Patent Application
20050208670
The present invention involves a simple to use and highly accurate method and device for determining concentrations of mercury, a highly toxic naturally occurring element, in biological matter such as fish.
Mercury, as a naturally occurring element, vaporizes in the air and leaches into rivers, lakes and oceans. Plant life, animals and fish consume mercury-containing bacteria and store mercury, generally as methyl mercury, its most toxic state, in various levels of concentration.
Although a wide variety of maladies have been attributed to mercury, medical researchers generally are in agreement that high levels of mercury can cause brain damage, infertility, and, in extreme cases, even death. The EPA warns that high level exposure to methyl mercury can impair central nervous system function, cause kidney, gastrointestinal, cardiovascular and immune system damage, and even lead to shock or death. The FDA warns pregnant women to avoid eating shark, swordfish, king mackerel and tilefish. The FDA also warns nursing mothers and young children as methyl mercury can damage nervous systems in the unborn and young.
Consumers are growing increasingly anxious about the possibility of ingesting methyl mercury when they consume biological material, particularly seafood. Ironically, many health-conscious consumers have reduced their red meat intake as reports were circulated of the ill effects of even moderate red meat consumption, due to the presence of growth hormones in most commercially available beef and the high saturated fat levels of beef generally. Many dietary experts have suggested seafood consumption as a healthier alternative to red meat. As a result, the most health conscious segment of our population began increasing seafood intake only to discover that the same “healthy” alternative may contain unsafe levels of mercury.
Based upon existing data, the FDA has set a one part per million level as the maximum safe concentration level for mercury in fish. Other agencies have weighed in on this issue. For example, California has brought suit against five of the largest grocery chains which operate in that state as well as 20 restaurant chains forcing the grocery chains and restaurants to post warning labels at deli counters and on signage that at least some of the food being offered for sale can pose a health hazard thus forcing compliance with California's Prop 65, the 1986 voter-approved initiative that requires businesses to notify customers if they are being exposed to toxic chemicals.
Because of the above-noted litigation as well as a general awareness of the insidious effects that mercury can have, particularly upon young children and the unborn, there is a desire on the part of consumers as well as grocery chains and restaurants to test food being vended to confirm that such food does not contain excessive levels of mercury and to preferably indicate the mercury content of food being sold for human consumption. Unfortunately, prior to the present invention, there has been no consumer friendly, low cost means to test biological matter for mercury contamination.
Thus, it is an object of the present invention to provide an automated low cost device for enabling consumers and vendors to self test seafood in order to accurately determine mercury levels found therein.
This and further objects will be more readily apparent when considering the following disclosure and appended drawings.
The present invention is directed to a method of determining mercury levels in a biological sample containing mercury as well as a device and kit for carrying out the claimed method. A biological sample containing mercury is at least partially dissolved in an acidic solution to release at least a portion of the mercury contained therein. The acid solution containing the mercury released from the biological sample is exposed to an anode and a cathode connected by an electromotive force causing at least a portion of the mercury released from the biological sample to adhere to a portion of the cathode surface. An alkaline metal salt solution can be incorporated into said acid solution or a second anode is exposed together with the cathode to an alkaline metal salt solution in a separate chamber under the influence of a second electromotive force established between the second anode and cathode. In either embodiment, an alkaline metal amalgam is formed on the surface of the cathode. After the amalgam has been created, the cathode is connected to a reference electrode and the voltage difference between the cathode and reference electrode is measured as an indicator of the mercury level in the biological sample.
The present device and method are capable of detecting fractions of a part per million of mercury in a biological sample. In fish, mercury is generally in the form of methyl mercury, that is, in its organic-bound form. As such, in order to accurately determine mercury levels, the biological matter must be at least partially decomposed to release the subject organic-bound metal.
It is recognized that a well accepted means of releasing metals from biological matter is through decomposition by incineration. However, in this instance, methyl mercury would tend to vaporize during incineration unless incineration conditions were strictly and carefully monitored. As such, incineration was not believed to be of practical value.
It has also been suggested that mercury in biological matter can be detected by the spectrographic analysis of an arc emission spectrum. However, spectrographic detection is sensitive to the presence of most other metals as well which would cause interfering conditions if one was to only seek an indicator of mercury.
Potentially, mercury concentration can also be determined by chemical methods whereby mercury (I) and/or (II) ions can be caused to react with certain reagents to provide colored compounds. However, it is often times difficult to differentiate between levels of such compounds in the fraction of parts per million concentrations such that distinguishing between the color and intensity of differing samples can prove to be a daunting experience. These various prior art bound limitations have effectively been overcome in practicing the present invention, described as follows.
The present invention can best be understood with reference to
In operation, cathode 3 is provided as including insulating coating 13 which covers the entire cathode except for exposed metallic tip proportion 11. In providing cathode 3 in this fashion, the exposed surface area of metallic tip portion 11 can be reproducibly established which greatly enhances reproducibility of the sought after mercury concentration results. Cathode 3 can be composed of one or more metals such as aluminum, platinum, gold, silver, zinc and copper. Optimally, electrode 3 is composed of aluminum.
A measured quantity of biological material, such as the fleshy portion of a fish body is inserted through port 9 and into chamber 1 containing a measured quantity of acidic solution 14. The quantity of the fish sample, generally from 0.5 to 5 gms, is provided for introduction within a measured quantity of acidic solution 14, generally from 0.5 to 5 mls, although larger samples can be measured using the present invention with corresponding larger quantities of acid and other reagents. As soon as the biological sample is introduced to acidic solution 14, decomposition begins thus releasing mercury ions from the intestacies of the biological matter. This step of the process can be carried out while stirring or mechanically or ultrasonically vibrating the solution to enhance uniformity. As such, stirrer 23 appended to motor 25 through shaft 24 can be employed or, alternatively vibrating motor or ultrasonic generator 16 can be used. It is proposed that digestion of the biological matter be conducted in the acidic solution in the presence of a strong oxidizing agent. Solutions which are applicable for practicing the present invention include hydrochloric acid with potassium chlorate, hydrochloric acid with chlorine, nitric acid alone or with sulfuric acid or with hydrogen peroxide or with potassium permanganate or with ammonium persulfate. As a preferred embodiment, the present invention has been carried out employing 12M concentrated hydrochloric acid together with potassium chlorate as oxidizer 10. This oxidizer is employed in quantities of from 0.1 to 0.5 grams when employing test samples of the quantity previously recited.
Through experimentation, it has been determined that a 3 gm sample of fish matter must remain in a concentrated hydrochloric acid solution for at least 70 hours in order to liberate all of the mercury contained therein. However, partial extraction, that is, the extraction of approximately 44% of the total mercury within the sample, can be achieved within approximately 5 minutes of digestion. This is an important recognition for a device requiring 70 hours to achieve a result would have, at best, limited practical utility.
It is noted that during the digestion process, gaseous chlorine (Cl2) is evolved in the presence of concentrated HCl and KClO3 according to the following reaction:
KClO3+6 HCl→3Cl2+KCl+3H2O
In proceeding with the digestion process, it is noted that Hg2Cl2 and HgCl2 are formed as chlorine oxidizes the subject organic mercury compounds. These inorganic compounds are soluble in acidic solution 14 with excess chloride ions (Cl−) resulting in the formation of complex ions, for example, HgCl4−2.
In carrying out the claimed method, mercury ions extracted from the biological matter and thus present in acidic solution 14 are deposited electrochemically on the surface of metallic tip portion 11 of cathode 3. This is accomplished electrochemically by applying an electromotive force between cathode 3 and anode 5. The anode can be composed of, for example, carbon or platinum and electrolysis carried out through the use of DC power source 7. DC power source 7 can be in the form of a dry cell battery creating approximately 1.5 to 6 volts at a current of approximately 5 to 150 mA. Alternatively a regulated DC power supply can be employed providing either a constant voltage or constant current, the later being preferred. First anode 5 can be applied to the inner side wall of digestion chamber 1 in the form of a rod or plate.
In the first embodiment of
In the first embodiment, contained within second chamber 2 is solution 15 which is a salt of alkaline metal such as NaCl and NaSO4. Ideally, solution 15 can comprise a buffered solution of sodium chloride caused to contact metallic tip portion 11 of cathode 3 although the alkaline metal could be any one of the members selected from the group consisting of potassium, sodium, lithium, rubidium and cesium. When this is carried out, cathode 3 can be electrically connected to second anode 35, again, constructed in the form of a rod or plate of, for example, carbon or platinum. A second electromotive force is applied between cathode 3 and second anode 35 resulting in the creation of an alkaline metal amalgam, in this case, sodium. During this step of the process, a voltage from approximately 7 to 15 volts is applied through power source 7 at a current of approximately 50 to 200 mA. The alkaline metal solution could have a pH from 5 to 8 and preferably 7 and can be in the form of an NaOH-KH2PO4 solution.
As an alternative embodiment, reference is made to
Whether the embodiment of
To summarize, mercury ions are first discharged and then form mercury spots on the surface of metallic tip portion 11 of cathode 3 during the period of time in which metallic tip portion 11 resides within digestion chamber 1. In doing so, the following reactions take place at the cathode and anode surfaces:
At the cathode:
Hg+2+2e−→Hg
Hg2+2+2e−→2Hg
2H++2e−→H2
At the anode:
2Cl−−2e−→Cl2
In creating the alkaline metal amalgam on the surface of metallic tip portion 11, it was recognized that an alkaline metal, such as sodium, thermodynamically cannot be deposited on the metal (aluminum) electrode surface if mercury is not already present on such surface. As such, the amount of alkaline metal electrochemically adhering to the cathode surface formed in chamber 2 (
At the cathode:
2H++2e−→H2
Na++Hg+e−→Na (in Hg)
At the anode:
2Cl−−2e−→Cl2
2OH−−2e−→O2+2H+
As a preferred embodiment, stability of the cathode could be enhanced by including a quantity of mercury ions in acidic solutions 14 or 45 to insure the creation of an alkaline metal amalgam in chamber 2 even if the biological sample was devoid of any mercury. In doing so any metering device used to reveal mercury content by measuring current between the cathode and reference electrode 6 would be adjusted to “zero” out the effects of the added mercury ions.
Fish solutions which contain known amounts of mercury were used for calibration. A 2 g fish (salmon) sample which was known to contain no mercury was added to a plastic container which contained 0.2 g of solid KClO3. 2 ml of 12 M HCl was then added into the mixture. A calibration solution of Hg(NO3)2 was then added after chlorine began evolving. Separate tests were conducted having known mercury concentrations of 0, 0.5, 1 and 2 micrograms that correspond to 0, 0.17, 0.33 and 0.67 ppm in the solution. Electrolysis of each solution was conducted using an aluminum cathode, carbon anode and batteries as a DC source. DC voltage was 4.5 V. Electrolysis time was 10 minutes. After electrolysis, electrodes were transferred into new cell for a second electrolysis. The new cell contained sodium chloride and buffer (pH=7) solution (NaOH—KH2PO4) as the electrolyte. Batteries were again used as the DC source. DC voltage was 7.5 V. Electrolysis time was 2 minutes. The aluminum cathode was then transferred into a separate cell which contained water and a reference electrode. Potentials of electrodes (cathode v. reference) were then measured. The cathode remained aluminum and the reference electrode was silver. The potential difference between electrodes in water was stable in limits of ±25 mV and representing a reliable indicator of the amount of mercury in the biological samples.
