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Technical Specifications Introduction Physical Specifications Chemical / Operational
Specifications Interference: Procedure for determining the concentration of CHLORIDE (Cl-) in WATER Apparatus Required: Ion-Selective Electrode for chloride ion (ELIT 8261 crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): 5 Molar NaNO3. ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10ml pipettes. Calibration: Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. NB: If the samples to be measured are expected to have a total ionic strength of greater than 0.01 Molar, then 2 ml of buffer solution should be added to each 100ml standard and mixed thoroughly to compensate for different activity coefficients between samples and standards. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation: For low ionic strength samples, no sample preparation is necessary. Simply take approximately 50 to 100 mls of sample in a plastic beaker, or even immerse the electrodes directly in a lake or river (but take care to avoid losing the electrodes!). For samples with high ionic strength, take 100mls of sample and add 2 mls of buffer solution and stir well before measurement. Sample Measurement: Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that, if measuring in beakers, the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results: The results will be displayed as ppm and mol/l. If buffer solution has been added equally to standards and samples then these figures will not need adjusting because they will all be affected by the same dilution factor. Procedure for determining the concentration of CHLORIDE (Cl-) in MILK The casein in milk tends to clog the ion selective membrane and thus reduce its sensitivity. This problem can be overcome by mixing one volume of milk sample with two volumes of dilute nitric acid (60 ml concentrated HNO3 diluted to 1 litre with de-ionised water) and shaking for one minute. The nitric acid is used instead of NaNO3 ISAB and must be added to all standards in the same proportion as the samples. After mixing with the nitric acid, samples are measured in the conventional manner. Apparatus Required: Ion-Selective Electrode for chloride ion (ELIT 8261 crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): Dilute Nitric Acid. ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10, 25ml pipettes. Calibration: Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. Mix the standards with nitric acid ISAB in the proportion 1:2. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation: Take 50ml of milk sample and mix thoroughly for at least 1 minute with 100ml of dilute nitric acid before measurement. Sample Measurement: Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results: The results will be displayed as ppm and mol/l. If buffer solution has been added equally to standards and samples then these figures will not need adjusting because they will all be affected by the same dilution factor. Procedure for determining the concentration of CHLORIDE (Cl-) in Meat To measure chloride in meat samples it is necessary to use 0.5M nitric acid as ISAB (made by diluting 31.25ml conc. HNO3 to 1 litre) and add this in the proportion 1:1 to all samples and standards. Chloride is extracted from meat products by liquidising 1g of meat with 100 ml of water. After filtration, 25 ml of the sample solution is mixed with 25 ml of ISAB and analysed as normal. The measured sample concentration must be multiplied by 100 to obtain the concentration in micrograms per gram of meat. Apparatus Required: Ion-Selective Electrode for chloride ion (ELIT 8261 crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): 0.5 Molar nitric acid. ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10, 25 ml pipettes. Calibration: Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. Before measuring, each standard must be mixed 1:1 with ISAB. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation: After filtration, take 25ml of each sample and mix with 25 ml of 0.5 Molar nitric acid ISAB. Sample Measurement: Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that, if measuring in beakers, the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results: The results will be displayed as ppm and mol/l. Since buffer solution has been added equally to standards and samples then these figures will not need adjusting because they will all be affected by the same dilution factor, but the ppm concentration in the solution will have to be multiplied by 100 to get the concentration in the meat in micrograms per gram (mg/Kg Procedure for determining the concentration of CHLORIDE (Cl-) in Butter Chloride is extracted from butter by heating with dilute nitric acid and measured by direct potentiometry. Apparatus Required Ion-Selective Electrode for chloride ion (ELIT 8261 – crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): Dil. nitric acid (dilute 60ml conc. HNO3 to 1 litre). ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10, 25 ml pipettes. Calibration Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. Before measuring, each standard must be mixed 1:1 with dil. HNO3 ISAB. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation 1) Weigh accurately about 10g of butter and place in a beaker with 100ml dil HNO3. 2) Heat until butter melts (do not boil) and stir well to ensure complete extraction of the chloride, but avoid emulsification. 3) Allow to cool so that the butter fat solidifies above the HNO3 solution. 4) Puncture the fat layer and pipette out 25mls of the solution. Dilute this 1:1 with deionised water. Sample Measurement Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that, if measuring in beakers, the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results The results will be displayed as ppm and mol/l in the solution. Since buffer solution has been added equally to standards and samples then these figures will not need adjusting because they will all be affected by the same dilution factor. The ppm concentration in the solution will have to be multiplied by 100 and divided by the sample weight to get the concentration in the butter in micrograms per gram (= ppm = mg/Kg) Procedure for determining the concentration of CHLORIDE (Cl-) in Fruit Juice Because of the complex matrix, high ionic strength, and other interfering factors in fruit juice, the concentration of ions in the solution is best determined using the Sample Addition method rather than direct potentiometry. Apparatus Required Ion-Selective Electrode for chloride ion (ELIT 8261 – crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10ml pipettes. Calibration Before use, the electrodes must be calibrated to find an accurate value for the slope under the current operating conditions and in the range of the expected sample concentrations. If sample concentration is completely unknown then it is best to make a quick sample measurement first, using direct potentiometry with an old calibration. Then make up and measure two standards which span the expected sample range - say 1 & 10ppm or 10 & 100ppm - or more closely spaced if working below the linear range of the electrode. Standard Selection Enter the slope and expected sample concentration and volume (usually 2, 5 or 10mls) into the Sample Addition software to calculate an appropriate standard concentration and volume. Make up the calculated standard concentration by serial dilution of the 1000ppm standard. Sample Measurement 1) Pipette the pre-determined standard volume (usually 50 or 100ml) into a beaker, immerse the electrodes, swirl the solution, and record the stable voltage after a few minutes of stabilization. 2) Add the calculated volume of sample, swirl or stirr well then wait for a new stable voltage when the solutions have completely mixed and the electrodes have re-equilibrated. The software will then calculate the sample concentration and give an estimate of the quality of the determination - if the sample concentration is very different from the expected value then you will be prompted to make a second measurement using a more appropriate volume or concentration of standard or volume of sample. Procedure for determining the concentration of CHLORIDE (Cl-) in Mayonnaise Chloride is extracted from mayonnaise by dissolving in 1Molar nitric acid and measured by direct potentiometry. Apparatus Required Ion-Selective Electrode for chloride ion (ELIT 8261 – crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): 1M Nitric Acid. ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10, 25ml pipettes. Calibration Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. Mix the standards with nitric acid ISAB in the proportion 1:1. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation Weigh accurately about 1g of mayonnaise and disperse in 500ml of 1M nitric acid in a 1l volumetric flask. Shake thoroughly, dilute to 1 litre with deionised water and mix again. Filter about 50 to 100mls of solution into a sample beaker. Sample Measurement Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results The results will be displayed as ppm and mol/l. Since buffer solution has been added equally to standards and samples, these figures will not need adjusting because they will all be affected by the same dilution factor. The measured values must be multiplied by 1000 and divided by the sample weight to get the concentration in the original sample. Procedure for determining the concentration of CHLORIDE (Cl-) in Soil Chloride is extracted from soil by shaking with deionised water and measured by direct potentiometry on the filtered solution. Apparatus Required Ion-Selective Electrode for chloride ion (ELIT 8261 – crystal membrane) Reference electrode: double junction potassium nitrate (ELIT 002) Dual electrode head (ELIT 201) Standard solution: 1000 ppm Cl as KCl Buffer solution (ISAB): 5 Molar NaNO3. ELIT Computer Interface/Ion Analyser, or Ion/pH/mV meter. 100 or 150 ml polypropylene beakers, 100ml volumetric flask, 1, 2, 5, 10ml pipettes. Calibration Before use, the electrodes must be calibrated by measuring a series of known standard solutions, made by serial dilution of the 1000ppm standard solution. For a full calibration, prepare 100ml of solutions containing 1000, 100, 10, 1ppm Cl. If the approximate range of concentrations of the samples is known, and this is within the specified linear range of the ISE, then it is only necessary to make two solutions which span this range: e.g. if samples are known to lie between, say, 30 and 130ppm then you could use standards of 10 and 200ppm or even 20 and 150ppm. NB: before measuring, 2 ml of buffer solution must be added to each 100ml standard and mixed thoroughly to compensate for different activity coefficients between samples and standards. Follow the instructions on the computer interface software to measure these standard solutions and prepare a calibration graph. Sample Preparation Weigh accurately about 4g of ground, air-dried soil and transfer to a 100ml screw cap shaking bottle. Add 50ml of deionised water and mix in a mechanical shaker for about 1 hour. Filter off the residue and wash thoroughly, retaining all washings. Dilute to 100ml in a volumetric flask. Transfer to a 150 ml beaker, add 2ml of buffer solution and stir well before measurement. Sample Measurement Follow the instructions in the computer interface software and/or electrode operating instructions to measure a series of samples and record the results. Briefly, it is important to note that the electrodes must be washed and dried between each sample, to avoid cross contamination, and sufficient time must be allowed (2 or 3 minutes), before taking a reading after immersion, to permit the electrode signal to reach a stable value. For the highest precision, frequent recalibration is recommended (see operating instructions). Results The results will be displayed as ppm and mol/l in the solution. Since buffer solution has been added equally to standards and samples, these figures will not need adjusting because they will all be affected by the same dilution factor. The measured ppm value must be multiplied by 100 and divided by the sample weight to obtain the concentration in the soil in mg/Kg. Top of Page |