Table 5.
Table summarizing the key differences in toxicity profiles, biodistribution, and regulatory challenges between UCNPs and other nanoparticles
Nanomaterial | Toxicity profile | Biodistribution | Regulatory challenges | References |
---|---|---|---|---|
Upconversion nanoparticles (UCNPs) | Generally lower toxicity; potential for lanthanide ion release causing oxidative stress. Biocompatible surface coatings often mitigate cytotoxicity. | Accumulate primarily in the liver and spleen; influenced by surface modifications. | Evolving frameworks due to novel properties and limited long-term data. | [35,66,136,183] |
Silver nanoparticles (AgNPs) | Higher toxicity; induces oxidative stress and apoptosis; and affects gene expression related to oxidative stress. Accumulates in various organs; hepatobiliary toxicity noted. | Primarily deposited in the mononuclear phagocyte system (MPS); widespread organ distribution was noted. | Heavily regulated due to toxic components; extensive safety data required for biomedical applications. | [184–186] |
Gold nanoparticles (AuNPs) | Moderate toxicity; size-dependent effects on cellular response, with smaller sizes causing necrosis or apoptosis. Primarily stored in the liver; lower systemic toxicity compared to AgNPs. | Accumulation in the liver, spleen, kidney, heart, lungs, testis, brain, and thymus; size influences distribution. | Regulatory scrutiny due to potential environmental impact; safety assessments needed. | [187–192] |
Copper nanoparticles (CuNPs) | Higher doses are required for toxicity; sex-related differences observed in response. Major accumulation in liver, kidney, and spleen; bio persistence concerns. | Notable accumulation in liver, kidney, and spleen; gastrointestinal exposure leads to higher public risk. | Increasing scrutiny due to health risks associated with copper exposure; requires thorough evaluations. | [193–195] |
Titanium dioxide nanoparticles (TiO2 NPs) | Size-dependent toxicity; smaller TiO2 NPs cause more oxidative stress and DNA damage. Potential lung toxicity upon inhalation; chronic exposure risks identified. | Biodistribution is influenced by size and shape; smaller particles show higher organ distribution | Regulatory concerns regarding inhalation risks and environmental persistence; ongoing assessments are needed. | [196] |
Quantum dots (QDs) | Higher toxicity due to heavy metals (e.g., cadmium); can cause significant cytotoxic effects. Toxicity varies based on size, surface chemistry, and concentration. | Tend to accumulate in the liver and kidneys. Long-term retention raises concerns about chronic toxicity. | Heavily regulated due to toxic components (e.g., cadmium). Extensive toxicity data required for approval in biomedical applications. | [197–200] |
Carbon nanotubes (CNTs) | Variable toxicity dependent on structure (SWCNTs vs. MWCNTs) and functionalization; can cause inflammation and cytotoxicity. Inhalation can lead to pulmonary toxicity and potential fibrotic responses. | Can penetrate biological barriers and accumulate in various organs, including the lungs. Persistence in biological systems can lead to long-term health risks. | Increasing scrutiny due to environmental impact and potential health risks. Thorough safety evaluations are needed; addressing concerns over environmental impact and potential health risks. | [201–205] |