Determining Trace Metal Concentrations in White Wines Andrea Barger*, Alex Havlik, Jamesa Hogges, Danielle Montanari and Siatta Adams Mercer University Department of Chemistry Lab Report by: Andrea Barger Abstract White wines have been shown to contain certain unsafe amounts of trace metals such as cadmium and lead; these elements could be absorbed by the body and do harm to the body’s cells. In this study, two brands of white wine from two different regions of the world were analyzed for trace metal content, along with the urine samples from two participants who drank the wine each day for three weeks using an acid digestion and an inductively coupled plasma instrument (ICP). The study found that wine from the United States contained approximately 1716.88 ppm Fe, negligible amounts of cadmium and lead, 0.0028 ppm Mg, and 0.0840 ppm V, and wine from Italy contained 268.18 ppm Fe, negligible amounts of cadmium, lead, magnesium, and 0.0831 ppm V. There also may be a correlation between these vanadium concentrations in wine and the amount in participants’ urine. White wine is a popular beverage for many adults of twenty one years of age or older in the United States. Based on a study done by Gallup.com, about 67% of adults drink alcohol in the United States, 48% of women and 17% of men say wine is their preferred beverage.1 Several studies have also been done on the health benefits of wine for human bodies. In general, alcohol in healthy moderation has been shown to elevate levels of good cholesterol and keep blood thinner.2 Specifically, wine has been shown to reduce the risk of getting Alzheimer’s disease, types of cancers, and heart disease. Wine has phytochemicals that act as antioxidants to oxidize free radicals and prevent them from harming the body’s cells.2 While it has been shown that several adults drink wine, some studies show that wine may contain trace metals that could be harmful to a person’s health. Trace metals such as lead can be present in wine from a phenomenon called “atmospheric fallout” where dust containing metals could settle on the grapes or from metal containing pesticides used in grape growing.3 The concentration of these metals could increase even more after bottling if the cork and bottling equipment aren’t clean during use.3 Elements such as lead and cadmium have been shown to be present in wines.4 From past studies on different types of wines, the researchers of this project determined five heavy metals that are likely to be found in wine, and these are lead, iron, cadmium, vanadium, copper, and magnesium. In the right concentrations, these metals can be harmful to the body. When ingested, a percentage of these metals in absorbed into the body and the kidney filters out the remaining harmful concentrations through the urine. Metal concentrations in urine can be indicative of the amount in the body. The unhealthy concentration levels in urine of the five metals listed above are found in table 1. Table 1. Metals analyzed and unsafe levels of metals in urine and water. Metal Lead (Pb) Unhealthy Amount of Metal in Urine 0.20 ppm Allowable/Recommended Limit of Metal 0.01 ppm Pb9 Nephrotoxicants Iron (Fe) 0.05 ppm 30 mg Fe / kg person10 Hepatotoxins Cadmium (Cd) 0.05 ppm 0.005 ppm Cd11 Nephrotoxicants Magnesium (Mg) > 240 ppm 1000 mg / day for average adult12 Hepatotoxins Vanadium (V) 0.01 – 0.03 ppm 1.0 – 1.2 ppb V in drinking water13 Respiratory Target Cell When these metals are absorbed by the body, they can harm several parts of the body. The body’s kidneys act as a filter for all toxic substances, and even though the kidneys only comprise 0.5% of total body mass, they receive 20 – 25% of the resting cardiac output. Therefore, chemicals in different body systems are delivered to the kidneys in relatively high amounts, and if toxic metals are in the blood at low, harmless concentrations, they can quickly reach unsafe concentrations in the kidneys. Iron, magnesium, and copper are hepatotoxins and can harm the liver and iron and copper cause hepatocyte death. Magnesium can cause a disease called canalicular cholestasis, which impairs the production of bile in the liver and causes jaundice. Cadmium and lead are nephrotoxicants, which are toxicants that can directly interfere with kidney function. Even in low doses, cadmium can affect several cellular pathways. Vanadium can also cause problems with respiration, such as airway irritation, overproduction of mucus, and chronic bronchitis. Generally, even low concentrations of metals in the body can cause harm. Because of these harmful effects caused by metals in the body, there are several recommended limits for the consumption of these metals. The consumption limits are listed in table 1. The FDA regulates the amounts of lead and cadmium in drinking water, which can be compared to the amounts of these metals in wine. There is also a small amount of vanadium in drinking water which can also be considered a safe amount. If the concentrations of these metals exceed these standards in wine, the wine could be harmful to the body. Also, if these metals are absorbed into the body through the consumption of wine, they would appear in the urine in smaller concentrations. These limits set forth by the FDA are allowable for the United States; however, wines from other countries could have different, little, to no standards on how much heavy metals can be present in food and drink of that country. Table 2. Information about wines used in this experiment. Wine Brand Region of the World Barefoot Wine California, United States Cavit Wine Year Flavor 2010 White Moscato Lombardy’s Provine of Pavia, Italy 2009 Moscato Store Purchased Publix, Macon, GA Kroger, Macon, GA No conclusive studies have been performed on metal content in wines and the body’s absorption of these metals from drinking the wine; this study incorporates all three of those components. In this experiment, two white Moscato wines from two different regions of the world were selected to be studied. Information about these wines is listed above in table 2. The wines were analyzed for the five metals listed in table 1 using an acid digestion and inductively coupled plasma – optical emission spectra (ICP-OES). Finally, two participants were asked to drink eight ounces of wine each night for three weeks to determine the amount of metals absorbed by the body. Urine samples were taken before wine consumption commenced and each week for three weeks afterwards. These urine samples were analyzed using an acid digestion and ICP-OES as well. Using acid digestion, a sample of each substance was acid digested and inductively coupled plasma – optical emission spectra (ICP-OES) was used to quantify metal levels. The acid digestion of the sample is essential for sample preparation because ICP must have an aqueous sample in order to nebulize the sample. Acid digestion is especially useful for getting the trace metals of the wine samples into an aqueous solution with a regulated pH. This experiment is designed to give accurate results on the trace metal levels in the substances analyzed. The ICP-OES will calculate the parts per billion of each metal per sample, and from the metal per sample, we can determine the metal per substance by a back calculation. We must calculate the amount of metal actually in the value returned by the ICP. We multiply the concentration by the amount of sample put into the system, and then divide that number by the total volume before heating to determine the actual concentration in the analyte of interest. General Methods. White wines are commercially available and were purchased at a local store in Macon, Georgia. Wines were decanted off Mercer’s campus and brought into the laboratory in appropriate containers. All glassware used was washed in a 10% HNO3 bath to remove traces of metal. Calibration solutions were made from serial dilutions using techniques in Methods for Preparation of Standard Solutions of Metals.8 Sample Preparation of Wine. A 25 mL sample of each wine was taken and diluted to 100 mL with ultrapure water in a volumetric flask. The pH of each diluted wine sample was measured to ensure the acidic nature of the wine. A method blank was also prepared, using ultrapure water. The pH of the method blank was adjusted to be in the range of the wine samples. (pH 1.00 – pH 1.70). Sample Preparation of Urine. Urine samples were collected each week in appropriate disposable collection vessels. From these samples, a 5 mL sample of each week of each participant was taken and mixed with 2.0 mL concentrated HNO3 and 1.0 mL 30 wt% concentrated H2O2. Samples were heated for one hour and volumes were recorded before and after heating. After heating, each sample was diluted to 50.0 mL with ultrapure water and filtered by gravity filtration with Whatman 41 filter paper. Then, the pH of the samples were tested and adjusted accordingly with concentrated HNO3 to standardize the pH to be in the range of 1.0 to 1.7, similar to wine. Inductively Coupled Plasma. ICP instrument was warmed up for two hours before sample analysis. A water blank, a method blank, urine samples in solution, wine samples in solution were placed into the ICP after digestion. The ICP calculations were done on the computer and converted using WinLab32™ ICP software from Optima™. The ICP-OES gave data at several different wavelengths for all five metals. Calibration curves were not constructed by the WinLab32™ ICP software because the software did not read the concentrations of the standards correctly. Calibration curves were constructed by Excel and can be found in Appendix 1. Only one particular wavelength was chosen to examine from each metal and the calibration curve was constructed from that data set. From the calibration curve, an equation was determined and the intensities given by the ICP were converted into concentrations using the equation. Data was taken on both Moscato wines and weeks one and three of urine samples. The urine samples from week zero before the wine consuming began did not give usable data because the instrument was clogged. The urine sample from week two for one of the participants had to be thrown out because she became ill and took antibiotics for a week and could not ingest wine. In iron, the wavelength chosen was 259.939 nm. This wavelength was chosen because it had the highest signal to noise ratio of all the wavelengths and returned a calibration curve with an R2 value of 0.9974. The concentrations of iron in each of the samples are listed in table 3. Table 3. Concentrations for iron in wine and urine. Sample Participant 1, week 1 Particiant 2, week 1 Participant 1, week 3 Concentration from ICP in sample, ppm Concentration of Fe in substance, ppm Not detectable 1.16 ppm Fe Not detectable Not detectable 0.23 ppm Fe Not detectable Participant 2, week 3 Barefoot Moscato Cavit Moscato Method Blank Not detectable 42921.92 ppm Fe 6704.42 ppm Fe Not detectable Not detectable 1716.88 ppm Fe 268.18 ppm Fe Not detectable The numbers above show that only the wine has a significant concentration of iron in it, and the wine from Italy actually has less iron than the wine from the United States. It is possible that this iron could come from pesticides used in the United States that are not used in Italy. Participant 2 had a small amount of iron in her urine during week 1; however, this is below the allowable limit and is considered safe. Participant 2 is a pescatarian; her larger amount of iron could be due to the amount of fish consumed, relative to Participant 1 who is an omnivore. In vanadium, the wavelength chosen for analysis was 310.23 nm. Again, this wavelength had the highest signal to noise ration and the calibration curve of these data points returned an R2 value of 0.9919. However, there is an iron peak at 309.278 nm that is overlapping with this vanadium peak, and it appears that the vanadium is contaminated with iron. This is possible if the machine were clogged or if the standards were made in close proximity to each other. Nonetheless, this wavelength’s data points returned workable, positive data, which is listed in the following table 4. Table 4. Concentrations for vanadium in wine and urine. Sample Participant 1, week 1 Particiant 2, week 1 Concentration from ICP in sample, ppm Concentration of V in substance, ppm 0.221 ppm V 0.454 ppm V 0.0442 ppm V 0.0908 ppm V Participant 1, week 3 Participant 2, week 3 Barefoot Moscato Cavit Moscato Method Blank 0.456 ppm V 0.455 ppm V 0.452 ppm V 2.101 ppm V 2.078 ppm V 0.0912 ppm V 0.0910 ppm V 0.0904 ppm V 0.0840 ppm V 0.0831 ppm V The urine concentrations of vanadium are higher than what is considered to be safe for vanadium levels in urine. However, because of the iron peak that overlaps with this vanadium wavelength, some of the iron’s fluorescence could be influencing the intensities of the vanadium concentrations in the samples. It is very possible that these concentrations are much lower than actually listed and quite reasonable. The vanadium levels in wine are below the reasonable limit for drinking water, which is much safer. However, these concentrations could be high as well. Vanadium is not usually found in high concentrations in the environment, and it is more reasonable to think that a negligible amount of the vanadium would be found in urine samples and wine samples. In both participants, the amount of vanadium in the urine increased from week one to week three. If these results are accurate, it could be reasonable to assume that the amount of vanadium in the wine is contributing to the increase in vanadium in the urine. Only about 10% of a vanadium sample is absorbed into the body, and over three weeks, the vanadium content the body is filtering out could increase in urine.7 However, the differences between the two participants’ concentrations of vanadium in their urine are quite different, indicating that there could be other factors at work such as diet. For cadmium, the original standard samples used did not return workable data. However, another set of cadmium standards were created and data was taken using those standards. The instrument had slightly different settings at this point, and this could alter the relative interpretations of the data of cadmium, compared to the data of the other metals. The cadmium wavelength chosen for analysis was 226.000 nm. This wavelength was chosen because it had a relatively high signal to noise ratio and the calibration curve returned an R2 value of 0.9997. The wavelength with the highest signal to noise ratio had a high baseline caused by a severe amount of fluorescence. It appeared that some cadmium standards had vanadium contamination and this could be a reason for the cause of fluorescence. It could also be that these standards had another unknown contaminant causing the baseline to move upwards. Nonetheless, the calibration curve did return an equation that was used to find the concentrations of Cd in the samples, which is listed below in table 5. Table 5. Concentrations for cadmium in wine and urine. Sample Participant 1, week 1 Particiant 2, week 1 Participant 1, week 3 Participant 2, week 3 Barefoot Moscato Cavit Moscato Method Blank Concentration from ICP in sample, ppm Concentration of Cd in substance, ppm 0.533 ppm Cd 0.971 ppm Cd Not detected 2.428146 ppm Cd Not detected Not detected Not detected 0.1066 ppm Cd 0.1942 ppm Cd Not detected 0.486 ppm Cd Not detected Not detected Not detected According to the data, all of the urine samples have concentrations of Cd above safe levels. However, the vanadium contamination that appeared to be present in this standard could be adjusting the intensities of the cadmium standards. It is reasonable to think that the cadmium levels are much lower than this, especially considering the graphs at other wavelengths. Cadmium standards had a lot of background noise that could be influencing the data and the unusual concentrations of cadmium in the urine samples could be caused by the clogged instrument or the adjusted settings of the instrument. However, in one urine sample, both wines, and the method blank, cadmium was not detected at all. This could be well representative data because the wine analyzed could not contain cadmium. This ideal situation is feasible, especially if the two countries do enforce regulations on trace metals in wine. There is no evidence to believe they do not enforce these regulations. The cadmium in participant two’s urine samples increased from week one to week three. However, because no cadmium was detected in the wine, it is hard to accredit this to the wine consumption. Therefore, the data could still be affected by the contamination and this increase is unfounded by wine consumption. For magnesium, the wavelength chosen to analyze was 279.553 nm because it was the only wavelength that data points were taken at. However, it had a high signal to noise ratio and the calibration curve of these data points gave an R2 value of 0.9974. The magnesium data at this wavelength is listed below in table 6. Table 6. Concentrations for magnesium in wine and urine. Sample Participant 1, week 1 Particiant 2, week 1 Participant 1, week 3 Participant 2, week 3 Barefoot Moscato Cavit Moscato Method Blank Concentration from ICP in sample, ppm Concentration of Mg in substance, ppm 8.541 ppm Mg 19.97 ppm Mg 16.13 ppm Mg Not detected 0.0700 ppm Mg Not detected 20.63 ppm Mg 1.71 ppm Mg 3.994 ppm Mg 3.226 ppm Mg Not detected 0.0028 ppm Mg Not detected 0.8252 ppm Mg The concentrations of magnesium in these samples are reasonable concentrations. Relatively, magnesium in higher concentrations is more common in urine than the other metals analyzed. Therefore, the magnesium concentrations in urine are reasonable. The third week for participant two contained an undetectable amount of magnesium; this could be normal for a person’s urine to not contain any magnesium at one specific time. Only the Barefoot Moscato had a small amount of magnesium detected; this magnesium could come from the pesticides used in the United States. Magnesium is also contained in tap water in the United States and in rain in general. The grape plants could soak up this metal and it could transfer to the grapes. Therefore, these amounts of magnesium in the urine and wine are reasonable amounts. Participant one, who was consuming the Barefoot Moscato, did experience an increase in magnesium in urine levels from week one to week three. This increase could be from the small amount of magnesium in the Barefoot Moscato, and the body could be absorbing the magnesium from the wine consumed. However, there is a large difference between week one and week three magnesium concentrations in the urine, so it is feasible that other factors such as diet are going into this increase in magnesium. Finally, in lead, the wavelength analyzed was 220.353 nm. This wavelength had the largest signal to noise ratio of the wavelengths that had data and the calibration curve for this data returned an R2 value of 0.998. However, these graphs had broad peaks and a large gap between each line. It also had a small amount of fluorescence that could be contributed to an iron peak that appears around 220.353 nm. The concentrations of lead in the samples are listed below in table 7. Table 7. Concentrations for lead in wine and urine. Sample Participant 1, week 1 Particiant 2, week 1 Participant 1, week 3 Participant 2, week 3 Barefoot Moscato Cavit Moscato Method Blank Concentration from ICP in sample, ppm Concentration of Pb in substance, ppm 9.444 ppm Pb 83.28 ppm Pb 47.19 ppm Pb 7.694 ppm Pb Not detected Not detected Not detected 1.89 ppm Pb 16.656 ppm Pb 9.44 ppm Pb 1.54 ppm Pb Not detected Not detected Not detected The above lead concentrations for urine are all above the safe lead concentration for urine. Particpant two’s week 1 is also extremely high. Participant one’s lead content in urine increased over the two weeks; however, participant two’s lead concentration decreased over the two weeks. It is likely that there is a contaminant in this sample that is once again influencing the intensities by increasing them dramatically. An iron peak could be interfering with these samples; it is also possible that the instrument’s settings were not properly controlled to take accurate readings. These lead concentrations aren’t plausible because they are so high above the healthy limits that a person would surely know if he or she were suffering from lead poisoning. The wine samples had undetectable levels of lead in them. These results are plausible because if countries do regulate the amount of trace metals in wine, it is possible that the iron has been taken out of wine. This means these lead levels in the wine are at healthy amounts. However, it is also possible that there was an error with the instrument and these values were incorrectly recorded. In conclusion, the data and results from this experiment are not conclusive to the amount of trace metals contained in these two white Moscato wines. For the first part of the data analysis, it is suspected that the instrument was clogged. This clog could have altered data for all the urine samples, and for one set of urine samples, it did not return usable data whatsoever. If the clog were fixed before the analysis of the samples, better, more reasonable data would have been obtained and analyzed. Also in the experiment was the inconvenience of the contamination in the standard solutions. The contamination influenced intensity values and made the results slightly unreasonable for the amounts of metals in urine samples and wine. If the standards were made in a more carefully controlled environment, the intensities would have more accurately reflected the concentrations of each trace metal in each sample. Because of the inconsistent data and suspected errors in this experiment, it is recommended that more trials of this experiment be performed before conclusive data is determined. Trace elements are likely to be found in wine to some extent and should be filtered out of the body by the kidneys. However, a longer study would need to be performed to get conclusive data. Three weeks is a short span of time for metals to build up in the body, and studies that have successful results usually experiment with people who have been drinking wine for years. Each participant in this study was no more than two years past the legal drinking age in the United States. Finally, the seeming connection between the increase in vanadium content in the urine from wine consumption should be investigated further before considered conclusive evidence. Because so many errors occurred and the unlikelihood of a high content of vanadium consisting in wine, it is suggested that these experiments be run again, with a closer record kept of other factors that may be influencing these metals, such as diet. References. 1. Gallup.com. U.S. Drinking Rate Edges Up Slightly to 25-Year High. http://www.gallup.com/poll/141656/drinking-rate-edges-slightly-year-high.aspx (accessed April 26, 2011). 2. Today Health. Is Wine Good for You? http://today.msnbc.msn.com/id/21478144/ns/todaytoday_health/ (accessed April 26, 2011). 3. Interlaboratory quality control for lead determination in wine by potentiometric stripping analysis. Froning, M.; Mohl, C.; Ostapczuk, P.; J. Anal. Chem. 345 (1993), 233 – 235 4. Mend, C.; Cabrera, C.; Lorenzo, M.L.; Lopez, M.C.; Science of Total Environment, 181, (1996), 201-208 5. Liva, R. Facing the Problem of Dietary-Supplement Heavy-Metal Contamination: How to Take Responsible Action. Integrative Medicine. June/July 2007. Pp 36-38. 6. World Health Organization: Food and Agriculture Organization of the United Nations. Joint FAO/WHO Expert Committee on Food Additives. http://www.fda.gov/ohrms/dockets/DOCKETS/95s0316/95s-0316-rpt0254-05-vol186.pdf (accessed April 27, 2011). 7. Hamilton, A.; Hardy, H.L. Industrial Toxicology; Publishing Sciences Group, INC.: Massachusetts, 1974; pp 79-186.Klaassen, C.D. Casarett and Doull’s Toxicology: The Basic Science of Poisons. Amdur, M.O.; Doull, J., Eds.; McGraw-Hill:1995; Vol. 5, pp 417-424. 8. M.S. Epstein. Methods for Preparation of Standard Solutions of Metals. P 411 – 432. 9. Food and Drug Administration. Guidance for Industry and FDA: 1991 Letter to Bureau of Alcohol, Tobacco and Firearms Regarding Lead in Wine. http://www.fda.gov/Food/GuidanceComplianceRegulatoryInformation/GuidanceDocuments/Che micalContaminantsandPesticides/ucm077878.htm (accessed April 26, 2011) 10. Center for Disease Control. Morbidity and Mortality Weekly Report. http://www.cdc.gov/mmwr/PDF/wk/mm4206.pdf (accessed April 26, 2011) 11. Agency for Toxic Substance and Disease Registry. Toxic FAQ: Cadmium. http://www.atsdr.cdc.gov/toxfaqs/tf.asp?id=47&tid=15 (accessed April 28,2011) 12. Health Supplement Choices. Magnesium Overdose. http://www.wealthychoices.com/magnesium-overdose.html (accessed April 28, 2011) 13. Agency for Toxic Substances and Disease Registry. ToxGuide for Vanadium. http://www.atsdr.cdc.gov/toxguides/toxguide-58.pdf (accessed April 28, 2011)