Figures
Abstract
Background
This study aims to investigate the connection between serum lipids, per- and polyfluoroalkyl substances (PFAS), and age-related macular degeneration (AMD) risk and assess whether serum lipids mediate the association between PFAS and AMD.
Methods
1605 participants were enrolled from NHANES 2005–2008. Four serum PFAS levels with high detective rates, including perfluorononanoic acid (PFNA), perfluorooctanoic acid (PFOA), perfluorooctane sulfonic acid (PFOS), and perfluorohexane sulfonic acid (PFHxS) were examined. Restricted cubic spline analysis (RCS) and weighted quantile sum (WQS) analysis were employed to detect nonlinear and mixed exposure effects.
Results
PFOS level was associated with any AMD (OR, 1.54; 95% CI, 1.12 to 2.11; P = 0.011), early AMD (OR, 1.43; 95% CI, 1.06 to 1.95; P = 0.024), and late AMD (OR, 3.35; 95% CI, 1.55 to 7.23; P = 0.004) risk. PFHxS (OR, 1.72; 95% CI, 1.01 to 2.93; P = 0.045) and PFOA (OR, 2.10; 95% CI, 1.21 to 3.63; P = 0.011) levels were associated with late AMD risk. The RCS showed a nonlinear connection between PFOS exposure and AMD risk (P nonlinear = 0.006). WQS analysis indicated a positive relationship between mixed PFAS exposure and AMD risk (OR, 1.34; 95% CI, 1.03 to 1.75; P = 0.030). Serum total cholesterol (TC) and high-density lipoprotein (HDL) cholesterol were associated with AMD risk (ORTC, 1.005; 95% CI, 1.001 to 1.009; P = 0.026. ORHDL, 1.028; 95% CI, 1.014 to 1.042; P<0.001), and mediated the relationship of PFOS exposure and AMD risk, with mediation proportions of 5.73% (P = 0.020) and 7.27% (P = 0.032), respectively.
Citation: Chen X, Li J, Xu N, Li X, Li J, Guo Q, et al. (2025) Serum lipids mediate the association of per- and polyfluoroalkyl substances exposure and age-related macular degeneration. PLoS ONE 20(1): e0317678. https://doi.org/10.1371/journal.pone.0317678
Editor: Linglin Xie, Texas A&M University College Station, UNITED STATES OF AMERICA
Received: September 26, 2024; Accepted: January 2, 2025; Published: January 31, 2025
Copyright: © 2025 Chen et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The datasets generated and/or analyzed during this study are publicly available from the NHANES (National Health and Nutrition Examination Survey) database without restriction at https://wwwn.cdc.gov/nchs/nhanes. This manuscript's minimal data set can be found at doi.org/10.6084/m9.figshare.28057925.
Funding: This work was supported by Beijing-Tianjin-Hebei Special Project (J200014, awarded to LH), Science and technology innovation project of Chinese academy of medical sciences(2019-RC-HL-019, awarded to LH), and the National Natural Science Foundation of China (Grant Number 81670870, awarded to LH). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
1. Introduction
Age-related macular degeneration (AMD) is an ocular neurodegenerative disease that leads to visual impairment and irreversibly vision loss, mainly affecting older adults [1]. Globally, 196 million patients suffered from AMD in 2020 [2]. Although the application of anti-vascular endothelial growth factor injections has made significant progression in the therapy of neovascular AMD (nAMD, a form of advanced AMD), many patients did not benefit much due to individual differences and no treatment was effective for early AMD [3, 4]. Besides, a patient with AMD treated with anti-VEGF therapy is expected to cost thousands of dollars per year [5]. AMD is considered to be caused by genetic and external factors [6]. Researchers have revealed many risk factors for AMD such as older age [7], tobacco smoking [8], diet [9], dyslipidemia [10], and cardiovascular diseases [11]. Currently, the effects of environmental pollutants exposure on AMD have become a research hotpot [12, 13].
Per- and polyfluoroalkyl substances (PFAS) are a group of synthetic fluorinated chemical substances [14]. PFAS are widely applied in plenty of industries, such as food packaging, textiles, and surfactants due to their properties, including stability, hydrophobicity, and oleophobic [15]. PFAS have a long biological half-life, resulting in a strong ability of bioaccumulation [16, 17]. The routes of PFAS exposure mainly include diet, indoor air, dust, and skin contact [18]. Serum PFAS levels were correlated with various human diseases such as kidney diseases, metabolic syndrome, and neurodegenerative diseases [19–21]. A study has revealed that perfluorooctane sulfonic acid (PFOS) was a biomarker for nAMD in a cohort with 46 nAMD patients who had undergone anti-VEGF therapy [22]. However, this study lacked the control group. A study has reported the relationship between PFAS exposure and ocular disorders, researchers found that high serum PFAS concentration was correlated with a higher prevalence of vision impairment and vitreous disorder in China [23]. Vitreous diseases are considered to be associated with AMD risk [24, 25]. Besides, it is reported that exposure to perfluorooctanoic acid (PFOA) could trigger inflammatory responses in retinal pigment epithelial cells [26], while inflammation engages in the development of AMD [27]. In addition, PFAS is widely reported to interfere with liver lipids metabolism and significantly increase the levels of serum lipids [28]. Drusen, the most distinguished histopathologic features of AMD, is mainly composed of lipids [29]. Altered lipid metabolism promotes the pathogenesis and development of AMD [10].
We aim to detect the connection between PFAS single and mixed exposure and AMD risk and perform a mediation analysis to assess whether serum lipids are involved in this relationship in a nationally representative cohort.
2. Methods
2.1 Participants
All data are sourced from the National Health and Nutrition Examination Survey (NHANES), and detailed information of NHANES is shown in its website [30]. The research involving human participants underwent a thorough review and received approval from the Research Ethics Review Board of the NCHS. All patients or participants gave written informed consent to be part of this study. This cross-sectional study started with the enrollment of 20497 participants from NHANES 2005–2006 and 2007–2008 cycles. After excluding those who lack data on the four PFAS (n = 16277) and examination of AMD (n = 2421), 1799 individuals remained. Then, participants with missing values on covariates were excluded (n = 194). Finally, 1605 individuals aged ≥40 were included (S1 Fig).
2.2 Fundus examination
Retinal images were captured in the NHANES 2005–2008 cycles using Canon CR6-45NM fundus imaging system [31, 32]. Early AMD: the presence of pigmentary abnormalities and/or soft drusen; late ARM: exudative ARM signs and/or geographic atrophy [33].
2.3 Assessment of PFAS
This study examined four highly detected PFAS compounds in the 2005–2008 NHANES cycle, including PFOA, perfluorohexane sulfonate (PFHxS), PFOS, and perfluorononanoic acid (PFNA). The results less than the low limits of detection (LLOD) were substituted as the LLOD value of each PFAS ⁄ square root of 2 [34].
2.4 Covariates
Carefully selected covariates were considered to control the potential effects of confounding factors: age, gender, education background, race, body mass index (BMI), serum high-density lipoprotein cholesterol levels (HDL, mg/dL), smoking (smoking at least 100 cigarettes in life were considered as smokers), family income-poverty ratio (PIR), drinking (having ≥ 12 alcohol drinks/year were defined as alcohol users), diabetes, history of cataract surgery, hypertension, and cardiovascular disease.
2.5 Statistical analysis
Following the guidelines for the complex oversampling data [35], we used subsample weights of PFAS (WTSA2YR in the 2005–2006 cycle and WTSC2YR in the 2007–2008 cycle). Characteristics of included individuals are recorded as means ± standard deviation (SD) or percentages. Data in skew distribution are reported as median ± interquartile range (IQR). Weighted logistic regression analyses were applied to determine 95% confidence intervals (CI) and odds ratios (OR). The logarithm-transformed PFAS (ln-PFAS) concentrations were added into the model as continuous variables, due to its non-normal distribution. The original PFAS serum concentration was also analyzed in tertiles. Crude model was not included any covariates; model 1 added age, sex, race, education level, family income-poverty ratio, and, BMI; model 2 additionally added serum HDL, alcohol drinking, hypertension, smoking, diabetes, history of cataract surgery, and cardiovascular diseases. We used restricted cubic spline curve (RCS) to find the nonlinear effect. The gWQS package of R software was employed to perform the weighted quantile sum regression (WQS) analysis for the four PFAS [36]. We divided 40% data into the test dataset and 60% into the validation dataset. Mediation analysis was done to assess whether the association of PFOS and AMD risk was mediated by serum lipids including low-density lipoprotein cholesterol (LDL), total cholesterol (TC), high-density lipoprotein cholesterol (HDL), and total triglyceride (TG). We achieved several sensitivity analyses. First, multiple imputation method was conducted to fill in the missing covariate data using R “mice” package [37]. Five imputed datasets were generated and one dataset was used for further analysis (sensitivity ⅰ). Second, we performed a sensitivity analysis by taking “age” as a categorical variable (<65 [n = 1052] or ≥65 [n = 553]) (sensitivity ⅱ). Third, we added serum cadmium into the model for further analysis (sensitivity ⅲ). All code of analyses were written with R 4.3.2.
3. Results
3.1 Study population
This study enrolled 1605 individuals. Among them, 114 participants were diagnosed with AMD (7.1%), of which 100 were early AMD and 14 were late AMD. 51.8% were females and 77.6% were non-Hispanic White. The average age was 56.0 years. Significant differences in age, race, family income-poverty ratio, serum HDL level, history of cataract surgery, and cardiovascular diseases were found between the two groups (P<0.05). Detailed information was shown in Table 1.
3.2 Exposure
Compared to those individuals without AMD, AMD patients (especially late AMD) showed higher serum PFHxS and PFOS concentration (P<0.05) (S1 Table). A significantly positive correlations among the four original PFAS concentrations were detected (S2 Fig). PFNA, PFOA, and PFOS were strongly correlated in pairs (r>0.6).
3.3 PFAS exposure and AMD risk
Table 2 showed the connection of PFAS and AMD risk. After adjusting for all covariates, ln-transformed PFOS level was connected with a higher risk of any AMD (OR, 1.54; 95% CI, 1.12 to 2.11; P = 0.011). Compared to the first tertile, the third tertile of PFOS showed an increased risk of any AMD (OR, 2.34; 95% CI, 1.27 to 4.33; P = 0.010).
Table 3 showed the connection between PFAS and different AMD type risk. Ln-transformed PFOS level was significantly associated with a higher risk of early AMD (OR, 1.43; 95% CI, 1.06 to 1.95; P = 0.024), and ln-transformed PFHxS (OR, 1.72; 95% CI, 1.01 to 2.93; P = 0.045), PFOA (OR, 2.10; 95% CI, 1.21 to 3.63; P = 0.011), and PFOS (OR, 3.35; 95% CI, 1.55 to 7.23; P = 0.004) levels were connected with a higher late AMD risk.
Fig 1 showed the RCS curve of each PFAS exposure and AMD risk. A nonlinear association was found between ln-transformed PFOS level and the risk of AMD (P for nonlinearity = 0.006).
PFOA, perfluorooctanoic acid; PFOS, perfluorooctane sulfonic acid; PFHxS, perfluorohexane sulfonic acid; PFNA, perfluorononanoic acid. The model was adjusted for age, sex, race, education level, family income-poverty ratio, BMI, serum HDL, smoking, alcohol drinking, hypertension, diabetes, history of cataract surgery, and cardiovascular diseases.
3.4 WQS analysis
WQS analysis indicated a significant positive relationship between mixed PFAS exposure and AMD risk (OR, 1.34; 95% CI, 1.03 to 1.75; P = 0.030). PFOS accounted for 93.9% of total weights (S3 Fig).
3.5 Subgroup analysis
After stratified by sex, ln-transformed PFOS level was connected with a higher risk of AMD in men (OR, 2.00; 95% CI, 1.26 to 3.18; P = 0.006). After grouping by hypertension, ln-transformed PFNA (OR, 1.49; 95% CI, 1.02 to 2.19; P = 0.042), PFOA (OR, 2.34; 95% CI, 1.22 to 4.49; P = 0.014), and PFOS (OR, 2.09; 95% CI, 1.45 to 3.04; P<0.001) levels were connected with AMD risk in those who suffered from hypertension. Besides, PFOS exposure was connected with AMD risk in those who were smokers (OR, 1.82; 95% CI, 1.28 to 2.59; P = 0.002), drinkers (OR, 1.79; 95% CI, 1.24 to 2.58; P = 0.004), and had cardiovascular diseases (OR, 1.88; 95% CI, 1.13 to 3.14; P = 0.020) (S2 Table).
3.6 Mediation analysis
After adding all covariates in the model, serum TC (OR, 1.005; 95% CI, 1.001 to 1.009; P = 0.026) and HDL (OR, 1.028; 95% CI, 1.014 to 1.042; P<0.001) levels were connected with AMD risk (S3 Table). Next, we performed a mediation analysis, which showed that serum TC and HDL levels significantly mediated the connection between PFOS exposure and AMD risk and the mediated proportions were 5.73% (P = 0.020) and 7.27% (P = 0.032), respectively, while no significant mediation effects were detected for LDL-C and TG (P > 0.05) (Table 4).
3.7 Sensitivity analyses
We used sensitivity analyses to validate our results (S4 Table), which showed comparable findings.
4. Discussion
This study indicated that PFOS exposure was connected with a higher risk of early, late, and any AMD, and exposure to PFHxS and PFOA was connected with a higher late AMD risk. Serum TC and HDL involved in the effects of PFOS on AMD risk. A nonlinear relationship was detected between PFOS exposure and AMD risk. WQS analysis displayed that PFOS had the most positive weight in the mixed PFAS exposure.
An isomer of the C8 Health Project in China found no significant connection between PFAS exposure and macular disorder and retinal disorder, researchers pointed out this might be attributed to the low prevalence such as macular disorder (2.3%) [23]. It was noteworthy that authors only observed ocular conditions (such as pigment disorder in the macular area) but did not evaluate the specific disease (such as AMD). In our study, AMD was diagnosed by two retinal specialists, with a prevalence of 7.1%. Besides, PFOS exposure showed the strongest association with AMD risk. Many studies reported that PFOS exposure was strongly associated with the prevalence of diseases compared to other PFAS monomers [38–40]. An experimental study revealed that PFOS showed the strongest ability of DNA damage to the HepG2 cell line among seven PFAS, including PFHxS, PFNA, PFOA, PFOS [41].
In the subgroup analysis, a positive relationship between PFOS exposure and AMD was observed in males. Compared to females, the four serum PFAS levels were higher in males (P < 0.001, data not shown) in this study. This may be attributed to the differences in exposure patterns metabolism or kinetics [42]. Higher concentrations may reach the threshold of inducing diseases. Besides, PFOS exposure was positively correlated with AMD risk, especially in those participants with risk factors of AMD, including smoking, alcohol drinking, hypertension, diabetes, and cardiovascular diseases [43, 44].
A recent study indicated that exposure to PFOS can cause significant apoptosis using the retinal pre-organoid model [45]. In addition, one study reported that PFOS exposure significantly reduced the expression of most genes that participated in the opsins in the process of the phototransduction cascade, leading to vision impairment [46]. PFOS could also cause the death of photoreceptors (661W) by upregulating inflammatory response [47]. Romano et al. have found that the cytotoxicity limit of PFOA on ARPE-19 cells was 28.4 ppm [48]. Recently, plenty of studies have provided evidence of the toxicity of PFOA exposure to ocular cells [48–50]. In this present study, PFOA was linearly associated with late AMD risk. The potential molecular mechanism is unclear. Given the lack of evidence, we hypothesized that several PFAS exposure-induced pathophysiological processes may participate in the onset and development of AMD, including lipid deposition, oxidative stress, and chronic inflammation. First, plenty of evidence has confirmed that exposure to PFAS could increase the risk of hepatic steatosis [51, 52] and dyslipidemia [53]. PFOS was significantly connected with higher serum lipids levels [28]. Lipids are a main component of drusen, and retinal pigment epithelium (RPE) cells can accumulate cholesterol from lipoproteins in the circulation and also can recycle it to the photoreceptors or eliminate it by the formation of high-density lipoprotein particles [54]. When some factors such as dyslipidemia disorder the process of reverse cholesterol transport, lipoprotein particles complex may deposit in the Bruch’s Membrane and RPE [55]. Thus, exposure to PFAS may accumulate lipids in the retina or plasma and involve the development of AMD. Second, the retina continuously converts light into electrical signals that require lots of energy and generate reactive oxygen species (ROS) [56]. Nevertheless, excessive ROS will trigger oxidative stress, causing the damage of cellular proteins, DNA, lipids, and impairing the structure and function of the retina [57]. Oxidative stress may be the central process in the onset and development of AMD [58]. PFAS has been reported strong ability to induce oxidative stress by upregulating multiple biomarkers [59, 60]. Third, some researchers propose that the combined factors of immune triggers and the resulting inflammatory response in the pathogenesis of AMD (also known as a two-level model hypothesis) [61]. In 2016, the US National Toxicology Program evaluated and reported PFOA and PFOS exposure-induced immunotoxicity [62]. PFAS has been widely reported to affect inflammation in various organs, such as the lungs, intestines, and liver [63–65]. Thus, PFAS is likely to induce inflammation and then influence the development of AMD. Our results showed that High TC and HDL were connected with a higher AMD risk, and TC and HDL significantly mediated the effects of PFOS on AMD risk. It is reported that a high-cholesterol diet can cause age-related macular degeneration-like pathology in rats [66]. In addition, high serum HDL was widely considered to have a causal relationship with an increased AMD risk [67]. More studies are required to explore the above and other potential mechanisms further in the future.
This current study had some advantages, including prospective strong national representativeness of the study population and multiple statistical methods consisting of logistical regression, RCS curve, WQS analysis, and mediation analysis, which can fully understand the connection between PFAS and AMD. Nevertheless, several limitations existed that should be considered rigorously when interpreting these findings. First, the causation could not be determined. Second, we only examined four highly detected PFAS, and other PFAS did not be analyzed. Third, though multiple covariates were adjusted in our model, the effects of other confounding factors, such as vitreoretinal surgery and genetic factors, could not be considered completely.
5. Conclusion
This study indicates that PFOS was strongly connected with a higher early and late AMD risk, and PFOA and PFHxS were connected with late AMD risk. Serum TC and HDL mediate the connection of PFOS and AMD risk. Further longitudinal studies are required to verify these findings.
Supporting information
S2 Fig. Correlation analysis.
PFOA, perfluorooctanoic acid; PFOS, perfluorooctane sulfonic acid; PFHxS, perfluorohexane sulfonic acid; PFNA, perfluorononanoic acid.
https://doi.org/10.1371/journal.pone.0317678.s002
(DOCX)
S3 Fig. Contribution of PFAS to WQS percentage for age-related macular degeneration.
PFOA, perfluorooctanoic acid; PFOS, perfluorooctane sulfonic acid; PFHxS, perfluorohexane sulfonic acid; PFNA, perfluorononanoic acid.
https://doi.org/10.1371/journal.pone.0317678.s003
(DOCX)
S1 Table. Serum concentrations of PFAS among groups.
https://doi.org/10.1371/journal.pone.0317678.s004
(DOCX)
S3 Table. The association between serum lipids and AMD risk.
https://doi.org/10.1371/journal.pone.0317678.s006
(DOCX)
Acknowledgments
The authors thank the participants and staff involved in data collection and management in the NHANES.
References
- 1. Rein DB, Wittenborn JS, Burke-Conte Z, Gulia R, Robalik T, Ehrlich JR, et al. Prevalence of Age-Related Macular Degeneration in the US in 2019. JAMA ophthalmology. 2022;140(12):1202–8. pmid:36326752
- 2. Wong WL, Su X, Li X, Cheung CM, Klein R, Cheng CY, et al. Global prevalence of age-related macular degeneration and disease burden projection for 2020 and 2040: a systematic review and meta-analysis. Lancet Glob Health. 2014;2(2):e106–16. pmid:25104651
- 3. Tadayoni R, Sararols L, Weissgerber G, Verma R, Clemens A, Holz FG. Brolucizumab: A Newly Developed Anti-VEGF Molecule for the Treatment of Neovascular Age-Related Macular Degeneration. Ophthalmologica Journal international d’ophtalmologie International journal of ophthalmology Zeitschrift fur Augenheilkunde. 2021;244(2):93–101. pmid:33197916
- 4. Gil-Martínez M, Santos-Ramos P, Fernández-Rodríguez M, Abraldes MJ, Rodríguez-Cid MJ, Santiago-Varela M, et al. Pharmacological Advances in the Treatment of Age-related Macular Degeneration. Current medicinal chemistry. 2020;27(4):583–98. pmid:31362645
- 5. Marques AP, Ramke J, Cairns J, Butt T, Zhang JH, Jones I, et al. The economics of vision impairment and its leading causes: A systematic review. EClinicalMedicine. 2022;46:101354. pmid:35340626
- 6. Ding X, Patel M, Chan CC. Molecular pathology of age-related macular degeneration. Progress in retinal and eye research. 2009;28(1):1–18. pmid:19026761
- 7. Smith W, Assink J, Klein R, Mitchell P, Klaver CC, Klein BE, et al. Risk factors for age-related macular degeneration: Pooled findings from three continents. Ophthalmology. 2001;108(4):697–704. pmid:11297486
- 8. Seddon JM, Willett WC, Speizer FE, Hankinson SE. A prospective study of cigarette smoking and age-related macular degeneration in women. Jama. 1996;276(14):1141–6. pmid:8827966
- 9. Agrón E, Mares J, Clemons TE, Swaroop A, Chew EY, Keenan TDL. Dietary Nutrient Intake and Progression to Late Age-Related Macular Degeneration in the Age-Related Eye Disease Studies 1 and 2. Ophthalmology. 2021;128(3):425–42. pmid:32858063
- 10. Lin JB, Halawa OA, Husain D, Miller JW, Vavvas DG. Dyslipidemia in age-related macular degeneration. Eye (Lond). 2022;36(2):312–8. pmid:35017697
- 11. Chakravarthy U, Wong TY, Fletcher A, Piault E, Evans C, Zlateva G, et al. Clinical risk factors for age-related macular degeneration: a systematic review and meta-analysis. BMC ophthalmology. 2010;10:31. pmid:21144031
- 12. Liu L, Li C, Yu H, Yang X. A critical review on air pollutant exposure and age-related macular degeneration. The Science of the total environment. 2022;840:156717. pmid:35709989
- 13. Ju MJ, Kim J, Park SK, Kim DH, Choi YH. Long-term exposure to ambient air pollutants and age-related macular degeneration in middle-aged and older adults. Environmental research. 2022;204(Pt A):111953. pmid:34454934
- 14. Savvaides T, Koelmel JP, Zhou Y, Lin EZ, Stelben P, Aristizabal-Henao JJ, et al. Prevalence and Implications of Per- and Polyfluoroalkyl Substances (PFAS) in Settled Dust. Current environmental health reports. 2021;8(4):323–35. pmid:34985714
- 15. Buck RC, Franklin J, Berger U, Conder JM, Cousins IT, de Voogt P, et al. Perfluoroalkyl and polyfluoroalkyl substances in the environment: terminology, classification, and origins. Integrated environmental assessment and management. 2011;7(4):513–41. pmid:21793199
- 16. Olsen GW, Burris JM, Ehresman DJ, Froehlich JW, Seacat AM, Butenhoff JL, et al. Half-life of serum elimination of perfluorooctanesulfonate,perfluorohexanesulfonate, and perfluorooctanoate in retired fluorochemical production workers. Environmental health perspectives. 2007;115(9):1298–305. pmid:17805419
- 17. Shoeib M, Harner T, G MW, Lee SC. Indoor sources of poly- and perfluorinated compounds (PFCS) in Vancouver, Canada: implications for human exposure. Environmental science & technology. 2011;45(19):7999–8005. pmid:21332198
- 18. Poothong S, Papadopoulou E, Padilla-Sánchez JA, Thomsen C, Haug LS. Multiple pathways of human exposure to poly- and perfluoroalkyl substances (PFASs): From external exposure to human blood. Environment international. 2020;134:105244. pmid:31711019
- 19. Weng X, Liang H, Tan Y, Chen J, Fei Q, Liu S, et al. Mixed effects of perfluoroalkyl and polyfluoroalkyl substances exposure on cognitive function among people over 60 years old from NHANES. Environmental science and pollution research international. 2022;29(21):32093–104.
- 20. Delcourt N, Pouget AM, Grivaud A, Nogueira L, Larvor F, Marchand P, et al. First observations of a potential association between accumulation of per- and polyfluoroalkyl substances in the central nervous system and markers of Alzheimer’s disease. The journals of gerontology Series A, Biological sciences and medical sciences. 2023.
- 21. Blake BE, Fenton SE. Early life exposure to per- and polyfluoroalkyl substances (PFAS) and latent health outcomes: A review including the placenta as a target tissue and possible driver of peri- and postnatal effects. Toxicology. 2020;443:152565. pmid:32861749
- 22. Künzel SE, Frentzel DP, Flesch LTM, Knecht VA, Rübsam A, Dreher F, et al. AI-driven discovery of blood xenobiotic biomarkers in neovascular age-related macular degeneration using iterative random forests. Graefes Arch Clin Exp Ophthalmol. 2024. pmid:38842593
- 23. Zeeshan M, Yang Y, Zhou Y, Huang W, Wang Z, Zeng XY, et al. Incidence of ocular conditions associated with perfluoroalkyl substances exposure: Isomers of C8 Health Project in China. Environment international. 2020;137:105555. pmid:32059142
- 24. Simpson AR, Petrarca R, Jackson TL. Vitreomacular adhesion and neovascular age-related macular degeneration. Survey of ophthalmology. 2012;57(6):498–509. pmid:23068973
- 25. Bakaliou A, Georgakopoulos C, Tsilimbaris M, Farmakakis N. Posterior Vitreous Detachment and Its Role in the Evolution of Dry to Wet Age Related Macular Degeneration. Clinical ophthalmology (Auckland, NZ). 2023;17:879–85. pmid:36960325
- 26. Tien PT, Lin HJ, Tsai YY, Lim YP, Chen CS, Chang CY, et al. Perfluorooctanoic acid in indoor particulate matter triggers oxidative stress and inflammation in corneal and retinal cells. Sci Rep. 2020;10(1):15702. pmid:32973190
- 27. Tan W, Zou J, Yoshida S, Jiang B, Zhou Y. The Role of Inflammation in Age-Related Macular Degeneration. Int J Biol Sci. 2020;16(15):2989–3001. pmid:33061811
- 28. Liu B, Zhu L, Wang M, Sun Q. Associations between Per- and Polyfluoroalkyl Substances Exposures and Blood Lipid Levels among Adults-A Meta-Analysis. Environmental health perspectives. 2023;131(5):56001. pmid:37141244
- 29. Mitchell P, Liew G, Gopinath B, Wong TY. Age-related macular degeneration. Lancet. 2018;392(10153):1147–59. pmid:30303083
- 30. Johnson CL, Paulose-Ram R, Ogden CL, Carroll MD, Kruszon-Moran D, Dohrmann SM, et al. National health and nutrition examination survey: analytic guidelines, 1999–2010. Vital and health statistics Series 2, Data evaluation and methods research. 2013(161):1–24. pmid:25090154
- 31. Klein R, Davis MD, Magli YL, Segal P, Klein BE, Hubbard L. The Wisconsin age-related maculopathy grading system. Ophthalmology. 1991;98(7):1128–34. pmid:1843453
- 32. Klein R, Klein BE, Jensen SC, Mares-Perlman JA, Cruickshanks KJ, Palta M. Age-related maculopathy in a multiracial United States population: the National Health and Nutrition Examination Survey III. Ophthalmology. 1999;106(6):1056–65. pmid:10366071
- 33. CDC. NHANES 2009–2010 Data Documentation, Codebook, and Frequencies. [Available from: https://wwwn.cdc.gov/Nchs/Nhanes/2007-2008/OPXRET_E.htm.
- 34. Hornung RW, Reed LDJAo, hygiene e. Estimation of average concentration in the presence of nondetectable values. 1990;5(1):46–51.
- 35. NHANES. Tutorial—weighting [Available from: https://wwwn.cdc.gov/nchs/nhanes/tutorials/Weighting.aspx.
- 36. Carrico C, Gennings C, Wheeler DC, Factor-Litvak P. Characterization of Weighted Quantile Sum Regression for Highly Correlated Data in a Risk Analysis Setting. Journal of agricultural, biological, and environmental statistics. 2015;20(1):100–20. pmid:30505142
- 37. Su YS, Gelman A, Hill J, Yajima M. Multiple Imputation with Diagnostics (mi) in R: Opening Windows into the Black Box. J Stat Softw. 2011;45(2):1–31.
- 38. Wen X, Wang M, Xu X, Li T. Exposure to Per- and Polyfluoroalkyl Substances and Mortality in U.S. Adults: A Population-Based Cohort Study. Environmental health perspectives. 2022;130(6):67007. pmid:35731224
- 39. Yi W, Xuan L, Zakaly HMH, Markovic V, Miszczyk J, Guan H, et al. Association between per- and polyfluoroalkyl substances (PFAS) and depression in U.S. adults: A cross-sectional study of NHANES from 2005 to 2018. Environmental research. 2023;238(Pt 2):117188. pmid:37775007
- 40. Liu Y, Zhang Z, Han D, Zhao Y, Yan X, Cui S. Association between environmental chemicals co-exposure and peripheral blood immune-inflammatory indicators. Frontiers in public health. 2022;10:980987. pmid:36483254
- 41. Wielsøe M, Long M, Ghisari M, Bonefeld-Jørgensen EC. Perfluoroalkylated substances (PFAS) affect oxidative stress biomarkers in vitro. Chemosphere. 2015;129:239–45. pmid:25455676
- 42. Lin PD, Cardenas A, Hauser R, Gold DR, Kleinman KP, Hivert MF, et al. Temporal trends of concentrations of per- and polyfluoroalkyl substances among adults with overweight and obesity in the United States: Results from the Diabetes Prevention Program and NHANES. Environment international. 2021;157:106789. pmid:34333293
- 43. Rastogi N, Smith RT. Association of age-related macular degeneration and reticular macular disease with cardiovascular disease. Survey of ophthalmology. 2016;61(4):422–33. pmid:26518628
- 44. Kuan V, Warwick A, Hingorani A, Tufail A, Cipriani V, Burgess S, et al. Association of Smoking, Alcohol Consumption, Blood Pressure, Body Mass Index, and Glycemic Risk Factors With Age-Related Macular Degeneration: A Mendelian Randomization Study. JAMA ophthalmology. 2021;139(12):1299–306. pmid:34734970
- 45. Wang Y, Yin N, Yang R, Zhao M, Li S, Zhang S, et al. Development of a simplified human embryonic stem cell-based retinal pre-organoid model for toxicity evaluations of common pollutants. Cutaneous and ocular toxicology. 2023;42(4):264–72. pmid:37602871
- 46. Lee HS, Jang S, Eom Y, Kim KT. Comparing Ocular Toxicity of Legacy and Alternative Per- and Polyfluoroalkyl Substances in Zebrafish Larvae. Toxics. 2023;11(12). pmid:38133422
- 47. Wu LY, Zhang JL, Zeeshan M, Zhou Y, Zhang YT, He WT, et al. Caspase-8 promotes NLRP3 inflammasome activation mediates eye development defects in zebrafish larvae exposed to perfulorooctane sulfonate (PFOS). Environ Pollut. 2024;356:124252. pmid:38815886
- 48. Romano MR, Gatto C, Giurgola L, Ragazzi E, D’Amato Tóthová J. Toxicity Threshold of Perfluorocarbon Liquids for Intraocular Use: Dose-Response Assessment of In Vitro Cytotoxicity of Possible Contaminants. Transl Vis Sci Technol. 2021;10(6):24. pmid:34111270
- 49. Srivastava GK, Andrés-Iglesias C, Coco RM, Fernandez-Bueno I, Medina J, García-Serna J, et al. Chemical compounds causing severe acute toxicity in heavy liquids used for intraocular surgery. Regul Toxicol Pharmacol. 2020;110:104527. pmid:31733229
- 50. Menz DH, Feltgen N, Lechner T, Menz H, Müller BK, Dresp J, et al. Hydrofluoric Acid and Other Impurities in Toxic Perfluorooctane Batches. Transl Vis Sci Technol. 2019;8(3):24. pmid:31171991
- 51. Zhang X, Zhao L, Ducatman A, Deng C, von Stackelberg KE, Danford CJ, et al. Association of per- and polyfluoroalkyl substance exposure with fatty liver disease risk in US adults. JHEP reports: innovation in hepatology. 2023;5(5):100694. pmid:36968216
- 52. Qi Q, Niture S, Gadi S, Arthur E, Moore J, Levine KE, et al. Per- and polyfluoroalkyl substances activate UPR pathway, induce steatosis and fibrosis in liver cells. Environmental toxicology. 2023;38(1):225–42. pmid:36251517
- 53. Dunder L, Lind PM, Salihovic S, Stubleski J, Kärrman A, Lind L. Changes in plasma levels of per- and polyfluoroalkyl substances (PFAS) are associated with changes in plasma lipids—A longitudinal study over 10 years. Environmental research. 2022;211:112903. pmid:35231461
- 54. Curcio CA, Millican CL, Bailey T, Kruth HS. Accumulation of cholesterol with age in human Bruch’s membrane. Investigative ophthalmology & visual science. 2001;42(1):265–74. pmid:11133878
- 55. Curcio CA, Johnson M, Huang JD, Rudolf M. Aging, age-related macular degeneration, and the response-to-retention of apolipoprotein B-containing lipoproteins. Progress in retinal and eye research. 2009;28(6):393–422. pmid:19698799
- 56. Yu DY, Cringle SJ. Retinal degeneration and local oxygen metabolism. Experimental eye research. 2005;80(6):745–51. pmid:15939030
- 57. Ruan Y, Jiang S, Gericke A. Age-Related Macular Degeneration: Role of Oxidative Stress and Blood Vessels. International journal of molecular sciences. 2021;22(3).
- 58. Abokyi S, To CH, Lam TT, Tse DY. Central Role of Oxidative Stress in Age-Related Macular Degeneration: Evidence from a Review of the Molecular Mechanisms and Animal Models. Oxidative medicine and cellular longevity. 2020;2020:7901270. pmid:32104539
- 59. Lin CY, Lee HL, Hwang YT, Su TC. The association between total serum isomers of per- and polyfluoroalkyl substances, lipid profiles, and the DNA oxidative/nitrative stress biomarkers in middle-aged Taiwanese adults. Environmental research. 2020;182:109064. pmid:31884197
- 60. Omoike OE, Pack RP, Mamudu HM, Liu Y, Strasser S, Zheng S, et al. Association between per and polyfluoroalkyl substances and markers of inflammation and oxidative stress. Environmental research. 2021;196:110361. pmid:33131681
- 61. Rozing MP, Durhuus JA, Krogh Nielsen M, Subhi Y, Kirkwood TB, Westendorp RG, et al. Age-related macular degeneration: A two-level model hypothesis. Progress in retinal and eye research. 2020;76:100825. pmid:31899290
- 62. Program NT. National Toxicology Program Monograph on Immunotoxicity Associated with Exposures to PFOA and PFOS. 2016.
- 63. Dragon J, Hoaglund M, Badireddy AR, Nielsen G, Schlezinger J, Shukla A. Perfluoroalkyl Substances (PFAS) Affect Inflammation in Lung Cells and Tissues. International journal of molecular sciences. 2023;24(10). pmid:37239886
- 64. Roth K, Yang Z, Agarwal M, Liu W, Peng Z, Long Z, et al. Exposure to a mixture of legacy, alternative, and replacement per- and polyfluoroalkyl substances (PFAS) results in sex-dependent modulation of cholesterol metabolism and liver injury. Environment international. 2021;157:106843. pmid:34479135
- 65. Li J, Wang L, Zhang X, Liu P, Deji Z, Xing Y, et al. Per- and polyfluoroalkyl substances exposure and its influence on the intestinal barrier: An overview on the advances. The Science of the total environment. 2022;852:158362. pmid:36055502
- 66. Dasari B, Prasanthi JR, Marwarha G, Singh BB, Ghribi O. Cholesterol-enriched diet causes age-related macular degeneration-like pathology in rabbit retina. BMC ophthalmology. 2011;11:22. pmid:21851605
- 67. Fan Q, Maranville JC, Fritsche L, Sim X, Cheung CMG, Chen LJ, et al. HDL-cholesterol levels and risk of age-related macular degeneration: a multiethnic genetic study using Mendelian randomization. Int J Epidemiol. 2017;46(6):1891–902. pmid:29025108