Work ability in vibration-exposed workers.

BACKGROUND: Hand-arm vibration exposure may cause hand-arm vibration syndrome (HAVS) including sensorineural disturbances. AIMS: To investigate which factors had the strongest impact on work ability in vibration-exposed workers. METHODS: A cross-sectional study in which vibration-exposed workers referred to a department of occupational and environmental medicine were compared with a randomized sample of unexposed subjects from the general population of the city of Gothenburg. All participants underwent a structured interview, answered several questionnaires and had a physical examination including measurements of hand and finger muscle strength and vibrotactile and thermal perception thresholds. RESULTS: The vibration-exposed group (47 subjects) showed significantly reduced sensitivity to cold and warmth in digit 2 bilaterally (P < 0.01) and in digit 5 in the left hand (P < 0.05) and to warmth in digit 5 in the right hand (P < 0.01), compared with the 18 referents. Similarly, tactilometry showed significantly raised vibration perception thresholds among the workers (P < 0.05). A strong relationship was found for the following multiple regression model: estimated work ability = 11.4 - 0.1 × age - 2.3 × current stress level - 2.5 × current pain in hands/arms (multiple r = 0.68; P < 0.001). CONCLUSIONS: Vibration-exposed workers showed raised vibrotactile and thermal perception thresholds, compared with unexposed referents. Multiple regression analysis indicated that stress disorders and muscle pain in hands/arms must also be considered when evaluating work ability among subjects with HAVS.

Trace element pattern in patients with fibromyalgia.

An imbalance of the trace element status in human tissues and body fluids has been suggested as a contributing factor for the development of fibromyalgia (FM). The study comprised 38 females with defined fibromyalgia (FM) according to generally accepted criteria from the American College of Rheumatology (ACR). They were compared with 41 females matched for age and geographic location. The concentrations of about 30 trace element and ions were determined in whole blood, urine and drinking water of all participants by inductively coupled plasma mass spectrometry (ICP-MS) and inductively coupled plasma optical emission spectroscopy (ICP-OES). Significantly higher concentrations in whole blood of Cd, Co, Cu, Fe, Se, Sn and Zn (p< or =0.046) were observed in the FM-cases in comparison with the referents. A different pattern was noted in urine with increased urinary excretion of Ag (p=0.003) among the FM-patients. The urinary excretion of the other elements were of the same magnitude or slightly lower in FM-cases as compared to referents. As nearly all of the concentrations of the studied elements in blood and urine were within reported reference intervals in non-occupationally exposed populations, the clinical significance of the differences observed seems to be limited. The element concentrations of the studied elements in drinking water were within present national and international guideline values (EU, WHO) and the concentrations of potentially toxic metals such as e.g. Cd, Hg and Pb were low. In conclusion, the present investigation could not demonstrate abnormal levels of trace elements in blood or urine of FM-patients and, thus, does not support the hypothesis that trace element abnormalities play a significant role in the development of FM.

Lung cancer in smelter workers--interactions of metals as indicated by tissue levels.

The concentrations of the elements antimony, arsenic, cadmium, chromium, cobalt, lanthanum, lead, selenium, and zinc were determined in lung tissue of 85 decreased smelter workers by neutron activation analysis and atomic absorption spectrophotometry. The concentrations of all these elements, except zinc, were significantly higher among the workers as compared with rural referents. Workers who died from lung cancer (N = 7) had the lowest lung selenium content relative to other metals, both compared with workers with other diseases and with rural (N = 15) and urban (N = 10) referents. The low lung tissue levels may have influenced the development of lung cancer. The highest lung cadmium concentrations were observed in the lung cancer group, in which, however, smokers and ex-smokers were over-represented. The observations make it likely that the excess lung cancer risk in this smelter environment is multifactorial in character, involving interactions between both carcinogenic and anticarcinogenic factors.

Evaluation of selected publications on reference values for lead in blood.

As a part of the global Tracy project, whose aim is to define metal concentrations in tissues and body fluids of reference populations, more than 1000 papers published from 1980 to 1994 were scrutinized that presented tentative reference values for lead in blood in occupationally unexposed adult populations. Ten studies exemplifying criteria for proper sampling, analysis and data treatment are presented and discussed. Levels of lead in blood are influenced by numerous factors. Accordingly, a wide variation in blood lead concentrations was observed. As an example, in a global study in 1983 of nonsmoking female schoolteachers, the geometric mean value for lead in blood varied from 52 micrograms. l-1 in Tokyo, Japan, up to 193 micrograms. l-1 in Mexico City. The Tracy survey demonstrates the importance of factors such as age, gender, ethnicity, food, drinking and smoking habits, hobbies, season and year of sampling, residential area, and geographic location. Lead in blood was shown to be both time and area specific. Thus it was not possible to establish a general reference value for lead in blood.

Biological monitoring of inorganic lead.

In exposure and risk evaluation, monitoring lead biologically has several advantages over technical exposure assessment. Traditionally, the concentration in blood (B-Pb) has been widely used. However, the erythrocytes tend to become saturated, and this phenomenon causes a nonlinear relationship between B-Pb and uptake and between metabolic and toxic effects and B-Pb. Recently, several techniques for determining lead in finger bone, tibia, or calcaneus in vivo by X-ray fluorescence have become available. Bone lead reflects long-term exposure and should prove valuable in epidemiologic studies. Mobilization tests have been widely used to monitor lead biologically. They mainly seem to reflect the lead in soft tissues and may not be an index of total body burden, most of which is in the skeleton. It thus seems that, at least in adults, mobilization tests do not provide more information than traditional lead determinations in blood and urine. A metabolic model for lead in humans is presented.

Normal concentrations of chromium in serum and urine--a TRACY project.

The validity of "normal" concentrations for total chromium in serum and urine (S-Cr and U-Cr, respectively) in papers published mainly in the last decade were evaluated and graded by two investigators according to TRACY criteria. The results were in close agreement. Because of possible contamination during sampling from stainless steel needles, the description of the sample collection method was considered important. Documentation of analytical quality control was emphasized. The chromium concentrations were categorized according to nonoccupational conditions that could influence the levels. Eighty-seven publications reporting chromium concentrations in blood and 58 on U-Cr were evaluated, 53 dealing with S-Cr and 41 with U-Cr being found suitable for the TRACY project. In selected publications the arithmetic mean values presented for S-Cr and U-Cr in individuals with no known exposure were within the following ranges: 1-3 nmol.1-1 for S-Cr and 2-10 nmol.1-1 or 0.2-1 mumol.mol creatinine-1 for U-Cr.

Lead concentrations in human plasma, urine and whole blood.

OBJECTIVES: Blood-lead levels (B-Pb), and to some extent urinary lead (U-Pb), are the most employed measures of lead exposure and risk. However, the small fraction of lead present in plasma (usually below 1% of that in blood) is probably more relevant to lead exposure and toxicity. Nevertheless, the lead content of plasma lead (P-Pb) has only seldom been used, mainly due to analytical limitations, which have now been overcome. We examined P-Pb in occupationally exposed subjects, as well as its relationship with B-Pb and U-Pb. METHODS: Blood samples were obtained from 145 male workers, 110 of whom were employed in lead work. After a simple dilution of plasma, P-Pb was determined by inductively coupled plasma mass spectrometry. The detection limit was 0.04 microg/l, and the imprecision was 5%. RESULTS: The lead concentration ranges were 0.20-37 microg/l for P-Pb, 0.9-176 microg/l (density adjusted) for U-Pb, and 9-930 microg/l for B-Pb. A close exponential relation was obtained between B-Pb and P-Pb. When B-Pb was plotted versus log P-Pb, a straight line (log P-Pb = 0.00225 x B-Pb - 0.58; r = 0.97) was obtained. Both the relation between U-Pb and P-Pb and that between U-Pb and B-Pb showed a large scattering (r = 0.78 in both cases). The relation to B-Pb appeared to be exponential, while that to P-Pb appeared to be linear. CONCLUSIONS: The low detection limit and good precision of P-Pb determinations make it possible to use P-Pb in assessments of lead exposure and risk. Furthermore, in relative terms, P-Pb is a more sensitive measure than B-Pb, especially at high lead levels. This development is of importance for studies of exposure, possibly also for studies of risks.

Antimony in lung, liver and kidney tissue from deceased smelter workers.

Tissue concentrations of antimony in lung, liver, and kidney tissue from a group of deceased smelter workers from northern Sweden have been compared with those of a group of persons without occupational exposure from a nearby area. Neutron activation analysis was used to determine the antimony concentration of lung tissue from exposed workers; these concentrations were 12-fold higher than those of referents (p less than 0.001). For lung tissue there was no tendency towards decreased antimony concentrations with time (up to 20 a) after the cessation of exposure, and this result indicates a long biological half-time. The highest values were found for workers who had worked for many years at the roasters and in the arsenic and selenium departments. There was no significant difference between the antimony concentration of the lung tissue from workers who had died of lung cancer and those of persons who died of other malignancies, cardiovascular disease, or other causes. This finding does not however rule out the possibility of a role for antimony in the etiology of lung cancer among smelter workers since multiple factors may have been operating. The antimony concentration of the liver tissue and the kidney cortex did not differ from the corresponding values of the reference group; this finding indicates either a short biological half-time or insignificance for the systemic distribution of antimony.

Environmental health in the Baltic region--toxic metals.

Recent reports on concentrations of lead, cadmium, methylmercury, arsenic and nickel in some biological media in populations in the Baltic region are reviewed. In particular, children in parts of Poland, the Czech Republic, and Germany have uptakes of lead sufficient to cause adverse effects on the central nervous system and kidneys. Cadmium exposure is also high in Poland. Slight cadmium-induced effects on the kidneys have been reported from Germany and Sweden. Methylmercury uptake is dependent upon the intake of fish, in particular from contaminated lakes and rivers in Sweden and Finland, as well as the eastern coast of the Baltic Sea. There are some indications of immunotoxic effects associated with the intake of such fish. However, fish also contain other immunomodulating agents. Exposure to arsenic seems to be low everywhere in the Baltic region. There is high nickel exposure in northern Russia.

Lung retention of antimony and arsenic in hamsters after the intratracheal instillation of industrial dust.

Airborne factory dust (with a volume median diameter of 5.0 micron and a geometric standard deviation of 2.1 micron) from a Swedish copper smeltery contained antimony (Sb) (1.6 weight %) and arsenic (As) (19 weight %). The dust was neutron activated and intratracheally instilled in hamsters. In vivo measurements of lung clearance were undertaken of the radionuclides 76As, 122Sb, and 124Sb. Comparison was made with pure substances of antimony trioxide (Sb2O3) and arsenic trioxide (As2O3). Two phases were recognized in the clearance curves. The approximate half-time for the initial phase was 13 h for As2O3, 20 h for arsenic dust, about 40 h for Sb2O3, and about 30 h for antimony dust. The second phase had an approximate half-time of 20-40 d for Sb2O3 and antimony dust. Because of the short physical half-life of 76As, the second phase of the lung clearance was not possible to follow for AS2O3 and arsenic dust. The observed differences in clearance were primarily related to the solubility of the dust particles in saline, while particle size seemed to be less important in this instillation experiment. The low solubility of antimony in factory dust combined with a long biological half-time may be of importance in explaining the observed lung accumulation of antimony in exposed workers. The greater solubility and shorter biological half-time restricted the lung retention of arsenic.

Fatal arsenic poisoning--a case report.

A worker was buried under arsenic trioxide in an industrial accident. He was almost immediately released but had inhaled and swallowed substantial amounts of arsenic dust. In spite of intensive treatment, circulatory collapse could not be prevented, and he died 6 h after the exposure. The treatment, autopsy findings, and arsenic concentrations in tissues and body fluids are described and discussed.

Lead intoxication caused by skeletal disease.

BACKGROUND: Inorganic lead is accumulated in the skeleton, which harbors more than 90% of the body burden of lead. If rapidly mobilized, this pool may constitute a health risk. However, clear evidence of this theory has been lacking. HISTORY: A previously healthy 36-year-old Swedish man with more than 10 years of work-related lead exposure developed headache, musculoskeletal pain, and paresthesia of both arms. Two months after the cessation of exposure, the lead level in his blood (B-Pb) was 5.5 mumol.l-1, and treatment with chelating agents was started. Shortly after the treatment period, he had an accident causing a fracture of the right collum femoris. The B-Pb was fairly stable around 1.5 mumol.l-1 for about two years after the end of exposure (95th percentile 0.6 mumol.l-1 for occupationally unexposed Swedish men). The examination showed that the patient had high skeletal turnover and clearly reduced bone density, as well as signs of tubular dysfunction. He was given the diagnosis idiopathic osteoporosis. His moderately raised bone lead concentration (about 20 micrograms.g wet weight-1; normal level in Sweden 4 micrograms.g-1) can only partly explain the raised B-Pb, remaining for years after the cessation of exposure. Instead, the main explanation is probably the increased skeletal turnover. CONCLUSIONS: A combination of a moderately increased bone lead pool and skeletal disease seems to increase the risk for lead poisoning.

Lead concentrations in tibial and calcaneal bone in relation to the history of occupational lead exposure.

OBJECTIVES: This study tested a simple model of the relationship between the lead concentration in bone (bone-Pb), exposure time, and lead in plasma (P-Pb) and whole blood (B-Pb) to make it possible to use bone-Pb as a retrospective exposure index. METHODS: Seventy-seven active lead workers and 24 referents were studied. The bone-Pb in tibia (T-Pb) and calcaneus (C-Pb) was measured by in vivo X-ray fluorescence. P-Pb was calculated from B-Pb by use of the nonlinear relationship between these variables. Cumulative B-Pb (cumB-Pb) and P-Pb (cumP-Pb) were calculated to the time of the bone-Pb measurements. In addition, cumP-Pb was adjusted by applying varying rate constants for the transfer of lead from bone to plasma. RESULTS: There were close linear associations between the lead concentrations in tibia (proportion of variance explained, R2 = 0.78) and calcaneus (R2 = 0.80), on one hand and the cumB-Pb on the other. The best fit of bone-Pb to the adjusted cumP-Pb (0.79 for T-Pb; 0.82 for C-Pb) was obtained for the terminal phase half-times of 13 and 12 years, respectively. CONCLUSIONS: The combined data on bone-Pb and exposure time make it possible to estimate previous mean P-Pb and B-Pb. Such estimates will be valuable in studies of toxic effects on long-term exposed lead workers when data on the intensity of previous exposure are lacking. The use of P-Pb in modeling bone-Pb kinetics is physiologically relevant, but the use of adjusted cumP-Pb, as compared with cumB-Pb, did not significantly change the variance in the relation to bone-Pb.

International project for producing reference values for concentrations of trace elements in human blood and urine--TRACY.

In assessing the concentrations of toxic metals, such as cadmium, chromium, and mercury, in human blood and urine samples to determine whether they are abnormal or not, reliable reference values are needed from populations of nonoccupationally exposed subjects. Numerous publications present concentrations claimed to be typical for the study populations, but they can differ by up to an order of magnitude for a particular element. This is the consequence of general problems that are related to the definition of the reference groups, and the sampling and analytical procedures used, and that make it difficult to define typical and unbiased values. An international group of experts now establishes criteria and procedures to evaluate publications containing information on the concentrations of metals in tissues and body fluids for reference populations. These evaluations have been compiled in a data base (TRACY).

Cumulative lead exposure in relation to mortality and lung cancer morbidity in a cohort of primary smelter workers.

OBJECTIVES: The purpose of this study was to determine the mortality and cancer incidence of long-term lead smelter workers at a primary smelter. METHODS: A cohort of 3979 workers employed for at least 1 year during 1928-1979 and a subcohort of 1992 workers employed in lead-exposed departments (lead only workers) was formed. The expected mortality in 1955-1987 and cancer incidence in 1958-1987 were calculated relative to the county rates, specified for cause, gender, 5-year age groups, and calendar year. A cumulative blood-lead index was used for the dose-response analyses. RESULTS: The lung cancer incidence of the total cohort [standardized incidence ratio (SIR) 2.8, 95% confidence interval (95% CI) 2.1-3.8] and the group with the highest exposure (SIR 3.1, 95% CI 2.0-4.6) was high. Similar risk estimates were observed with a latency of 15 years. The workers hired before 1950 had higher lung cancer risk estimates (SIR 3.6, 95% CI 2.6-5.0) than the workers hired later (SIR 1.3, 95% CI 0.6-2.6, no latency period). The risk estimates for lung cancer were further elevated in the subcohort of lead-only workers (SIR 5.1, 95% CI 2.0-10.5 in the highest exposed subgroup; latency period of 15 years). No excesses of other malignancies were noted. CONCLUSIONS: The increased relative risks were probably mainly due to interactions between lead and other carcinogenic exposures, including arsenic. Further study is required concerning such possible interactions before a role in the induction of lung cancer can be ascribed to lead.

Lead in tissues of deceased lead smelter workers.

Smelter workers are exposed to a number of metals and other substances in dust, fumes and gases. The concentrations of lead in liver, lung, kidney, brain, hair and nails were determined in 32 deceased, long-term exposed male lead smelter workers, and compared with those of 10 male controls. The lead levels in liver, lung, kidney and brain were analyzed by atomic absorption spectrophotometry. X-ray fluorescence was used for the determinations in hair and nails. Lead in blood had been determined repeatedly in the lead workers since 1950, which made it possible to calculate a time-integrated blood lead index for each worker. The highest lead levels in soft tissues were found in liver, followed in order of concentration by kidney, lung and brain, among both exposed workers and controls. These organ lead concentrations were all significantly higher among the workers as compared with the control group (p < or = 0.02). The largest difference between workers and controls was found in brain tissue (ratio between median values = 5.6). The lead levels in hair and nails were of the same magnitude in the two groups. The workers showed positive correlations between lead concentrations in liver and kidney (Spearman's rho = rs = 0.59; p < 0.001), liver and hair (rs = 0.51; p = 0.003), liver and nails (rs = 0.52; p = 0.002) and hair and nails (rs = 0.52; p = 0.002). Lead concentrations in kidney correlated well with lead levels in hair (rs = 0.57; p = 0.001) and nails (rs = 0.51; p = 0.003), respectively. The positive correlation between the lead concentrations in liver and kidney indicates that these organs belong to the same soft tissue lead pool in the body. In retired lead workers, positive correlations were observed between the lead concentrations in liver and the cumulative blood lead index (CBLI) (rs = 0.50; p = 0.016), as well as between lead levels in kidney and CBLI (rs = 0.51; p = 0.014).

Acid precipitation--effects on trace elements and human health.

Environmental pollution by acid precipitation increases the solubilization and mobilization of toxic metals. Through the food chain, this may alter the intake of toxic and essential elements in man. Potential adverse health effects could follow after increased human exposure. For the general population, the exposure pattern and health effects caused by aluminium, cadmium, lead and mercury are of particular concern. Although there are several indications that the exposure to toxic elements (e.g. aluminium, cadmium, lead and methylmercury), as well as the intake of essential elements (e.g. selenium), may be affected by acid precipitation, there is presently no firm evidence of adverse health effects in man. However, the present data clearly indicate that the safety margins are small. Thus, the ongoing acidification in many areas must be stopped before such effects become evident. The effects on trace element status and human health by acid precipitation were discussed at the ISTERH (International Society for Trace Element Research in Humans) Conference in Stockholm, May, 1992. The main findings are briefly summarized here.

Urine mercury levels and associated symptoms in dental personnel.

Dental personnel are exposed to low concentrations of mercury vapor in their working environment and from their own amalgam fillings. This study included 505 occupationally exposed individuals working at 82 dental clinics in northern Sweden and 41 controls without occupational mercury exposure. The concentration of mercury in air was measured. Urine mercury was determined for all participants, who also answered a questionnaire focused on four symptoms known from the literature to be connected with mercury exposure, namely loss of appetite, tremor, insomnia and anxiety. The median value of mercury vapor in air in the dental surgeries was low compared with other investigations; 1.5 micrograms m-3 in public dental care and 3.6 micrograms m-3 in private dental care. The urine mercury concentrations (HgU) were low, and of the same order of magnitude as for the Swedish population as a whole. Median values among different groups of dental personnel ranged from 1.4 to 2.9 nmol Hg/mmol creatinine. For those occupationally exposed, the load from their own amalgam fillings was estimated to be of the same order of magnitude as from the working environment. The prevalence of any of the four symptoms investigated in the groups of exposed personnel and controls as low, less than or equal to 11%. In our study, which included mercury intakes up to twice the contribution from amalgam fillings, no increase in the prevalence of symptoms could be detected in relation to mercury concentrations in urine.

Multielemental assay of tissues of deceased smelter workers and controls.

Concentrations of 23 elements in lung, liver and kidney from deceased smelter workers are compared with those from rural and urban controls. The analyses were made by neutron activation analysis and atomic absorption spectrophotometry. Significantly higher levels of antimony, arsenic, cadmium, chromium, cobalt, lanthanum, lead and selenium were found in the smelter workers lungs (n = 85) compared with the rural controls (n = 15). Significantly higher concentrations of antimony, arsenic and lead were observed among all smelter workers compared with urban controls (n = 10). The highest increase, about 11-fold, was found for antimony in smelter workers compared with non-exposed controls. A six-fold increase was noted for arsenic. Workers who died from lung cancer (n = 7) had the lowest lung selenium content relative to concentrations of other metals, both compared with other disease categories among the workers (GI-cancer, other cancers, cardiovascular diseases, cerebrovascular diseases, other causes) and with the two control groups. The low lung selenium concentrations may have influenced the development of lung cancer. The highest lung tissue levels of cadmium were found in the lung cancer group. Smokers and ex-smokers were over-represented in this group and tobacco is a known cadmium source. The highest, or one of the highest, lung values for some of the other metals (antimony, arsenic, cadmium, lanthanum and lead) were observed in one or several of the lung cancer cases. Metal concentrations in liver (metabolism) and kidney (excretion) reflect the systemic distribution. The highest cadmium levels in the liver and the lowest selenium content in the kidney were found among the lung cancer cases. A multifactorial genesis for the development of lung cancer is concluded from this study, which visualizes the need for systematic health surveillance and follow-ups both in active and retired workers.

Distribution of cadmium, lead and zinc in lung, liver and kidney in long-term exposed smelter workers.

Increased mortality due to various malignancies is reported from long-term exposed, non-ferrous smelter workers. In the present study the post-mortem distribution of cadmium, lead and zinc in lung, liver and kidney is reported and related to exposure and mortality. The study involved 86 male copper smelter workers who died after April 1975. Lung samples were taken from all workers and liver and kidney samples were taken from about one-quarter of the workers. Two control groups were used. The exposed workers were divided into six groups based upon diagnoses in medical records and autopsy protocols. Lead and zinc were analyzed by atomic absorption spectrophotometry and cadmium by neutron activation analysis. For the skewly distributed tissue levels, non-parametric statistical processing was used. Of the workers, 53% died from cardiovascular diseases and 30% from malignancies (8% from lung cancer). Cardiovascular diseases predominated in the two control groups: about 75 and 100%, respectively. Lung and liver cadmium concentrations were significantly higher in the lung cancer group of smelter workers than in the other groups of smelter workers (p less than 0.05) and rural controls (p less than 0.01). Cadmium in kidney, and lead in lung and liver were significantly higher (p less than 0.03) in the lung cancer group than in rural controls, but did not differ from that of the other workers. Zinc in lung, liver and kidney did not differ between exposed workers and controls. Rather strong Spearman rank-order correlation coefficients were found between the cadmium content of lung, liver and kidney tissue, especially in non-smoking smelter workers and rural controls. Smoking was more common in the lung cancer group than in the total group of smelter workers. Cadmium levels in the lungs of exposed workers were significantly higher (p less than 0.001) in smokers than in both ex-smokers and non-smokers. Earlier studies of the same workers gave significantly lower selenium levels in lung tissue compared with other groups of smelter workers and controls. As other carcinogenic substances are present in the working environment, e.g. arsenic, chromium and benzo [alpha]-pyrene, the specific effect of cadmium in the development of lung cancer cannot be evaluated at present.