John Siller Laboratory 3 LC, HPLC, and IC Introduction Liquid Chromatography is a separation technique that relies on the partitioning effect caused by a liquid mobile phase and a solid-liquid stationary phase. Liquid chromatography is similar to gas chromatography but differs in mobile phase and column designs. The objective of a good chromatography technique is to maximize the number of theoretical plates and minimize the plate height. These parameters are changed by varying the separation column and packing materials within the column. Another key aspect of any chromatography technique is the detector used at the end of the separation. Detectors range from mass analyzers to fluorometers, and can be used to identify separated analytes using different techniques. High performance liquid chromatography (HPLC) is a liquid chromatography technique that uses high pressure to quickly separate analytes in a mixture. In this lab we used liquid chromatography mass spectroscopy (LCMS) and HPLC to separate and analyze caffeine in an aqueous solution. In addition to liquid chromatography we also ran samples of water from various sources around Campbell Hall using ion chromatography (IC). The IC results reported various metal ion concentrations in water from two different water fountains. The water fountains were the one closest to the men’s bathroom (A) and the one closest to the girl’s bathroom (B). Due to time constraints and lack of nitrogen on the first day we were not able to run as many different samples as we would have liked, but we were able to use all three instruments successfully. Procedure LCMS Turn on Nitrogen Open software and activate profile Build acquisition set to program automated sampling Place samples in auto sampling vial positions Run samples using computer program Analyze the data using list data, peak list, and data file Deactivate LCMS and shut down. HPLC Degas methanol and water if there is not enough Turn on computer Check pump lines A and B to ensure no gas bubbles If gas bubbles execute purge with pump Purge the lines by opening valve and hitting the purge button Close valve and quickly hit purge button again Turn pump back on Turn detector on Select the method and align parameters Run standards before running unknowns IC Check helium pressure on tank in gas room and on instrument Make sure regenerate and eluent bottles are more than half full If bottles are less than half full they must be refilled Equilibrate system with pumps controlled by the software After 20 to 30 minutes check the hoses to insure proper flow rate Run program on the software by imputing proper parameters Run the sequence by injecting sample Each run takes 16 minutes After run is completed analyze the peaks Shut down computer program and IC Data All LCMS, HPLC, and IC chromatograms can be found in my lab notebook. Below are the calibration curves created on Excel using the intensity of the strongest peak for each concentration. The first graph reports the calibration curve for the LCMS with standard concentrations of 10 ppm, 20 ppm, 100 ppm, 200 ppm, and 400 ppm. Each standard was run twice therefore the peak heights reported are the average of the two spectra collected. Peak Height (cpsX10^6) 14 Calibration Curve LCMS 12 10 8 6 y = 0.0308x R² = 0.7986 4 2 0 0 100 200 300 400 Concentration (ppm) Figure 1: Calibration curve for LCMS using 5 calibration standards. 500 8000000 Calibration Curve HPLC 7000000 Peak Area 6000000 5000000 y = 47270x + 2E+06 R² = 0.9966 4000000 3000000 2000000 1000000 0 0 20 40 60 80 100 120 Concentration (ppm) Figure 2: Calibration Curve for HPLC using 3 calibration standards. (10 ppm, 20 ppm, and 100 ppm) Calculations Dilution factors: 400 ppm (V1)(1000ppm)=(100mL)(400ppm) V1 =40 mL 200 ppm (V1)(1000ppm)=(100mL)(200ppm) V1 = 20 mL 100 ppm (V1)(1000ppm)=(100mL)(100ppm) V1 = 10 mL 20 ppm (V1)(1000ppm)=(100mL)(20ppm) V1 = 2 mL 10 ppm (V1)(1000ppm)=(100mL)(10ppm) V1 = 1 mL IC Concentrations: Standards Ion Fluoride Chloride Nitrite Bromide Nitrate Phosphate Sulfate Peak Height (µS) 16.407 18.888 29.705 22.498 25.909 18.110 49.651 Concentration (mg/L) 30 30 100 100 100 150 150 Multiplication Factor 0.5469 0.629 0.29705 0.22498 0.25909 0.1207 0.331 Water Fountain A Ion Fluoride Chloride Nitrite Bromide Nitrate Phosphate Sulfate Peak Height (μS) 4.432 17.906 8.150 5.918 11.329 4.722 16.057 Concentration (mg/L or ppm) 2.424 11.263 2.421 1.331 2.935 0.570 5.315 Peak Height (µS) 0.496 16.851 N/A 0.466 6.266 N/A 5.705 Concentration (mg/L or ppm) 0.271 10.600 N/A 0.105 1.623 N/A 1.888 Water Fountain B Ion Fluoride Chloride Nitrite Bromide Nitrate Phosphate Sulfate Results Ion Concentrations Concentration (ppm) 12 Fluoride 10 Chloride 8 Nitrite 6 Bromide 4 Nitrate 2 Phosphate Sulfate 0 Water Fountain A Water Fountain B Figure 3: Ion concentrations found in fountain water in Campbell Hall using IC For both the LCMS and HPLC we unfortunately did not have enough time to prepare any unknown caffeine solutions using different types of tea. Looking at our calibration curves however, this was probably a blessing because any data would not be reportable due to lack of confidence. Our calibration curves were not uniform enough to use to accurately report caffeine concentrations. We were able to produce usable IC data however. The graph of ion concentrations in drinking fountain water is reported above. Safe levels of these ions vary from state to state. For example in Pennsylvania the nitrate concentration for public drinking water cannot exceed 45 mg/L (45 ppm). Both fountains were significantly under this mark and therefore are safe to drink by this standard. Additionally the chloride level, which appears high compared to other ions, is well within the Pennsylvania standard of 250 mg/L. It is interesting to note the difference between the ion concentrations of the two different fountains. This could be due to different distances the water has to travel in pipes from the source to the fountains. This could also be explained by experimental error and therefore more testing must be done before any conclusions are made, but from these results it appears that our drinking water does not contain dangerous levels of ion concentration. These results are important to me because I drink out of fountain B almost every day, but now I am considering walking a little farther to fountain B. Conclusion Time constraints really hurt us during the process of this lab. Nitrogen is needed to run the LCMS, and on the first day, when we planned to run the LCMS, the nitrogen tank was empty. This caused us to make adjustments on the fly. We decided to instead work on the HPLC, but because we were unfamiliar with the instrument and the programming used to control it we were only able to run four standard solutions on Monday. This left us with a lot of work to do on Wednesday and as a result we were not able to prepare and run unknown caffeine samples from tea. Therefore the only data we were able to produce on the LCMS and HPLC were calibration standards. This was unfortunate, but if we did run any unknown samples our calibration curves did not come out as organized as possible and would have led to inconclusive results. Luckily the IC worked as it should, but again we were only able to analyze two unknown samples due to time constraints. I would have preferred to run the water collected from each fountain multiple times to ensure the results accuracy. Given that we were required to run three instruments in two days and the nitrogen was empty on day one, I am content with the amount of data collected. If this lab was repeated there would be many changes including being much more organized and prepared to run the HPLC and IC on day one. The IC was originally included in another lab. This would have allowed us to just focus on the liquid chromatography techniques, and we would have been able to prepare unknowns and possibly correct our calibration standards. It would have also been nice to spend more time with the IC to confirm our drinking water findings. Overall this lab was rushed and a little sloppy, but we learned from our mistakes and future labs will benefit from these experiences.