|Year : 2005 | Volume
| Issue : 1 | Page : 15-21
Decreased total and ionized calcium levels and haematological indices in occupational lead exposure as evidence of the endocrine disruptive effect of lead
JI Anetor1, TS Akingbola2, F AA Adeniyi1, GO Taylor1
1 Department of Chemical Pathology, College of Medicine, University of Ibadan, Ibadan, Nigeria
2 Department of Haematology, College of Medicine, University of Ibadan, Ibadan, Nigeria
J I Anetor
Department of Chemical Pathology, College of Medicine, University of Ibadan, Ibadan
Source of Support: None, Conflict of Interest: None
The multisystem and prime environmental and occupational toxin, lead (Pb) is seldom included in the list of endocrine disruptors group like bisphenols A, B and F, nonylphenol, benzoquine, equiline etc.
One hundred and thirty-seven subjects consisting of 86 lead workers and 51 unexposed individuals (as controls) participated in the study. Dietary intake including dairy products and micronutrients as assessed by 24-hour dietary recall was similar between lead workers and controls. Calcium homeostasis and haematological indices were evaluated in all subjects.
Blood lead level was significantly higher in the lead workers than in controls (P<0.001). Total and ionized calcium levels were in contrast significantly decreased in lead workers compared with controls (P<0.01, P<0.001 respectively). Inorganic phosphate level though slightly raised compared to controls did not reach statistical significance (P>0.05).
The haematological indices, haemoglobin, haematocrit, and mean cell haemoglobin concentration like calcium levels were all significantly reduced (P<0.001) in all cases.
Semi-quantitative assessment of erythrocyte protoporphyrin was trace (±) in both lead workers and controls (i.e. similar). Serum copper level was significantly higher in Pb workers than in controls (P<0.005).
These decreases are consistent with a repression of the endocrine systems regulating both erythropoiesis and calcium homeostasis resident in the proximal convoluted tubule(PCT) of the kidney; the most vulnerable site to Pb damage.
Our findings therefore, appear to provide evidence or a reminder that Pb satifies the conditions defining EDCs and should be recognized as one, especially in developing countries where high environmental Pb and malnutrition co-exist and may magnify this effect
Keywords: Blood lead, endocrine disruptors, 1, 25-dihydroxycholecalciferol, serum calcium, haematological indices, erythropoietin
|How to cite this article:|
Anetor J I, Akingbola T S, Adeniyi F A, Taylor G O. Decreased total and ionized calcium levels and haematological indices in occupational lead exposure as evidence of the endocrine disruptive effect of lead. Indian J Occup Environ Med 2005;9:15-21
|How to cite this URL:|
Anetor J I, Akingbola T S, Adeniyi F A, Taylor G O. Decreased total and ionized calcium levels and haematological indices in occupational lead exposure as evidence of the endocrine disruptive effect of lead. Indian J Occup Environ Med [serial online] 2005 [cited 2017 Apr 28];9:15-21. Available from: http://www.ijoem.com/text.asp?2005/9/1/15/16036
Global concerns have been raised in recent years over the potential adverse endocrine effects that may arise from exposure to chemicals in the environment or work place. These chemicals have the potential to interfere with or alter the endocrine system in humans and wildlife.1],2] Lead is an environmental chemical and one of the oldest occupational and environmental toxins known.[3-5] Lead in contrast to calcium is not an essential nutrient and has no established toxicity threshold concentration. As a biochemical analogue of calcium, lead interferes with calcium metabolism and many of its physiological functions.[7-9] The principal mechanism of the perturbation of calcium metabolism by lead lies in the metabolic activation of the hormone 1, 25-dihydroxychole calciferol (calcitriol). Recent studies indicate that low levels of lead exposure are correlated with kidney dysfunction among others.6],11]
The kidney is also an endocrine organ producing erythropoietin (EPO), a glycoprotein (hormone) which regulates both steady-state and accelerated erythrocyte production in the proximal renal tubule (PRT)12],13] where lead accumulates. Others are rennin from the juxta glomerular apparatus (JGA). The kidney also elaborates l, a-hydroxylase enzyme also from the proximal convoluted tubule for the metabolism of the prohormone 25-OH cholecalciferol from the liver to the active hormone 1, 25-(OH)2-cholecalciferol. The cells lining the proximal tubules appear to be the tissue in the kidney most highly sensitive to Pb. Anaemia is one of the most recognized clinical signs and symptoms of lead poisoning though the mechanism is multifactoral and the mechanism of which is not entirely clear,[16-18] surprisingly this ancient toxin (Pb) is often left out when endocrine disruptive chemicals (EDCs) such as bisphenol A, bisphenol B, bispherol F, benzophenone equilin, nonyphenol mixture etc and methods of their assays are discussed.19],20] This is probably because lead has assumed a lower priority status in the developed countries in contrast to the situation in most developing countries where environmental lead is still a significant public health problem. Moreover, lead is sufficiently prevalent at low level (no threshold value) to cause a number of metabolic aberrations including endocrine disruption. This study, a part of a larger study on the evaluation of the nutritional, metabolic and immune status presents evidence that lead is an endocrine disruptive substance which to the knowledge of the investigators has not been documented and appears relevant for the recognition of the continuing scientific and medical rationale for ameliorating plumbism.
| Materials and Methods|| |
Chemicals and reagents
(a) Ammonium pyrollidinedithirocarbamate (APDC) and Methyllsobutylketone (MIBK) were obtained from Wako chemicals. (Wako Pure Chemicals Industries, Osaka, Japan). (b) Ethylacetate, American Chemicals Society (ACS) certified was obtained from Fisher Scientific (Fisher Scientific Fairlawn, NJ, USA). Methyllsobutylketone (MIBK) was obtained from Wako Chemicals (Wako Pure Chemicals Industries, Osaka, Japan/ (c) Triton-X100 was obtained from British Drug Houses (BDH) (BDH Chemicals Ltd, Poole, England).
Other common chemicals and acids such as hydrochloric acid, (HCl), nitric acid (HNO3), trichloroacetic acid (TCA) acetic acid (CH3 COOH) all of "analar" grade were obtained from BDH (BDH Chemicals Ltd, Poole, England).
Reagents and Diagnostic Kits
Total calcium and inorganic phosphate kits were obtained from Medical Analysis System (MAS) (MAS, Inc., Camarillo, USA).
Total bilirubin Kits was obtained from Miles Laboratories (Miles Inc., Diagnostic Division, Elkhart, Indiana, USA).
Total protein and albumin kits were obtained from Sigma Diagnostic (Sigma Diagnostic, St. Louis, Missouri, USA).
Hemoglobin kit was also obtained from Miles Laboratories (Miles Inc., Diagnostic Division, Elkhart, Indiana, USA).
Lead Standard Solution (spectrosol) was obtained from BDH (BDH Laboratory Supplies, Poole, England). Microhaematocrit tubes (heparinized) were obtained from Becton-Dickins on (Becton-Dickinson, NJ, USA).
The subjects for this study are as previously described in our earlier report. The subjects were all resident at the same altitude of which the current study comprises a component, but is briefly summarized here. One hundred and thirty-seven subjects involved in common lead-based occupations and unexposed individuals were selected for the study. Eighty-six (86) subjects were lead workers while 51 individuals who were not known to be either occupationally exposed nor involved in any lead dependent hobby served as controls. The subjects were all males and age and sex matched with Pb workers, nutrient intake including dairy fruit and vegetables intake was similar between both populations. This was ascertained by 24-hour dietary recall.
At least 15 ml of venous blood was collected from each subject at the antecubital fossa with minimal stasis using pyrogen free disposable needles and syringes (Becton-Dickinson, Dublin). Five mililitres of the venous blood was dispensed into hepanin vacutainer tubes (Becton-Dickinson, NJ, USA) for Pb assay while 2 mls were dispensed into EDTA tubes (Becton-Dickinson, NJ, USA) for haematological studies. The rest were dispensed into anticoagulant free vacutainer tubers to yield serum for other biochemical investigations. The sera were frozen at - 20o C until time for analysis.
Blood Lead Assay
Assay was performed according to the modified method previously described. Briefly the method is based upon chellation technique, blood is haemolysed with 5% Triton X100 solution, the Pb is chellated with 2% APDC and extracted with MIBK. The organic solution containing Pb is analysed by flame atomic absorption spectrophotometry (AAS) AGW AES Model 200A (Analysengerate GMbH, Germany) at 283.3 nm.
There was strict adherence to clean trace element handling procedures. Quality control was ensured by recovery studies, use of pooled samples and duplicate analysis.
Assessment of Calcium homeostasis
The colourimetric method using cresophthalein complexone (CPC) employed in this study is based on the modified method of Baginsky et al using the MAS kit (MAS, Inc. Camarillo, USA). The complex formed between calcium and cresolphthalein complexone in alkaline medium was measured spectrophotometrically in a spectronic 21D (uv-vis) (Milton Roy, Analytical products Division, Rochester, NY, USA). 8-hydroxyquinoline was added to the solution to minimize interference by other metallic ions especially magnesium.
Estimation of ionized calcium
Serum ionized calcium was estimated by employing the method of Mclean and Hastings as adopted by Beeler and Catrou using the following formula. Ionized calcium (mg/dl) =
SCa (mg/dl) X 6 - SPr (g/dl) X 0.33
SPr (g/dl) + 6
were SCa = Serum calcium and
SPr = Serum protein
Inorganic Phosphate Assay
The method of Fiske and Subarrow in a kit supplied by Sigma (Sigma Diagnostics, St. Louis Mo, USA) in turn modified by Martinek was used. The modification by Martinek has improved the sensitivity and specificity of this method. The assay was performed as instructed by the manufacturers. Briefly supernatant fluid is obtained with TCA by removing protein and lipid phosphorus. The supernatant fluid reacts with ammonium molybdate in an acid solution to form phosphomolybdate. A mixture of sodium bisulphate, sodium sulphite and 1-amino-2-naphthol-4-sulphonic acid reduces the phosphomylybdenum blue complex.
Total protein and albumin assay
Total serum protein was determined by the classical biuret reaction using the Sigma Diagnostics total protein reagent kit (Sigma Diagnostic Co. St. Louis, Mo, USA). The assay was performed according to the method of Doumas et al and read at 540nm in a 21 UVD Spectrophotometer (Milton Roy, Analytical products Division, Rochester, USA).
This was determined by using the Sigma bromocresol purple (BCP) reaction according to the modified method previously described by Pinnell and Northern. The principal reaction being that serum albumin reacts with BCP to form a stable - blue - purple colour complex with an absorption maximum at 600nm and read in the same spectrophotometer as for total protein.
Determination of Haematological Indices
Haemoglobin (Hgb) was determined with a solid phase test strip impregnated with potassium ferricyanide using seralyser reflectance photometry, as employed in the Ames Seralyser Reflectance Photometer (Ames Coporation, Elkhart, USA). Essentially the reaction is based on the quantitation of Hgb in the form of methaemoglobin; oxidation of Fe2+ in Hgb to Fe3+ by potassium ferricyanide (K3 Fe (CN)6).
Determination of Haematocrit (HCt), Mean cell haemoglobin concentration (MCHC) and red cell morphology. These were performed according to standard procedures, as recommended by the British Committee for standards in Haematology.
Erythrocyte protoporphyrin (EPP) level was semiqualitatively evaluated by the method of Varley et al. Essentially 2 drops of whole blood from EDTA tubes were added to 2.5 ml - ether-ethyl acetate mixture (5:1 v/v) in a 10 x 160 mm glass test tube. This was thoroughly mixed and decanted. To the supernatant was added 0.5 ml, 3M HCl. This was examined under UV light, using model UVG-54 UV lamp (Ultraviolet products Inc., San Gabriel, Carlifornia, USA).
Total bilirubin determination
This was assayed by a modification of the classical Vanden Bergh reaction as used by Rand and Pasqua.
The test was performed with the seralyser (Miles, Diagnostic Division, Elkhart. The Strip is based on the reaction between bilirubin and a diasonium salt in the presence of dyphyline and p-toluene sulphonic acid. Resulting in azobilirubin, a red-purple substance. The test was performed as instructed in the Ames Technical Mannual (Miles, Diagnostics Division, Elkhart, Indiana, USA).
Determination of Serum Copper
Copper was determined by the method of Osheim et al by AAS using the same equipment as for Pb. Serum was diluted using ultra pure water (ASL, IITA, Ibadan, Nigeria), The solution was thoroughly mixed and analysed for Cu at 324.7nm. The principle of the reaction is essentially as described for Pb.
A commercial standard obtained from BDH Chemicals (BDH Chemicals Ltd, Poole, England) was prepared in 10% glycerol to ensure similar viscosity between serum and the aqueous standard used thus ensuring similar aspiration rate into the AAS flame.
All data were initially analysed with the students' t-test to determine if there were differences between exposed and the referent (control) groups. When significant difference was evident (P <0.05) the person's product moment correlation test was employed to determine correlation between lead and other variables. Further analyses were carried out for multiple comparisons between groups with multiple regression analysis.
Finally, the principal component analysis was used to assess for the degree of interaction between lead and other variables. Results were expressed as mean ± SEM.
| Results|| |
Blood lead assay
This was significantly higher in the Pb workers than in controls (P <0.001) [Table - 1]. The levels in the control (occupationally unexposed) group was however much higher than currently accepted levels in unpolluted environments. The Pb level in the exposed group did not vary with duration of exposure. Neither did it vary with severity of exposure (see exposure category).
The haematological indices assessed in this study are shown in Table 2. Haematocrit, haemoglobin and mean cell haemoglobin concentration, MCHC were all significantly lower in lead workers than in controls (P <0.001) in all cases.
Erythrocyte morphology was similar in both Pb workers and controls (no hyperchromasia evident) [Table - 2].
Erythrocyte protoporphyrin,EPP assessment was also similar in Pb workers and controls, present in trace amounts in both groups [Table - 2].
Serum copper level, an important factor in erytropoiesis was significantly higher in Pb workers than in controls (P <0.005) [Table - 2]. Total bilirubin, a degradative product of protoporphyrin was significantly lower in Pb workers than in controls (P <0.001) [Table - 2].
| Discussion|| |
A number of disorders have been ascribed to the environmental and occupational toxicant lead. Though endocrine dysfunction has also been associated with this ubiquitous toxicant such as its role in calcium homeostais through its impairment of calcitriol (1, 25-DHCC) or impairment of erythropoietin synthesis in the kidney, a principal target organ for Pb toxicity, Pb is rarely referred to as an endocrine disruptive chemical. We report decreased total and ionised calcium levels as well as haematological indices as evidence of endocrine disruption in an occupational cohort exposed to Pb.
The significantly elevated Pb level in the Pb workers was associated with decreases in total and ionized calcium levels. This decreased calcium level confirms earlier experimental and clinical reports and reflects perturbation of calcium metabolism.15],41] Lead is a biochemical analogue of calcium, thus it interferes with calcium in several metabolic pathways. Of the several mechanisms that may lead to Pb-induced decreases in calcium levels the most widely accepted is the interference of Pb with the final metabolism of vitamin D to the active metabolite, calcitriol (1,25-DHCC), a hormone required for adequate calcium absorption.10],24],42] The 19% compared with 4% of the Pb workers and controls respectively with serum calcium levels with 2.0 mm ul/L (8 mg/dl) appears to indicate the magnitude of impairment of calcium metabolism in Pb workers.
Though the mechanism of the reduction of ionized calcium is still not clearly understood it is not unlikely that parathyroid hormone (PTH) which has a more direct effect on ionized calcium was also perturbed by the elevated Pb level. Similarly, although the elevation of inorganic phosphate level is not statistically significant it may be considered as part evidence for a corresponding slightly depressed PTH level. Hyperparathyroidism is associated with phosphaturia resulting in reduced serum phosphate level (hypophosphataemia). Thus the level seen here may represent a case of early or borderline pathology of this endocrine system. Our results therefore, appear to indicate that Pb is an endocrine modulator and thus a candidate for the endocrine disruptors group. Other factors that could have contributed to altered calcium metabolism such as total protein and albumin were not significantly different between Pb workers and controls; excluding these in the pathogenesis of the disorder.
The haematological indices that were decreased in these workers suggesting subclinical or preclinical anaemia is consistent with earlier reports.14],16-18] Though the mechanisms involved are not completely elucidated, elevated blood lead levels are associated with impaired haem synthesis[43-45] this is unlikely to be the explanation in this study as erythrocyte protoporphyrin activity was similar between Pb workers and controls. Additionally, we previously reported in our observations on the haemopoietic system in this cohort that the haembiosynthetic pathway was uninhibited.
Moreover it has also been observed by earlier investigators that in Pb intoxication the absolute depression in haem synthesis is inconsequential and cannot explain the fall in a major haematological index, Hgb.44],45] One of the most likely contributors to this decrement, and the currently most accepted major contributor to this reduction in haematological indices is impaired synthesis of erythropoietin. This glycoprotein hormone regulates both the equilibrium and synthesis of 90% of erythrocytes. It is produced in the proximal renal tubule (PRT)12],13] where lead accumulates. This site coincidentally is also where the important calcium regulating hormone calcitriol (1, 25-(OH)2O3) is synhthesized. A more recent report has demonstrated that EPO is significantly depressed among pregnant women with moderately raised blood lead level. Thus it appears more likely that the decreases in haematological indices reflect gradually decreasing ability to produce EPO. The normocytic normochromic morphology of the erythrocytes in addition to similar serum iron level in our previous report suggest that iron deficiency is excluded.
The significantly raised copper level though may be suggestive of oxidative stress23],47-49] appears to corroborate that iron deficiency anaemia is unlikely, as it rules out inadequate feroxidase activity of copper a contributor to refractory microcytic hyprochromic anaemia as a factor. The significantly lower level of the protoporphyrin degradative product, bilirubin and absence of hyperchromasia in the erythrocyte morphology (which may arise from increased erythropoietic activity, active bone marrow activity or bone marrow hyperplasia) together rule out increased haemolysis as a factor in the decrement of haematological indices. The reduced bilirubin level may however, corroborate the existence of oxidative stress in these lead workers.
It is interesting to note that the bone of which the major mineral is calcium is the major repository of lead, over 90% of the body lead burden is in the bone. Bone metabolism is closely regulated by the combined endocrine activities of calcitoriol and PTH. It has been suggested that bone lead may be a major important biomarker of continuing Pb toxicity than blood lead level. By corollary, an elevated blood lead level suggest a high bone burden. It has also been suggested that the observed association between bone Pb and Pb toxicity might be a reflection of inhibition of haematopoiesis through depression of erythropoietin with bone serving as a proxy for kidney lead. It should also be recalled that though EPO is elaborated by the kidneys it acts in the bone marrow. These observations all point to Pb as an endocrine modulator or endocrine disrupting chemical (EDC) not only of calcium homeostasis but also that regulating both steady - state and increased production of erythropoietin and is consistent with an earlier observation that in acute toxicity, there is rapid red cell destruction followed by active marrow hyperplasia indicating active EPO synthesis (inretrospect). In chronic Pb toxicity on the otherhand, as in occupational exposure in this cohort, EPO is depressed due to chronic renal impairment Consistent with Marrow hypoactivity arising from a gradually decreasing ability of the kidneys to produce EPO. Indeed one of the haematological hallmarks of chronic renal impairment is normocytic normochromia. Thus though EPO was not measured in this study a previous study has shown that serum EPO concentration is depressed at blood Pb level substantially lower than the level in this study. Secondly Hgb is a strong determinant of EPO concentration. High BPb level in this country derives mainly from the hitherto high Pb content of Nigeria's gasoline.
It is worthy of note that high environmental heavy metal concentration including Pb and Cd leads to high PBb in the general population and gradual impairment of calcium metabolism and induces anaemia.[16-18,42] These processes may insidiously develop in unexposed populations. Thus the high Pb level compared to currently acceptable level42],56] may also be associated with subtle endocrinopathies in the general population.
Though most of the reported studies on endocrine disrupting chemicals appear to have concentrated on direct endocrine effects of EDCs, some other mechanisms are recognized. [The mechanism or mode of action of EDCs is not limited to those agents that interact directly with hormone receptors]. Other mechanisms of interest include hormone synthesis, transport, or metabolism and activation of receptors through processes such as receptor phosphorylation or the release of cellular complexes for hormone action.1],2],57] Another feature of EDSs is that their concentrations are magnified through bioaccumulation increasing their potency. The mechanism of disruption of the hormones 1, 25(OH)2D3 and erythropoietin are consistent with some of those of established EDCs. From the foregoing Pb at least in part qualifies to be included in the list of endocrine disruptive substances.
To our knowledge, attention has not been drawn to the endocrine disruptive effect of lead. This study has provided evidence or a reminder that the ancient toxin, Pb is an endocrine disruptive chemical. This is principally through its inhibition of calcitriol and erythropoietin synthesis as a result of the pathological effects of Pb on the proximal renal tabular cells. This leads to a decrease in both calcium levels and haematological indices. parathyroid hormone may also be slightly depressed in these subjects. Though great efforts have been expended in reducing the lead level in the environment this goal is yet to be achieved in most developing countries. Thus for these countries excessive Pb in the environment probably combined with hydrocarbons (HCs),42],58] may be among the most important endocrine disruptors; probably not the bisphenols that need focus.
| References|| |
|1.||Giwercman A, Skakeback NE. The human testis - an oragn at risk. Int J Androl 1992;15:373-5. |
|2.||Danzo BJ. Environmental xenobiotics may distrucpt normal endocrine function by interfering with the binding of physiological ligands to steroid receptor and binding protein. Environ. Health Perspect 1997;105:294-301. [PUBMED] |
|3.||Killington AT. Lead in the working atmosphere and in the environment: Impact of legislation on the use and control of lead within the industry. Chem Indu Str 1983;7:261. |
|4.||Landrigan PJ. Current Issues in the epidemiology and toxicology of occupational exposure to lead. Environ Health Perspect 1990;89:61-6. [PUBMED] |
|5.||Goyer RA. Lead toxicity: Current concerns. Ennvironn Health Perspect 1993;100:177-87. [PUBMED] |
|6.||NRC (National Research Council) (1993). Measuring lead exposure in infants, children and other sensitive populations. National Research Council, Washington, DC. |
|7.||Hu H, Aro A, Payton M. et al. The relationship of bone and blood lead to hypertension JAMA 1996;275:1171-6. |
|8.||Mahaftey HR. Nutrition and lead: Strategies for Public health. Environm. Health Perspect 1995;103:191-6. |
|9.||Sargent JD. The role of nutrition in the prevention of lead poisoning in children. Pediatr Ann 1995;23:636-42. |
|10.||Goyer RA, Rhyne B. Pathological effects of lead. Int Rev Exp Pathol 1973;12:177. |
|11.||Staessen JA, Lauweys RR, Bulpit CJ, Tondia D, Vanretergehmy, et al. Impairment of renal function with increasing blood lead concentrations in the general population. N Engl J Med 327:151-7. |
|12.||Caro J, Ersler AJ. Biologic and immunologic erythropoietin in extracts from hypoxic whole rat kidneys and their glomerular and tubular fractions. J Lab Clin Med 1984;103:922-31. |
|13.||Ersler AJ, Caro J. Physiologic and Molecular biology of erythropoietin. Med Oncol Tumor Pharmcother 1986;3:159-64. |
|14.||Factor-Litvak P, Glaxkovich V, Liu X, Popovac D, Preteni E. et al. Hyperproduction of erythropoietin in nonanemic lead-exposed children. Envrion. Health Perspect 1998;106:361-4. |
|15.||Rosen JF, Chessney RW, Hamstra A, Deluca HF, Mahaftey KR. Reduction in 1, 25-dihydroxyvitamin D in children with increased lead absorption. N Engl J Med 1980;302:1228-31. |
|16.||Aub JC, Fairhall LT, Minot AS, Reznikoff P. Lead poisoning. Medicine 1925;4:1-250. |
|17.||Baker EL, Jr. Landrigan PJ, Barbour AG, Cox DH, Folland DS, Ligo RN, et al. Occupational lead poisoning in the united States: Clinical and Biochemical findings related to blood lead levels. Br J Ind Med 1979;36:314-22. |
|18.||Schwartz J, Landrigan PJ, Baker EL Jr, Orenstein WA, Von-lindern H. Lead-induced anaemia: Dose-response relationships and evidence for a threshold. Am J Public Health 1990;80:169-72. |
|19.||Yamasaki K, Takeyoshi M, Yakabe Y, Sawaki M, Imatanaaka N, Takatsuki M. Comparison of reporter gene assay and immature rat uterotrophic assay of twenty-three chemicals. Toxicology 2002;170:21-30. |
|20.||Takeyoshi M, Yamasaki K, Sawaki M, Makai M, Noda S, Takatsuki M. The efficacy of endocrine disruptor screening tests in detecting anti-estrogenic effects downstream of receptor-ligand interactions. Toxicology Lett 2002;126:91-8. |
|21.||Pirkle JL, Brody EW, Gunter RA, Kramer DC, Pascal KM, Flegal Matti TP. The decline in blood lead levels in the United States. JAMA 1994;272:284-91. |
|22.||Nriagu JO, Blankson ML, Ockran K. Childhood lead poisoning in Africa: A growing public health problem. Sci Total Envrion 1996;181:93-100. |
|23.||Anetor JI, Adeniyi FAA. Lead poisoning in Africa: A silent epidemic African Scientist 2001;1: 249-56. |
|24.||Anetor JI, Adeniyi FAA, Taylor GOL. Biochemical indicators of metabolic poisoning associated with lead-based occupations in nutritionally disadvantaged communities. Afr J Med Sci 1999;28:9-12. |
|25.||Hessel DW. A simple and rapid quantitative determination of lead in blood. Atom Absorpt Newslett 1968;70:50-5. |
|26.||Baginski ES, Maries ES, Clark WI, Zak B. Calcium in biological fluids. Clinichim. Acta 1973;46:49. |
|27.||Mcleans FL, Hastings AB. The state of calcium in the fluids of the body. J Biol Chem 1935;108:285-322. |
|28.||Beeler MF, Catrou PG. Disorders of calcium metabolism. In: Interpretations in Clinical Chemistry: A Textbook Approach to Chemical Pathology. Chicago: American Society of Clinical Pathologist; 1983. p. 34-44. |
|29.||Fiske CH, Subarrow Y. The colorimetric determination of phosphate.J Biol Chem 1925;66:375-400. |
|30.||Martinek RG. Review of methods for determining, inorganic phosphorus in biological fluids. J Am Med Technol 1970;32:337. |
|31.||Doumas BT, Bayse DD. Carter RJ. A candidate reference method protein in serum. Clin Chem 1981;27:1642. |
|32.||Pinnell AE, Northern BE. New automated dye-binding method for serum albumin determination with bromocresol purple. Clin Chem 1978;24:80. |
|33.||BCSH (British Committee for Standards in Haematology). Standard Haematology Practice. Oxford: Blackwell Scientific Publication; 1991. |
|34.||Varley H, Gowenlock AH, Bell M. Porphyrins, haemoglobins, and related compounds. In: Practical Clinical Biochemistry, Vol. 1, 5th Ed. London: William and Heinemann Medical Books; 1980. p. 960. |
|35.||Vanden Bergh AAH, Snapper J. Farben Stffe des blutserums. Disc Urch Klin Med 1913;110:540-1. |
|36.||Rand RN, Dipasqua A. Determination of serum bilirubin. Clin Chem 1962;8:570. |
|37.||Osheim DC. Atomic absorption determination of copper: A collaborative study. J Assoc Off Anal Chem 1983;66:1140-2. |
|38.||Damstra T. Toxicological properties of lead. Envrion. Health Perspect 1977;19:297-07. |
|39.||Anetor JI. Serum uric acid and standardized urinary protein: Reliable bioindicators of lead nephropathy in Nigerian lead workers. Afr J Biomed Res 2002:5;19-24. |
|40.||Graziano JH, Glavkovich V, Factor-litvak P. Depressed serum erythropoietin in pregnant women with elevated blood lead. Arch Environ Health 1991;46:347-50. |
|41.||Long GJ, Rosen JF, Lead perturbs 1, 25-ditrydroxy vitamin D3 modulation of intracellular calcium metabolism in clonal rat osteoblastic (ROS 17/12.8) Cells Life Sci 1994;54:1395-402. |
|42.||Anetor JI. The probable situation of endocrine disruption in the highly polluted Nigerian environment. (Abstract). In: Scientific Committee on Problems of the environment (SCOPE) / International union of Pare and Applied Chemistry IUPAC International Symposium on Problem on Endocrine Disruptive Substances. Yokohama, Japan: Book of collective abstract and programme; 2002. p. 67-8. |
|43.||Litchman HC, Feldman FC. In vitro pyrrol and porphyrin synthesis in lead poisoning and iron deficiency. J Clin Invest 1963;42:830-9. |
|44.||Piomelli S, Lamola AA, Poh-Fitzpatrick MB, Seaman C, Harber LC. Erythroopoietic protoporphyria and lead intoxication: The molecular basis for difference in cutaneous photosensitivity. 1. Difference rates of disappearance of protoporphyrin from the erythrocytes, both in vivo and vitro. J Clin Invest 1975;56:1519-27. |
|45.||Piomelli S, Seaman C, Zullow D, Curran A, Daviddow B. Threshold for lead damage to heme synthesis in urban children. USA: Proc Natl Acad Sci; 1982;79:3335-9. |
|46.||Brunette MC, Chan M, Ferriere C, Robers K. Site of 1,25(OH)2D3 synthesis in the kidney. Nature 1978;276:287-9. |
|47.||Autor AL. Pathology of oxygen. New York: Academic Press; 1982. p. 361. |
|48.||Monteiro HF, Abdalla DSP, Arcuri AS, Bechara EJC. Oxygen toxicity related to exposure to lead. Clin Chem 1985;31:1673-6. |
|49.||Costa CA, Trivelato GC, Pinto AMP, Biechara EJN. Correlation between Plasma 5-aminolevulinic acid concentrations and indicators of oxidative stress in lead-exposed workers. Clin Chem 1997;43:1196-202. |
|50.||Stocker R, Yamamoto Y, Mendonagen AF. Bilirubin as an antioxidant of possible physiological importance. Science 1987;235:1045-6. |
|51.||Silbergeld EK. Lead in bone: Implications for toxicology during pregnancy and lactation. Environ Health Perspect 1991;9:63-70. |
|52.||Hu H, Watanabe H, Payton M, Korrick S. Rotnitzky A. The relationship between bone lead and haemoglobin. JAMA 1994;272:1512-7. |
|53.||Griggs RC. Lead poisoning: Haematologic aspects. Prog Hematol 1964;4:117-37. |
|54.||Anetor JI. High blood lead levels in the general Nigerian population: Causes and implications. In working paper No.6: Clean Air Initiative in Sub-Saharan African Cities - National Conference on the Phase - out of leaded Gasoline in Nigeria, Abuja, Nigeria, November 15-16 proceedings (November 2001). Wastington DC, USA: The World Bank; 2001. p. 27-37. |
|55.||Staessen JA, Amery A, Benard T, et al. Effect of exposure to cadmium on callium metabolism: A population study. Brit J Ind Med 1991;48:710-4. |
|56.||WHO (World Health Organization). WHO Air quality Guidelines for Europe 2nd Ed. Copenhagen, Denmark: WHO; 2000. |
|57.||Damstra T, Barlow S, Bergman A, Kaylock R, Kraak GVD, editors. Global Assessment of the state-of-the science of Endocrine Disruptors. Geneva, Switzerland: World Health Organisation; 2002. |
|58.||Reutman SR, Lemasters GK, Knetch EA, Shukla R, Lockey JE, Burraughs GE, et al. Evidence of reproductive endocrine effects in women with occupational fuel and solvent exposures. Environ Health Perspect 2002;110:805-11. |
[Table - 1], [Table - 2]
|This article has been cited by|
||Relationship Between Blood Lead Levels and Hematological Indices in Pregnant Women
| ||Osmel La-Llave-León,Rodrigo Lugo-Soto,Marisela Aguilar-Durán,Sergio Estrada-Martínez,José-Manuel Salas-Pacheco,Ada Sandoval-Carrillo,Francisco Xavier Castellanos-Juárez,Marcel Barraza-Salas,Fernando Vázquez-Alanís,Gonzalo García-Vargas |
| ||Women & Health. 2015; 55(1): 90 |
|[Pubmed] | [DOI]|
||Biochemical effects of lead exposure on battery manufacture workers with reference to blood pressure, calcium metabolism and bone mineral density
| ||Dongre, N.N. and Suryakar, A.N. and Patil, A.J. and Hundekari, I.A. and Devarnavadagi, B.B. |
| ||Indian Journal of Clinical Biochemistry. 2013; 28(1): 65-70 |
||Effect of lead toxicity on cytogenisity, biochemical constituents and tissue residue with protective role of activated charcoal and casein in male rats
| ||Azoz, H.A. and Raafat, R.M. |
| ||Australian Journal of Basic and Applied Sciences. 2012; 6(7): 497-509 |
||Effects of gasoline engine emissions on health status of auto rickshaw drivers at DIR (L) Khyber Pukhtunkhwa
| ||Sami Ullah, Ayaz Ali Khan, Mir Azam Khan, Iltaf Ahmed |
| ||Toxicological and Environmental Chemistry. 2011; : 1 |
|[VIEW] | [DOI]|
||Influence of soil chemistry on metal and bioessential element concentrations in nymphal and adult periodical cicadas (Magicicada spp.)
| ||Robinson Jr., G.R., Sibrell, P.L., Boughton, C.J., Yang, L.H. |
| ||Science of the Total Environment. 2007; 374(2-3): 367-378 |
||Influence of soil chemistry on metal and bioessential element concentrations in nymphal and adult periodical cicadas (Magicicada spp.)
| ||G.R. Robinson,P.L. Sibrell,C.J. Boughton,L.H. Yang |
| ||Science of The Total Environment. 2007; 374(2-3): 367 |
|[Pubmed] | [DOI]|