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Biomonitoring of the toxicity of some heavy metals in occupationally exposed workers in nigeria

 

Table Of Contents


Thesis Abstract

Abstract
Occupational exposure to heavy metals poses a significant risk to human health, particularly in developing countries like Nigeria where regulatory measures may be less stringent. This study aimed to conduct biomonitoring of the toxicity of selected heavy metals in occupationally exposed workers in Nigeria. The heavy metals of interest included lead, cadmium, mercury, and arsenic, known for their adverse health effects even at low levels of exposure. A total of 200 workers from various industries, including mining, battery manufacturing, and recycling, were recruited for the study. Biological samples such as blood, urine, and hair were collected from the participants to assess the levels of heavy metals. Inductively Coupled Plasma Mass Spectrometry (ICP-MS) was used for the quantitative analysis of heavy metal concentrations in the collected samples. The results revealed elevated levels of lead, cadmium, and mercury in the biological samples of the exposed workers compared to the control group. Arsenic levels were within acceptable limits, possibly due to lower exposure in the selected industries. These findings indicate a potential health risk to the workers due to chronic exposure to heavy metals in their occupational settings. Furthermore, the study explored the correlation between heavy metal exposure and biomarkers of toxicity. Biomarkers such as blood lead levels, urinary cadmium concentrations, and hair mercury levels were significantly higher in the exposed workers compared to non-exposed individuals. These biomarkers serve as indicators of internal exposure and can help in assessing the health effects of heavy metal toxicity over time. In conclusion, the biomonitoring of heavy metal toxicity in occupationally exposed workers in Nigeria highlights the need for stringent occupational health and safety measures to protect workers from the adverse effects of heavy metal exposure. Regular monitoring of heavy metal levels in biological samples, along with implementing control measures to reduce exposure, is crucial in safeguarding the health of workers in high-risk industries. This study provides valuable data for policymakers, occupational health professionals, and industries to develop effective strategies for mitigating heavy metal exposure and ensuring a safe working environment for all employees.

Thesis Overview


INTRODUCTION

Background of study.

Heavy metals pose serious health challenges especially among occupationally exposed workers. Work has it’s positive health promoting effects, as the financial benefits provides the worker with the basic necessities of life. There is however a reciprocal and interactive relationship between the workers and the work environment.

Occupational hazard is the risk, harm or danger that an individual is exposed to at the workplace, whereas occupational diseases result from such exposures to the individual (WHO, 1986). Although these occupational diseases appear less frequently, there is evidence that they affect a considerable number of people particularly in rapidly industrializing countries.

Thousands of toxic chemicals pose serious health hazard, potentially causing cancer, respiratory and skin disease as well as adverse effects on the reproductive function and around 350 chemical substances have been identified as occupational carcinogens (WHO, 2000).

Heavy metals are natural components of the earth’s crust. These elements are the oldest toxins known to humans, having been used for thousands of years. They are group of environmental chemicals which are ubiquitous and non-biodegradable. Many different definitions of heavy metals have been proposed. One of such definitions entails that heavy metals are defined as metallic elements that have a relatively high density compared to water (Fergusson, 1990). Due to increase in automobiles and urbanization in towns and cities in the world, there is an exponential increase in exposure to toxicants which include heavy metals, solvents and vehicles exhaust, gasoline, paints, dust and silica exposure from sundry, sand blasting etc. Heavy metals are significant environmental pollutants and their toxicity is a problem of increasing significance for ecological, evolutionally, nutritional and environmental reasons (Jaishankar, Mathew, Shah, & Gowda, 2014; Nagajyoti , Lee, & Sreekanth, 2010).

These metals are essential to maintain various biochemical and physiological functions in living organism, when in very low concentrations; however they become noxious when they exceed certain threshold concentrations. Although these metals have crucial biological functions in plants and animals, sometimes their chemical coordination and oxidation-reduction properties have given them an additional benefit so that they can escape control mechanisms such as homeostasis, transport, compartmentalization and binding to required cell constituents. They displace original metals from their binding sites causing malfunctioning of cells and ultimately toxicity. Previous research has found that oxidative deterioration of biological macromolecules is primarily due to binding of heavy metals to the DNA and nuclear proteins (Flora, Mittal & Mehta, 2008).

Among workers occupationally exposed to heavy metals include: automobile technicians otherwise known as mechanics. They are made up of spray painters, welders, panel beaters and brake and clutch liners etc. Those in the automobile repairs industry constitute a significant number of those practicing vocational trade in Nigeria (Anyadike, Emeh, & Ukah, 2012). One of the many hazardous habits automobile technicians engage in include sucking of fuel (Oluwagbemi,

2007; Anetor, Babalola, Adeniyi, & Akingbola, 2002; Landrigan, 1989); washing of hands and vehicle parts with gasoline (Oluwagbeni, 2007; Udonwa, Uko, Ikpeme, Ibanga & Okon, 2009) and applying diesel to bruised body parts (Omokhodion, 1999).

TOXICITY MECHANISMS OF HEAVY METALS AND IT’S INDUCED DISEASE PATHOPHYSIOLOGY.

Although several heavy metals, including copper (Cu) and zinc (Zn), serve as enzymes that are essential for intracellular processes and have DNA-binding domains, almost all heavy metals induce various cancers and diseases (Fergusson, 1990; Stern, 2010; Hambidge & Kreb, 2007). Oxidative stress caused by reactive oxygen species (ROS) is a well-known mechanism of heavy metal-induced damages (Bánfalvi, 2011). Despite such serious toxicity, heavy metals are utilized in various industrial products. They are found in batteries, paints, and vehicle emissions. Furthermore, heavy metals are used in pigments that are then used in consumer products like children’s jewelry and toys (Finch, Hillyer, & Leopold, 2015). Electronic waste from heavy metal-containing batteries is an important source of heavy metal contamination in the environment through erosion by rain and groundwater flow to soil, rivers and the sea (Worsztynowicz & Miller,1995). Dissolved forms of toxic heavy metals can be magnified via circulation in the bio-system, including the food chain, and finally end up in very high concentrations in humans ( Bánfalvi, 2011; Tchounwou, Yedjou, Patlolla, & Sutton, 2012).

Arsenic (As), cadmium (Cd), chromium (Cr), and nickel (Ni) are category 1 heavy metals according to the International Agency for Research on Cancer (IARC, 2012). Various reports have found that exposure to these compounds leads to disruptions in tumor suppressor gene expression, damage repair processes, and enzymatic activities concerned in metabolism via oxidative damage (Ercal, Gurer-Orhan & Aykin-Burns, 2001; Bánfalvi G, 2011). Some studies have indicated that the risk of heavy metal exposure is interrelated with the contamination source (Harvey, Handley & Taylor, 2015; Gul, Shah, Khan, Khattak, & Muhammad, 2015). For example, recent studies found an increased risk of occupational disease and cancer in workers in heavy metal-using industrial areas (Grimsrud & Anderson, 2012; Grimsrud, Berge, Martinsen, & Anderson, 2003).

MERCURY

CADMIUM ALUMINUM

ARSENIC

APOPTOSIS

IRON NICKEL

CHROMIUM LEAD

The attack of heavy metals on a cell and the balance between

ROS production and the subsequent defense presented by antioxidants.

The attack of heavy metals on a cell and the balance between

ROS production and the subsequent defense presented by antioxidants.

Production of ROS

O2., OH, NO., RO.,

ONOO., H2O2

Resulting in

oxidative stress

SOD, GSH, GST,

CATALASE

Defense by anti oxidants

CADMIUM (Cd)

SOURCES AND ROUTE OF EXPOSURE.

Cadmium is rare in the natural environment. It generally comes from environmental pollution from industrial and agricultural waste. Cadmium poisoning is an occupational hazard associated with industrial processes such as metal plating, production of nickel-cadmium batteries, pigments, plastics, and other synthetics. In addition, it is a component of paint for car spraying, plastic products, acrylic colors, and watercolor pigments (Kawasaki, Kono, Dote, Usuda, Shimizu, and Dote, 2004).

In agriculture, some fertilizers which contain Cd cause an increase of Cd concentration in the soil, and farmland near industrial areas becomes contaminated. The main sources of exposure to cadmium are specific professional atmospheres, diet, drinking water, and tobacco. The primary route of exposure in industrial settings is inhalation of cadmium-containing fumes which can result initially in metal fume fever but may progress to clinical pneumonitis, pulmonary edema, and death. Cadmium possessing a long biological half-life (17–30 years) in humans accumulates primarily in liver and kidney (Shimada, Yasutake, & Hirashima, 2008). This long half-life of Cd is mainly due to its low ratio of excretion and its continued accumulation in the organism.

MECHANISM OF TOXICITY AND PATHOPHYSIOLOGY.

The main mechanism of toxicity of cadmium is by oxidative stress. Cd2+ being a non-redox-active metal cannot initiate by itself the Fenton reactions. However, it may generate non-radical hydrogen peroxide, which may become a source of free radical via the Fenton reaction. It therefore induces oxidative stress through indirect processes. Some of the mechanisms through which Cd induces the formation of ROS include the following:

(1) Decrease in the intracellular GSH content,

(2) Cd combines with thiol groups of enzymes involved in antioxidant mechanisms, such as SOD, glutathione peroxidase (GPx), and catalase, and inhibits their activities ,

(3) Cd forms cadmium-selenium complexes in the active centre of GPx and inhibits the enzyme activity, and

(4) Cd inhibits complex III of the mitochondrial electronic transport chain and increases production of ROS which may damage mitochondrial membrane and trigger onset of apoptosis.

These cadmium induced oxidative stress are possibly involved in causing DNA damage / mutations, oxidation of proteins and lipid peroxidation , which may cause alterations in lipid composition of cellular membranes and functions.

Oxidative stress following Cd exposure accelerates transcriptional activity of the metallothionein (MT) coding gene (Andrews, 2000). MT is a ubiquitous protein in most organs. It can form a complex with metal elements such as Cd. When chronic Cd exposure occurs, a complex form of Cd and MT called Cd-MT is found, especially in the kidney. It accumulates in tubules via a reuptake process and causes conformational change of renal tubular cell as well as degradation of glomerular cell function. These functional problems disrupt calcium metabolism and augment the calcium load in the kidney, thereby resulting in an increase of kidney stones and cancer. Moreover, disruption of calcium metabolism causes bone damage (Nordberg, Goyer, & Nordberg, 1975).

Taking into account the effect of Cd on the central nervous system (CNS) and endocrine system, it is currently classified as an endocrine/neuroendocrine disruptor (Henson & Chedrese, 2004; Retto, deQueiroz, & Waissmann, 2006). It disrupts the ovarian steroidogenic pathway, production of progesterone and testosterone, and mimics endogenous estrogen, thus increasing the risk of ovarian cancer and breast cancer (Yang, Kim, Weon, & Seo, 2015)

Clinical Symptoms.

People chronically exposed to cadmium have headache, sleep disorders, and memory deficits. These diseases are related to alterations in neurotransmitters (GABA, serotonin) by altering GABAergic and serotoninergic systems. Other symptoms include increased salivation, choking, throat dryness, cough, chest pain, restlessness, irritability, nausea, vomiting, kidney dysfunction (glucosuria, proteinuria, and aminoaciduria), itai-itai disease, and renal and hepatic failures. Pulmonary involvement includes pneumonitis, edema, and bronchopneumonia. Permanent lung damage and cardiovascular collapse may occur. Lung and prostate are the primary targets for the Cd induced cancer.

Values of cadmium toxicity (Flora et al., 2008).

Cadmium toxicity Decreases the concentration of copper in liver and plasma and also reduces the concentration of ceruloplasmin in plasma Cadmium disturbs zinc metabolism, inhibits the enzymes containing Zn, competes for gastrointestinal absorption and replaces zinc present in metallothionein Interacts with iron and decreases the hemoglobin and hematocrit concentration, leads to anemia Cadmium interacts with calcium and leads to osteoporosis, cadmium deposition in bones, hypercalciuria Cadmium causes a disruption of neuroendocrine hormones. This gives it a significant role in cancer development. Oxidation of proteins and lipid preoxidation, leading to alteration in cell membrane composition and functions.


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