Abstract
Heavy metals (HMs) contamination significantly threatens plants, animals, aquatic ecosystems, and public health. HMs’ accumulation in aquatic environments has become a serious environmental issue due to their high stability, bioaccumulation, and biomagnification properties. These metals enter ecosystems through both natural sources and/or human activities. The toxicity of HMs poses a threat to the aquaculture sector’s sustainability by negatively affecting fish growth, reproduction, and overall physiology. Exposure to HMs in various forms can cause environmental damage, which may affect human health through direct poisoning symptoms or other adverse effects. One such effect is the increased production of reactive oxygen species (ROS), crucial metabolites that modulate the functions of pathogenic organisms and lead to oxidative stress. This, in turn, can contribute to the onset and exacerbation of numerous diseases that threaten human health. This review article examines the potential sources of HMs contamination in aquatic organisms, the impact of this contamination on the generation of ROS, and the implications for human health resulting from the consumption of contaminated aquatic products.
1 Introduction
Heavy metals (HMs) are a group of elements characterized by their high density, generally exceeding 5,000 kg/m3 (), which is at least five times greater than the density of water (). This group primarily consists of transition metals, along with some metalloids, actinides, and lanthanides (Shahid et al., 2014). HMs are classified as trace elements due to their presence in trace concentrations (< 10 ppm) in various environmental matrices (Tchounwou et al., 2012). Some HMs, such as copper (Cu), iron (Fe), cobalt (Co), zinc (Zn), molybdenum (Mo), nickel (Ni), manganese (Mn), vanadium (V) and selenium (Se), play crucial roles in biological functions. However, elevated concentrations of these metals can become toxic, causing damage to living organisms’ cells (Munir et al., 2021; ). Conversely, several other HMs, including cadmium (Cd), arsenic (As), lead (Pb), mercury (Hg), and chromium (Cr), are not essential for biological systems and exhibit toxicity even at low concentrations, primarily due to their non-biodegradable nature (Mitra et al., 2022). The degree of HMs toxicity generally varies depending on the metal concentration, as shown in Table 1. Additionally, Co metal is a component of vitamin B12, and increasing its concentrations to >700 µg/L can cause toxic health effects (Leyssens et al., 2017). On the other hand, the toxicity of Se varies depending on its chemical form, with inorganic forms being more poisonous than organic ones (). However, increasing the daily dose of Se beyond 400 µg can lead to toxic effects (Misra et al., 2015). Although Mo toxicity is relatively low in humans, prolonged exposure to daily doses over 2 mg can lead to serious health consequences (Novotny and Peterson, 2018).
Table 1
| Heavy metal | Cut-off point in blood | Reference |
|---|---|---|
| Copper | 1495 μg/L | () |
| Nickel | 2.62 μg/L | () |
| Cadmium | 0.15 μg/L | () |
| Iron | 40 μmol/L | (Kontoghiorghes, 2023) |
| Lead | 10 μg/dL | () |
| Chromium | 1.86 μg/L | () |
| Mercury | 4.11 μg/L | (Lee et al., 2017) |
| Zinc | 5234 μg/L | () |
| Manganese | 18.3 μg/L | () |
| Arsenic | 3.12 μg/L | () |
The cut-off value of blood HMs concentration concerning toxicity.
Although HMs are naturally present in the environment, their overuse in many industries for various purposes has drastically changed the ecological system by releasing excessive HMs into the soil and aquatic systems (). In aquatic ecosystems, both water and sediments can contain HMs that can contaminate aquatic organisms. Therefore, this contamination poses a serious threat to associated aquatic fauna, particularly fish (Taslima et al., 2022). After entering aquatic systems, HMs dissolve in the water and readily accumulate in the various organs of organisms before moving to the bodies of human consumers (). HMs that are bioaccumulative, non-biodegradable, and have a lengthy persistence period can concentrate within the food chain and have toxic effects at locations distant from the original source of pollution (Wahiduzzaman et al., 2022; Wang et al., 2022). Toxicity triggered by HMs in fish involves several aspects; however, each metal has different effects, leading to distinct toxicological symptoms. Toxic HMs in dissolved form can accumulate through circulation in aquatic organisms (Tchounwou et al., 2012), causing several complications to their health and physiological function. As a result, toxic HMs are transmitted into the food chain and eventually reach high concentrations in the human body, posing a serious threat to public health (). These metals cause the oxidative degradation of biomolecules (DNA, proteins, and lipids) by generating free radicals (; Kumar et al., 2023).
One of the mechanisms by which HMs damage tissues is through the generation of reactive oxygen species (ROS) and the induction of oxidative stress in organisms exposed to this type of pollution (; Rady et al., 2023). Furthermore, ROS are important mediators of metal-induced cellular responses and cancer development (Wang and Shi, 2001; Wang et al., 2021c). Disruptions in ROS equilibrium have also been observed in various diseases, and recent studies have suggested a dual role for ROS in carcinogenesis and the immune response in tumors (Yu et al., 2024). Considering this, there is a growing interest in investigating the effects of HMs in aquatic ecosystems since small quantities can be toxic to both aquatic organisms and humans (Kumar et al., 2023). Nevertheless, there are insufficient studies that demonstrate how consuming fish contaminated with HMs directly affects human organs. Specifically, more research is needed to accurately track the types and concentrations of HMs in fish, as well as their absorption rates in the human body, to better understand the implications of this pollution on public health. This review article examines the contamination of fish with HMs and the effect of this contamination on the generation of ROS in aquatic organisms, as well as the repercussions on human health.
2 HMs pollution sources
HMs are naturally occurring elements that can be transported through both natural phenomena and/or human activities, causing pollution in various habitats (Kumar et al., 2023). The Earth’s crust is the primary source of HMs in the environment (). Subsequently, natural phenomena and conditions such as weathering, rocks erosion, ore deposits (Muhammad et al., 2011), dust storms (Soleimani-Sardo et al., 2023), volcanic activities, sediment resuspension, spring waters (; ), forest fires, and biogenic processes (Zaynab et al., 2022) play a crucial role in extracting and transporting HMs to different ecosystems (; ). Human interventions are the primary cause of HMs contamination and its transmission (Kumar et al., 2023). Key sources include industrial activities such as battery production, mining, pigment manufacturing (yellow Cd), and plastic production (Muhammad et al., 2011; ). Agricultural practices, including the use of sewage water for irrigation, pesticides, and fertilizers, also contribute significantly to this issue (Srivastava et al., 2018; Kumar et al., 2023). Other sources include fuel combustion (e.g., tetraethyl lead), automobile exhaust, tanneries, electroplating, uranium mining, petrochemical spills, and sewage sludge ().
HMs enter aquatic environments through various pathways, including flooding, erosion, leaching, and direct human activities such as industrial effluents and municipal waste disposal. Pollution from crude oil exploration also leads to increased HM levels in water bodies (Figure 1). A substantial amount of industrial activity occurs in coastal areas, leading to the release of various chemical effluents into these environments (). Furthermore, metals released from industrial facilities can be transported over long distances via wet or dry deposition (Shahid et al., 2013).
Figure 1
Once in the environment, HMs are transported to natural streams and rivers via household, industrial, or agricultural waste, making aquatic ecosystems the final destination for HMs pollution (Kumar et al., 2023). Intentional discharges of industrial waste and other pollutants into rivers, seas, and oceans further exacerbate the contamination of aquatic habitats, leading to ecological degradation and endangering aquatic life (; Shahjahan et al., 2022). Thus, one of the most serious environmental concerns affecting humans, animals, plants, and ecosystem safety is HMs contamination of water (Wang et al., 2021a; Zaynab et al., 2022). The indiscriminate release of these pollutants into the environment without appropriate treatment poses a severe threat to the existence of living organisms. Figure 1 depicts the main sources of HMs pollution originating from natural phenomena and human activities. Anthropogenic, such as those mentioned previously, can redistribute HMs pollutants across different environmental matrices including the aquatic environment. For example, crude oil exploration can be a potential source of HMs contamination in some aquatic environments, as HMs are components of crude oil, excavated earth layers, and the drilling fluids used (; Umeoguaju et al., 2023). Some studies have indicated that the areas surrounding crude oil exploration locations are polluted with high levels of HMs (). Another major source of environmental HM contamination is waste containing HMs, such as electronic waste. Natural conditions, like erosion, can transport this waste into the soil and then into rivers and seas due to rain and the flow of groundwater ().
3 Fish contamination with HMs
Fish are among the most extensively spread species in aquatic environments, making them more susceptible to HMs. HMs contamination of the aquatic ecosystem is one of the greatest environmental concerns due to its negative impact on both ecosystems and human health (; Wahiduzzaman et al., 2022). Therefore, this type of pollution is one of the most prominent problems threatening water quality worldwide. The extent of HM’s toxicity to aquatic organisms varies according to their properties and the characteristics of the water source in which they live (). Since HMs are non-biodegradable, they can cause toxicity in fish and other aquatic faunal communities, which can continue to be harmful indefinitely (Taslima et al., 2022). Due to these properties, HMs are deposited, assimilated, or incorporated into water and sediments of the aquatic ecosystems ().
In the aquatic ecosystem, fish are hypersensitive to environmental conditions, which make them useful bioindicators for environmental monitoring, as they can easily metabolize, detoxify, and accumulate HMs in their bodies (Shahjahan et al., 2022). Aquatic organisms are adversely affected by heavy metal-mediated toxicity, which negatively impacts their interaction with their surroundings (). Aquatic organisms can acquire metals by ingesting particulate matter suspended in water, ingesting contaminated food, exchanging ions across lipophilic membranes such as gills, and adsorbing them on tissues and membrane surfaces (). The aquatic environment’s acidity may also facilitate the absorption of free divalent ions of different HMs through fish gills (Naz et al., 2023). In some fish species, toxic chemicals are rapidly absorbed through the gills, where HMs can accumulate in the gills due to their large surface area and less effective detoxification system compared to the liver (). Aquatic organisms can ingest HMs at low concentrations through water uptake, and these concentrations can increase during biomagnification process (). Both bioaccumulation (the accumulation of pollutants in an organism’s tissues over its lifetime) and biomagnification (the increasing concentration of pollutants at higher trophic levels) of HMs can have severe biological effects. Consequently, HMs concentrations in large aquatic organisms usually increase with the organism’s size/age (i.e. bioaccumulation) and in higher trophic levels (i.e. biomagnification), meaning that top predators, large and long-living organisms are most affected by HMs ().
Aquatic organisms can absorb these metals through the skin, gills, or the digestive system (contaminated food), allowing HMs to move through the bloodstream to the various organs (), such as the liver, where biotransformation occurs (). HMs can also be absorbed through the osmoregulation process, which is an essential physiological function, leading to similar toxic effects (). Large amounts of HMs may accumulate in fish tissues such as muscles, gills, intestines, liver, and kidneys depending on metal concentrations, exposure duration, and other environmental factors like temperature, salinity, pH, and metal hardness (). The uptake of HMs in fish gills indicates their presence in aquatic systems, while accumulation in the liver reflects the deposition of these metals, which is influenced by the fish’s size, sex, age, feeding behaviors, and living environment (Kumar et al., 2023). Additionally, the uptake process of HMs in the liver is associated with its metabolic functions (Zhao et al., 2012).
The presence of HMs in aquatic environments exposes fish and other organisms to oxidative stress due to their ability to undergo redox cycles. These HMs can interact with biological particles that contain sulfur, nitrogen, oxygen, and other elements, which affect or alter the structures and functions of enzymes, proteins, hormones, and other substances, thus ultimately leading to damage in fish tissues and organs (Shahjahan et al., 2022).
HMs toxicity in fish can cause various physiological and biochemical changes, including reduced growth and reproductive activity, as indicated by lower gonad somatic index (GSI), fecundity, fertilization, and hatching rates (). Some HMs can also exhibit carcinogenic (Kortei et al., 2020) and mutagenic () properties in aquatic organisms, including fish. They can cause structural damage, functional and biochemical disorders, oxidative stress, genotoxicity, as well as fatal pathology in the liver, kidneys, and reproductive, respiratory, and nervous systems (). HMs can also affect the blood’s ability to carry oxygen by altering the hemoglobin (Hb), hematocrit (Hct), and red blood cells (RBCs) values in various ways, depending on the fish species, metal type, and exposure duration (). Numerous studies have assessed and analyzed the risk of HMs contamination in various rivers, seas, and lakes, with high concentrations reported in the Gulf of Guinea (Nyarko et al., 2023), Buriganga river (), Buriganga and Turag rivers (), Thamirabarani river (), Dhaleswari river (Wahiduzzaman et al., 2022), Ganga river (Siddiqui et al., 2019), Turag-Tongi-Balu river channel (), Amazon river estuary (Viana et al., 2023), Brazilian amazon (), the Niger Delta region of Nigeria (Umeoguaju et al., 2022), Bardawil lake (), and Caspian sea (). Additionally, the concentrations of many HMs were found to be significantly higher in polluted sites in the Red Sea compared to unpolluted reference sites ().
4 Reactive oxygen species
Molecular oxygen has two unpaired electrons with parallel spins in its outer valence shell, which makes it unable to react with most organic molecules directly. Instead, the most prevalent mechanism of oxygen reduction involves stepwise single-electron transfers that produce free radicals (Magnani and Mattevi, 2019). These free radicals are unstable molecules resulting from oxidative stress (Kumar et al., 2023). ROS are bioactive molecules that are natural byproducts of a series of reactions originating from the metabolism of cellular oxygen (; Nakamura and Takada, 2021). These ROS are naturally produced due to the transfer of electrons to oxygen on the inner mitochondrial membrane (Parvez et al., 2018; Rauf et al., 2024). This term refers to all highly reactive oxygen derivatives (O2) that participate in cellular electrons (; ).
Aerobic organisms continuously generate ROS, such as superoxide radicals (O2•−), hydroxyl radical (•OH), and hydrogen peroxide (H2O2) (). ROS are produced during oxidative metabolism and function as cell signaling molecules (Wang et al., 2021c). The generation of ROS, which is essential for many signaling pathways, is mediated by mitochondrial respiration (), and numerous physiological and biochemical activities in cells (Mansoor et al., 2023). Therefore, mitochondria are regarded as the most significant cellular ROS generators due to their continuous activity throughout metabolism (). The adenosine triphosphate (ATP) generation from oxygen and simple carbohydrates is facilitated by this process, which is integral to oxidative phosphorylation (Li et al., 2013). Five pivotal protein complexes are involved in this complex process: complex I is nicotinamide adenine dinucleotide (NAD) + hydrogen (H) (NADH); complex II is succinate; complex III is ubiquinol; complex IV is cytochrome c oxidase; and complex V is F1F0-ATP synthase (Yu et al., 2024). These complexes produce superoxide (O2•–) due to electron leakage. Afterward, superoxide is converted into H2O2 in intermembrane space by the enzyme superoxide dismutase 1 (SOD1) (Li et al., 2013). Additionally, a subgroup of ROS is generated by nicotinamide adenine dinucleotide phosphate (NADPH) oxidases (NOX) as a transmembrane protein family. These enzymes transport electrons across biological membranes and catalyze the conversion of oxygen into superoxide. The catalytic subunit NOX2 plays a significant role in this process (). During the metabolic processes, the peroxisome catabolizes biomolecules using some enzymes to remove hydrogen in an oxidative reaction, creating ROS such as hydrogen peroxide as a metabolic byproduct ().
Low to medium levels of these species are essential for maintaining the oxidation-reduction equilibrium and numerous necessary physiological functions, including regulating blood pressure and cognitive and immune functions (). However, the overproduction of ROS can disrupt oxidation-reduction equilibrium, leading to oxidative stress. This damage can irreparably harm cell structures, resulting in apoptosis and necrosis due to the oxidation of proteins, lipids, carbohydrates, DNA, and RNA (; ; ). The influence of ROS at a cellular level depends on the species, concentration, location, and duration of exposure (). Consequently, the overproduction of ROS can aggravate the development of inflammatory symptoms and contribute to the onset of many associated diseases (Liu et al., 2023).
ROS includes free radical such as O2•–, •OH, peroxyl (RO2•–), alkoxyl radicals (RO•) and hydroperoxyl (HO•2); and non-free radical oxygen intermediates (i.e. peroxides), which contain unpaired valence shell electrons (; Shields et al., 2021). Non-radical ROS include H2O2, singlet oxygen (1O2), hypochlorous acid (HOCl) (Pizzino et al., 2017), the hydroxide ion (OH–) and organic peroxides (ROOH) (Shields et al., 2021). These non-radical species have volatile O-O bonds (). The non-free radical ROS can undergo redox reactions to produce free radicals as shown in chemical Equations 1-5 (Shields et al., 2021).
Other common ROS include nitrogen dioxide radical (NO2•), peroxynitrite (the physiological combination of peroxynitrite, ONOO− and its more reactive protonated version, peroxynitrous acid, ONOOH), carbonate radical anion (CO3•−), hypohalous acids (HOCl), and hypobromous acids (HOBr) (Murphy et al., 2022). Furthermore, nitric oxide radical (NO•), which has important physiological functions, is generated during the oxidation of L-arginine by nitric oxide synthase (NOS) (Kumar and Pandey, 2015).
The O2•– and H2O2 are the main agents in ROS signaling generated by the mitochondrial electron transport chain (Sinenko et al., 2021). As well as ROS compounds are generated by lipid metabolism in peroxisomes (), the activity of different cytosolic enzymes including cyclooxygenases (Martínez-Revelles et al., 2013), or proteins in plasma membranes that use NADPH as an electron donor (). Furthermore, ROS are generated by many enzymes including NADPH oxidases (NOXs), nitric oxide synthases, xanthine oxidases, peroxisomal components (Magnani and Mattevi, 2019; ), thymidine phosphorylase, lipoxygenases, and cyclooxygenase (Yu et al., 2024). Moreover, they are generated by ionizing, ultraviolet (UV) radiation, and the metabolism of many drugs and xenobiotics (), with cytochromes P450 enzymes playing a crucial role in reducing molecular oxygen to generate O2•– and H2O2 (). Additionally, oxidants are released during protein folding and disulfide bond formation in the endoplasmic reticulum, leading to the production of highly reactive species, including O2•–, H2O2, •OH, and 1O2 (). Both enzymatic and non-enzymatic processes result in the constant production of ROS (Rauf et al., 2024). ROS can be produced constitutively by cells and serve as intracellular signaling molecules, activating redox-sensitive signaling pathways that alter the levels of cytoprotective regulators (Zhang et al., 2016; ).
5 Effect of HMs on ROS generation
In biological systems, ROS are generated as a natural byproduct of cellular aerobic metabolism (). The vast majority of oxygen (> 90%) consumed by eukaryote organisms is converted to energy in the form of ATP using four-electron mechanisms by cytochrome oxidase in the electron transport chain (ETC) without releasing ROS. In contrast, the remaining oxygen is reduced through one-electron successive pathways that begin with converting molecular oxygen to the O2•–, which can then be reduced by a one-electron mechanism to generate H2O2, •OH, and water (Lushchak, 2016). Molecular oxygen is necessary for all aerobic organisms and plays a crucial role in biological processes. Despite its beneficial function, oxygen is a potent oxidant that causes oxidative stress when exposed to environmental stressors such as HMs (Kumar et al., 2023). Intracellular ROS levels rise in response to various stimuli, causing the oxidation of cysteine residues in cytoplasmic proteins, including phosphatases and kinases, affecting signal transduction pathways ().
The primary endogenous sources of ROS generation typically include oxidative phosphorylation, P450 cytochrome, peroxisomes, and the activation of inflammatory cells (). Moreover, there are supporting factors such as immune cell activation, ischemia, pathogens, cancer, strenuous exercise, psychological stress, and aging (Pizzino et al., 2017). On the other hand, ROS can be generated by exogenous causes such as exposure to air pollutants, tobacco, asbestos, toxins, and radiation (; Wang et al., 2021c). Exogenous sources of ROS generation also include exposure to HMs, such as Hg, As, Fe, Pb, and Cd. Once these substances enter the body, they undergo degradation or metabolism, and free radicals are produced as byproducts (Pizzino et al., 2017). Long-term exposure to HMs induces fish to produce large amounts of ROS and accumulate them, which in turn leads to the oxidation of major biomolecules in fish tissues (). Furthermore, toxic substances such as HMs can increase ROS production due to their ability to alter mitochondrial membrane permeability and inhibit ROS clearance enzymes in the cellular antioxidant tract (Sun et al., 2022; Mansoor et al., 2023). HMs contamination enhances the generation of ROS through various mechanisms. It has been established that exposure to HMs can disrupt the cellular redox state and mitochondrial electron transport, causing increased production of ROS (). In addition, HMs such as Cd, As, Fe, Cu, Ni, Pb, Cr, and Hg can deplete enzyme activities through lipid peroxidation and react with nuclear proteins and DNA, generating reactive radicals that can damage cells (Madkour, 2020). HMs also have the ability to alter various physiological and biochemical processes, including enzymatic functions and cell respiratory rates. This is because HMs can interact with different elements of the ETC, changing their activity and mostly causing an increase in ROS production (Mansoor et al., 2023). As shown in Figure 2. some of these HMs (Cd, Pb, and Hg) can interfere with mitochondrial functions by binding to the ETC’s components in organism cells, causing electron disruption and partial reduction of oxygen, resulting in O2•− formation, which is considered the beginning of the generation of other ROS such as H2O2 and OH• (Reddam et al., 2022). In the same context, Cd prevents ATPase, glutathione peroxidase (GPx), lactate dehydrogenase (LDH), and superoxide dismutase (SOD) activities, promoting lipid peroxidation levels and ROS generation (). Moreover, HMs such as As, Cd, and Hg can deplete thiol groups (−OH) in glutathione, a key antioxidant that neutralizes ROS, leading to decreased availability for ROS scavenging (Lushchak, 2016).
Figure 2
Other metals, particularly iron, can produce ROS through the Fenton reaction (Equation 5) without the aid of enzymes, where, Fe2+ reacts with H2O2 to produce a highly reactive hydroxy radical (•OH), resulting in damage to DNA and other related biomolecules (). On the other hand, ions with variable valence are among the most common inducers of oxidative stress. Their capacity to accept/donate electrons make them susceptible to free radical processes. Among these ions, Fe, Cu, Mn, and Cr are the most commonly studied due to their important biological properties and ability to stimulate ROS generation by involvement in the Haber–Weiss reaction (Lushchak, 2016), as shown in Equation 6. Additionally, in the Haber–Weiss reaction, O2•– reacts with H2O2 (Equation 7) to generate HO• radicals as well ().
Where Me is a metal ion with variable valence
The toxic effects of many HMs are caused by redox cycling, which generates ROS. Lipid peroxidation (LPO) is the most common effect of ROS and is thus commonly used as an indicator of fish health (). Additionally, redox inactive metals such as Cd, Pb, and Zn inhibit key antioxidant constituents in cells, notably non-enzymatic and enzymatic antioxidants containing thiols (). HMs activate NADPH oxidase and protein kinase C (PKC), leading to the intensified generation of intracellular ROS (Sun et al., 2022). Cells treated with Cr generate ROS by inducing NADPH oxidase (NOX) (Wang et al., 2011).
6 Implications of fish-HMs contamination on human health
Fishes are classified as one of the foods that occupy the top of the food pyramid. Therefore, they are susceptible to the biomagnification of HMs and are most likely to serve as carriers of HMs to humans (Kumar et al., 2023). The accumulation of HMs in seafood exposes human consumers to the harmful consequences of these metals (Umeoguaju et al., 2023). Because of this, fish are frequently employed as crucial biological indicators to examine metal concentrations in their habitats and to evaluate the ecological and health hazards related to the discharge of waste resulting from human activities (Naz et al., 2023). HMs can directly interact with mitochondria, altering the physiological conditions of cells such as intracellular calcium homeostasis. This affects the dynamics and function of mitochondria and cells, ultimately impacting the body’s physiological state, which can contribute to the onset and progression of certain illnesses (Sun et al., 2022). Risk assessment is a valuable tool for evaluating the potential effects of HMs pollutants, as it considers the total exposure of individuals to these pollutants in a specific location (Zaghloul et al., 2024).
Aquatic organisms, especially fish, are an essential source of polyunsaturated omega-3 fatty acids, vitamins, minerals, and high-value proteins. As HMs can accumulate in fish bodies, they can readily enter the human body mainly through the consumption of seafood products, causing acute and long-term negative health complications (). Humans can absorb HMs through the digestive system (contaminated food and water), skin, or inhalation (Witkowska et al., 2021). Thus, the absorption rate of HMs in the human body depends on the HM’s type and how it enters the body. For example, HMs accumulate in the human body when contaminated fish are consumed (), causing severe dysfunction, malnourishment, and immune system destruction (Mehnaz et al., 2023). Furthermore, HMs affect the kidneys, brain, nerves, liver, skin, and heart, among other organs in the human body (Mitra et al., 2022). HMs interfere with the functioning of native proteins by attaching to free thiols or other functional groups, causing side chain oxidation in amino acids, obstructing protein folding, and/or displacing necessary metal ions from enzymes (Witkowska et al., 2021). Exposure to HMs, either permanently or at concentrations above safe levels, can lead to serious short-term or long-term health problems, such as disorders of the gastrointestinal, respiratory, neurological, reproductive, cardiovascular, renal, and hematopoietic systems (; Witkowska et al., 2021).
The peroxidative activity of some HMs generates significant levels of ROS, aiding in protumorigenic signaling, and the growth of cancerous cells (Mitra et al., 2022). The liver and kidneys have a strong propensity to accumulate HMs at higher concentrations than other tissues in the human body (). Increased exposure to these metals can have serious negative effects on these organs and the rest of the body (Table 2). HMs effects depend on several factors, including the dose, exposure manner, chemical species, exposed individuals’ ages, genders, genetics, and nutritional status of the exposed individuals (Tchounwou et al., 2012). Moreover, different cooking procedures can affect the HMs content in fish ().
Table 2
| Heavy metal | Effect on human health | Reference |
|---|---|---|
| Copper | - Causes mutations and aggregation of mitochondrial proteins, leading to reduced activity of the primary antioxidant enzyme and increased production of toxic ROS - Fibrosis in renal tissues - Affects male reproductive function, resulting in decreased sperm count and motility - Obesity - The development of neurodegenerative disorders | () (Niu et al., 2020) (Tvrda et al., 2015) (Yang et al., 2019) (Witt et al., 2021) |
| Nickel | - Preterm delivery - Diabetes - Congenital heart defects - Immunological disorders, including Type I hypersensitivity and Type IV immune reactions | () (Titcomb et al., 2021) (Yu and Zhang, 2017) () |
| Cadmium | - Cd has been shown to stimulate the release of antithrombotic substances in the vascular endothelium, resulting in the generation of a variety of inflammatory markers - The growth and spread of prostate cancer and basal breast tumors. Breast tumor cells may face a decline in their antioxidant defenses, which can trigger the formation of ROS formation - Nephron destruction | (Sears et al., 2021) () (Yan and Allen, 2021) |
| Iron | Excessive iron levels have been linked to an increased risk of cardiovascular disease, fetal complications, gestational diabetes, along with the generation of oxidative stress and cellular damage. | (Quezada-Pinedo et al., 2021) |
| Lead | - Neurological disorders, including Parkinson’s disease, amyotrophic lateral sclerosis, Alzheimer’s, and attention-deficit/hyperactivity disease - Cardiovascular diseases - The effects of lead exposure on kidney and liver function, as well as serum urea, white blood cell count, hemoglobin, aspartate transaminase, creatinine, alanine transaminase, and hematocrit levels - Lead exposure negatively affects physical growth in children, especially in boys - Lead exposure may change sex hormone levels, affecting reproductive system function | (Wang et al., 2020b) (Obeng-Gyasi et al., 2021) (Nakhaee et al., 2019) (Zhou et al., 2020) () |
| Chromium | - Possible effects on bronchial epithelial cells include abnormal modulation of apoptosis-related proteins, energy metabolism-associated proteins, and cytoskeletal proteins - Toxic effect on fetal growth. - Developing lung cancer - Hyperpigmentation of the skin | (Xia et al., 2022) (Peng et al., 2018) () () |
| Mercury | - Effect on child growth, possibly due to reduced parasympathetic modulation of heart autonomic activity among children - Mercury exposure can elevate blood pressure levels in children. - High mercury levels can cause dyslipidemia in adults - Mercury exposure significantly increased liver enzymes | (Papadopoulou et al., 2021) () () (Lee et al., 2020) |
| Zinc | - Zinc can influence the immune system and modify levels of high-density lipoprotein. - Liver damage and gastrointestinal diseases. | () (Zhou et al., 2016) |
| Manganese | - Manganese may affect the brain and cause neurological toxicity - Impaired fine motor control, memory problems, tremors, and cognitive deficits | (Neal and Guilarte, 2012) (Kulshreshtha et al., 2021) |
| Arsenic | - Effects on the cardiovascular, hepatic, neurological, renal, respiratory, hematological, endocrine, and reproductive systems - Effects during pregnancy may increase the risk of infant mortality, preterm birth, spontaneous abortion, stillbirth, delayed growth in children, low birth weight, reduced IQ, compromised immune function, neurotoxicity, and neurodevelopmental impairments - Hypertension | (Rahaman et al., 2021; Shaji et al., 2021) (Vahter, 2008) (Wang et al., 2021b) |
Negative effects of heavy metal contamination on human health.
Although the natural production of ROS by cells is regulated, an increase in ROS can be pathological and result in oxidative stress and several diseases (). As previously explained, oxidative stress occurs when there is an imbalance between the generation of ROS and the antioxidant defense mechanisms of the body (Wang et al., 2020a; Nakamura and Takada, 2021). This disruption in the oxidation-reduction (redox) balance causes molecular damage (). Consequently, oxidative stress has been implicated in the development of several chronic diseases, such as cancer, aging, diabetes, and hypertension (Pizzino et al., 2017; Sharifi-Rad et al., 2020). The free radicals and reactive molecules in biological systems, produced during electron transfer reactions by either losing or accepting an electron, are derived from ROS or reactive nitrogen species (RNS) (). reported that alongside genetic mutations, excessive ROS leads to irreversible oxidative change in lipids, proteins (including oxidation and peroxidation), and glycans (resulting in advanced lipoxidation and glycation end products), which impair their function and can stimulate illness or cell death. The lipid peroxidation process converts unsaturated fatty acids into small hydrocarbon molecules, forming lipid-free radicals classified as ROS. These radicals are highly damaging to proteins, lipids, and carbohydrates due to oxidative damage resulting from the inhibition of antioxidant mechanisms (). In addition, the release of ROS damages cellular proteins, lipids, and DNA, causing cell damage and potentially leading to carcinogenesis (Reczek and Chandel, 2017). Certain HMs impair the sensitivity of cancer to treatment and accelerate its growth through various mechanisms, such as breaching DNA structure, decreasing antioxidant protection, and inhibiting the activity of enzymes involved in repairing damage (Romaniuk et al., 2017; Pietrzak et al., 2021; Witkowska et al., 2021). HMs can also damage organelles and cell components such as membranes, mitochondria, lysosomes, nuclei, and endoplasmic reticulum (Wang and Shi, 2001). Finally, increased ROS concentrations in semen plasma can lead to male infertility (; ).
7 Conclusions and recommendations
HMs contamination is a significant contemporary environmental challenge, driven by an increasing number of pollution sources and the widespread dispersion of these toxic elements. The contamination of water and soil with HMs adversely impacts human health, as well as terrestrial and aquatic ecosystems. The bioaccumulation of HMs can severely impact the physiology of aquatic organisms, hindering their growth and reproduction. Aside from their toxic effects, the presence of HMs enhances the generation of ROS in both aquatic life and humans, leading to oxidative stress. This condition is a major contributor to various health issues, including cancer, kidney damage, liver disease, and skin problems. To effectively address the issue of HMs contamination, more preventive measures must be implemented. This includes enacting stricter laws regarding the disposal of heavy metal-containing waste and strengthening environmental regulations. Furthermore, targeted remediation efforts, such as soil and water decontamination techniques, may be required in areas with high levels of HMs contamination. Collaboration among policymakers, environmental agencies, and the general public is required to develop and implement effective strategies to address this pressing environmental concern.
Statements
Author contributions
YW: Writing – original draft, Writing – review & editing. AN: Writing – original draft, Writing – review & editing. CZ: Writing – original draft, Writing – review & editing. WA: Writing – original draft, Writing – review & editing. SA: Writing – original draft, Writing – review & editing.
Funding
The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. This study was supported by Demonstration course of curriculum ideology “Food Safety”, and Promotion and practice of food innovative experiment based on “two abilities and one degree”.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
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Summary
Keywords
heavy metals, fish contamination, reactive oxygen species, oxidative stress, human health
Citation
Wang Y, Noman A, Zhang C, AL-Bukhaiti WQ and Abed SM (2024) Effect of fish-heavy metals contamination on the generation of reactive oxygen species and its implications on human health: a review. Front. Mar. Sci. 11:1500870. doi: 10.3389/fmars.2024.1500870
Received
24 September 2024
Accepted
12 November 2024
Published
29 November 2024
Volume
11 - 2024
Edited by
Heba H. Abdel-Kader, National Institute of Oceanography and Fisheries (NIOF), Egypt
Reviewed by
Tariq Aziz, University of Ioannina, Greece
Rania G. Elbaiomy, Sichuan University of Science and Engineering, China
Updates
Copyright
© 2024 Wang, Noman, Zhang, AL-Bukhaiti and Abed.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Anwar Noman, anwarnoman15@yahoo.com
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