Patent Application
20140141522
The present invention generally relates to a method for selective detection of cyanide. Moreover, the invention relates to a kit for selective detection of cyanide and to uses thereof. Furthermore, the invention relates to a device for removing hydrogen cyanide from gaseous phase e.g. tobacco smoke.
Cyanide is highly toxic to humans and most animals because of inactivation of cytochrome C oxidase. It is widely used for important industrial applications and is stored in form of cyanogenic glycosides in more than 2′000 plants such as bamboo, flax seed or cassava (Manihot esculenta Crantz). The latter represents common foodstuff for hundred of millions of people in the developing countries. Inadequately processed cassava products might cause severe acute and chronic health problems. In view of all the above, there is considerable interest in sensitive and selective methods for detecting cyanide in relevant environments such as drinking water, foodstuffs and industrial wastewaters.
Several methods for detecting cyanide are known in the art. Recently, numerous novel reagents for the colorimetric detection of cyanide have been reported. In particular, DE 196 08 808 A1 discloses a colorimetric detection principle based on a positively charged cobinic acid amide compound loaded on an cation exchanger acting as an indicator for cyanide anions or hydrogen cyanide.
The optical detection of cyanide with corrinoids under homogenous conditions has also been demonstrated. See, e.g.: Zelder, F. H. Inorg. Chem. 2008, 47, 1264-1266; Männel-Croise, C.; Zelder, F. Inorg. Chem. 2009, 48, 1272-1274.
Nevertheless, it would be desirable to have further cyanide sensors with even higher sensitivity. In particular, it would be desirable to have a method for visual detection of cyanide below the guideline value of cyanide in drinking water of the World Health Organization (WHO; 0.05 mg/l) (i), the simultaneous visual detection of cyanide and thiocyanate (ii) as well potential applications for the detection of cyanide in foodstuff as well as HCN in cigarette smoke (iii).
Solid-phase extraction (SPE) has generally proven very useful for sample preparation in modern analytical chemistry. The method includes sample preconcentration and prepurification for subsequent further analysis by chromatography, mass spectrometry and other techniques. Applications in almost all areas of chemical analysis including pharmaceutical research, food analysis and drinking water control have been reported. Colorimetric solid phase extraction (C-SPE) describes the concentration and quantification of an analyte directly on a solid support with diffuse reflectance UV-Vis (DRUV-Vis) spectroscopy and has been successfully applied for the quantification of analytes such as I−/I2, formaldehyde, Ni(II), Mo(VI), Pb(II) or As(V). See, e.g.: Arena, M. P.; Porter, M. D.; Fritz, J. S. Anal. Chem. 2002, 74, 185-190.
According to one aspect of the invention, there is provided a method for selective detection of cyanide in a liquid sample, the method comprising determining a color change of a corrinoid compound caused upon direct contact with said sample, wherein said corrinoid compound is selected from the group consisting of (see below for definitions):
In the above, the compounds of formula (I) are as follows:
and the compounds (II), (III) and (IV) are as follows:
Surprisingly, it was found that by adsorbing the above mentioned corrinoid compounds as chemosensors on a solid phase it is possible to realize a highly sensitive and convenient colorimetric detection system for cyanide.
The chemosensors are either commercially available or readily synthesized from commercially available precursors and have been adsorbed on the solid phase without further chemical modifications.
It shall be understood that for any of the above compounds that are chiral, it will generally be acceptable to have a mixture of diastereomers as far as the principle of this invention is concerned. On the other hand, certain compounds will naturally be produced by bacteria in a specific diastereomeric form, which thus will be available more readily than another diastereomeric form.
The term “hepta C1-4 alkyl ester” shall be understood as any linear or branched alkyl ester with up to 4 carbon atoms.
The solid phase acting as an adsorber may be any suitable solid with a large surface area, particularly a material customarily used for chromatography applications. In view of the colorimetric detection principle, the solid phase should be basically white. Depending on the application, it may be a comparatively polar material such as aluminum oxide. For many application, it was found advantageous to use a non-polar solid phase, particularly a C4-C18 silica phase.
According to a preferred embodiment, the corrinoid compound is a cobalamine compound, particularly one of the vitamin B12 vitamers β-cyanocobalamine or β-aquocobalamine or β-hydroxocobalamine. As will generally be known, the latter two compounds are produced by certain bacteria and are converted to β-cyanocobalamine in the process of being purified in activated charcoal. Therefore, β-cyanocobalamine (1) is considered to be a most preferred compound for the purpose of this invention.
Systems with immobilized B12 as the chemosensor show high sensitivity combined with excellent selectivity towards cyanide. Without being bound by theory, it appears that the up to 130 times higher sensitivity of immobilized B12 towards cyanide compared to the optical detection in water results mainly from two different effects: (i) the extraction and concentration of cyanide from the sample solution, as well as (ii) the altered coordination geometry of the immobilized chemosensor within the hydrophobic solid-phase. The latter effect makes cyanide binding more likely.
According to another embodiment, the corrinoid compound is one of several so-called “incomplete” corrinoids such as a cyano-aqua-cobyrinic acid hepta C1-4 alkyl ester (2), cyano-aqua-cobyrinic acid (3) or cyano-aqua-cobinamide (4). These B12 derivatives lacking the nucleotide at the f-side chain were found to be even more sensitive and allowed the visual detection of cyanide below the guideline value for drinking water of the World Health Organisation (WHO; 0.05 mg/l).
According to one embodiment, the method according to this invention is applied for detecting cyanide ions in an aqueous medium.
By virtue of the high selectivity and specificity of the colorimetric reactions, the method according to the present invention may also be applied with samples that also contain further species such as thiocyanate ions and/or isocyanate ions and/or iodide ions, which often cause problems in other cyanide detection methods.
According to a further embodiment, the method of detecting cyanide further comprises the step of also detecting any thiocyanate ions and/or isocyanate ions and/or iodide ions that are present in the sample.
It will be understood that the colorimetric detection step may be realized in several ways. Under certain circumstances it is possible to detect the presence or absence of cyanide by simple visual inspection, i.e. by checking for a discernible color effect. In a further embodiment, the detection is carried out by measurements of diffuse reflectance in the UV/visible spectral range. Further embodiments, which are particularly useful for an automated and fast screening, comprise the use of a digital camera with red/green/blue (RGB) channel encoding.
According to a further embodiment, the method of detecting cyanide further comprises the step of removing at least one interfering colored component contained in the sample. This is particularly helpful for removing green colored components that may be present in liquid samples containing raw extracts from plants.
In many embodiments the direct contact between the liquid sample and the corrinoid compound adsorbed on a solid phase is achieved by transporting the liquid sample to a suitable solid carrier onto which the appropriate corrinoid compound has previously been adsorbed. In another embodiment, however, the liquid sample and the corrinoid compound are brought together in a liquid phase, the latter usually containing an appropriate solvent, and this liquid phase is then transported to a suitable carrier, to which the corrinoid compound will be adsorbed together with the sample species. This latter method is particularly useful for detection of cyanide in a liquid blood sample.
According to a further aspect of the invention, there is provided a kit for selective detection of cyanide in a sample, the kit comprising at least one first colorimetric solid phase extraction device, said first device comprising a non-polar solid phase loaded with a first corrinoid compound selected from the group consisting of:
In a further embodiment, the kit as defined above further comprises at least one further colorimetric solid phase extraction device, said further device comprising a non-polar solid phase loaded with a further corrinoid compound selected from the group consisting of
In general, such a multi-detection kit will also include an adsorber stage that removes one of the detected species, e.g. cyanide, from the sample after it has passed the respective detection stage. Such adsorber stage will thus generally be arranged between two detection stages.
Moreover, it may be advantageous if the detection kit further comprises at least one clearing device for removing interfering components contained in a liquid sample, said clearing device arranged before said first colorimetric solid phase extraction device.
The kits of the present invention are particularly useful for the visual detection of cyanides in drinking water or foodstuff or industrial wastewaters.
As a separate application, the kits of the present invention may be used for the visual detection of cyanide and/or hydrogen cyanide in a colored liquid phase. It will be understood that, e.g. in an aqueous phase, the relative amounts of cyanide ions and hydrogen cyanide will depend on the pH-value.
According to still another aspect of the invention, there is provided a device for removing hydrogen cyanide from tobacco smoke, the device comprising an adsorption medium containing a corrinoid compound adsorbed on a solid phase substrate. Basically, such a device could be incorporated in the filter portion of a cigarette.
According to still another aspect of the invention, there is provided a device for removing hydrogen cyanide from a subject's blood, the device comprising an adsorption medium containing a corrinoid compound adsorbed on a solid phase substrate. In particular, such a device could be incorporated in a hemodialysis apparatus. It will be understood that the underlying principle could also be applied by admixing the corrinoid compound into the subject's blood and subsequently adsorbing the corrinoid compound together with the cyanide by adsorption on a solid phase substrate.
The above mentioned and other features and objects of this invention and the manner of achieving them will become more apparent and this invention itself will be better understood by reference to the following description of various embodiments of this invention taken in conjunction with the accompanying drawings, which show the following:
a) Experimental set-up for the use of C18ec columns for the detection of cyanide in aqueous solution.
b) Experimental set-up for the detection of HCN in the smoke of a cigarette with C18ec cartridges.
a) (From left to right) Side and top views on 1SP (20 nmol; red coloured ring) and after passing solution of CN− (0.26 mg/l, 5 ml, [Ches]=20 mM, pH 9.5) through the column.
b) Corresponding DRUV-vis spectra.
a) DRUV-vis spectra of 2SP (20 nmol) and 2SP (20 nmol) after passing solutions (5 ml, [Ches]=20 mM, pH 9.5) of CN− (0.039 mg/1, 0.078 mg/1, 0.130 mg/l and 0.182 mg/l) through the column.
b) Corresponding CIELab values: L*, a*, b*, and ΔE. ΔL*, Δa*, Δb*=±0.1, (ref.=reference).
a) (From left to right) Top and side views on 2SP (20 nmol, orange coloured ring) and 2SP (20 nmol) after passing solutions (5 ml, [Ches]=20 mM, pH 9.5) of CN− (0.039 mg/1, 0.078 mg/l and 0.182 mg/l) through the column.
b) Calibration curve for CN− at 583 nm and pH 7.5 (a) or pH 9.5 (b) of 2SP-CN.
a) (from left to right): Side and top view on 2SP (20 nmol, orange coloured ring) and 2SP (20 nmol) after passing solutions (5 ml, [Hepes]=20 mM, pH 7.5) of CN− (0.039 mg/1, 0.078 mg/l and 0.182 mg/l) through the column.
b) Corresponding CIELab values: L*, a*, b*, and ΔE. ΔL*, Δa*, Δb*=±0.1, (ref.=reference).
a) DRUV-vis spectrum of 1SP (dashed line, λmax=532 nm) and 1SP after passing the smoke of a cigarette through the C18ec-cartridge (solid line, 1SP-CN, λshoulder=579 nm).
b) DRUV-vis spectrum of 2SP (dashed line, λmax=525 nm) and 2SP after passing the smoke of a cigarette through the C18ec-cartridge (solid line, 2SP-CN, λ=578 nm).
a) UV-Vis spectra of 2 (40 μM in water; [Ches]=20 mM; pH 9.0) and after addition of CN− (20 μM; [Ches]=20 mM; pH 9.0), SCN− (5 mM; [Ches]=20 mM; pH 9.0), and a mixture of CN− and SCN− (20 μM and 5 mM; [Ches]=20 mM; pH 9.0), b) UV-Vis spectra of 1 (40 μM in water; [Ches]=20 mM; pH 9.0) and after addition of CN− (20 μM; [Ches]=20 mM; pH 9.0) and SCN− (5 mM; [Ches]=20 mM; pH 9.0).
a) Experimental set-up before injecting green colored sample;
b) Experimental set-up after passing green colored sample through the device;
c) DRUV-vis spectra of 1SP before (black) and after (red) passing the solution through the device.
a) DRUV-Vis spectra of 2SP (red) and 2SP-CN (black) upon blood spiked with cyanide passed the column (c(CN-)blood=91 μM;
b) Experimental set-up for the detection of cyanide in diluted fresh blood (pH 9.5, Ches 20 mM).
Materials. General information
Potassium cyanide, Vitamin B12 (1), dicyano-cobyrinic acid heptamethylester (2-CN), dicyano-cobinamide (4-CN), Ches and Hepes were obtained from Fluka (Buchs, CH) or Sigma Aldrich. Cyano-aqua-cobyrinic acid heptamethylester 2, cyano-aqua-cobyrinic acid 3 and cyano-aqua-cobinamide 4 were synthesized as pairs of diastereomers from their corresponding dicyano-forms through non-selective displacement of either the (upper) 0- or the (lower) α-cyanide as described elsewhere. Compounds 2 and 2-CN are susceptible for hydrolysis at the ester side chains, especially at basic pH. Therefore also compounds with partially hydrolysed side chains can be applied. KCN stock solutions (10−3 M) were prepared freshly before use. The desired pH values of the stock solutions of the buffers Ches (0.1 M; pH 9.5) and Hepes (0.1 M; pH 7.5) were adjusted by the addition of either a solution of 2 N NaOH or 1 N HCl. All measurements were performed at a final buffer concentration of 20 mM.
Chromabond C18ec polypropylene columns (100 mg) and Chromafix C18ec cartridges (270 mg) were obtained from Machery-Nagel AG Schweiz. In this paper we will use the terms C18ec columns for the former, C18ec cartridges for the latter, and C18ec material for both types, respectively. Polygram polyester sheets Alox N and Octadecyl-modified nano silica layers RP-18W were also obtained from Machery-Nagel AG Schweiz. Solvents of HPLC grade of highest purity and doubly distilled water were used. Waxed cassava roots (Manihot esculenta Crantz), imported from Costa Rica, and cigarettes were purchased at local supermarkets in Zurich, Switzerland. Leaves from Manihot esculenta Crantz were a generous gift from the botanical garden of the university of Zurich.
The colorimetric solid phase extraction (CSPE) devise consisted of a 10 ml syringe that was either connected directly or via a Chromabond adapter PP (Macherey-Nagel) to C18ec columns or C18ec cartridges (
1. Conditioning. The C18ec filter was washed with methanol (0.5 ml) and water (10 ml).
2. Adsorption of Chemosensor. The chemosensor 1 was adsorbed on the top of the C18ec material while an aqueous solution of 1 (0.5 ml; 40 μM) was passed through the filter material. The immobilized chemosensor 1SP (SP for “solid phase”) was visible as a red coloured-ring (height ˜1 mm). 3. Analysis. A sample solution was passed through the filter. Detection with 1SP was indicated by color change. 4. Washing. The solid support was washed with water (10 ml). 5. Regeneration. 1SP was regenerated from 1SP-CN while passing 0.1-1% of aqueous citric acid, acetic acid or trifluoroacetic acid (3 ml) and water (20 ml) through the filter.
Polygram polyester sheets Alox N and Octadecyl-modified nano silica layers RP-18W from Machery-Nagel AG Schweiz were used as test strips. The Alox-sheets and the RP-18W-plates were cut in test stripes of diameters of 15×5 mm for the former and 12×15 mm for the latter, respectively. The test strips were dipped (2 sec) into an aqueous solution of 3 (1 mM) for Alox N and of 2 (1 mM) for RP-18W. Afterwards they were dried for 10 min at 60° C. and then for 1 h at 22° C.
The impregnated test strips were dipped for at least 10 minutes into the analyte solution. In the presence of cyanide, a color change from orange to violet was observed within this time. The color of the test strips remained stable for at least 8 h.
UV-vis spectra were measured at T=21±1° C. with a Cary 50 spectrometer using quartz cells with a path length of 1 cm. DRUV-vis spectra were recorded on a Perkin-Elmer Lambda 50 spectrometer equipped with an integrating sphere setup (diameter 110 mm) and pure MgSO4 as reference material.
For DRUV-vis measurements of immobilized chemosensors and immobilized chemosensor-analyte complexes, the cartridges or columns were opened under greatest care. The top layer containing the immobilized chemosensor-analyte complex was removed from the cartridges or columns, dried 30 min on air) and used for DRUV-vis measurements.
The percentage of reflectance (R) was measured with respect to silica C18ec or to an unmodified Alox-plate as standard white. The Kubelka Munk equation gives the relation between the percentage of reflectance (R) and the concentration of the analyte under assumption of a constant molar absorptivity (ε) and scattering coefficient (s) for a given wavelength:
F(R)=(1−R)2/2R
F(R)=εC/s.
A handheld spectrophotometer CM-2900d from Minolta was used to measure the differences of color in the CIELAB-system with Specular Component Excluded (SCE). All values are averaged from at least 8 measurements. The differences in color ΔE have bee estimated according to:
ΔE=[(ΔL*)2+(Δa*)2+(Δb*)2]1/2.
For the description of color differences the major sphere of ΔE was used.
Detection of Endogenous Cyanide in Foodstuff with C-SPE
Preparation of a cassava root extract was performed as described earlier. The crude solution (20 μl) was diluted with water (980 μl; pH 9.5 [Ches]=0.1 M). Afterward this sample solution was used for C-SPE.
Detection of HCN in Cigarette Smoke with C-SPE
To detect hydrogen cyanide (HCN) in the smoke of a cigarette, two C18ec cartridges were connected as shown in
A vacuum (400 mbar) was applied to pull the smoke of the cigarette through the cartridges. The top layer of cartridge 2 containing the immobilized chemosensor-analyte complex was carefully removed, dried (10 min at 45° C. and 30 min on air) and used for DRUV-vis measurements.
C-SPE with B12 and B12-Derivatives Immobilized on Polymeric Columns and Discs Containing C18 Material
Empore™ SPE material (EC-SPE, 1 ml, product number 4115) with C18-SD was also useful for the visual detection of cyanide. In particular, cyanide was also detected using a self-made filter holder device and polymeric discs containing 1SP and 2SP on C18 filter material (Empore™, product number 2215). Empore™ SPE columns (EC-SPE, 1 ml, product number 4115) and Empore™ extraction discs (C18, diameter of 47 mm, product number 2215) were obtained from 3M Deutschland GmbH. Discs of smaller diameter (4 mm) were made from Empore™ extraction discs using a hole puncher. Immobilization of 1 and 2 onto the polymer and detection of cyanide was performed with 1SP and 2SP as described for the C18ec-columns. These disks were inserted into a filter holder device that was constructed in the mechanical workshop of the Institute of Inorganic Chemistry of the University of Zurich.
Colorimetric Solid Phase Extraction (C-SPE) with Vitamin B12
The detection of cyanide with vitamin B12 (1) is based on the replacement of the intramolecularly bound dimethylbenzimidazole (Dmbz; B) base of 1 with cyanide to form a negatively charged ‘base off’ dicyano-B12 species (1-CN; Scheme 1, equilibrium I). This reaction is accompanied by a red shift of the absorption maxima (λmax=45 nm) and a color change from red to violet.
To apply C-SPE for the detection of cyanide, 1 was immobilized on a commercially available chromabond C18ec column as described in the experimental section. Thereby 1 was concentrated as 1SP (SP for “solid phase”) on the surface of the white C18 material, visible as a red colored ring (
The DRUV-vis spectrum of 1SP looks similar to the absorption spectrum of a mixture of both, the ‘base on’ and ‘base off’ forms of 1. ‘Base off’ 1 has been earlier observed for a supramolecular 1-cucurbit[7]uril complex, in which the α-(lower side) coordinated Dmbz base of 1 has been encapsulated into the hydrophobic host.
In accordance with these studies, we assume partial dissociation of the Dmbz base of 1 from the cobalt center and its binding within the hydrophobic C18-chains of the solid-phase (Scheme 1, equilibrium II). This behavior reassembles the binding of cobalamines (Cbl) in their ‘base off’ form in certain protein-Cbl and nucleic acids-Cbl complexes. ‘Base off’ 1SP contains a cobalt(III)-bound water at the α-side (lower side) of the macrocycle (Scheme 1, equilibrium II). Evidence of the proposed binding mode of 1SP was obtained from comparison with a reflectance spectrum of 1 adsorbed as 1Silica on the surface of unmodified silica material. In this case, the DRUV-vis spectrum of lSilica was different to that of 1SP, but comparable to that of ‘base on’ 1 in water (
When aqueous solutions of cyanide (0-1.04 mg/l) were passed through the C18ec material with 1SP at pH 7.5, the color of 1SP changed immediately from red to violet. This suggests the formation of immobilized 1SP-CN. The colored 1SP-CN complex at the top layer of the C18 matrix material was subsequently investigated with DRUV-vis spectroscopy. The reflection spectrum with a typical maximum of the γ-band at 583 nm is comparable to the absorption maxima of 1-CN under homogenous conditions. Concentrations as low as 1.0 mg/l of cyanide could be detected by the ‘naked-eye’ at pH 7.5 when a 5 ml sample solution was passed through the column (Table 1, entry 3). This value represents a 130 times lower concentration (Table 1, S: Sensitivity) and 13 times lower quantity of cyanide per quantity of chemosensor compared to the detection of cyanide with 1 under homogenous aqueous conditions (Table 1, entries 1 vs 3).
[a][1] = [2] = 40 nmol, [Hepes] = 20 mM, V = 1 ml.
[b] (Zelder, F. H. Inorg. Chem. 2008, 47, 1264-1266).
[c][1] = [2] = 40 nmol; [Ches] = 20 mM, V = 1 ml.
[d][1SP] = [2SP] = 20 nmol, [Hepes] = 20 mM, V = 5 ml.
[e][1SP] = [2SP] = 20 nmol; [Ches] = 20 mM, V = 5 ml.
[f] (Männel-Croise, C.; Zelder, F. Inorg. Chem. 2009, 48, 1272-1274).
[g]>10% over the minimum visual detectable concentration of cyanide
[h]RQ: Ratio of quantities, RQ = n[CN]/n[CS], CS: chemosensor
[i]F: hydrophobic effect, F = RQ/RQSP.
[j]S: Sensitivity, S = cSP(CN−)/c(CN−).
The latter effect (F) can be explained by the altered coordination geometry of the metal-based chemosensor within the hydrophobic solid-support that made the substitution of the Dmbz base with cyanide more likely. The enormous increase in sensitivity by applying C-SPE and B12 (1) has apparently two reasons (i, ii); the extraction of cyanide with 1SP as 1SP-CN complex from the larger sample volume (i) and the weaker intramolecular coordination of the Dmbz base in 1SP due to the hydrophobic heterogeneous environment (ii).
The detection of cyanide with 1SP under basic conditions led to a further increase in sensitivity in accordance with experiences for the detection of cyanide under homogenous conditions. However the impact of the hydrophobic effect was less pronounced (F=5, Table 1, entry 2 vs 4). At pH 9.5 concentrations as low as 0.3 mg/l of cyanide can be visually detected with 1SP (Table 1, entry 4;
When one of the following different anions F−, Cl−, Br−, I−, NO3−, H2PO4−, SO42−, ClO4−, OCN−, SCN−, C2O42−, HCO3−, OAc− (0.1 M; 5 ml; [Ches]=20 mM, pH 9.5) or even high concentrations of halides (1 M; 5 ml; [Ches]=20 mM, pH 9.5) were passed through the column, the red color of immobilized 1SP remained unaffected.
Colorimetric Solid Phase Extraction (C-SPE) of Cyanide with Corrinoids Lacking the Dmbz Base
C-SPE was also used to detect cyanide with B12-derivatives lacking the Dmbz base at the f-side chain, which are generally called ‘incomplete’ corrinoids (see Scheme 2).
Substitution of cobalt(III)-coordinated water from the ‘incomplete’ corrinoid 2SP with cyanide led to the formation of 2SP-CN as indicated by DRUV-vis spectroscopy (Δλmax=45 nm,
Chemosensor 2SP showed good, but lower selectivity for cyanide than 1SP. Most perturbing for the visual detection of cyanide with 2SP were concentrations of 35 mg/l of SCN− (5 ml) and 640 mg/l of I− (5 ml).
Passing higher concentrated solutions (1 ml; 1 M) of I−, SCN− or OCN− through 2SP, led to dark violet coloured iodo-cyano (2SP-I), brown-violet coloured thiocyanato-cyano (2SP-SCN) and red colored cyanato-cyano (2SP-OCN) complexes. The trends in the shifts of the reflection maxima after ligand coordination to 2SP were in good agreement with the behavior of the corresponding complexes in organic solvents. Chloride was apparently not nucleophilic enough to bind to 2SP. Washing the violet coloured 2SP-X SCN− or OCN−) complexes with water resulted in the backformation of red coloured 2SP. Compared to that, 2SP-CN having the stronger coordinating cyanide as an axial ligand was not affected by this washing procedure. All of the following tested anions F−, Cl−, Br−, NO3−, H2PO4−, SO42−, ClO4−, C2O42−, HCO3−, OAc− (0.1 M; 5 ml; [Ches]=20 mM, pH 9.5) showed no interference upon passing 5 ml sample solution through the column of 2SP at pH 9.5 and pH 7.5.
Regeneration of immobilized 1SP-CN, 2SP-CN and 4SP-CN to 1SP, 2SP and 4SP, respectively had been realized by washing the filter with 0.1-1% of diluted aqueous acids (3 ml) and than with water (20 ml). The regeneration of the chemosensor is accompanied by back formation of the red color. During this process, 1SP and 2SP remained adsorbed on the top of the filter material. A series of ten subsequent runs of cyanide detection and regeneration showed no apparent loss of sensitivity or alteration of the quality of immobilized 1SP and 2SP. We assume that much more consecutive tests are possible with this system.
Applications Potential applications of 1SP-4SP were tested for cyanide detection in liquid and gaseous phase. Endogenous cyanide liberated enzymatically from cyanogenic glycosides in samples of freshly ground cassava (Manihot esculanta cruz) or flax seed was detected as indicated by a colour change from red (1SP-4SP) to violet (1SP-CN-4SP-CN) as confirmed with DRUV-Vis spectroscopy (
The simultaneous optical detection of anions by serial connection of SPE cartridges in C-SPE is briefly presented. This approach is distinct from parallel detection and has two major advantages (i-ii). The procedure requires less sample volume (i) and the selectivity of the immobilized chemosensor can be adjusted by consecutive extraction of potentially interfering analytes (ii). We demonstrated herein the principle of this method by the selective visual detection of mM SCN− in the presence of μM CN−. In aqueous solution the visual detection of both, μM cyanide and mM thiocyanate within one sample is not possible with the corrin-based chemosenors 1-4 for two reasons (i, ii) as shown in
With this strategy the optical detection of both, μM of cyanide and mM of SCN− present in a single sample was possible. Cyanide was indicated by a color change from red (Up) to violet (1SP-CN) in Filter 1) (
Comparison of C-SPE with Test Stripes
As an alternative method for the rapid, semi-quantitative visual detection of cyanide, test strips impregnated with corrin-based chemosensors were developed as described in the Experimental Section. Most promising was the immobilization of 3 with seven negatively charged carboxylate side chains as 3TLC on Alox N/UV254 TLC plates and of 2 with seven hydrophobic ester side chains as 2TLC on RP-18 HPTLC plates. Initial studies showed that the reaction of 3TLC to 3TLC-CN and 2TLC to 2TLC-CN was completed after dipping the test stripes for ten minutes into cyanide containing sample solutions.
C-SPE with B12 and B12-Derivatives Immobilized on Polymeric Columns and Discs Containing C18 Material
Empore™ SPE columns (EC-SPE, 1 ml, product number 4115) with C18-SD were also useful for the visual detection of cyanide. 1 and 2 were absorbed as 1SP and 2SP on the polymeric material in the Empore™ SPE columns. The visual detection limits for cyanide corresponds to the values obtained with the C18ec columns that are 0.039 mg/l of cyanide for 2SP and 0.26 mg/l of cyanide for 1SP at pH 7.5.
On the basis of these experiments cyanide was also detected using a self-made filter holder device and polymeric discs containing 1SP and 2SP on C18 filter material (Empore™, product number 2215) as described in the Experimental Section. The sensitivity was comparable to that with the Empore™ SPE columns. Advantageously of this system was the manageability of the system. After passing the sample solution through the disc, the filter device can be easily opened for visual detection of cyanide by determination of the color of 1SP or 2SP. After use, the disc can be easily exchanged. Another advantage was the possibility to further reduce the amount of sensor of 1SP or 2SP from 20 nmol down to 5 nmol without loss in sensitivity.
The technique of C-SPE with spatially separated extraction and detection zones was found to render possible the visual detection of cyanide in colored samples. This form of analysis is not possible in solution. The principle has been demonstrated further above for dark colored cigarette smoke and is shown here for liquid samples by identifying endogenous cyanide in samples of green colored cassava leaves (Manihot esculenta Crantz).
The device contains an extraction zone (silica C18ec column) for removal of colored interferents, before cyanide and/or hydrogen cyanide is detected with an immobilized corrinoid in the detection zone (
When a freshly prepared green-colored sample of a cassava leaf was passed through the device, the colored interferents remained adsorbed in the extraction zone (FIG. 12)—because of attractive hydrophobic interactions with the C18 material. Endogenous cyanide was afterward indicated in the detection zone by a color change of 2SP from orange to violet (
The following methods allow the detection of cyanide in fresh blood or in (acidified) stored blood.
Fresh blood (100 μl) was voluntarily donated and spiked with cyanide (1 mM; 10 μl). The concentration of cyanide in blood is thus 91 μM. It was subsequently dissolved in 100 μl H2O (pH 9.5, Ches 100 mM) and stored for 5 mins. Aquacyanocobyrinic acid heptamethylester (20 μl; 1 mM) was added and upon further 5 mins the sample was pressed through a C18ec column (1 ml). Subsequent the column was washed with 2 ml water to remove adhering blood from the C18ec material. Thereby a violet colored ring of dicyanocobester was visible in the top of C18ec material of the column (
Fresh blood was obtained from the slaughterhouse of the University of Zürich and stored with sodium citrate 3.8% to avoid coagulation. Blood (0.5 mL) was spiked with cyanide (CN−)blood=0-100 μM). 15 mins later, the blood was adjusted to pH 9.6 with Ches buffer (0.47 ml, 1M) and aquacyanocobyrinic acid heptamethylester (30 μl; 1.4 mM) was added.
After 1 min the sample was pressed through a C18ec column (1 ml) using a 10 mL syringe, connected via a Chromabond adapter PP (Macherey-Nagel) to the C18ec column. The column subsequently was washed with 3 ml water to remove adhering blood from the C18ec material. Thereby a red to violet colored ring of dicyanocobester was visible in the top of C18ec material of the column (
In addition to the DRUV-Vis measurements on the filter material, removing of the dicyanocobester from C18ec material is possible with methanol. Spectroscopic UV-vis measurements and thus quantification in solution can also be performed.
Vitamin B12 and B12 derivatives adsorbed on commercially available C18ec filter have been used for the straightforward and rapid detection of low concentrations of cyanide in water. In contrast to the application of the same class of chemosensors under homogenous conditions, the visual detection of cyanide below the guideline value for cyanide in drinking water of the World Health Organization (WHO; 0.05 mg/l) was possible. This method therefore improves significantly existing applications of corrinoids for the optical detection of cyanide and extends colorimetric solid-phase extraction (C-SPE) for cyanide sensing. Recently, Dai and Boon reported about the optical detection of cyanide with a heme cofactor bound in an engineered′ protein binding pocket. Reminiscent of certain ‘base-off’ B12-protein complexes we present herein systems with immobilized B12-chemosensors having a weaker intramolecular coordination of the Dmbz base to the cobalt center of the natural product. This behavior explains the up to 130-fold higher sensitivity compared to the visual detection under homogenous conditions. Applications for the selective detection of biological cyanide in food and hydrogen cyanide in cigarette smoke as well recycling of the system have been demonstrated. Furthermore, it was shown that optical detection of different analytes within a single sample was possible for a mixture of μM CN− and mM SCN− with SPE-cartridges in series connected. A distinction of these anions could not be obtained with the same class of chemosensors under homogenous conditions. In principle, the simultaneous detection of other analytes with suitable chemosensors should be possible following this approach. Applications of such easy-to-use and low-cost devices for environmental, medical and food safety control are envisaged. As an important aspect for the practical implementation of the method, the detection of cyanide and/or hydrogen cyanide in colored samples is made possible by including a clearing device for the removal of interfering colored components contained in the sample.
| Number | Date | Country | Kind |
|---|---|---|---|
| 11161228.9 | Apr 2011 | EP | regional |
| 11179084.6 | Aug 2011 | EP | regional |
| 11193853.6 | Dec 2011 | EP | regional |
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/EP2012/056331 | 4/5/2012 | WO | 00 | 12/19/2013 |
