disorder or dysfunction in attention, executive function, visuospatial, and constructional abilities, learning and memory, and psychomotor function were performed. Results: The abnormal rate in neuropsychological diagnosis was 9.3% in the exposed group, which was much higher than the 2.1% rate obtained in the nonexposed group (P < 0.01). The neuropsychological abnormal rate showed a significant dose-response association with CE created with biological monitoring data. The results also suggest that biological monitoring can provide impressive and effective information for quantitative exposure assessment, even in epidemiology studies. Received: 2 April 1998 / Accepted: 23 September 1998     

锑短期暴露对大鼠健康效应的影响

目的 针对饮水中短期暴露锑所致健康风险开展动物实验研究。方法 选择健康SD大鼠60只（雌雄各半）随机分为6组,实验组大鼠经口给予酒石酸锑钾,锑浓度分别为0.06、0.35、0.6、6和60 mg/kg,阴性对照为超纯水,连续灌胃14 d。染毒期间,每周称量大鼠体重,于染毒后d14腹主动脉取血检测血生化指标,处死大鼠后取肝、肾、脾、胸腺、甲状腺称重并进行病理学检查。结果 最高剂量组（60 mg/kg）与阴性对照组相比,雄性大鼠体重明显降低(P＜0.05)、肝脏体比升高(P＜0.01)、血清总胆固醇（TC）浓度降低 (P＜0.01);雄性大鼠碱性磷酸酶（ALP）随染毒剂量增加浓度逐渐上升,在0.6 mg/kg组中达到最高值(P＜0.05),随后ALP浓度逐渐减低,在最高剂量组（60 mg/kg）出现显著性降低(P＜0.01);0.6 mg/kg组葡萄糖（GLU）浓度降低 (P＜0.05);雄性大鼠血清T4浓度自6 mg/kg组开始逐渐降低(P＜0.05);雌性大鼠血清FT4浓度从6 mg/kg组开始逐渐升高(P＜0.05),而FT3的浓度逐渐降低 (P＜0.05);雄性血清FT3浓度、雌性血清T4浓度则仅在0.6 mg/kg组下降（P＜0.05）。结论 锑短期经口暴露能够显著引起大鼠代谢功能异常。     

Biological monitoring of controlled toluene exposure

Objectives: Widespread exposure to toluene occurs in the printing, painting, automotive, shoemaking, and speaker-manufacturing industries. The relationship between air concentrations and the absorbed dose is confounded by dermal exposure, personal protective devices, movement throughout the workplace, and interindividual differences in toluene uptake and elimination. Methods: To determine the best biological indicator of exposure we examined the blood and alveolar breath concentrations of toluene as well as the urinary excretion rates of hippuric acid and of o-, m-, and p-cresols from 33 controlled human inhalation exposures to 50 ppm for 2 h. Results: Among the metabolites, o-cresol was least influenced by background contributions, whereas the p-cresol and hippuric acid rates were obscured by endogenous and dietary sources. Toluene levels in alveolar breath proved to be the most accurate and noninvasive indicator of the absorbed dose. A physiologic model described blood and breath data using four measured anthropometric parameters and the fit values of extrahepatic metabolism and adipose-tissue blood flow. Conclusions: After breathing rate and extrahepatic metabolism had been set to conservative (protective) values (the 97.5th and 2.5th percentiles, respectively) the model predicted that pre-final-shift breath levels of ≤10 μmol/m³ and post-final-shift levels of ≤150 μmol/m³ corresponded to average workplace exposure levels of ≤50 ppm toluene. Alternately, we used the distributions and covariances of the measured and fit model parameters to yield conservative pre-final-shift levels of ≤7.3 μmol/m³ and post-final-shift breath levels of ≤120 μmol/m³ that were reflective of workplace exposure levels of ≤50 ppm toluene. Received: 30 December 1997 / Accepted: 12 June 1998     

Biological monitoring of exposure to pyrethrins and pyrethroids in a metropolitan population of the Province of Quebec, Canada

Pyrethroid and pyrethrins are neurotoxic insecticides widely used to control agricultural and domestic insect pests. The general population is potentially chronically exposed through food consumption, but the actual exposure is poorly documented in Canada. This study aimed at obtaining an indication of the absorption of those insecticides in residents of Montreal Island, the largest metropolitan area of the Province of Quebec, Canada. We randomly recruited 120 adults and 120 children aged 18–64 and 6–12 years old, of which 81 adults and 89 children completed the study. The absorption of pyrethroids and pyrethrins was assessed through measurements of six urinary metabolites: chrysanthemum dicarboxylic acid (CDCA), cis- and trans-2,2-(dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acids (cDCCA and tDCCA), cis-2,2-(dibromovinyl)-2,2-dimethylcyclopropane carboxylic acid (DBCA), 3-phenoxybenzoic acid (PBA) and 4-fluoro-3-phenoxybenzoic acid (FPBA). Metabolites were determined in 12-h urine collections for children and 2-consecutive 12-h collections for adults, and were analyzed by gas-chromatography/mass spectrometry. In both adults and children, the relative distribution of the various metabolites was as follows: tDCCA>PBA>cDCCA>CDCA>DBCA>FPBA. In adults, median (95th percentiles) cumulative amounts of these metabolites were 12.0 (231.1), 8.2 (177.9), 5.0 (110.1), 0.3 (8.2), 0.1 (4.7) and 0.1 (0.5) pmol/kg bw, respectively, in nighttime 12-h urine collections. Corresponding values in children were 12.6 (207.7), 10.2 (73.2), 5.1 (59.6), 2.1 (14.2), 0.1 (4.9) and 0.1 (0.8) pmol/kg bw. The main metabolites observed are indicative of exposure mainly to permethrin and cypermethrin and amounts absorbed are in the same range in adults and children. The distribution levels of the main metabolites in our sample also appeared similar to those reported in the US population.     

Biological exposure limits estimated from relations between occupational styrene exposure during a workweek and excretion of mandelic and phenylglyoxylic acids in urine

Summary Styrene exposure of 18 workers in fiber-glass reinforced plastic industries was measured for 30-min periods throughout each workday for a week. The styrene uptake was estimated using pulmonary ventilation measurements. All urine voidings were collected separately and the styrene metabolites, mandelic acid (MA) and phenylglyoxylic acid (PGA) were determined. The relationship between both exposure and uptake versus excretion of these metabolites was studied. Styrene metabolite concentrations and excretion rates (with 95% tolerance limits) were calculated to correspond to a constant 8-h exposure at the Swedish exposure limit level (25 ppm) or an uptake of an exposure limit related styrene dose (6.3 mmol). The tightest tolerance limits were obtained for excretion rate of MA + PGA per 24 h. The calculated biological exposure limit was 3.4 (± 0.7) mmol MA + PGA/24 h for a dose of 6.3 mmol styrene.     

Applicability of homogeneous exposure groups for exposure assessment in the chemical industry

The purpose of the study was to assess occupational exposure to chemicals, by taking the aspects presented in European standard EN 689 into account, especially with respect to homogeneous exposure groups and their suitability as the basis for exposure assessment. In addition, dermal exposure to chemicals was assessed when appropriate. The industries studied included a plywood factory, a paint factory and a sewage treatment plant of an oil refinery. The workers were classified into homogeneous exposure groups by the persons in charge of occupational health issues in the respective workplaces. The concentrations of the contaminants were measured in workplace air by breathing-zone and stationary sampling, and these approaches were compared. Dermal exposure was measured when applicable. The homogeneity of the grouping was tested with analysis of variance whenever possible. The tasks studied in plywood manufacturing fulfilled the criteria of homogeneous exposure groups for both respiratory and dermal exposure. The group of operators in the sewage treatment plant was highly homogeneous. The complicated organization of the tasks made the use of homogeneous exposure groups (HEG) unsuitable at the paint factory. These findings show that reliable exposure assessment cannot be achieved with a formal standard; instead, comprehensive occupational hygiene evaluation is needed. It should also have a great importance when exposure models are developed. Received: 27 December 1999 / Accepted: 6 May 2000     

Biological monitoring of carbon disulphide and phthalate exposure in the contemporary rubber industry

Objectives: We studied the range in urinary levels of 2-thiothiazolidine-4-carboxyl acid (TTCA), a metabolite of CS₂ and phthalic acid (PA), a common metabolite of phthalates, across factories and departments in the contemporary rubber manufacturing industry. Methods: Spot urine samples from 101 rubber workers employed in nine different factories were collected on Sunday and during the workweek on Tuesday, Wednesday and Thursday at ∼4 pm. In total, 386 urine samples were successfully analyzed. Results: Levels of both biomarkers increased significantly by a factor 2 (paired t-test P-value <0.05) during the working week as compared to the Sunday biomarker levels with absolute increases of approximately 70 μg/l and 5 μmol/mol creatinine for PA and TTCA, respectively. Levels in both biomarkers did not differ markedly between working days. Increases seemed to be restricted to specific factories and/or departments (e.g. molding and curing). Conclusions: The results of this study demonstrate that rubber workers in the contemporary rubber industry are exposed to phthalates and low levels of CS₂ (∼0.05 ppm) as measured by PA and TTCA, respectively. Exposures to both compounds are largely driven by specific circumstances in factories. Therefore, when estimating exposures to phthalates and CS₂ detailed information should be collected on the type and amount of phthalate containing ester plasticizers, dithiocarbamates and thiurams used. Preferably, personal exposure data should be collected. In this case, biological monitoring seems a reasonable approach. However, in the case of PA attention should be given to individual background levels as this could lead to a substantial overestimation of the occupational contribution to total phthalate exposure.     

Biological monitoring values for occupational exposure: a United Kingdom perspective

Policy developments in the United Kingdom have been aimed at facilitating the appropriate use of biological monitoring. Recent initiatives have established clear criteria for the interpretation of biological monitoring results, and new guidance that deals with the ethical and practical issues involved in operating an effective biological monitoring programme has been promulgated. The United Kingdom now has a system of non-statutory biological monitoring guidance values. There are two types, the health guidance value and the benchmark guidance value. Over a number of years, biological monitoring programmes have shown that they help in reducing exposure by regular monitoring and demonstrating adequate control. Received: 2 March 1999 / Accepted: 25 March 1999