Mean Lead Level Research Articles

Lead-contaminated drinking waters in the public schools of Philadelphia.

Lead exposure is a preventable environmental health concern. Young children between the ages of 1 to 6 are most susceptible to its clinical effects. This article reports the results of lead level determinations in the drinking water of Philadelphia's public school buildings and remediation efforts aimed at dealing with this public health concern. Water samples were collected from drinking sources in 292 school buildings in Philadelphia from May 2000 through January 2001. These samples were collected and sent to reference laboratories for determination of lead levels. A total of 42.5% (124) of schools had water lead levels not exceeding the action level of 20 ppb, of which 3.1% had nondetectable levels or levels less than 5 ppb. A total of 28.7% of buildings had water lead levels ranging from 20 to 50 ppb, 11.6% had levels between 50-100 ppb, and 17.1% had water lead levels of 100 ppb or more. A total of 57.4% of Philadelphia's public school buildings had water lead levels exceeding the Environmental Protection Agencies (EPA) action level of 20 ppb, and 28.7% of school buildings had water with mean lead levels in excess of 50 ppb. Depending on the volume of water consumed, drinking water from school buildings may be a significant source of lead exposure for children in their formative years of development. Although Philadelphia's public school buildings were evaluated, lead-contaminated drinking water in schools is not only an urban concern. School buildings in suburban and rural areas may have similar water lead levels, and testing programs are desirable.

Blood lead levels of both mothers and their newborn infants in the middle part of China

A cross-sectional investigation on maternal and umbilical blood lead levels in an urban area, an industrial town and a rural area of middle China is reported. Blood samples from 89 mothers during delivery, from the umbilical cords and from 105 non-pregnant women were collected. Self-administered questionnaires including the medical history and the pregnancy-related complaints were performed. After acid digestion, the whole blood lead levels were determined by a 180-80 flame atomic absorption spectrometer. The geometric mean for lead levels in blood of non-pregnant women was 66.9 microg/l (range: 25.0-201.0 microg/l) in the urban, 66.9 microg/l (range: 30.5-198.8 microg/l) in the industrial town, and 53.3 microg/l (range: 16.0-170.5 microg/l) in the rural area. The geometric mean of lead levels in blood of pregnant women at delivery both in the rural area (74.4 microg/l, range: 35.2-245.6 microg/l) and industrial town (65.9 micro/l, range: 20.0-172.0 microg/l) were higher than in the urban region (54.3 microg/l, range: 27.9-187.0 microg/l; p < 0.05). Compared with non-pregnant women at the same area, the blood lead levels of pregnant women was lower in urban (p < 0.05), but higher in rural areas (p < 0.05). The geometric mean for lead level in umbilical cord blood was significantly higher in rural (84.1 microg/l, range: 28.0-185.0 microg/l) than in the other areas (53.5 microg/l, range: 23.5-156.7 microg/l in the urban; 60.1 microg/l, range: 12.5-168.3 microg/l in the industrial town). The total geometric mean for lead level in cord blood was 69.0 microg/l (range: 12.5-185.0 microg/l), and 17.8% samples were above the blood lead threshold of health concern (> or =100 microg/l) for children (CDC, 1991), but the body weight and length of newborn babies have not been affected. The correlation between maternal and cord blood was 0.6805 (p < 0.01). Most of the pregnant women did not take the calcium supplements recommended during pregnancy. In conclusion, there were some lead burdens on both the mothers and their newborn babies in these areas. All possible measures should be taken to reduce the environmental lead exposure. It is also crucial that maternal nutrient intake, particularly calcium, should be sufficient.

Heavy metal levels of pasture grasses in metropolitan area

Urban agriculture is becoming an important lucrative activity in Dar es Salaam City even though the city is subject to traffic and industrial pollution pressures. Poor planning has left only limited spaces, particularly road reserves, for cultivation and foraging animals. While there is increasing road traffic no study has been conducted determine levels of trace metals in pasture grasses. This study, therefore, reports on the levels of cadmium, manganese, lead and zinc of cynodon grasses in road vicinity in the city. Results show that the trace metal levels (ppm ± SDE) in Cynodon grass species were: Cd (0.24 ± 0.06 - 2.58 ± 0.15), Mn (41.5 ± 13.6 - 345.0 ± 124.3), Pb (1.15 ± 0.64 - 25.53 ± 1.29) and Zn (25.97 ± 3.69 - 95.36 ± 19.61). The mean levels of lead and zinc varied exponentially with distance off the road up to 15 m distance. Lead and zinc levels correlated with average daily traffic in the roads while cadmium and manganese did not. This suggests that lead and zinc in grasses owe their sources from the passing motor vehicles in agreement with other reported studies. It is recommended that pasture grasses in road vicinities must not be used for foraging dairy cattle and goats for public health reasons.

Lead in Young Herring Gulls: Paradoxical Effects of Exercise on Tissue Concentrations

Exposure to lead prenatally and early in life affects physiological, behavioral, and intellectual development in humans and other animals. The movement and storage of lead within tissues and organs and its elimination from the body influence the amounts reaching sensitive target organs such as the developing brain. In this study, young herring gulls, Larus argentatus, were used to examine the effect of mild exercise on the deposition of lead in bone, to clarify possible differences between free-ranging birds in nature and confined birds in the laboratory. Forty 2-day-old chicks were randomly assigned to one of four groups: lead treatment with and without exercise, and controls with and without exercise. Chicks in the lead treatment group received a single intraperitoneal injection of lead acetate solution (100 mg/kg); weight-matched control chicks were injected with an equal volume of isotonic saline at the same age. Chicks in the exercise groups were taken outside and encouraged to move about for 2.5 h/d; others were confined in standard cages. Chicks were sacrificed at 45 d of age and lead was analyzed by graphite furnace atomic absorption. The interaction of exercise and lead dose significantly influenced the amount of lead in the three bones examined (rib, humerus, tibiotarsus), but not in the other tissues. For the lead-treated birds, mean bone lead levels were lower in the exercised versus nonexercised birds, while the reverse was true for control chicks. The data suggest that lead storage can be partly ameliorated by exercise, that young chicks would be the most affected by lead, and that older chicks that move and have larger territories in which to move may suffer lesser effects than those in dense territories.

Effect of maternal bone lead on length and head circumference of newborns and 1-month-old infants.

The authors evaluated the effects that maternal bone lead stores have in anthropometry at birth in 223 mother-infant pairs. The participants were recruited between April and November 1994. Anthropometric data were collected within the first 12 hr following delivery. Maternal information was obtained 1 mo after delivery occurred. Bone lead burden was determined with in-vivo K-x-ray fluorescence of the tibia (cortical bone) and the patella (trabecular bone). The authors transformed anthropometric measurements to an ordinal 5-category scale, and the association of measurements with other factors was evaluated with ordinal logistic-regression models. Mean bone lead levels were 9.8 microgram/gm bone mineral and 14.4 microgram/gm bone mineral for the tibia and patella, respectively. Birth length of newborns decreased as tibia lead levels increased. Compared with women in the lower quintiles of the distribution of tibia lead, those in the upper quintile had a 79% increase in risk of having a lower birth length newborn (odds ratio = 1.79; 95% confidence interval = 1.10, 3.22). The authors adjusted by birth weight, and the effect was attenuated--but nonetheless significant. Patella lead was positively and significantly related to the risk of a low head circumference score; this score remained unaffected by inclusion of birth weight. The authors estimated the increased risk to be 1.02 per microgram lead/gm bone mineral (95% confidence interval = 1.01, 1.04 per microgram lead/gm bone mineral). Odds ratios did not vary substantially after the authors adjusted for birth weight and other important determinants of head circumference.

Correlates of bone and blood lead levels among middle-aged and elderly women.

In 1993-1995, the authors evaluated risk factors for elevated blood and bone lead levels in 264 Boston, Massachusetts, area women previously selected for a case-control study of lead and hypertension. Bone lead was measured at the tibia and patella with K x-ray fluorescence. Blood lead was analyzed by graphite furnace atomic absorption. Participants were aged 46-74 years and had mean lead levels of 3 (standard deviation, 2) micro g/dl (blood), 13 (standard deviation, 9) micro g/g (tibia), and 17 (standard deviation, 11) micro g/g (patella). In multivariate linear regression models, use of postmenopausal estrogen (inverse) and alcohol intake (positive) were significantly associated with blood lead levels. Both bone lead measures were significantly and positively associated with blood lead but only among postmenopausal women not using estrogen; for example, an increase from the first to the fifth quintile of tibia lead level (19 micro g/g) was associated with a 1.7- micro g/dl increase in blood lead (p = 0.0001) in this group. Older age and lower parity were associated with higher tibia lead; only age was associated with patella lead. The observed interaction of bone lead with estrogen status in determining blood lead supports the hypothesis that increased bone resorption, as occurs postmenopausally because of decreased estrogen production, results in heightened release of bone lead stores into blood.

Bioaccumulation of lead in Xenopus laevis tadpoles from water and sediment

The overall objective of this research was to monitor the uptake kinetics of lead in an amphibian model and correlate metal content with embryo development. Based upon the concentration of lead found in the water and sediment of a Louisiana swamp adjacent to a Superfund site, a controlled laboratory experiment exploring lead uptake from water and sediment by Xenopus laevis tadpoles was conducted. For 5 weeks, tadpoles were exposed to water and a simulated sediment, kaolin, spiked with 1, 5, or 10 times the concentration of lead found in field water and sediment samples. Additionally, organisms were exposed to the 5× condition for 3 and 6 weeks. The experimental controls consisted of unexposed tadpoles and ones exposed to lead originating from water or sediment exclusively. At the end of the exposure periods, developmental data, i.e., body weight and developmental stage, were recorded, and the tadpoles were analyzed for whole body lead concentration. Lead extraction was accomplished by dry ashing, and its amount was quantified polarographically. Results showed that lead inhibited the normal development of these amphibians, in a manner that generally was more severe as exposure level increased. The hindrance of tadpole development also coincided with an increase in whole body lead concentration at higher exposures. Temporally, at the 5× exposure concentration, the mean lead level increased with time, but this difference was not statistically significant ( P<.05). Additionally, control animals exposed to lead (either in water or in sediment) showed no statistical difference with regard to weight and lead uptake, indicating that lead originating from both water and sediment is incorporated into the tadpole. The controlled laboratory experimental protocol used here is thus capable of investigating the uptake of a single metal (Pb in this case) and determining its effect on the development of tadpoles while differentiating the significance of multiple sources of exposure.

Reconstruction of a decline of ambient lead levels in the Ruhr area (Germany) by studying lead concentrations in antlers of roe deer ( Capreolus capreolus)

We determined lead concentrations in antlers ( n=132) of roe bucks ≥2 years of age, killed between 1951 and 1999 in the northern Ruhr area, Germany. The lead content of the antlers ranged between 0.6 and 19.0 mg/kg dry weight of bone, and overall markedly declined over the study period. As a consequence, mean lead levels in younger samples were always significantly ( P<0.001) lower than those in older ones (for the periods: 1951–1969, 1970–1979, 1980–1989 and 1990–1999). Annual mean antler lead concentrations were positively correlated ( r s =0.74, P<0.001) with annual mean lead concentrations in airborne particulate matter of the Rhine-Ruhr area during the period 1974–1999. The findings of the present study underscore that roe deer antlers are well suited for a monitoring of temporal trends in environmental lead levels in a cost-effective way.

Lead levels in primary teeth of children in Karachi.

The majority of children in Karachi have blood lead levels above 10 micrograms/dl, the upper safety limit set by the United States Centers for Disease Control and Prevention. A study was undertaken to evaluate chronic lead exposure in children by measuring lead levels in shed primary teeth collected from primary school children in Karachi. A total of 309 teeth were collected from nine different schools, and analysed for lead content by atomic absorption spectrophotometry with electrothermal atomization. The mean (SD) age of the subjects was 7.6 (1.2) years and the mean lead level was 5.78 micrograms/g of whole tooth (dry weight), ranging from 0.42 to 39.75 micrograms/g. Incisor teeth had a significantly higher mean (SD) lead level, 6.42 (4.19) micrograms/g, than canines and molars which contained 4.91 (5.12) micrograms and 4.50 (2.67) micrograms lead whole tooth (dry weight), respectively. Significant differences were observed between different schools. No difference was observed between boys and girls and the accumulation of lead in teeth was not correlated with chronological age.

Gender Differences in Blood Lead and Hemoglobin Levels in Andean Adults with Chronic Lead Exposure

A field study of the prevalence of lead (Pb) intoxication was conducted in 158 adults (67 men and 91 women) living at 2,500-2,800 meters in Ecuadorian Andean villages with high Pb contamination from local small-scale Pb-glazing cottage industries. Venous blood samples showed mean blood lead (PbB) levels of 34.5 microg/dL (SD 22.2) for men and 27.0 microg/dL (SD 18.4) for women; this difference was significant (t-test, p = 0.022; Mann-Whitney U, p = 0.044). An ANOVA showed no significant main effect for gender (F = 0.118, p = 0.782) or age (F = 2.479, p = 0.117), and no significant gender-by-age interaction (F = 0.273, p = 0.602). In the Pb-glazing study group, 39% of the men had PbB levels > or = 40 microg/dL, while 41% of the women had PbB levels > or = 30 microg/dL (the WHO health-based biological limits). A reference group of 39 adults (24 men and 15 women) had a mean PbB level of 5.9 microg/dL (SD 2.8; range: 1.8-16.8), significantly different from that of the 158 subjects in the study group (t-test, p < 0.0001). The difference in mean PbB levels of men (6.8 microg/dL) and women (4.7 microg/dL) in the reference group was significant (t-test, p = 0.026; Mann-Whitney U, p = 0.019). The mean altitude-corrected hemoglobin levels in the study group were lower than normal, 11.3 g/dL for men and 10.9 g/dL for women.

Blood lead levels in copper smelter workers in Japan.

Lead exposure of workers in a Japanese copper smelter was assessed by determining lead levels in blood, air and flue cinder at the copper smelting processes. All the samples were analyzed for lead by atomic absorption spectrometry. Mean lead levels of air were highest at the anode department followed by the converter, smelter and blend departments. The mean level of blood lead of the workers in the anode department was also the highest among the four smelting departments. The mean blood lead levels of the workers in each department were positively correlated with their air lead levels (r = 0.99, p < 0.01). This study indicates therefore that workers in copper smelters have been exposed to lead in their workplace. Though this finding has already been reported in preceding studies, the Ordinance on Prevention of Lead Poisoning in Japan has not included copper smelter into its target job categories if their lead concentration in the raw material is less than 3%. The limitation of the present Ordinance which defines the targets by the types of job and not by the actual exposure, is discussed.

Effect of Season of the Year on Lead Levels in Young Children

Lead poisoning is a serious health concern for child care providers of young children. This study examined blood lead levels in 1,190 children residing in Mississippi. Children ranged in age from six to 81 months, mean age was 32.9 months. Mean lead level was 5.2 micrograms per decaliter (mcg/dl). Boys had a higher lead level than girls, and Black children had a higher lead level than White children. The percentage of children with lead toxicity, or lead levels of 10 mcg/dl or higher was 8.5%. The winter season (December 21 to March 19) had a significantly lower (p = .03) lead level than Autumn (September 23 to December 22), 4.9 mcg/dl and 5.5 mcg/dl, respectively. The Summer season (June 21 to September 22) and Spring (March 20 to June 20) had lead levels of 5.2 mcg/dl, which was not significantly different from the other seasons of the year.

Andrew Jackson's exposure to mercury and lead: poisoned president?

Historians have suggested that US president Andrew Jackson (1767-1845) experienced lead and mercury poisoning following his therapeutic use of calomel (mercurous chloride) and sugar of lead (lead acetate). To evaluate these claims, we performed direct physical measurement of 2 samples of Jackson's hair (1 from 1815, 1 from 1839). Following pretreatment and acid digestion, mercury was measured using cold vapor generation techniques, while lead levels were measured by electrothermal atomic absorption spectrophotometry. Mercury levels of 6.0 and 5.6 ppm were obtained from the 1815 and 1839 hair specimens, respectively. Lead levels were significantly elevated in both the 1815 sample (mean lead level, 130.5 ppm) and the 1839 sample (mean lead level, 44 ppm). These results suggest that Jackson had mercury and lead exposure, the latter compatible with symptomatic plumbism in the 1815 sample. However, Jackson's death was probably not due to heavy metal poisoning.

Lead and cadmium in tissues from horse, sheep, lamb and reindeer in Sweden

Levels of lead and cadmium were determined in tissues of muscle, liver and kidney from horse, lamb, sheep and reindeer in Sweden during the years 1994–1997. Mean levels of lead in muscle, liver and kidney from horse were <0.002, 0.13 and 0.047, from lamb <0.002, 0.031 and 0.053, from sheep <0.002, not analysed and 0.046, and from reindeer 0.003, 0.13 and 0.13 mg/fresh weight, respectively. The mean levels of cadmium in muscle, liver and kidney from horse were 0.042, 2.5 and 18, from lamb 0.0019, 0.031 and 0.12, from sheep 0.0034, not analysed and 1.0, and from reindeer 0.003, 0.60 and 2.7 mg/fresh weight, respectively. Comparisons with literature data were attempted. In some cases the results could differ by several orders of magnitude. It cannot be ruled out that some of the differences between studies might be due to analytical differences, making comparisons very difficult.

Dental lead levels in residents from industrial and suburban areas of Kuwait

The present study describes lead concentrations in whole incisor teeth (non-carious) of 216 Kuwaiti resident's aged 3–74, collected from industrial and suburban areas of Kuwait. The mean concentration of lead in all age groups (3–74) showed a significant correlation between both the sexes. Statistical analysis showed a significant correlation between lead levels of males compared with industrial and suburban areas. A similar correlation was also noted in the case of females supporting that industrial residents were more exposed to lead levels than those in suburban areas. A further significant correlation was noted between males and females of industrial and suburban areas which showed that males accumulate more lead concentration than females. A significant correlation was not observed when each age group was compared with that of the respective sexes representing industrial and suburban areas. However, a significant correlation was noted when lead levels in each age group was compared with that of the other age groups except in age groups ranging 35–42. The mean lead levels of 216 teeth were in the range 2.21–2.50 μg/g which is less than the range indicated by other investigators in the recent past.

Uptake of lead by Pomphorhynchus laevis cystacanths in Gammarus pulex and immature worms in chub (Leuciscus cephalus).

The uptake of lead by cystacanths of the acanthocephalan Pomphorhynchus laevis in naturally infected amphipods, Gammarus pulex, and by immature parasites in experimentally infected fish, Leuciscus cephalus, was examined following 3-week experimental exposures (0.01 and 0.1 mg l(-1) Pb2+). Both G. pulex and the cystacanths of P. laevis accumulated lead but concentrations in the parasites were lower than in the host tissues at the low lead dose and significantly lower at the high dose. P. laevis from chub exposed to 0.01 mg l(-1) lead contained significantly more of the metal than the tissues of their host. Interestingly, there was an increase in the mean lead levels in the parasites from the control chubs which was concurrent with a decrease in host tissue concentrations. The results of this experimental study therefore confirm previous suggestions that heavy metals are predominantly accumulated by acanthocephalans inside the fish definitive host and not by cystacanths in the haemocoel of the amphipod intermediate host. The microhabitat of the parasite is therefore of primary importance rather than its developmental stage. Furthermore, metal concentrations in adult acanthocephalans will respond rapidly to changes in environmental exposure of their hosts.

Accuracy and reproducibility of blood lead testing in commercial laboratories.

To assess the proficiency of commercial laboratories in analyzing lead in clinical blood samples from subjects without overt lead exposure. We submitted masked duplicate blood lead specimens to 8 masked laboratories. Each laboratory received blood aliquots immediately following drawing (time 1) and 2 weeks later (time 2) from 7 human subjects and 3 bovine blood samples with known lead levels of 0.26, 0.57, and 0.79 micromol/L (5.4, 11.8, and 16.4 microg/dL). Of the 8 laboratories, 5 were commercial laboratories, 1 was a state laboratory, 1 was a research laboratory, and 1 was the Centers for Disease Control and Prevention reference laboratory. Correlation coefficients were calculated, and differences within and between laboratories were assessed by analysis of variance. Results were obtained for all specimens, with all the human subjects' overall mean lead levels being less than 0.48 micromol/L (<10 microg/dL). Each laboratory reported all human blood specimens appropriately, as having lead levels less than 0.48 micromol/L (<10 microg/dL) and within 0.14 micromol/L (3 microg/dL) of the overall mean for that subject. All internal reproducibilities were very high (range, 0.92-1.00) except for one (0.60), possibly lower because of 1 pair of specimens. Mean differences between blood samples analyzed at time 1 and time 2 ranged from -1.4 to 1.2, with only 2 laboratories having significant differences (P<.01). Overall, there was strong reproducibility within and among laboratories, with no overall time trend or interlaboratory or intralaboratory variance. The storage conditions did not seem to affect the aggregate results. The data suggest that through implementation of the Centers for Disease Control and Prevention/Wisconsin Blood Lead Proficiency Testing Program, the Centers for Disease Control and Prevention's Blood Lead Laboratory Reference System, and mandated federal and state proficiency programs, laboratories in this geographic region have improved their performance as compared with previous published studies and an unpublished study.

Indoor and outdoor household dust contamination in Cincinnati, Ohio, USA

Despite some progress in reducing the average lead level in the USA, the streets of Cincinnati, Ohio, are still contaminated by heavy metals. High levels of heavy metals will have significant unequivocal ecological impacts and pose a potential health hazard. This study evaluates the level of heavy- metal contamination in household dust and examines its relationships with the external environment. Samples of outdoor and indoor dust were collected from middle-income residential homes in the Greater Cincinnati Metropolitan District and the metal content was analysed by inductively coupled plasma atomic emission spectrophotometry. Results showed that the mean levels of lead in outdoor and indoor dusts are 650 μg g⊃-1 and 377 μg g⊃-1 and the copper levels are 253 μg g⊃-1 and 510 μg g⊃-1, respectively. The median levels are 156 μg g⊃-1 and 139 μg g⊃-1 for outdoor and indoor lead dusts and 35 μg g⊃-1 and 124 μg g⊃-1 for outdoor and indoor copper dusts. The degree of contamination may be ascribable to the age of the dwelling unit and the neighbourhood, the time when the unit was last painted, the presence of pets and the type of space heating. In addition, car exhausts seems to be a possible source of contamination.

Lead in primary teeth from Norway: changes in lead levels from the 1970s to the 1990s

Lead is one of the most important and widely distributed pollutants in the environment. In the human population children are particularly at risk. Local dentists in all 19 counties in Norway collected 2746 primary teeth from 1990 to 1994. Tooth substance from whole, ground teeth were analyzed for lead concentration by electrothermal atomic absorption spectrophotometry. The geometrical mean for the entire material was 1.27 μg lead/g tooth substance (S.D. 1.87). The mean lead levels in each of the counties were significantly lower than those obtained in a corresponding study in the 1970s. Two counties, Oslo and Vest-Agder, had significantly higher lead levels than the majority of the other counties. Tooth lead concentration and atmospheric deposition of lead in the same areas were significantly and positively correlated, as shown by analysis of naturally growing moss. We conclude that lead concentrations in primary teeth from children in Norway have been reduced by approx. 50% from the 1970s to the 1990s. The reduction probably reflects a decrease in the environmental lead burden in Norway.

Lead levels in roadside soils and vegetation of Damascus city

This study concentrates on seasonal variations of lead levels in roadside soils, vegetables and plants of Damascus city. Lead concentrations in soil samples varied from 78.4 ppm to 832 ppm while mean lead levels in plants ranged from 2.6 ppm to 19.3 ppm; the highest levels were found to be in grass (44 ppm). In addition, lead levels were lower in soil samples during the wet period (December to April) whereas, it is higher in plants during the same period. Moreover, traffic density, distance from traffic roads, climate and area topography (up- and down hill) were influencing factors in lead levels in both the soil and plant samples. The results have also shown that lead concentration in most of the analyzed vegetable samples was high and normal washing does not decrease it to an acceptable level.