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Micro/nanoplastics and kidney—Letter to the Editor
Micro/nanoplásticos y riñón—Carta al Editor
Visitas
101
Leonard Whye Kit Lim
Faculty of Resource Science and Technology, Universiti Malaysia Sarawak, Kota Samarahan, Sarawak, Malaysia
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Table 1. The research summary of micro/nanoplastics in kidney.
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Dear Editor,

The rapid accumulation of plastic waste poses a significant global threat, with micro/nanoplastics emerging as key pollutants. Common plastic polymers degrade into micro/nanoplastics, which contaminate oceans and enter the human body via ingestion, inhalation, or dermal absorption. Once inside, micro/nanoplastics can accumulate in organs such as the lungs, kidneys, and brain, triggering oxidative stress, inflammation, and endocrine disruption. Annual human intake is estimated at 39,000–121,000 particles.1 Recent studies suggest a growing link between MNP exposure and kidney dysfunction, making nephrotoxicity a rising concern2,3 (Table 1).

Table 1.

The research summary of micro/nanoplastics in kidney.

Model type  Species/subtype  Exposure route  Main findings  Limitations 
Model organismMale mice  Ingestion  Mortality increase; weight loss  Small sample size (10–13 mice for each group) 
Juvenile rat  Ingestion  Oxidative stress  Small sample size (8 in each group) 
Zebrafish larvae  Direct exposure  Kidney damage; innate immune suppression  Short period of exposure (7 days) 
Organoid  3D human kidney organoid  Whole-body exposure and airborne  Renal blood flow disturbance; kidney damage  Small sample size (n=5) 
Human cell lineImmortalized human podocytes and human glomerular endothelial cells  Direct exposure  Alteration in morphology and cytoskeleton  Sample size not reported 
HK-2  Direct exposure  Upregulation of Arg2 gene expression  Moderate sample size (n=24) 
Model organisms

The effects of polystyrene micro/nanoplastics (50nm polystyrene nanoplastic as well as 4μm, 600nm and 300nm polystyrene microplastic) were examined on male mice kidney.4 As a result, histological impairment and inflammation of the kidney were observed beside the increase in mortality rate and significant weight loss observed across all treatments.4 Furthermore, they have identified a plethora of biomarkers such as SOD, IL-6, MCP, CAT, IL-10, MDA and GSH-Px that are altered across control and micro/nanoplastic treatments in mice.4 A long-term (28 days) polystyrene microplastic (1000nm) ingestion experiment was conducted on juvenile rats.5 The outcome showed that microplastics induced oxidative stress in both endoplasmic reticulum and kidney of treated rats.5 Significant increase in apoptosis associated gene expression (caspase-12, Bax, caspase-3, Bcl-2 and caspase-9) was also detected in microplastic treated rats.5

The polystyrene micro/nanoplastic effects was experimented on kidney of model fish species zebrafish (Danio rerio) larvae.6 Both the polystyrene microplastic (5μm) and polystyrene nanoplastic (100nm) induced severe kidney damage and innate immune function suppression in zebrafish larvae.6 These micro- and nanoplastic treated larvae were also discovered to be more susceptible to Edwardsiella piscicida bacterial infection as compared to the negative controls. Additionally, the transcriptomic analysis revealed that cytosolic DNA-sensing and C-type lectin receptor pathways were compromised in both micro- and nanoplastics treated zebrafish groups.6 They concluded that nanoplastics introduced stress within the endoplasmic reticulum whereas microplastics can lead to lipid accumulation in zebrafish larvae.6

Organoids

The toxicological effects of renal injury induced by inhalation of airborne polystyrene nanoplastics were investigated using a kidney organoid.7 First, they set up a whole-body exposure system to allow the simulation of airborne nanoplastic inhalation exposure. Then, they have also established a cost-effective, reliable, and high-performing protocol for culturing 3D human kidney organoids.7 Their results indicated that airborne nanoplastics deposition in kidney is possible via inhalation alone.7 Polystyrene nanoplastics showed a tendency to promote apoptosis through the NR4A1/CASP3 signaling pathway and simultaneously activated the TF/F12 pathway, initiating an external coagulation cascade.7 These polystyrene nanoplastics also contributed to dysfunction in the renin–angiotensin–aldosterone system (RAAS), impairing renal circulation and worsening kidney damage.7 They deduced that chromic exposure to these airborne nanoplastics can lead to severe embryotoxicity, renal blood flow disturbance and nephrotoxicity.7 However, due to limitations in experimental models, they mentioned that caution is advised when applying these findings to human health.

Human cell line

The effects of 0.05μm polystyrene nanoplastics on the kidney was investigated via cultured immortalized human podocytes and human glomerular endothelial cells.8 The resultant treated podocytes and glomerular endothelial cells experienced alteration in both morphology and cytoskeleton, but the cell specific markers did not depict significant differential expressions across treated and non-treated cells.8 Micro/nanoplastics was subjected to normal human adult male kidney HK-2 cell line used commonly in toxicology researches.9 Interestingly, they unearthed that the Arg2 gene expression was increased significantly upon micro/nanoplastic exposure in HK-2 cells.9 The Arg2 gene encodes arginase 2, a mitochondrial enzyme involved in arginine metabolism. This enzyme plays indispensable roles in vascular function, metabolic processes as well as inflammation. Following lentivirus-induced knockdown of the Arg2 gene, HK-2 cells exposed to micro/nanoplastics during sepsis exhibited SOD, GSH, and MDA levels comparable to those in non-septic HK-2 cells.9 This indicates an enhanced resistance to oxidative stress adapted by the HK-2 cells treated with micro/nanoplastics. In the same study, they have also conducted similar treatment to mice and as a result the mortality rate of mice was elevated due to exacerbated kidney damage induced by micro/nanoplastic ingestion.9 Similarly, the Arg2 gene expression in micro/nanoplastic treated mice was also found to be significantly abundant than their non-treated counterparts.9

Future outlooks

Currently, no established method exists to remove nanoplastics from human kidneys, but emerging strategies include enhancing renal clearance through hydration and nephroprotective agents, using nanomedicine tools like plastic-binding nanoparticles, and improving dialysis techniques. Experimental approaches such as magnetic nanocarriers, AI-driven detox planning, and gut microbiota modulation are also being explored. Continued interdisciplinary research is crucial to develop safe, effective removal techniques for this growing environmental and health concern. Standardized exposure models, 3D organoids, and omics approaches10 are essential for deeper insight. Integrating AI3 can accelerate research and boost prediction accuracy. Interdisciplinary efforts are vital to understand chronic impacts and guide public health and regulatory responses.

References
[1]
K.D. Cox, G.A. Covernton, H.L. Davies, J.F. Dower, F. Juanes, S.E. Dudas.
Human consumption of microplastics.
Environ Sci Technol, 53 (2019), pp. 7068-7074
[2]
L.W.K. Lim.
Linking microbiome to cancer: a mini-review on contemporary advances.
Microbes, 6 (2025),
[3]
L.W.K. Lim.
Implementation of artificial intelligence in aquaculture and fisheries: deep learning, machine vision, big data, Internet of things, robots and beyond.
J Comput Cogn Eng, 3 (2024), pp. 112-118
[4]
X. Meng, J. Zhang, W. Wang, G. Gonzalez-Gil, J.S. Vrouwenvelder, Z. Li.
Effects of nano- and microplastics on kidney: physicochemical properties, bioaccumulation, oxidative stress and immunoreaction.
Chemosphere, 288 (2022),
[5]
W. Wang, J. Guan, Y. Feng, L. Nie, Y. Xu, H. Xu, et al.
Polystyrene microplastics induced nephrotoxicity associated with oxidative stress, inflammation, and endoplasmic reticulum stress in juvenile rats.
Front Nutr, 9 (2023),
[6]
H. Yang, J. Ju, Y. Wang, Z. Zhu, W. Lu, Y. Zhang.
Micro-and nano-plastics induce kidney damage and suppression of innate immune function in zebrafish (Danio rerio) larvae.
Sci Total Environ, 931 (2024),
[7]
L. Chen, B. Han, S. Yang, L. Guo, L. Zhao, P. Liu, et al.
Toxicological effects and mechanisms of renal injury induced by inhalation exposure to airborne nanoplastics.
J Hazard Mater, 488 (2025),
[8]
Y. Melina, H. Michelle, H. Marie, K. Mustafa, M. Zeynad, S. Mario, et al.
Effects of nanoplastic particles on the kidney.
J Am Soc Nephrol, 35 (2024),
[9]
Y. Zha, Y. Cheng, S. Yu, Y. Cheng, J. Wang, X. Han, et al.
Long-term micro/nanoplastic ingestion promotes sepsis by worsening kidney damage: a transcriptomics and metabolomics study.
Environ Sci Nano, (2025),
[10]
L.W.K. Lim.
Comparative genomic analysis reveals the origin and global distribution of melon necrotic virus isolates.
Gene Rep, 29 (2022),
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