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Original Article

Mercury and the Risk of Coronary Heart Disease in Men

Kazuko Yoshizawa, Sc.D., Eric B. Rimm, Sc.D., J. Steven Morris, Ph.D., Vickie L. Spate, Chung-cheng Hsieh, Sc.D., Donna Spiegelman, Sc.D., Meir J. Stampfer, M.D., and Walter C. Willett, M.D.

N Engl J Med 2002; 347:1755-1760November 28, 2002

Abstract

Background

A high dietary intake of mercury from consumption of fish has been hypothesized to increase the risk of coronary heart disease.

Methods

Using a nested case–control design, we investigated the association between mercury levels in toenails and the risk of coronary heart disease among male health professionals with no previous history of cardiovascular disease or cancer who were 40 to 75 years of age in 1986. Toenail clippings were collected in 1987 from 33,737 cohort members, and during five years of follow-up, we documented 470 cases of coronary heart disease (coronary-artery surgery, nonfatal myocardial infarction, and fatal coronary heart disease). Each patient was matched according to age and smoking status with a randomly selected control subject.

Results

The mercury level was significantly correlated with fish consumption (Spearman r=0.42, P<0.001), and the mean mercury level was higher in dentists than in nondentists (mean, 0.91 and 0.45 μg per gram, respectively; P<0.001). After age, smoking, and other risk factors for coronary heart disease had been controlled for, the mercury level was not significantly associated with the risk of coronary heart disease. When the highest and lowest quintiles of mercury level were compared, the relative risk of coronary heart disease was 0.97 in the highest level (95 percent confidence interval, 0.63 to 1.50; P value for trend=0.78). Adjustment for intake of n–3 fatty acids from fish did not appreciably change these results.

Conclusions

Our findings do not support an association between total mercury exposure and the risk of coronary heart disease, but a weak relation cannot be ruled out.

Media in This Article

Table 1Base-Line (1986) Characteristics of the Controls According to Quintile of Mercury Level in the Toenails.
Table 2Relative Risk of Coronary Heart Disease during Three Years of Follow-up According to Toenail Mercury Levels in 934 Subjects.
Article

Several lines of evidence suggest that oxidation of low-density lipoprotein (LDL) in the arterial intima has an important role in atherogenesis.1-3 Mercuric chloride increased hydrogen peroxide formation and depleted glutathione in rats.4 In a prospective cohort study in eastern Finland, fish consumption and the levels of mercury in the hair were positively associated with the risk of coronary heart disease and with serum titers of immune complexes containing oxidized LDL. The authors hypothesized that the associations were due to catalysis of lipid peroxidation by mercury, with which fish in the region are highly contaminated.5

Cadmium is also postulated to increase the risk of hypertension and coronary heart disease,6,7 but the evidence is limited and inconsistent.8 In studies in animals, the administration of mercury modifies the distribution and retention of injected cadmium in various organs,9,10 a result that suggests an interaction between cadmium and mercury. Selenium is thought to antagonize some of the adverse effects of mercury.11-16

In this analysis, we assessed the association between base-line levels of mercury in the toenails and the subsequent risk of coronary heart disease among men in the Health Professionals Follow-up Study. Because the majority of participants are dentists, who have occupational as well as dietary exposures to mercury, the range of mercury burden was unusually wide. The assessment included the evaluation of possible interactions of mercury with cadmium and selenium.

Methods

Study Population

The Health Professionals Follow-up Study is a prospective cohort study of the relation between diet and coronary heart disease and cancer among 51,529 men who were 40 to 75 years old in 1986. The population includes 29,683 dentists, 10,098 veterinarians, 485 pharmacists, 3745 optometrists, 2218 osteopathic physicians, and 1600 podiatrists. The study began in 1986, when all cohort members completed a mailed questionnaire about dietary intake, risk factors for heart disease, and medical history. Every two years, follow-up questionnaires were sent to obtain updated information on newly diagnosed heart disease during the previous two years. In 1987, the cohort members supplied 33,737 sets of toenail clippings; these were stored for subsequent analyses of trace elements in nested case–control studies. The analysis excluded 1595 men whose reported daily energy intake according to the 1986 semiquantitative food-frequency questionnaire was below 800 kcal per day or greater than 4200 kcal per day or who left 70 or more questions blank on the questionnaire. The men who reported a diagnosis of cancer (other than nonmelanoma skin cancer), myocardial infarction, angina, stroke, coronary-artery bypass surgery, or percutaneous transluminal coronary angioplasty on the 1986 questionnaire were also excluded. This study was approved by the Harvard School of Public Health committee for the protection of human subjects; after participants were informed in writing of the purpose of the study, return of nail specimens by mail was deemed to indicate consent.

Ascertainment of Cases

The participants in the Health Professionals Follow-up Study receive a mailed questionnaire every two years. We searched the National Death Index for deaths among those who did not respond to the questionnaires. Through January 31, 1992, we had received questionnaires from, or confirmed the deaths of, more than 94 percent of eligible participants.17,18

Men who had fatal coronary heart disease, nonfatal myocardial infarction, coronary-artery bypass surgery, or percutaneous transluminal coronary angioplasty between the return of toenail clippings in 1987 and January 31, 1992, were considered case patients. A letter was sent to all men who reported a newly diagnosed myocardial infarction on the 1988, 1990, or 1992 follow-up questionnaire to confirm the report and to ask for permission to review their medical records.

A myocardial infarction was confirmed by a study physician using World Health Organization criteria19 or autopsy reports. Fatal coronary heart disease was considered confirmed if it was listed on the death certificate as the underlying cause and a new diagnosis of coronary heart disease was confirmed by records or interviews. Myocardial infarction was considered the probable cause of death if the medical records could not be obtained but the patient required hospital admission and the diagnosis was corroborated by correspondence or telephone interview of a family member or personal physician. Confirmation of coronary-artery bypass surgery or percutaneous transluminal coronary angioplasty was based on self-report only; hospital records obtained for a sample of 102 men confirmed the procedure for 96 percent of them. Sudden death was considered to be due to coronary heart disease, because most sudden deaths in men are due to myocardial infarction.17,18 During five years of follow-up between 1987 and January 1992, coronary heart disease developed in 470 participants eligible for this analysis (234 had nonfatal myocardial infarctions; 109 died of coronary heart disease, including 45 who died suddenly; and 127 underwent coronary-artery bypass grafting or percutaneous transluminal coronary angioplasty). For the main analyses, we used the first end point for men with more than one coronary heart disease outcome during follow-up.

For each patient with coronary heart disease, a control subject without coronary heart disease, who was alive at the time the patient received his diagnosis, was chosen randomly from the cohort participants who returned toenail clippings. The patient and the control were matched according to age (within one calendar year), smoking status (current smoker; former smoker, matched according to the number of years since stopping; or nonsmoker [i.e., never smoked]), and the date on which the clippings were returned (within one month). In this analysis we included 442 matched pairs, as well as an additional 28 patients and 22 controls for whom the matched participant had missing data on nail trace-element values or other variables.

Assessment of Exposure

The levels of mercury, selenium, and cadmium in the toenails were analyzed by instrumental neutron-activation analysis at the University of Missouri Research Reactor.20,21 Before analysis, the toenail clippings were washed in a sonicator with deionized water. Case and control specimens were analyzed together, but in random order, with the case status of the toenail specimens unknown to the laboratory personnel.21,22 In a quality-control study, the average coefficient of variation was 3.0 percent for selenium, 6.2 percent for mercury, and 14.2 percent for cadmium. Because toenails incorporate mercury during formation but are of different lengths, nail clippings taken from all toes at the same time reflect the incorporation of mercury that has occurred over approximately one year. In a study of nurses, the correlation between mercury levels in nails from the same women collected at an interval of six years was 0.58.21

Nutrient intakes were calculated from the 1986 dietary questionnaire.23 In a food-based validation of the 1986 questionnaire, correlations corrected for week-to-week variation were 0.73 for canned tuna fish and 0.58 for dark-meat fish.24

Statistical Analysis

Because the distribution of cadmium levels was skewed to the right, the values were log-transformed to improve normality. The Pearson correlation coefficient for the log-transformed cadmium level and the sample weight was –0.48 (P<0.001). Therefore, the cadmium level was adjusted for the weight of the toenail sample with the use of residuals from the regression of log cadmium values on the specimen weight. A constant, the predicted log cadmium level for the mean of sample weight, was added back to the residuals, and the antilog values were then calculated.

Differences in means between patients and controls were tested by paired t-tests after log transformation or by Wilcoxon signed-rank tests. Spearman correlation coefficients were calculated to assess associations between the levels of the metals in the toenails and the consumption of specific foods.

Mercury values were categorized into quintiles on the basis of their distribution among the controls. The association between the level of mercury in the toenails and the risk of coronary heart disease was expressed as the relative risk, estimated as an odds ratio, with the 95 percent confidence interval, when the lowest quintile was used as the reference category. Multiple logistic-regression analysis was used to control for known and potential risk factors. The intake of nutrients and the body-mass index were also grouped into quintiles. Alcohol intake was grouped into four categories: 0.0, 0.1 to 5.0, 5.1 to 30.0, and 30.1 or more grams per day. Age was grouped into six categories: less than or equal to 50, 51 to 55, 56 to 60, 61 to 65, 66 to 70, and 71 or more years. Smoking status was grouped into three categories (never smoked, former smoker, and current smoker), and the current smokers were further grouped into two categories (1 to 24 and 25 or more cigarettes per day).

Conditional and unconditional logistic regression gave similar overall results; therefore, in this paper only the results from the latter method are given, to increase power in the subgroups by using the data from all patients and controls. Tests for trend were conducted by assigning the median value for each quintile to all persons in that group and using these values as a continuous, five-level variable. Interactions between mercury and selenium or cadmium were assessed by stratified analysis and the use of a cross-product term, with both elements as continuous variables. In the stratified analysis, the association between mercury levels and coronary heart disease was assessed separately within three levels of cadmium or selenium. In the evaluation of joint classification, nine categories were generated by grouping the amounts of each trace element into three levels.

Results

The range of mercury levels among the control participants was 0.03 to 14.56 μg per gram. Table 1Table 1Base-Line (1986) Characteristics of the Controls According to Quintile of Mercury Level in the Toenails. shows the proportion of dentists, the level of fish consumption, and potential confounding factors according to the level of mercury in the toenails. The mean (±SD) mercury level was 0.91±1.47 μg per gram in dentists, as compared with 0.45±0.40 μg per gram among nondentists (P<0.001 by nonparametric unpaired test). Fish consumption among all participants was higher with higher mercury levels. The median toenail mercury levels were 0.29, 0.34, 0.44, 0.62, and 0.75 μg per gram for increasing quintiles of fish consumption (median intake, 20.7, 26.1, 30.4, 37.2, and 51.0 g per day) (Spearman r=0.42, P<0.001).

The mean mercury level was similar in the patients and the controls, both among matched pairs (mean, 0.74±1.21 μg per gram for patients and 0.72±1.40 μg per gram for controls; P=0.76 by the nonparametric paired test) and among all patients and controls (mean, 0.72±1.40 μg per gram for the 470 patients and 0.74±1.21 μg per gram for the 464 controls; P=0.36 by the nonparametric unpaired test). The relative risks of coronary heart disease according to quintile of toenail mercury level are shown in Table 2Table 2Relative Risk of Coronary Heart Disease during Three Years of Follow-up According to Toenail Mercury Levels in 934 Subjects.. After adjusting for age, smoking, and other risk factors for coronary heart disease, we found no evidence of an increased risk of coronary heart disease with higher mercury levels. Furthermore, inclusion of n–3 fatty acid intake from fish in the multivariate model did not change the relative risks appreciably.

Toenail cadmium levels were not associated with the risk of coronary heart disease (P for trend=0.18) after adjustment for age, smoking, alcohol intake, presence or absence of a family history of coronary heart disease, high blood pressure, hypercholesterolemia, and diabetes, and body-mass index (the relative risks [and 95 percent confidence intervals] for increasing quintiles of cadmium were 1.00, 0.95 [0.62 to 1.45], 1.11 [0.72 to 1.71], 0.98 [0.64 to 1.52], and 1.31 [0.85 to 2.03]). For men in the highest category of both mercury and cadmium levels (in which the risk was hypothesized to be the greatest), the relative risk, as compared with those who were in the lowest categories of both, was 1.18 (95 percent confidence interval, 0.68 to 2.04). The interaction was not significant (P=0.87).

Table 3Table 3Relative Risk of Coronary Heart Disease during Three Years of Follow-up According to Toenail Mercury and Selenium Levels among Patients and Controls. shows the relative risks of coronary heart disease according to toenail mercury levels within three roughly equal categories of toenail selenium level (low, medium, and high). The toenail mercury levels within the low and medium selenium categories were not significantly associated with the risk of coronary heart disease. Within the highest nail selenium category, men with the highest mercury level had a higher risk of coronary heart disease than those with the lowest mercury level; however, the result of the test for trend did not attain statistical significance. The subjects were also divided into three groups according to levels of mercury, as well as according to selenium levels. For men in the highest category for mercury and the lowest category for selenium, in which the risk was hypothesized to be the greatest, the multivariate relative risk, as compared with those in the lowest category for mercury and the highest category for selenium, was 0.99 (95 percent confidence interval, 0.57 to 1.72), after age and other risk factors were controlled for (P for interaction=0.89).

In separate multivariate analyses, the relative risk of nonfatal myocardial infarction or fatal coronary heart disease for men in the highest versus the lowest quintile of mercury level was 1.04 (95 percent confidence interval, 0.65 to 1.68; P for trend=0.68), and for coronary-artery bypass grafting or percutaneous transluminal coronary angioplasty, the relative risk was 0.96 (95 percent confidence interval, 0.48 to 1.90; P for trend=0.65).

The form of mercury in fish is primarily methylmercury, and that to which dentists are occupationally exposed is elemental mercury. Because it is possible that different forms of mercury may have different effects on cardiovascular risk, we repeated our analyses after excluding dentists. Although the statistical power was substantially reduced (220 cases), we observed a nonsignificant association with the toenail mercury level. The multivariate relative risk for the highest (0.84 μg per gram) versus the lowest (0.13 μg per gram) quintile of mercury was 1.27 (95 percent confidence interval, 0.62 to 2.59; P for trend=0.43); with additional control for intake of eicosapentaenoic acid plus docosahexaenoic acid, the relative risk was 1.70 (95 percent confidence interval, 0.78 to 3.73; P for trend=0.41).

Discussion

Among the participants in this study, dentists and those who ate more fish had significantly higher levels of mercury in their toenails. However, our data do not support an association between mercury levels and an increased risk of coronary heart disease, as has been reported previously5 and also in a study reported in this issue of the Journal.25 The absence of any clear association is probably not due to methodologic bias, because this study used a nested case–control design within a large prospective cohort, and because the toenail specimens were collected prospectively before the coronary heart disease events occurred. The absence of an association between mercury levels and coronary heart disease could be due to a limited range of mercury exposure. It is also possible that mercury levels in nails are not a good indicator of long-term mercury intake. However, the strong relation between mercury levels in nails and the intake of fish, as measured by a food-frequency questionnaire, and the much higher levels in dentists than nondentists support the validity of mercury levels in nails as a measure of exposure. Because of the occupational exposure of dentists, the range of mercury levels was greater than would be seen in the general U.S. population. Toenail mercury levels have previously been demonstrated to be a valid measure of dietary mercury exposure.26 Nail mercury levels also provided an indicator of the long-term body burden of mercury among women in the Nurses' Health Study.21

We speculated that there might be some beneficial effects of n–3 fatty acids in fish that could counterbalance the effect of mercury. However, the multivariate analysis that controlled for n–3 fatty acid intake did not change the relative risks appreciably. Furthermore, in the same Health Professionals Follow-up Study cohort, increasing fish intake (from one to two servings per week to five to six servings per week) was not associated with the overall incidence of coronary heart disease, although an inverse trend was seen with the small number of sudden deaths.27 The positive association between fish consumption and the risk of coronary heart disease in the Finnish study5,28 could be due to differences in the nutrient composition of the fish, unique contaminants, or different risk-factor characteristics among fish eaters. The concentrations of mercury in hair from subjects in the Finnish study and in toenails from the recent European study25 are similar to or lower than those reported in our study.

The form of mercury consumed in fish is primarily methylmercury, and that due to the occupational exposure of dentists is primarily elemental mercury. As indicated by the strong associations with toenail mercury concentrations in our study, both forms of mercury are absorbed, and both can have serious neurologic toxic effects.29 However, there are some differences in the clinical and pathological manifestations of neurologic toxicity from these two forms of mercury, so the possibility exists that they might influence the risk of cardiovascular disease differently. We found a positive but nonsignificant association between mercury levels and the risk of coronary heart disease in an analysis excluding dentists.

The marginally significant increased risk of coronary heart disease associated with higher mercury levels among men in the highest third of the group with respect to selenium level was probably due to chance, because the combination of high mercury and low selenium levels was not associated with excess risk. The higher proportion of current smokers in the lowest mercury-level category in this study is probably due to the participants' lifestyles, because health-oriented men may eat more fish in addition to not smoking.

In conclusion, toenail mercury levels measured by neutron activation reflect occupational exposure of dentists and intake of fish. However, we found no evidence, over a wide range of mercury exposures, that the overall levels were associated with any substantial increase in the risk of coronary heart disease. Furthermore, we found no increase in risk of coronary heart disease associated with higher mercury levels in combination with low selenium or high cadmium levels. However, a weak relation between mercury exposure, particularly from fish consumption, and the risk of coronary heart disease cannot be excluded.

Supported by research grants from the National Institutes of Health (HL35464 and CA55075).

We are indebted to the participants in the Health Professionals Follow-up Study for their continued cooperation and participation; to Alvin Wing, Lydia Liu, Karen Corsano, and Mira Kaufman for computer assistance; and to Betsy Frost-Hawes, Kerry Pillsworth-Demers, and Mitzi Wolff for compiling the data.

Source Information

From the Departments of Nutrition (K.Y., E.B.R., M.J.S., W.C.W.) and Epidemiology (E.B.R., C.H., D.S., M.J.S., W.C.W.), Harvard School of Public Health, Boston; the Channing Laboratory, Department of Medicine, Brigham and Women's Hospital and Harvard Medical School, Boston (E.B.R., M.J.S., W.C.W.); and the Research Reactor Center, University of Missouri–Columbia, Columbia (J.S.M., V.L.S.).

References

References

  1. 1

    Steinberg D, Parthasarathy S, Carew TE, Khoo JC, Witztum JL. Beyond cholesterol: modifications of low-density lipoprotein that increase its atherogenicity. N Engl J Med 1989;320:915-924
    Full Text | Web of Science | Medline

  2. 2

    Steinberg D, Witztum JL. Lipoproteins and atherogenesis: current concepts. JAMA 1990;264:3047-3052
    CrossRef | Web of Science | Medline

  3. 3

    Steinberg D. Antioxidants and atherosclerosis: a current assessment. Circulation 1991;84:1420-1425
    Web of Science | Medline

  4. 4

    Lund BO, Miller DM, Woods JS. Studies on Hg(II)-induced H2O2 formation and oxidative stress in vivo and in vitro in rat kidney mitochondria. Biochem Pharmacol 1993;45:2017-2024
    CrossRef | Web of Science | Medline

  5. 5

    Salonen JT, Seppanen K, Nyyssonen K, et al. Intake of mercury from fish, lipid peroxidation, and the risk of myocardial infarction and coronary, cardiovascular, and any death in eastern Finnish men. Circulation 1995;91:645-655
    Web of Science | Medline

  6. 6

    Linder MC, ed. Nutritional biochemistry and metabolism: with clinical applications. 2nd ed. New York: Elsevier, 1991:268.

  7. 7

    Schroeder HA. The trace elements and man: some positive and negative aspects. Old Greenwich, Conn.: Devin-Adair, 1973.

  8. 8

    Kristensen TS. Cardiovascular diseases and the work environment: a critical review of the epidemiologic literature on chemical factors. Scand J Work Environ Health 1989;15:245-264
    Web of Science | Medline

  9. 9

    Chmielnicka J, Bem EM, Kaszubski P. Organ and subcellular distribution of cadmium in rats exposed to cadmium, mercury, and selenium. Environ Res 1983;31:266-272
    CrossRef | Web of Science | Medline

  10. 10

    Komsta-Szumska E, Chmielnicka J. Effects of zinc, cadmium or copper on mercury distribution in rat tissues. Toxicol Lett 1983;17:349-354
    CrossRef | Web of Science | Medline

  11. 11

    Parizek J, Ostadalova I. The prospective effect of small amounts of selenite in sublimate intoxication. Experientia 1967;23:142-143
    CrossRef | Medline

  12. 12

    Ganther HE, Goudie C, Sunde ML, Kopecky MJ, Wagner P. Selenium: relation to decreased toxicity of methylmercury added to diets containing tuna. Science 1972;175:1122-1124
    CrossRef | Web of Science | Medline

  13. 13

    Ganther HE, Sunde ML. Effect of tuna fish and selenium on the toxicity of methylmercury: a progress report. J Food Sci 1974;39:1-5
    CrossRef | Web of Science

  14. 14

    Stoewsand GS, Bache CA, Lisk DJ. Dietary selenium protection of methylmercury intoxication of Japanese quail. Bull Environ Contam Toxicol 1974;11:152-156
    CrossRef | Web of Science | Medline

  15. 15

    Sumino K, Yamamoto R, Kitamura SA. Role of selenium against methylmercury toxicity. Nature 1977;268:73-74
    CrossRef | Web of Science | Medline

  16. 16

    Singhal RK, Anderson ME, Meister A. Glutathione, a first line of defense against cadmium toxicity. FASEB J 1987;1:220-223
    Web of Science | Medline

  17. 17

    Rimm EB, Giovannucci EL, Willett WC, et al. Prospective study of alcohol consumption and risk of coronary disease in men. Lancet 1991;338:464-468
    CrossRef | Web of Science | Medline

  18. 18

    Rimm EB, Ascherio A, Giovannucci E, Spiegelman D, Stampfer MJ, Willett WC. Vegetable, fruit, and cereal fiber intake and risk of coronary heart disease among men. JAMA 1996;275:447-451
    CrossRef | Web of Science | Medline

  19. 19

    Rose GA, Blackburn H. Cardiovascular survey methods. 2nd ed. World Health Organization monograph series. No. 56. Geneva: World Health Organization, 1982.

  20. 20

    Cheng T-P, Morris JS, Koirtyohann SR, Spate VL, Baskett CK. The analysis of human nails for 24 elements via k0 and cyclic neutron activation analysis. Nucl Instr Methods Phys Res 1994;353:457-460
    CrossRef | Web of Science

  21. 21

    Garland M, Morris JS, Rosner BA, et al. Toenail trace element levels as biomarkers: reproducibility over a 6-year period. Cancer Epidemiol Biomarkers Prev 1993;2:493-497[Erratum, Cancer Epidemiol Biomarkers Prev 1994;3:523.]
    Web of Science | Medline

  22. 22

    Hunter DJ, Morris JS, Chute CG, et al. Predictors of selenium concentration in human toenails. Am J Epidemiol 1990;132:114-122
    Web of Science | Medline

  23. 23

    Rimm EB, Giovannucci EL, Stampfer MJ, Colditz GA, Litin LB, Willett WC. Reproducibility and validity of an expanded self-administered semiquantitative food frequency questionnaire among male health professionals. Am J Epidemiol 1992;135:1114-1126
    Web of Science | Medline

  24. 24

    Feskanich D, Rimm EB, Giovannucci EL, et al. Reproducibility and validity of food intake measurements from a semiquantitative food frequency questionnaire. J Am Diet Assoc 1993;93:790-796
    CrossRef | Web of Science | Medline

  25. 25

    Guallar E, Sanz-Gallardo I, van't Veer P, et al. Mercury, fish oils, and the risk of myocardial infarction. N Engl J Med 2002;347:1747-1754
    Full Text | Web of Science | Medline

  26. 26

    MacIntosh DL, Williams PL, Hunter DJ, et al. Evaluation of a food frequency questionnaire-food composition approach for estimating dietary intake of inorganic arsenic and methylmercury. Cancer Epidemiol Biomarkers Prev 1997;6:1043-1050
    Web of Science | Medline

  27. 27

    Ascherio A, Rimm EB, Stampfer MJ, Giovannucci EL, Willett WC. Dietary intake of marine n-3 fatty acids, fish intake, and the risk of coronary disease among men. N Engl J Med 1995;332:977-982
    Full Text | Web of Science | Medline

  28. 28

    Rissanen T, Voutilainen S, Nyyssonen K, Lakka TA, Salonen JT. Fish oil-derived fatty acids, docosahexaenoic acid and docosapentaenoic acid, and the risk of acute coronary events: The Kuopio Ischaemic Heart Disease Risk Factor Study. Circulation 2000;102:2677-2679
    Web of Science | Medline

  29. 29

    Magos L. Physiology and toxicology of mercury. Met Ions Biol Syst 1997;34:321-370
    Web of Science | Medline

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  15. 15

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  16. 16

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  17. 17

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    CrossRef

  18. 18

    Yu-Feng Li, Liang Hu, Bai Li, Xiaohan Huang, Erik H. Larsen, Yuxi Gao, Zhifang Chai, Chunying Chen. (2011) Full quantification of selenium species by RP and AF-ICP-qMS with on-line isotope dilution in serum samples from mercury-exposed people supplemented with selenium-enriched yeast. Journal of Analytical Atomic Spectrometry 26:1, 224
    CrossRef

  19. 19

    Chang-Hun You, Byoung-Gwon Kim, Jung-Man Kim, Seung-Do Yu, Yu-Mi Kim, Rock-Bum Kim, Young-Seoub Hong. (2011) Relationship Between Blood Mercury Concentration and Waist-to-Hip Ratio in Elderly Korean Individuals Living in Coastal Areas. Journal of Preventive Medicine and Public Health 44:5, 218
    CrossRef

  20. 20

    Eman M. Alissa, Gordon A. Ferns. (2011) Heavy Metal Poisoning and Cardiovascular Disease. Journal of Toxicology 2011, 1-21
    CrossRef

  21. 21

    Kyong Park, Dariush Mozaffarian. (2010) Omega-3 Fatty Acids, Mercury, and Selenium in Fish and the Risk of Cardiovascular Diseases. Current Atherosclerosis Reports 12:6, 414-422
    CrossRef

  22. 22

    S.G. Donaldson, J. Van Oostdam, C. Tikhonov, M. Feeley, B. Armstrong, P. Ayotte, O. Boucher, W. Bowers, L. Chan, F. Dallaire, R. Dallaire, É. Dewailly, J. Edwards, G.M. Egeland, J. Fontaine, C. Furgal, T. Leech, E. Loring, G. Muckle, T. Nancarrow, D. Pereg, P. Plusquellec, M. Potyrala, O. Receveur, R.G. Shearer. (2010) Environmental contaminants and human health in the Canadian Arctic. Science of The Total Environment 408:22, 5165-5234
    CrossRef

  23. 23

    Guiqing Wen, Aihui Liang, Zhiliang Jiang, Xianjiu Liao, Jianfu Li, Hesheng Jiang. (2010) Resonance scattering spectral detection of ultratrace Hg(II) using herring sperm DNA modified nanogold probe as catalyst. Luminescence 25:5, 373-377
    CrossRef

  24. 24

    Diana Rucker, Ravi Thadhani, Marcello Tonelli. (2010) Trace Element Status in Hemodialysis Patients. Seminars in Dialysis 23:4, 389-395
    CrossRef

  25. 25

    Takashi Yorifuji, Toshihide Tsuda, Saori Kashima, Soshi Takao, Masazumi Harada. (2010) Long-term exposure to methylmercury and its effects on hypertension in Minamata. Environmental Research 110:1, 40-46
    CrossRef

  26. 26

    P. Holmes, K.A.F. James, L.S. Levy. (2009) Is low-level environmental mercury exposure of concern to human health?. Science of The Total Environment 408:2, 171-182
    CrossRef

  27. 27

    Kimberly M Smith, Leila M Barraj, Mark Kantor, Nadine R Sahyoun. (2009) Relationship between fish intake, n-3 fatty acids, mercury and risk markers of CHD (National Health and Nutrition Examination Survey 1999–2002). Public Health Nutrition 12:08, 1261
    CrossRef

  28. 28

    Denise Grotto, Michele M. Castro, Gustavo R. M. Barcelos, Solange C. Garcia, Fernando Barbosa. (2009) Low level and sub-chronic exposure to methylmercury induces hypertension in rats: nitric oxide depletion and oxidative damage as possible mechanisms. Archives of Toxicology 83:7, 653-662
    CrossRef

  29. 29

    L. A. MacDonald, A. Cohen, S. Baron, C. M. Burchfiel. (2009) Occupation as Socioeconomic Status or Environmental Exposure? A Survey of Practice Among Population-based Cardiovascular Studies in the United States. American Journal of Epidemiology 169:12, 1411-1421
    CrossRef

  30. 30

    E. B. Levitan, A. Wolk, M. A. Mittleman. (2009) Fish consumption, marine omega-3 fatty acids, and incidence of heart failure: a population-based prospective study of middle-aged and elderly men. European Heart Journal 30:12, 1495-1500
    CrossRef

  31. 31

    Duane A. Rogers, Steven J. Ray, Gary M. Hieftje. (2009) An electrospray/inductively coupled plasma dual-source time-of-flight mass spectrometer for rapid metallomic and speciation analysis: instrument design. Metallomics 1:1, 67
    CrossRef

  32. 32

    Yuee Yan, Yan Hu, Guopo Zhao, Xingming Kou. (2008) A novel azathia-crown ether dye chromogenic chemosensor for the selective detection of mercury(II) ion. Dyes and Pigments 79:2, 210-215
    CrossRef

  33. 33

    M.I. Castro-González, M. Méndez-Armenta. (2008) Heavy metals: Implications associated to fish consumption. Environmental Toxicology and Pharmacology 26:3, 263-271
    CrossRef

  34. 34

    Martin Kainz, Michael T. Arts, Asit Mazumder. (2008) Essential versus potentially toxic dietary substances: A seasonal comparison of essential fatty acids and methyl mercury concentrations in the planktonic food web. Environmental Pollution 155:2, 262-270
    CrossRef

  35. 35

    C. Rubio, Á. Gutiérrez, A. Burgos, A. Hardisson. (2008) Total dietary intake of mercury in the Canary Islands, Spain. Food Additives & Contaminants: Part A 25:8, 946-952
    CrossRef

  36. 36

    José G. Dórea. (2008) Persistent, bioaccumulative and toxic substances in fish: Human health considerations. Science of The Total Environment 400:1-3, 93-114
    CrossRef

  37. 37

    Kathryn R. Mahaffey, Robert P. Clickner, Rebecca A. Jeffries. (2008) Methylmercury and omega-3 fatty acids: Co-occurrence of dietary sources with emphasis on fish and shellfish. Environmental Research 107:1, 20-29
    CrossRef

  38. 38

    Jesus Olivero-Verbel, Boris Johnson-Restrepo, Rosa Baldiris-Avila, Jorge Güette-Fernández, Elizabeth Magallanes-Carreazo, Lenis Vanegas-Ramírez, Nakamura Kunihiko. (2008) Human and crab exposure to mercury in the Caribbean coastal shoreline of Colombia: Impact from an abandoned chlor-alkali plant. Environment International 34:4, 476-482
    CrossRef

  39. 39

    Marie-Claire Bélanger, Marc-Edouard Mirault, Eric Dewailly, Michel Plante, Line Berthiaume, Micheline Noël, Pierre Julien. (2008) Seasonal mercury exposure and oxidant-antioxidant status of James Bay sport fishermen. Metabolism 57:5, 630-636
    CrossRef

  40. 40

    J. M. Guthrie, J. D. Brockman, J. S. Morris, J. D. Robertson. (2008) The “One Source” cohort — evaluating the suitability of the human toenail as a manganese biomonitor. Journal of Radioanalytical and Nuclear Chemistry 276:1, 41-47
    CrossRef

  41. 41

    Yu-Feng Li, Chunying Chen, Bai Li, Wei Li, Liya Qu, Zeqin Dong, Masaharu Nomura, Yuxi Gao, Jinxuan Zhao, Wei Hu, Yuliang Zhao, Zhifang Chai. (2008) Mercury in human hair and blood samples from people living in Wanshan mercury mine area, Guizhou, China: An XAS study. Journal of Inorganic Biochemistry 102:3, 500-506
    CrossRef

  42. 42

    Gary L. Ginsberg, Brian F. Toal. (2008) Quantitative Approach for Incorporating Methyl MercuryRisks and Omega-3 Fatty Acid Benefits in Developing Species-Specific Fish Consumption Advice. Environmental Health Perspectives
    CrossRef

  43. 43

    Anna L. Choi, Pal Weihe, Esben Budtz-Jørgensen, Paul J. Jørgensen, Jukka Tapio Salonen, Tomi-Pekka Tuomainen, Katsuyuki Murata, Hans Petur Nielsen, Maria Skaalum Petersen, Jórun McTiernan, Philippe Grandjean. (2008) Methylmercury Exposure and Adverse Cardiovascular Effects in Faroese Whalingmen. Environmental Health Perspectives
    CrossRef

  44. 44

    Anna L. Choi, Philippe Grandjean. (2008) Methylmercury exposure and health effects in humans. Environmental Chemistry 5:2, 112
    CrossRef

  45. 45

    Jane L. Guentzel, Enrique Portilla, Katherine M. Keith, Edward O. Keith. (2007) Mercury transport and bioaccumulation in riverbank communities of the Alvarado Lagoon System, Veracruz State, Mexico. Science of The Total Environment 388:1-3, 316-324
    CrossRef

  46. 46

    Susan N. Hansen, William S. Harris. (2007) New evidence for the cardiovascular benefits of long chain omega-3 fatty acids. Current Atherosclerosis Reports 9:6, 434-440
    CrossRef

  47. 47

    Lucio G. Costa. (2007) Contaminants in Fish: Risk-Benefit Considerations. Archives of Industrial Hygiene and Toxicology 58:3, 367-374
    CrossRef

  48. 48

    Donna Mergler, Henry A. Anderson, Laurie Hing Man Chan, Kathryn R. Mahaffey, Michael Murray, Mineshi Sakamoto, Alan H. Stern. (2007) Methylmercury Exposure and Health Effects in Humans: A Worldwide Concern. AMBIO: A Journal of the Human Environment 36:1, 3-11
    CrossRef

  49. 49

    José L. Domingo, Ana Bocio, Gemma Falcó, Juan M. Llobet. (2007) Benefits and risks of fish consumption. Toxicology 230:2-3, 219-226
    CrossRef

  50. 50

    Tomoko Ohno, Mineshi Sakamoto, Tomoko Kurosawa, Miwako Dakeishi, Toyoto Iwata, Katsuyuki Murata. (2007) Total mercury levels in hair, toenail, and urine among women free from occupational exposure and their relations to renal tubular function. Environmental Research 103:2, 191-197
    CrossRef

  51. 51

    Judy R Rees, Stefan Sturup, Celia Chen, Carol Folt, Margaret R Karagas. (2007) Toenail mercury and dietary fish consumption. Journal of Exposure Science and Environmental Epidemiology 17:1, 25-30
    CrossRef

  52. 52

    Yu-Feng Li, Chunying Chen, Bai Li, Qing Wang, Jiangxue Wang, Yuxi Gao, Yuliang Zhao, Zhifang Chai. (2007) Simultaneous speciation of selenium and mercury in human urine samples from long-term mercury-exposed populations with supplementation of selenium-enriched yeast by HPLC-ICP-MS. Journal of Analytical Atomic Spectrometry 22:8, 925
    CrossRef

  53. 53

    Ted Gayer, Robert W. Hahn. (2006) Designing environmental policy: lessons from the regulation of mercury emissions. Journal of Regulatory Economics 30:3, 291-315
    CrossRef

  54. 54

    Esben Budtz-Jørgensen, Philippe Grandjean, Pal Weihe. (2006) Separation of Risks and Benefits of Seafood Intake. Environmental Health Perspectives 115:3, 323-327
    CrossRef

  55. 55

    Marie-Claire Bélanger, Éric Dewailly, Line Berthiaume, Micheline Noël, Jean Bergeron, Marc-Édouard Mirault, Pierre Julien. (2006) Dietary contaminants and oxidative stress in Inuit of Nunavik. Metabolism 55:8, 989-995
    CrossRef

  56. 56

    Katsuyuki Murata, Mineshi Sakamoto, Kunihiko Nakai, Miwako Dakeishi, Toyoto Iwata, Xiao-Jie Liu, Hiroshi Satoh. (2006) Subclinical effects of prenatal methylmercury exposure on cardiac autonomic function in Japanese children. International Archives of Occupational and Environmental Health 79:5, 379-386
    CrossRef

  57. 57

    Cathy W. Levenson, Donald M. Axelrad. (2006) Too Much of a Good Thing? Update on Fish Consumption and Mercury Exposure. Nutrition Reviews 64:3, 139-145
    CrossRef

  58. 58

    Kimberly M. Smith, Nadine R. Sahyoun. (2005) Fish Consumption: Recommendations Versus Advisories, Can They Be Reconciled?. Nutrition Reviews 63:2, 39-46
    CrossRef

  59. 59

    Erik Berg Schmidt, Harald Arnesen, Raffaele de Caterina, Lars Hvilsted Rasmussen, Steen Dalby Kristensen. (2005) Marine n-3 polyunsaturated fatty acids and coronary heart disease. Thrombosis Research 115:3, 163-170
    CrossRef

  60. 60

    Mark A. Moyad. (2005) An introduction to dietary/supplemental omega-3 fatty acids for general health and prevention: Part II. Urologic Oncology: Seminars and Original Investigations 23:1, 36-48
    CrossRef

  61. 61

    William S. Harris. (2004) Are omega-3 fatty acids the most important nutritional modulators of coronary heart disease risk?. Current Atherosclerosis Reports 6:6, 447-452
    CrossRef

  62. 62

    Venkat L. Prasad. (2004) Subcutaneous Injection of Mercury: "Warding Off Evil". Environmental Health Perspectives 112:13, 1326-1328
    CrossRef

  63. 63

    Deborah C Rice. (2004) The US EPA reference dose for methylmercury: sources of uncertainty. Environmental Research 95:3, 406-413
    CrossRef

  64. 64

    Kathryn R Mahaffey. (2004) Fish and shellfish as dietary sources of methylmercury and the ω-3 fatty acids, eicosahexaenoic acid and docosahexaenoic acid: risks and benefits. Environmental Research 95:3, 414-428
    CrossRef

  65. 65

    David N. Juurlink. (2004) Mercury, Coronary Heart Disease, and the Limits of Observational Epidemiology. Therapeutic Drug Monitoring 26:3, 242-243
    CrossRef

  66. 66

    Mark A Moyad, Peter R Carroll. (2004) Lifestyle recommendations to prevent prostate cancer, part II: time to redirect our attention?. Urologic Clinics of North America 31:2, 301-311
    CrossRef

  67. 67

    J LECERF. (2004) Poisson, acides gras oméga 3 et risque cardiovasculaire : données épidémiologiques. Cahiers de Nutrition et de Diététique 39:2, 143-150
    CrossRef

  68. 68

    C. Cahu, P. Salen, M. de Lorgeril. (2004) Farmed and wild fish in the prevention of cardiovascular diseases: Assessing possible differences in lipid nutritional values. Nutrition, Metabolism and Cardiovascular Diseases 14:1, 34-41
    CrossRef

  69. 69

    (2004) Fish Consumption, Mercury Exposure, and Heart Diseases. Nutrition Reviews 62:2, 68-72
    CrossRef

  70. 70

    Pascale Anderle, Pierre Farmer, Alvin Berger, Matthew-Alan Roberts. (2004) Nutrigenomic approach to understanding the mechanisms by which dietary long-chain fatty acids induce gene signals and control mechanisms involved in carcinogenesis. Nutrition 20:1, 103-108
    CrossRef

  71. 71

    J. Morton, H. J. Mason, K. A. Ritchie, M. White. (2004) Comparison of hair, nails and urine for biological monitoring of low level inorganic mercury exposure in dental workers. Biomarkers 9:1, 47-55
    CrossRef

  72. 72

    Clarkson, Thomas W., Magos, Laszlo, Myers, Gary J., . (2003) The Toxicology of Mercury — Current Exposures and Clinical Manifestations. New England Journal of Medicine 349:18, 1731-1737
    Full Text

  73. 73

    (2003) Oily fish and pregnancy. Nutrition Bulletin 28:3, 247-251
    CrossRef

  74. 74

    (2003) Mercury and the Risk of Myocardial Infarction. New England Journal of Medicine 348:21, 2151-2154
    Full Text

  75. 75

    Mark A. Moyad. (2003) The use of complementary/preventive medicine to prevent prostate cancer recurrence/progression following definitive therapy: Part I. lifestyle changes. Current Opinion in Urology 13:2, 137-145
    CrossRef

  76. 76

    Bolger, P. Michael, Schwetz, B.A., . (2002) Mercury and Health. New England Journal of Medicine 347:22, 1735-1736
    Full Text

  77. 77

    Guallar, Eliseo, Sanz-Gallardo, M. Inmaculada, Veer, Pieter van't, Bode, Peter, Aro, Antti, Gómez-Aracena, Jorge, Kark, Jeremy D., Riemersma, Rudolph A., Martín-Moreno, José M., Kok, Frans J., . (2002) Mercury, Fish Oils, and the Risk of Myocardial Infarction. New England Journal of Medicine 347:22, 1747-1754
    Full Text

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