- Methodology article
- Open Access
Detecting and minimizing zinc contamination in physiological solutions
© Kay; licensee BioMed Central Ltd. 2004
- Received: 05 December 2003
- Accepted: 15 March 2004
- Published: 15 March 2004
To explore the role of zinc (Zn) in cellular physiology it is important to be able to control and quantify the level of Zn contamination in experimental solutions. A technique that relies on a Zn-sensitive fluorimetric probe is introduced for measuring Zn concentrations as low as 100 pM. The method depends on the combination of the Zn-probe FluoZin-3 together with a slow Zn-chelator, Ca-EDTA, that reduces the background Zn levels and allows repeated measurements in the same solution.
The method was used to determine which common labware items could leach Zn into solution. Contamination was predictably found to arise from stainless steel and glass. Perhaps less expectedly it was also introduced by methacrylate cuvettes, plastic tissue culture dishes and other plastic labware. The release of nickel from stainless steel electrodes was also imaged using the fluorescent probe Newport Green.
Zn contamination may arise from rather unexpected sources; it is important that all aspects and components used in the course of an experiment be analyzed for the possibility of introducing contaminants.
- Metal Contamination
- Cochlear Implant
- Stainless Steel Electrode
- Metal Release
- Water Immersion Objective
There is increasing evidence for the involvement of transition metal ions at all levels of function within cells; as catalysts, structural elements and possibly as second messengers . In particular Zn (this abbreviation will be used to denote Zn2+) a non-redox active metal has come to the fore recently as a candidate cellular messenger.
Investigations of the role of Zn in cellular processes has been facilitated by the development of sensitive fluorimetric probes that have allowed the measurement of Zn both extracellularly and intracellularly [2–4]. In exploring the role of metal ions it is important to ensure that solutions have little metal contamination, as well as being able to control the free metal concentration level with a chelator [5–7].
If the role of a metal ion is to be explored in a cellular process it is often necessary to use solutions that have very low transition metal concentrations while maintaining calcium and magnesium at normal levels (~2 mM). There are essentially two strategies for implementing such a regime. Firstly, physiological solutions can be cleaned by treatment with metal chelating resins and then taking precautions to prevent contamination of the solution [5, 8, 9]. Secondly, a metal chelator which does not suffer interference from Ca or Mg, can be added to the solution to hold the free transition metal concentrations at very low levels . For example, EDTA saturated with calcium can be used because EDTA has a far higher affinity for transition metals than it does for Ca and Mg, and will chelate transition metals with the displacement of Ca or Mg . With this strategy it is possible to hold the free metal ion concentration at very low levels, however, the chelator could strip metals from exposed metal binding sites. Moreover, the chelator or the chelator-metal complex may act as agonists or antagonists of receptors .
It is certainly possible to reduce the metal contamination in water to levels below ~100 nM with a standard laboratory deionization systems, however as I will show below, metals may be reintroduced into the solution through contact with items that might not seem likely to contaminate the solution.
Metal electrodes since their introduction into experimental neurobiology by Galvani in the eighteenth century have provided an important tool for triggering and recording neuronal activity. There is increasing use of metal electrodes in prostheses for stimulating nerves such as cochlear implants. However, metal ions in solution are often toxic and one has to guard against electrodes serving as a source for ions through leaching or electrolysis.
In this paper I introduce a method for detecting Zn at concentrations as low as 50 pM and use it to determine if common labware items release Zn into solution.
A sensitive method for detecting Zn
FluoZin-3 is a recently developed fluorimetric probe with a high affinity for Zn (Kd 15 nM), yet because it has three carboxyl groups rather than the four of its parent compound fluo-4, has little affinity for Ca or Mg . FluoZin-3 is particularly sensitive to changes in Zn concentration because of the high ratio between the fluorescence of the probe saturated with Zn and that in its absences (140 ± 9, mean ± SEM, n = 3). The free-acid form of FluoZin-3 unlike Zinquin  is not membrane permeant so that if it is delivered intracellularly or extracellularly it does not cross compartment boundaries and can be used to detect the release of Zn into the extracellular space .
FluoZin-3 is as sensitive to cadmium as it is to Zn and therefore the assay cannot distinguish between these two metals. If the occurrence of Cd is suspected, its presence can only be confirmed with a physical technique like inductively coupled mass spectrometry (ICPMS) . FluoZin-3 has a very low sensitivity to iron, while copper quenches its fluorescence.
Sources of Zn contamination
The starting levels of Zn contamination in physiological solutions relies on the purity of the deionized water and chemicals. Preventing contamination depends on avoiding contact with items that might introduce metals into the solution. I found that the initial levels of contamination can be minimized by using water dispensed from a high-grade water purification system (Barnstead, Nanopure, in my case), the highest purity reagents and storing the solutions in Teflon bottles. Furthermore, solutions should be brought up to volume in polymethylpentene cylinders (Nalgene) and transferred with metal-free pipettor tips (Fisher Scientific). Chemicals should be transferred for weighing with a Teflon coated spatula (Fisher Scientific). Even the most transient contact with glass or stainless steel can result in contamination. Using these precautions the contaminating Zn levels could be kept below ~100 nM. If lower Zn levels are required the solution should be treated with a metal chelating resin .
To determine the levels of contamination in water and fluorescent probe, 500 nM of FluoZin-3 was added to a 1 mM Hepes solution that was mixed by slowly aspirating the solution 5 times into a 1 ml pipette tip. Inversion of the cuvette with the open end covered with parafilm led to increases in Zn levels probably through the more vigorous stirring action. The Zn concentration was estimated from the fluorescence using the addition of 1 nM ZnSO4 to calibrate the signal and the linear relationship between fluorescence and Zn in the concentration range of 0.1 to 10 nM (data not shown). Under these conditions the level of contamination corresponded to 7.0 ± 0.4 nM (mean ± SEM, n = 3). Soaking the cuvette in 2 mM EDTA for up to 4 days did not change the level of contamination suggesting that it arises from the water, Hepes and/or the probe. Little metal contamination was found in the probe (personal communication Dr. Kyle Gee, Molecular Probes) and so most of the Zn probably arises from the water and Hepes. If the same experiment was performed with the Hepes saline the levels of Zn contamination was found to be 10.8 ± 1.1 nM (mean ± SEM, n = 5).
As a starting point for analyzing how solutions might be contaminated with Zn through contact with various labware items I used the example of an experiment attempting to image Zn release from hippocampal slices, testing all components that came into contact with the physiological saline during the experiment [15, 17]. For example, in the course of such experiments I initially used a polyethylene transfer pipette (Fisher Scientific) to move slices from the holding chamber to the experimental apparatus. However, the pipette introduced significant contamination. Indeed, aspirating metal-free buffered solution for only a few seconds was sufficient to introduce detectable levels of Zn into solution.
Passage of a solution through a Hamilton syringe with a metal tip led to the introduction of Zn into the solution even for very short sojourns. Immersing the tip of the syringe into the detection solution for only one to two seconds also introduced contaminating Zn.
Zn-leaching by common labware items. Items were tested by immersion in 2 ml of Hepes saline containing 500 nM FluoZin-3 and 25 μM Ca-EDTA in Hepes saline for 5 s and were scored as 'Zn-leaching' if the increase in fluorescence was greater than that induced by the introduction of 0.5 nM ZnSO4.
Glass cover slips
Cell culture dishes (Becton Dickinson, 35 mm)2
Cylinders (polymethylpentene, Nalgene)
Latex gloves (Fisher examination gloves powder free)
Metal-free pipette tips (Fisher Scientific)
Methacrylate cuvettes (Fisher Scientific)1
MicroFil syringe needle (WPI)
Sintered glass bubblers (Fisher Scientific)
Saran Wrap™ (S.C. Johnson & Son, Inc.).
Tuberculin syringe (Becton Dickinson)
Plastic bubblers (Discard-a-stone, Lee's aquarium and pet products)1
Plastic cover slips (Ted Pella)2
Sylgard (Dow Corning)
Transfer pipettes (Fisher Scientific)2
Some items, even if they were washed extensively with water, introduced Zn contamination. Only if they were soaked in 2 mM EDTA (1–2 days) could they be cleared of contamination. This was the case for Tygon tubing and methacrylate cuvettes. Soaking plastic tissue culture dishes (Becton Dickinson, 35 mm) in 10% nitric acid for two days eliminated the metal contamination whereas EDTA was ineffective. While 10% nitric acid was ineffective in treating methacrylate cuvettes. Others items such as Hamilton syringes, glass and tuberculin syringes served to contaminate solutions even after extensive washing in EDTA or 10% nitric acid.
It is worth bearing in mind that most physiological solutions need to be aerated with a gas dispersion tube, which if it is fabricated from glass, will introduce Zn contamination. Disposable plastic fish tank bubblers (Discard-a-stone) presoaked in EDTA can be used to avoid contamination during bubbling.
Zn release from glass
A quartz cuvette (Hellma) exhibited an even more dramatic slow increase in fluorescence than the methacrylate cuvettes. Soaking the cuvette for 2–4 days in 2 mM EDTA or 10% nitric acid reduced the slow increase, however, if the treatment was not repeated, the slow increase returned within 2–3 days. This suggests that EDTA or acid removes Zn from the superficial layers that are then repopulated by diffusion of the metal from within the quartz.
In imaging experiments brain slices are often placed in a chamber with a glass bottom, while in some cases water immersion objectives are used, both of which can leach Zn into the solution. This can be prevented by wrapping both the slide and objective with a single layer of Saran Wrap™. Alternatively a plastic cover slip (Ted Pella) can be used or a glass cover slip can be coated with a thin layer of Sylgard™.
Metal release from electrodes
I have introduced a technique that can detect Zn at very low levels that can be calibrated internally and allows for the reuse of probes that are rather expensive. The method is comparable in its sensitivity to the state-of-the-art physical methods such as ICPMS that require costly dedicated equipment .
The sources of metal contamination can be rather unexpected and it is important to analyze all phases of the experiment to determine if contaminating metals might be introduced . My test of labware was of course not comprehensive but the method provides a simple cost effective one for testing any solution or labware.
The method also provides a way of visualizing the release of metals from electrodes such as nickel that can exert a pharmacological action upon the tissue. In addition the technique may prove of value in determining the leakage of metals through breaks in insulation and the leaching of metals from implantable biomedical devices such as stents .
The passage of current through a stainless steel electrode can induce the release of metal ions through electrolysis. Therefore, in imaging experiments in biological tissues, where for example Zn release is to be imaged with a fluorimetric probe, artifacts may arise. This can best be guarded against by using tungsten electrodes.
It is perhaps worth mentioning that glass microelectrodes may leach metals into solution and into the adjacent tissue [22–24]. Patch recordings are typically made with an intracellular solution that contains a chelator that can prevent metal diffusing into the cell but may strip metals from intracellular proteins.
Diffusion of metal ions can occur within glass as it is an amorphous solid . Although EDTA or nitric acid can remove metals from the surface layers, diffusion from the depths of glass may replenish the surface metal. This may hold true for other materials, and it is therefore important to test if after EDTA treatment or nitric acid treatment Zn contamination might recur through this mechanism. The method introduced here may be of value in measuring the diffusion of metals within glass.
A simple method is presented for measuring the zinc concentrations above ~50 pM. I have shown that metal contamination may arise from a number of different sources and that rather than acting on faith, it is best to test labware items for their tendency to leach metals into solution. Stainless steel electrodes release nickel, which may lead to artifactual signals in imaging experiments.
Excitation-emission spectra and fluorescent time-courses were determined on a Hitachi F-4500 spectrofluorimeter using a methacrylate cuvette whose temperature was controlled by a circulating water bath (26°C). Spectra and time-courses were measured in a Hepes buffered saline containing (in mM): 140 NaCl, 2.5 KCl, 2 CaCl2, 2 MgSO4 and 10 Hepes (pH 7.4).
Electrodes were imaged with a 10 × water immersion objective on an Olympus BX50WI. Illumination was provided by a Till Photonics monochromator at 480 nm, passed through a dichroic (Q495lp, Chroma) and then though a filter (HQ530/60 Chroma) onto the faceplate of a Princeton Instruments cooled CCD camera. Data was acquired by the MetaFluor program (Universal Imaging Corp) and the images were analyzed using the ImageJ (NIH) program.
Current passage through 5 MΩ metal electrodes (stainless steel or tungsten, A-M Systems) was controlled by pClamp software (Axon Instruments) gating a constant current device (AMPI).
FluoZin-3 and NPG (Molecular Probes), Hepes (Calbiochem), MgSO4, NaCl, KCl (Sigma), Nitric acid (Fisher Scientific, Optima Grade), EDTA & CaCl2 (Fluka). All Zn solutions were prepared from a standard solution of ZnSO4 purchased as a 0.051 M standardized solution (Aldrich)
This work was supported by a grant from the Carver Scientific Research Initiative, University of Iowa. I thank Drs. Christoph Fahrni, Kyle Gee and Jason Telford for comments on an earlier version of this manuscript and Dr. Thomas O'Halloran for helpful discussions.
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