1. Introduction
Ferroptosis is characterized by an iron-dependent accumulation of lethal reactive oxygen species (ROS) and lipid radicals. The most frequently occurring free radicals and reactive molecules in biological systems are derived from oxygen (ROS) and nitrogen (Reactive Nitrogen Species, RNS). ROS or RNS are formed during electron transfer reactions, by losing or accepting electron(s) [
1,
2]. While low levels of ROS are important for cellular proliferation, differentiation, migration, apoptosis, and necrosis, excessive ROS causes oxidative stress, inducing ROS-mediated damage to cellular biomolecules including DNA, proteins, and membranes [
3,
4]. Oxidative stress is characterized by a shift in equilibrium between the formation and elimination of free radicals. Oxidative stress is involved in various aspects of human pathogenesis in chronic diseases, aging and cancers [
5]. Human normal as well as tumor cells have an enhanced antioxidant system to remove/detoxify ROS formed. They include superoxide dismutase (SOD), catalase (CAT) and glutathione peroxidases (GPXs), as well as reduced glutathione [
2] to protect cells from ROS-induced toxicity [
6]. Excess ROS and lipid ROS formation causes damage to cellular membranes inducing ferroptosis, a form of cell death which is morphologically, biochemically, and genetically distinct from apoptosis, necrosis, and autophagy [
7,
8,
9]. As ferroptosis is distinct from other forms of cell death it has been suggested to play an important role in cancer therapy.
Glutathione peroxidase 4 (GSH/GPX4) and system Xc-, are two major signaling pathways which are known to play pivotal roles in ferroptosis [
7]. System Xc- are the family of heterodimeric amino acid transporters and SLC7A11 functions to exchange L-cystine and L-glutamate [
10]. Erastin, a ferroptosis inducer, inhibits the function of system Xc- and depletes glutathione (GSH), resulting in inhibition of GPX4 and the accumulation of ROS and lipid peroxides which in turn causes ferroptosis.
Ferroptosis has recently been suggested to play a significant role in toxicology due to its unique cell death mechanism that is driven by iron-dependent lipid peroxidation. This mechanism has become extremely relevant to toxicology because exposure to certain toxins (e.g., heavy metals, environmental pollutants, and industrial chemicals) can intensify oxidative stress, leading to ferroptotic cell damage (and death) in organs like the liver, kidneys, and lungs [
11]. Many drugs, especially chemotherapy agents, have been shown to increase ROS formation and disrupt cellular iron metabolism, causing ferroptosis [
12]. Thus, understanding the mechanisms and pathways involved in ferroptosis will help in predicting, preventing, or treating drug-induced tissue damage, especially in high-risk organs.
Ferroptosis has been implicated in neurotoxicity due to its role in oxidative damage and iron accumulation, which are common in neurodegenerative diseases like Alzheimer’s and Parkinson’s [
13]. Since some neurotoxic substances can elevate iron or lipid peroxidation in the brain, insights into ferroptosis could lead to new protective strategies for managing neurotoxin exposure and associated diseases.
The liver, as a central organ in detoxification, is highly susceptible to ferroptosis [
14]. This is especially relevant for drugs that induce iron overload and/or oxidative stress, triggering ferroptosis and causing hepatotoxicity and liver fibrosis.
Exposure to environmental toxins, such as heavy metals (e.g., arsenic, cadmium) and other industrial pollutants, can influence cellular iron metabolism or redox balance, increasing the risk of ferroptosis in exposed tissues [
15,
16]. Further studies on ferroptosis can provide strategies to mitigate these toxic effects and improve public health outcomes. By targeting ferroptosis pathways, researchers can significantly reduce toxicity and prevent cell death from toxic xenobiotics or drugs. Ferroptosis inhibitors may then be utilized to mitigate damage in ferroptosis-sensitive tissues/organs during exposures or poisonings from environmental pollutants, providing a new avenue for therapeutic intervention in toxicology.
2. Perfluoroalkyl and Polyfluoroalkyl Substances (PFAS)
PFAS are a group of persistent chemicals that are widely present in environment due to their extensive use as protective coatings for carpets and clothing, water repellents, paper coatings, and surfactants [
17,
18,
19]. PFAS are now found in water and food, as well as in indoor air settings, leading to significant exposures [
18]. Unfortunately, efforts to control and decrease the use of PFAS have not been very successful as they are still detected in humans, animals, and water due to both their extensive world-wide application and lack of biodegradability. Air pollution and cigarette smoke have been shown to contain high concentrations of PFOS, a key member of PFAS family. PFAS causes oxidative stress [
20,
21], mitochondrial dysfunction [
22], and inhibition of gap junction intercellular communication [
23], resulting in serious human health problems including endocrine disruptions, liver damage, kidney cancer, obesity, hypertension, and immunotoxicity [
24].
In vitro and
in vivo experiments, as well as population studies, have suggested that exposure to PFAS is associated with increased oxidative stress. PFAS generate reactive ROS in human hepatocytes, inducing oxidative stress and causing DNA damage with genotoxic and cytotoxic potential [
25]. In addition, PFAS exposures have been shown to enhance oxidative stress in kidney, leading to disruptive effects on the peroxisome proliferator-activated receptor (PPAR) and its downstream functions [
21]. Several studies in humans have shown that serum PFAS concentrations are strongly associated with biomarkers of oxidative and nitrative stress as PAFS increase the levels of both 8-nitroguanine and 8- hydroxy-2-deoxyguanosine (8-OHdG) [
26]. Furthermore, in a randomized control trial in senior Koreans with elevated serum levels of perfluorododecanoic acid (PFDoDA), and PFOS blood concentrations showed higher levels of malondialdehyde and 8-OHdG in urine [
27].
PFAS is known to accumulate in the kidneys and research indicates a strong link between exposure to PFAS with kidney toxicity, showing that PFAS can negatively impact kidney function and potentially contribute to the development of chronic kidney disease. Further studies have reported that PFAS exposure induces oxidative stress in the kidney, causing lipid peroxidation and DNA damage, increased production of mitochondrial transport chain proteins, decreased cell proliferation, and apoptosis [
21,
28,
29,
30]. Multiple pathways have been implicated in PFOS exposure to cause renal damage, including dysregulation of PPARa and PPARg, key nuclear receptor hormones. These are highly expressed in the proximal renal tubule and involved in lipid metabolism, lipogenesis, glucose homeostasis, and cell growth and differentiation [
21]. Recently, the use of N-acetylcysteine (NAC) and taurine—both known inhibitors of oxidative stress—has been found to reduce complications in diabetic and hypertensive patients with chronic kidney disease Recently, the use of N-acetylcysteine (NAC) and taurine—both known inhibitors of oxidative stress—has been found to reduce complications in diabetic and hypertensive patients with chronic kidney disease [
31].
PFAS can cross the blood-brain barrier and accumulate in the brain which negatively impacts brain function and disrupt neurotransmitter systems, potentially leading to cognitive impairments and neurodevelopmental issues [
32,
33]. This is particularly important when exposure occurs during critical developmental stages since PFAS can cross disrupt various mechanisms within the brain, including calcium homeostasis and mitochondrial function and alterations in neurotransmitters of neurons [
34].
PFAS exposure has been shown tom disrupt the cellular antioxidant balance by decreasing the activity of GPX4, a key enzyme responsible for preventing lipid peroxidation and ferroptosis. Studies have found elevated intracellular iron levels, increased lipid peroxidation, and altered expression of ferroptosis-related proteins like ACSL4 (acyl-CoA synthetase long-chain family member 4) when cells are exposed to PFAS.
2.1. Heavy Metals
Heavy metals (e.g., arsenic, cadmium, and mercury) are found in the Earth’s crust with varying concentrations and are not easily detoxified into less toxic compounds through metabolic processes. Thus, they persist for a long time and are taken up by plants, leading to accumulation in various animals and humans at high toxic levels, causing harmful impacts on both the environment and human health [
35,
36].
Many heavy metals can interfere with the synthesis or function of glutathione, a crucial antioxidant that protects against lipid peroxidation, thereby promoting ferroptosis. Copper has been reported to inhibit GPX4 activity, leading to its degradation through autophagy and promoting ferroptosis [
37]. GPX4 is the key enzyme for the removal of cellular lipid peroxide formed, inhibiting ferroptosis. Heavy metals disrupt mitochondrial function, leading to increased ROS production and further promoting ferroptosis [
15]. Exposure to heavy metals, especially lead and mercury, are linked to neurodegenerative diseases like Alzheimer's and Parkinson's. Methylmercury (CH
3-Hg) has been shown to react with GSH, generate ROS and cause oxidative stress Ferroptosis has been suggested as a potential mechanism of neuronal death [
13,
16]. Combination of metals like iron with carbon tetrachloride can cause liver damage through ferroptosis [
38].
Heavy metals have been reported to disrupt cellular redox homeostasis and contribute to iron dysregulation, promoting ferroptosis [
39]. Cadmium exposure can induce iron accumulation in cells, enhancing the production of ROS and lipid peroxidation, inducing ferroptosis [
40]. Thus, ferroptosis in response to heavy metal exposure primarily impacts organs with high iron content or metabolic activity, such as the liver and kidneys [
14,
38]
. Exposure to arsenic can cause ferroptosis in liver cells, contributing to arsenic-induced liver injury and increasing the risk of hepatotoxicity and fibrosis [
41].
2.2. Industrial Pollutants and Airborne Particulates
Particulate matter (PM) is the principal component of indoor and outdoor air pollution. PM includes a range of particle sizes, such as coarse, fine, and ultrafine particles. Industrial pollutants, especially airborne particulate matter from sources like vehicle exhaust and industrial emissions, contain metals and organic compounds [
42,
43,
44]. Particles that are <100 nm in diameter are defined as ultrafine particles (UFPs). Chronic exposure to air pollutants that induce ferroptosis can damage lung tissue, leading to chronic obstructive pulmonary disease (COPD) and lung cancer [
45]. When inhaled, these particles can produce oxidative stress in lung cells, causing ferroptosis and leading to respiratory diseases. Inhalation of PM exacerbates respiratory symptoms in patients with chronic airway disease, but the mechanism for this response is not clear currently.
2.3. Pesticides
High lipophilic pesticides are known to integrate into cell membranes and initiate lipid peroxidation which in the presence of iron lead to ferroptosis [
46]. Paraquat, a pesticide and a ROS generator [
47,
48], has been shown to induce ferroptosis in neural and other cell types, leading to neurodegenerative conditions like Parkinson’s disease [
49,
50]. Ferroptosis induced by pesticides exposure poses significant neurotoxic risks, as brain cells are highly susceptible to oxidative damage and lipid peroxidation, elucidating why long-term exposure to certain pesticides has been associated with increased risks of neurological disorders [
51,
52].
Imidacloprid (IMI) is among the common neonicotinoid insecticides used in agriculture worldwide, posing a potential toxic threat to non-target animals and humans. Numerous studies have shown that ferroptosis is involved in the pathophysiological progression of renal diseases [
53,
54]. Chlorpyrifos is an organophosphate pesticide that can trigger ferroptosis, causing liver toxicity [
55]. Interestingly, Vitamin E (a strong antioxidant) supplementation has been reported to help reverse the effects of ferroptosis caused by chlorpyrifos [
56]. Various other pesticides e.g., Acetochlor, an herbicide that causes skin irritation, cancer, and developmental issues, has been reported to trigger ferroptosis [
57].
3. Ferroptosis Combined with Apoptosis and Necrosis
Exposure to environmental pollutants can also cause other forms of cell death such as apoptosis and necrosis [
29,
58,
59]. Ferroptosis can act synergistically with apoptosis, significantly enhancing tissue damage. Thus, simultaneous exposure to multiple pollutants, may increase ferroptotic damage, especially when both iron-dependent mechanisms and lipid peroxidation are enhanced. Cells exposed to chronic low doses of environmental pollutants may initially activate protective mechanisms (like antioxidant defenses) to counteract ferroptosis. However, prolonged exposure can overwhelm these defenses, tipping the balance toward ferroptosis, which could explain why chronic, low-level pollutant exposure is linked to long-term health risks.
4. Biomarkers of Ferroptosis
Biomarkers are important tools for early detection of tissue damage in any biological process, in the treatment of cancers by chemotherapy or exposure to environmental toxins. Thus, the identification of biomarkers of ferroptosis can significantly enhance the field of toxicology by providing tools to monitor, predict, and potentially mitigate cell death related to iron-dependent lipid peroxidation. Furthermore, biomarkers of ferroptosis can be advantageous in toxicology as environmental toxins (drugs) induce ferroptosis in healthy organs like the liver, kidneys, heart and brain, leading to toxic side effects. Biomarkers of ferroptosis can then help assess which organs are at risk of damage, allowing preemptive measures to protect these tissues.
Certain chemicals and pollutants, like heavy metals and industrial pollutants, directly or indirectly trigger ferroptosis. By measuring biomarkers of ferroptosis in animal models or cell cultures exposed to these substances, researchers can identify chemicals that pose significant health risks and implement safer guidelines for exposure levels. Biomarkers also serve as early indicators of ferroptosis-related damage in non-cancerous tissues. For example, if elevated levels of lipid peroxidation markers are detected in the blood following chemotherapy or toxins exposure, it could indicate liver or kidney toxicity, allowing clinicians to modify the treatment regimen to mitigate damage. When ferroptosis biomarkers suggest unwanted toxicity in healthy cells, ferroptosis inhibitors like ferrostatin-1, liproxstatin-1 or vitamin E could be utilized to mitigate tissue damage. Thus, biomarkers may be helpful to guide when and where these inhibitors are needed to protect healthy organs or cells. Several biomarkers of oxidative stress are biomarkers of ferroptosis such as glutathione depletion, GPX4 (glutathione peroxidase 4) inhibition, or formation of lipid peroxidation products. We have recently found that opthalamate levels were highly elevated during tumor cells undergoing ferroptosis [
60]. Opthalamate levels have been shown to be elevated in during oxidative stress caused by the depletion of glutathione in liver [
61]. Additionally, several genes, known markers of oxidative stress (e.g. CHAC1 and heme oxygenase), have been shown to be elevated during ferroptosis [
62,
63,
64].
Several specific biomarkers of ferroptosis are particularly valuable in toxicity research. Lipid peroxidation products (e.g., MDA, 4-HNE) are good indicators of lipid peroxidation and oxidative damage that can indicate ongoing ferroptosis. Iron dysregulation is another key feature of ferroptosis and measuring intracellular iron levels or proteins like ferritin and transferrin can indicate ferroptosis risk. Glutathione depletion and inhibition of GPX4, an enzyme that prevents lipid peroxidation, are central to ferroptosis. Measuring these markers can help detect cells in the process of ferroptosis. Additionally, ferroptosis depends on cysteine uptake via the cystine/glutamate antiporter (system Xc−) to synthesize glutathione. Reduced system Xc− activity can indicate a heightened risk of ferroptosis.
Development of easy-to-use biomarker probes can then assess the degree of cellular stress and risk of ferroptosis from exposure to environmental toxins, drugs, or pollutants. By understanding how these exposures lead to ferroptosis, researchers can better understand the potential for organ damage and disease. By tracking ferroptosis biomarkers, toxicologists can measure cumulative oxidative stress and iron overload in tissues exposed to harmful substances over time. These data can guide interventions, such as antioxidant treatments or iron chelation therapies, to reduce the likelihood of ferroptosis-related damage in at-risk populations. Biomarkers can help detect the early stages of ferroptosis-related toxicity before clinical symptoms appear, offering a window for intervention. For example, in cases of heavy metal exposure, ferroptosis biomarkers could signal the need for treatments that counter oxidative stress or iron accumulation, preventing progression to severe tissue damage. In both chemotherapy and toxicology, understanding the presence and levels of ferroptosis biomarkers can inform the design of drugs aimed at modulating ferroptosis. In toxicology, they can assist in creating protective drugs that inhibit ferroptosis in response to environmental toxins.
For diseases associated with ferroptosis (e.g., neurodegenerative diseases, liver disease), biomarkers can guide therapeutic interventions that either promote or inhibit ferroptosis as needed. For example, in neurodegeneration, where excessive ferroptosis can be damaging, biomarkers could be used to develop and test drugs that protect neurons from ferroptotic cell death.
5. Conclusions and Future Developments
While significant progress is being made in the understanding of environmental pollutant- induced toxicity to humans, there is still a lot of research needed to further our understanding on the long-term effects of these pollutants. Furthermore, we do not know what effects of combinations of these pollutants have on human health, e.g. effects of PFAS with low doses of heavy metal or particulates combined with heavy metals.
There is a number of steps that must be taken in order to be more effective in discovering biomarkers and utilizing these biomarkers for effective interventions to help support long term effects on humans. One way is to combine high throughput screening and developing cost-effective assays of non-invasive biomarkers. In addition, implementing cost-effective validation strategies and c ollaborating across fields, we can conduct ferroptosis biomarker discovery in a budget-conscious manner. These approaches should help in streamlining processes, prioritize high-impact biomarkers, and reduce redundancy, paving the way for affordable, scalable research in both toxicology and chemotherapy.
There is a strong need for proper models to identify biomarkers of ferroptosis. Currently, the model for ferroptosis, human or animal cell lines are utilized to screen for ferroptosis biomarkers in response to toxicants which are more cost-effective than
in vivo animal models. Well-characterized cell lines sensitive to ferroptosis can provide relevant insights at a fraction of cost. However, it has been found that such models (2D) differ from modifications in mice or humans in the process of drug screening and or discovery of biomarkers [
65]. Using CRISPR/Cas9 or RNAi to knock down or knock out ferroptosis-related genes in cell models can help rapidly identify potential biomarkers without the need for more expensive or labor-intensive techniques.
With the recent advancement in 3D culture technology, normal (non-tumor), tumor organoid culture technology could be utilized which may be beneficial for discovery of biomarkers to prevent/mitigate diseases. Compared with traditional 2D culture and tumor tissue xenotransplantation, organoid models have a significantly higher success rate [
65]. Other models have also been recently proposed to evaluate biomarkers of ferroptosis [
66,
67]. If animal models are necessary, zebrafish may be the most cost-effective alternative for studying toxicology and ferroptosis, given their low maintenance costs, rapid development, and high genetic homology with humans for relevant pathways [
68].
6. Ferroptosis Inhibitors in Therapeutic and Preventive Measures
Research into ferroptosis has highlighted potential therapeutic strategies, including ferroptosis inhibitors like ferrostatin-1 and liproxstatin-1, which can prevent lipid peroxidation (Figure 1). These inhibitors might be used to mitigate the effects of pollutant-induced ferroptosis in high-risk populations. Supplementing with antioxidants (e.g., vitamin E, selenium) may help prevent lipid peroxidation, offering a potential preventive measure against ferroptosis for individuals exposed to environmental pollutants. Additionally, monitoring iron intake and iron levels could reduce susceptibility to ferroptosis in populations at risk.
7.Summary
Ferroptosis’s link to environmental pollutants has provided new understanding how toxicants can cause organ damage, neurotoxicity, and chronic disease. This cell death pathway highlights the importance of iron metabolism and lipid peroxidation in toxicology, as it offers potential therapeutic targets to reduce the impact of pollutants. Ferroptosis serves as a critical nexus between environmental exposures and cellular dysfunction. Recognizing the role of environmental pollutants in triggering ferroptosis not only enhances our understanding of disease pathogenesis but also guides the development of targeted interventions to protect public health. With increasing industrialization and repeated exposures to these toxicants and particulate matters, it is more critical to understand, evaluate and find correct solutions if we are to maintain a healthy lifestyle today and for future generations.
Nuclear factor erythroid 2–related factor 2 (NRF2), a transcription factor, plays a critical role in regulating cellular defenses against oxidative stress induced by environmental toxins such as per- and polyfluoroalkyl substances (PFAS) and heavy metals [
35]. NRF2 is central to maintaining cellular homeostasis by modulating antioxidant responses, detoxification pathways, metabolism, and inflammation. It regulates various antioxidant genes, including the cystine/glutamate antiporter (system Xc⁻), specifically SLC7A11, which facilitates cystine uptake for glutathione (GSH) synthesis [
69]. Since glutathione peroxidase 4 (GPX4) requires GSH to detoxify lipid peroxides and prevent ferroptosis [
70], NRF2 activation is generally associated with ferroptosis inhibition [
71]. However, the role of NRF2 in ferroptosis is context-dependent and complex. In some cases, NRF2 upregulation promotes ferroptosis. For instance, in lung cancer cells, elevated NRF2 levels have been shown to sensitize tumor cells to ferroptosis by increasing multidrug resistance-associated protein 1 (MRP1) expression. Additionally, heightened NRF2 activity induces heme oxygenase-1 (HMOX1), leading to the production of biliverdin and the release of redox-active iron, which triggers lipid peroxidation in neuroblastoma and fibrosarcoma cells. Moreover, NRF2-driven upregulation of ABCC1 (MRP1) can deplete intracellular GSH, further contributing to ferroptosis in tumor cells [
72].
While the specific effects of PFAS on system Xc⁻ remain unclear, certain heavy metals are known to inhibit SLC7A11 and induce ferroptosis. PFAS are known inducers of oxidative stress and may potentially impair GSH synthesis by inhibiting SLC7A11, thereby affecting system Xc⁻ activity. A proposed pathway for environmental pollutant-induced ferroptosis is shown in
Figure 1.
Funding
This research was supported by the intramural research program (Grant number ZIA E505013922 and CARCI-HEI#) of the National Institute of Environmental Sciences, NIH. Statements contained herein do not necessarily represent the statements of, opinions or conclusions of NIEHS, NIH, or the US government.
Acknowledgments
Authors thank Erik Tokar and Alex Bruce Merrick for their critical evaluation of the manuscript.
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