The differential rate law of a chemical reaction relates the rate of the reaction in M/s to the concentration of the reactants raised to various exponents called orders of reaction. For a generalized reaction of A with B the rate law will have the form:

In this equation k is the rate law constant which makes the proportion into an equation. The rate law constant varies with temperature and all experiments in this investigation will be carried out at constant temperature. The exponents n and m must be determined experimentally. In this investigation you will determine the values of these exponents and therefore define the rate law for the following chemical reaction:

By varying the concentrations of iodide and iron(III) ions in solution and measuring the effect on the rate you will be able to determine the order of reaction with respect to each reactant and determine a and b in the following equation:

The task in this lab is to determine the values of a, b, and k. We will do so by using the method of initial rates. This works by comparing rates of reaction for different initial concentrations of reactants. By doing three experiments with carefully chosen initial concentrations it is possible to mathematically isolate the exponents. Once the exponents, or orders of reaction, are known for both reactants the value of k may be calculated from the known rate and known initial concentrations.

The formation of elemental iodine in this reaction makes it possible to measure the progress of the reaction spectrophotometrically. The iodine absorbs light at 450 nm so when the absorbance of the solution is measured as a function of time the rate of the production of iodine can be indirectly measured. By graphing absorbance vs. time a straight line is produced, the slope of which is proportional to the rate of the reaction. Recall that when Beer’s Law applies, concentration is directly proportional to absorbance. By plotting absorbance on the y-axis and time on the x-axis the slope will have units of absorbance over time. Since we do not have measurements of the proportion between concentration and absorbance we cannot measure the rate of reaction directly in this lab.

Absorbance Measurements

General Spectrophotometer diagram

Vernier SpectroVis Instrument diagram

Colored chemicals absorb specific wavelengths of light. Yellow food color absorbs blue light very strongly. Blue food coloring absorbs red and orange light. This can easily be demonstrated using a spectrophotometer or with an overhead projector and a diffraction grating.

Absorbance of light at a particular wavelength can be used to measure the concentration of colored chemicals. The larger the concentration of a colored chemical, the darked the color, and the stronger the absorbance. The mathematical definition of absorbance is based on the percentage of light that is transmitted. To make a measurement, the brightness of the light source is measured with no sample or with a so-called blank. This provides the initial intensity. Once a sample is placed into the spectrophotometer the intensity of light at the chosen wavelength can be measured, which is reduced compared to the blank. The ratio of these intensities, expressed as a percent is called the percent transmittance. As a function of concentration the percent transmittance does not produce a linear relationship. By taking the negative log₁₀ of the transmittance (expressed as a decimal) the absorbance may be calculated (A = -log(%T)). This calculation is performed automatically by the instrument. The absorbance is a measure of the amount by which a chemical has reduced the intensity of light. The higher the absorbance, the more strongly the light is absorbed. Absorbance has a simple, linear relationship to the concentration of a chemical and so it can be used to measure concentration. If measured as a function of time, absorbance provides a measure of changes in concentration. This is how we will use the instrument.

Measuring Rate of Reaction

We will not attempt to collect data which directly connects absorbance to concentration but since they are directly proportional the rate of change of the absorbance will serve perfectly well to stand in for the true rate of reaction. The slope of a graph of absorbance (y-axis) vs. time (x-axis) will have units of A/s. When measured at 450 nm the absorbance increases as the reaction under study progresses. The reaction rate slows down as products build up and so it is not a constant with a simple linear appearance on the graph. In order to compare rates between experiments we will find an average rate of reaction by using Excel to calculate the slope of a linear trendline for a specific range of time, say from 10 s to 70 s.

In the sample data displayed at right the slope is about 5.6 × 10^–3. This is the only number we need from the many data points you will collect. You will perform a given experiment three times, discard any trials which you know are poor data (based on your execution), and average the trials to find a rate of reaction for that experimental setup.

Given how rate is determined in these experiments a true value for k, the rate constant, cannot be calculated exactly. In order to be able to calculate a value we will be taking the rates determined here to be in units of M/s rather than A/s.

Calculating Order of Reaction

To find order of reaction you will use data from two experiments. Use the average rate and the calculated initial concentrations of reactants.

Experiment 1 Concentration of I–
(vol. of KI soln) 1.0 mL 
                  ------ × 0.020 M = 0.0067 M
(total volume)    3.0 mL 

Experiment 3 Concentration of I–
(vol. of KI soln) 2.0 mL 
                  ------ × 0.020 M = 0.013 M
(total volume)    3.0 mL 

Experiment 1 and 3 Concentration of Fe3+
(vol. of FeCl3 soln) 1.0 mL 
                     ------ × 0.020 M = 0.0067 M
(total volume)       3.0 mL 

 Rate = k[Fe3+]a[I–]b
 
 Rate1 = k[0.0067]a[0.0067]b
---------------------------
 Rate3 = k[0.0067]a[0.013]b
 
  5.6 × 10–3 = k[0.0067]a[0.0067]b
----------------------------------
 1.1 × 10–2 = k[0.0067]a[0.013]b
 
 
 0.5 = k/k × 1 × (0.5)b
 so b = 1 since only 0.51 = 0.5

Practical Matters

You will use syringes to measure volumes. Do not use syringes in the bottles of stock solution to avoid possible contamination. Obtain about 10 - 12 mL of each solution in a separate, labeled beaker. Draw some solution into the syringe and then expell it in order to exclude air bubbles. Fill the syringe to a larger volume than what you need. Deliver the amount you need by difference between two points on the scale on the side of the syringe. For example, deliver 1.0 mL by pressing the plunger down so that it moves from 3 mL to 2 mL.

Use a different, clean cuvet for each experimental setup. Between trials carefully clean the cuvet and make it as dry as possible so that you do not affect the outcome of the next trial.

Objective

Determine the rate law for the reaction under investigation by collecting rate vs. initial concentration data.

Materials

The following list does not cover all possible hazards, just the ones that can be anticipated. Move slowly and carefully in the lab: haste and impatience have caused more than one accident.

Always leave stock solution bottles tightly closed when not in immediate use!

• Both stock solutions used in this lab experiment are dilute and so are relatively safe to use. As always, wash hands before leaving the lab, eating, or drinking, or going to the bathroom.
• Wear chemical splash goggles, gloves, and a chemical-resistant apron.
• Iron(III) chloride is a skin and tissue irritant; it is corrosive and toxic (LD₅₀ = 260 mg/kg), and causes stains. Use care in handling the solution.
• Potassium iodide (KI) is non-toxic.
• The iodine (I₂) produced in the reaction is corrosive and toxic but is produced in minute amounts in this lab and so is of minor concern.
• All solutions used in this lab must be collected for hazardous waste disposal. Neither the elemental iodine nor the iron(II) or iron(III) ions may be dumped into the sewer system.

Collect all waste in the designated bottle by pouring the solution out of the cuvet, rinsing the cuvet by filling it once with tap water and pouring it into the bottle, and the closing the bottle again. Use the funnel provided to make splashing outside the bottle less likely.

Procedure

1. Prepare a blank solution by mixing 1 mL KI solution with 2 mL distilled water in a cuvet. Place it into the spectrophotometer with the flat, smooth sides facing the white circle and triangle.
2. Plug the SpectroVis Plus unit into the USB port of the computer and start the Logger Lite or Logger Pro software. Or if you are using a Chromebook, use the search function to find “Vernier Spectral Analysis”.
3. Calibrate the Spectrometer by finding this function in your software. This step is critical because it provides the baseline for brightness measurements to determine the absorption of light.
4. A dialog box will pop up to inform you that the lamp is warming up. Do not skip this step, it only requires 90 seconds.
5. Pick up a cuvet by touching the grooved sides. Handling the smooth sides will put fingerprints on it which could have a small effect on the data collection. Fill a cuvet with the blank solution and place a cap on it. Once warm-up is complete place the cuvet into the SpectroVis device so that the smooth sides face the white circle and white arrow. Click “Finish Calibration”.
6. Once Calibration is complete, click OK.
7. Set up the data collection to be ‘Absorbance vs. Time’ for an individual wavelength. You must do this before beginning any data collection or else you have to start from scratch. Select the wavelength listed that is nearest to 450 nm . As the iodine is produced it has an absorbance maximum at this wavelength.
8. The default is to collect data at one data point per second for 200 seconds. This can be changed in the options for the experiment. Collect one data point per second for 120 seconds.
9. Using the quantities in the table at right perform three trials for each set of quantities.
10. To run a trial start by mixing water and KI solution in the cuvet. Have a syringe filled with FeCl₃ ready to deliver the needed volume. When ready, add the iron(III) chloride solution by measuring by difference, cap the cuvet, shake vigorously, and place the cuvet in the spectrophotometer.
11. Immediately begin data collection by pressing the ’Collect‘ button. Try to perform these actions as repeatably as possible so that data collection always begins after the same delay to measure the FeCl₃ solution, the same amount of shaking, and the same time before placing the cuvet in the device.
12. Immediately enter the data into a spreadsheet program in order to generate a graph and determine the slope of the line. Keep one spreadsheet file and add your data in labeled columns so that you can identify all of your trials later.
13. The graph of all of the data for a trial will show a curve from a steep upward slope over toward a horizontal line. This is because the production of iodine (I₂) will slow down as the reaction progresses. Use the spreadsheet software to make a linear trendline which displays the slope of the graph for the interval from 10 s to 70 s. This span may be adjusted if it seems necessary, so use your judgement. Often the data is a bit noisy right at the start but has more regular behavior after a short delay. This will be an average rate over the time span but if you always use the same interval then you can compare trials and experiments.
14. Calculate a slope for all three trials for each set of reactant quantities. Find an average slope for each set of trials with the same quantities of reactants. Only use this average in your analysis.
15. If a trial produces a slope that is clearly different from the other two then either repeat the trial or discard it from your analysis.
16. Continue data collection and analysis until three trials for each set of quantities have been performed and you have a reasonable average slope for the absorbance vs. time graphs for each experimental setup.
17. When you are finished, tidy your lab station. Package up and put away the spectrophotometer. Dispose of solutions properly. Wash glassware with soapy water. Clean cuvets with only clean water. Do not use soap because they are very hard to rinse out.

Analysis