Lead is a persistent toxic metal and associated with impairment of various body functions in occupational workers. The main objective was to determine the lead-induced oxidative stress and adverse health effects by biochemical markers in industrial workers. One hundred and forty-eight males consisting of 87 lead-exposed industrial workers and 61 controls were included. Blood lead level (BLL) was determined on a 3010B ESA lead analyzer. Blood complete counts were done on a hematology analyzer. Biochemical markers including serum uric acid, urea, creatinine, phosphate, alanine aminotransferase (ALT), and gamma glutamyltransferase (GGT) were measured on a Selectra E auto analyzer. Serum malondialdehyde (MDA) was measured spectrophotometrically and C-reactive protein (CRP) on Immulite-1000. Results revealed that lead-exposed workers had significantly high BLLs, median (range), 29.1 (9.0-61.1) microg/dL compared with controls, 8.3 (1.0-21.7) microg/dL. Oxidative stress (MDA, GGT) and inflammatory markers (high-sensitivity CRP) were significantly increased (P < or = 0.05). Blood pressure was raised, whereas hemoglobin was decreased in exposed group (P < or = 0.002). Serum urea, uric acid, phosphate, and ALT were significantly raised in lead-exposed workers (P < or = 0.001). Serum albumin, total proteins, and glomerular filtration rate (GFR) were decreased. Blood lead showed a significant positive correlation with serum GGT (r = 0.63), MDA (r = 0.71), CRP (r = 0.75), urea (r = 0.34), creatinine (r = 0.51), and uric acid (r = 0.29) (P < or = 0.01). It is concluded that lead exposure increases oxidative stress that correlates with adverse changes in hematological, renal, and hepatic function in the occupational workers. Elevated blood lead has positive correlation with oxidative stress, inflammatory and biochemical markers that might be used to detect impairment in the body function in lead exposed workers.
Lead exposure is an important environmental health problem particularly affecting the children of occupational workers living in the lead-contaminated environment. The objectives of the study were to find out the frequency, potential sources and adverse health effects of elevated blood lead level (BLL) in the children of lead-related occupational workers. It was a comparative cross-sectional study. A total of two hundred forty six children aged 1-6 years, comprising an equal number (n = 123) from lead smelters/battery recycle plant workers living close to the industries at Wah/Gujranwala, Pakistan (lead-exposed group) and those living 30 km away from the industrial area (controls) were included. Demographic and clinical data of each subject was collected. Blood lead analysis was carried out by using kits on the lead analyzer (3010 B ESA, USA). Biochemical tests of renal and hepatic profile were analyzed on Selectra E auto analyzer. The median age of children was 4 years; comprising of 69 boys and 54 girls. The lead-exposed children had significantly high BLLs median (range) 8.1 (1-20.9) microg/dL as compared to controls 6.7 (1-13.3) microg/dL (p
A B S T R A C TSources of radioactivity in the aquatic environment include naturally occurring radionuclides, fallout from the atmospheric and radioactive effluent from nuclear facilities that was released either accidentally or routinely. Depending upon the element and the chemical form, radionuclides may accumulate in bottom sediment or remain in the water column in the dissolved state. Marine organisms receive external radiation exposure from radionuclides in water and sediment. Radiological risk assessment was made for marine fish that are exposed to 137 Cs, 226 Ra, 228 Ra and 40 K along Manora channel Karachi coast of Pakistan using ERICA tool software. The ERICA tool is a software system that has a structure based upon the tiered ERICA integrated approach to assessing the radiological risk to terrestrial, freshwater and marine biota. The results were calculated using Tier 1 and Tier II assessments which are based on media concentration and use pre-calculated environmental media concentration limits to estimate risk quotients. If the sum of the risk quotients is <1, then it can be assured that there is a very low probability that the assessment dose rate to any organism exceeds the incremental screening dose rate and therefore the risk to non-human biota can be considered negligible. Risk quotient in this study is far below 1 which reveals that there is no evidence of deleterious effect of radionuclide for marine biota of the area under study.
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