Background BIOCHEMISTRY LAB CHE-554. Experiment #1 Spectrophotometry

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1 1 BIOCHEMISTRY LAB Experiment #1 Spectrophotometry CHE-554 In day 1 we will use spectrophotometry as an analytical technique using a known extinction coefficient to assess the precision and accuracy of a common operation in a biological chemistry lab: pipetting. In day 2 we will undertake an experiment wherein we will determine the extinction coefficient of a protein thus permitting direct determination of concentration in the future. We will also use a common indirect method wherein a dye is used in a chromogenic assay. Relevant material is provided Professor in the text Testa in experiment 1, beginning page 15. However, we will use the Bradford reagent instead of Folin-Ciocalteau, we will omit studies of riboflavin and adenine. (We will instead demonstrate a direct protein assay.) (Introductory material beginning on page 3 of the text may also prove useful.) 2 Background! Photometry relates to the study of light.! An experimental tool for producing and measuring a spectrum of light, visible or ultraviolet, is the UV-VIS spectrophotometer.! The UV-VIS spectrophotometer produces incident light and measures the light that passes through the sample (is not absorbed). The machine calculates how much light was absorbed, and presents that to the user.! Solutions absorb at specific wavelengths (energy levels) of light, and this is a function of the material in the solution. Particular materials have a characteristic absorption spectra through a range of wavelengths. Therefore, one can obtain information about a solution by measuring its absorbance.! The absorption of a solution at a specific wavelength also depends on the concentration of sample. Therefore, one can measure the concentration of known material via UV-VIS spectroscopy.! In the visible range, wavelengths of light not absorbed by the sample make up the color of the sample that you see.

2 Theory of absorbance -1 Each photon has a probability γ of being absorbed if it encounters a molecule of dye (absorbing substance). Theory of absorbance -2 # photons absorbed = # photons entering dye x γnaπr 2 C l = # photons entering dye x ζ C l d (# photons) = - # photons x ζ C dl X photons incident (1-γ)X photons transmitted Upon passage through a small amount of solution, the path length is very short: dl (a small change in position l ) 3 γx photons absorbed (γ = here) r If a photon s path passes through a solution with C x NA molecules of dye per L, we consider that a photon affects molecules within a cross-section of area πr 2 and the length of the path through the dye is l (letter l ), then the photon is expected to encounter C x NA x πr 2 x l molecules and have a probability γ C NA πr 2 x l of being absorbed. r is assumed to depend only on the molecule s identity and the wavelength of light. C is the concentration (moles L -1 ). # photons absorbed = # photons entering dye x (γnaπr 2 ) C l l 4 dp= -ζ C dl x P dp/p = - ζ C dl ln(p)-ln(po) = -ζ Cl - - ζ C 0 ln(p/po) = -ζ Cl P/Po = e -ζcl Incident light Po (power at zero thickness of absorber) The number of photons changes by a small amount: dp. l (letter l) ln (P/Po) = log(p/po) log(p/po) = -ζ Cl /2.303 = - εcl, ε=ζ /2.303 transmitted light Pl (power at l thickness of absorber)

3 Theory of absorbance -3 log(io/i) = A = εcl, Eq. 1-7 C is concentration, l is path length, ε is molar extinction coefficient. ε (and therefore A) is a function of the wavelength of the light. If the dye is too concentrated, some molecules may be in the shade of others and not have their expected probability of absorbing a photon. Non-linear regime, Beer-Lambert law no longer holds for high C or long path lengths. Plot A/ Cl = ε The Beer-Lambert Law A = ε c l This equation relates the concentration of the lightabsorbing compound and the path-length of incident light to the absorbance of a solution. A is the measured absorbance of the sample ε is the extinction coefficient, which is a constant that depends on the structure of the material, the wavelength of incident light, and the solvent C is the calculated concentration of the sample l is the length of the path that the incident light travels through the sample A = εcl, slope = εl Units of ε: M -1 cm -1 In these experiments, measure the absorbance using a spectrophotometer and calculate the concentration of sample in solution. 5

4 The electromagnetic spectrum Absorbance vs. wavelength λ (nm) ε (M -1 cm -1 ) nm ! ! in ethanol band II band I

5 Significance of wavelength Transitions between electronic states λ = c/ν, ΔE = h ν, = hc/λ ν is the frequency, λ is the wavelength and c is the speed of light. h is Planck s constant, = 6.6 x J/s λmax is the wavelength with the maximal ε for a given band. It corresponds to the energy of the transition associated with that band. Long wavelength photons carry less energy, shortwavelength photons carry more energy. Longer wavelengths n-π* transitions, mid-wavelenths π-π* transitions. In biochemistry nm, 180 nm, respectively. Eg. N-containing bases of DNA: 260 nm absorbance. Hence the danger of UV light to DNA

6 The visible portion of the EM spectrum Making a measurement Violet: nm Indigo: nm Blue: nm Green: nm Yellow: nm Orange: nm Red: nm Spectrophotometer 11

7 Selecting a wavelength Spectrophotometer Slit Why use absorbance?! It is often a MUCH more accurate way to know concentrations than the weights and volumes used to produce them.! The advantage provided depends on the magnitude of the extinction coefficient (why?)! Accuracy is different from precision (how?) Sample! This is the object of our activities on Day 1. 14

8 Sample standard curve Sample standard curve Sample data set Interpolation or the use of the equation of the line allows determination of the unknown concentration. In this case the unknown falls out of range and requires extrapolation, which is much more dangerous than interpolation. A A 15 C (M) A non-zero intercept may be real, for example due to a reaction with the buffer. 16 C (M)

9 Sample standard curve In this case the unknown falls out of range and requires extrapolation, which is much more dangerous than interpolation. Sample standard curve Determination of the extinction coefficient. A = εc + 0 (with a 1 cm path length) Assuming an intercept 0, the slope is ε. Why do we use the slope instead of just one (C, A) pair? A A 17 C (M) 18 C (M)

10 What we will do Day 1: Validation of techniques and refresher on uncertainties. Bromophenol blue Concentration? c = mass/mw vol Make an illegal measurement, break Beer- Lambert s law. Concentration? c = A/εl? Dilute to A < 1 Concentration? c = A/εl Statistics based on independent repetitions of the dilutions and absorbance measurements. Validation based on comparison with authentic standard solution

11 Day 2, Experiment 1: A chromogenic assay! Non-absorbing compounds can be detected via a reaction that generates a chromophore in proportion to the compound s concentration.! Either a known ε or a standard curve are used to relate the A to the starting compound s concentration. (The standard curve in-essence yields ε).! We will use the Bradford reagent, which is a solution of Coomassie blue G250 in ethanol/phosphoric acid. This is less tricky than the text s recommendation of Folin- Ciocalteau.! The product sheet for Sigma s Bradford reagent is provided on the course web site. We will use a variant of the standard procedure A Bradford Assay! Marion Bradford published and patented the assay. Bradford, M. M. (1976) Anal. Biochem. 72: (This is one of the most heavily cited scholarly articles of all time).! Based on a shift in the absorbance maximum of Coomassie brilliant blue G-250 upon binding to arginine side chain (red form of dye converted to a more blue form).! Two chemical bases for the λmax shift: Acidic dye is added to protein, λmax of the dye shifts from 465 nm to 595 nm. Dye binds to basic and aromatic amino acids especially Arg. Detergents and alkaline phs interfere with the dye s colour shift.

12 Coomassie brilliant blue G-250! At acidic ph, the Ns are protonated, the sulfonates remain ionized, net charge is +1 colour is red.! At neutral ph the Ns are deprotonated, only one is +ve, molecule is an an anion. Molecule is green with ε ~ 43,000 M -1 cm -1.! Binding to protein stabilizes the anion, and produces the blue-green form even when free dye molecules remain cationic (red).! Initially used to dye wool (keratin). - +Arg + R-250 lacks two methyl groups Precautions for Chromophorogenic assays! The reaction must be limited ONLY by the compound to be measured. (Every molecule of compound is counted)! A linear relationship must be demonstrated for the absorbance and the reactant that forms the dye.! Conduct the experiment in such a way that the readings corresponding to unknown samples fall within the reading that make up the standard curve.! If necessary, make dilutions of the unknown. Do this BEFORE conducting the reaction. 23 Structure of Coomassie brilliant blue G Coomassie_Brilliant_Blue 24

13 Day 2, Experiment 2: Direct absorbance measurement on a protein! We will exploit the strong absorbance of UV radiation by tryptophan (Trp) and tyrosine (Tyr) side chains in a protein.! Each protein species has a characteristic 3D structure that places its various Trp and Tyr side chains in unique environments and causes them to have extinction coefficients that vary quite widely.! However if a protein is denatured to a random coil all the side chains are exposed to the medium and behave as if they were all simply amino acids dissolved in that medium Amino acids that absorb strongly in the UV. Garrett and Grisham, 3rd ed. Fig. 4.15

14 A typical protein: Lysozyme UV-absorbing amino acids 27 2ZYP.pdb 28 6 Trp and 3 Tyr.

15 UV-absorbing amino acids! 6 Trp Trp and and 3 Tyr. Tyr.! Some are buried, others are stacked. 29 Denatured protein! In a denaturing medium, the extinction coefficient of the protein at 280 nm can be approximated as the sum of the contributions of the Trps and the Tyrs: εprotein = ntrp εtrp + ntyr εtyr! We will use the protein lysozyme from chicken egg white. the amino acid sequence of this protein is known 1 : LYS VAL PHE GLY ARG CYS GLU LEU ALA ALA ALA MET LYS ARG HIS GLY LEU ASP ASN TYR ARG GLY TYR SER LEU GLY ASN TRP VAL CYS ALA ALA LYS PHE GLU SER ASN PHE ASN THR GLN ALA THR ASN ARG ASN THR ASP GLY SER THR ASP TYR GLY ILE LEU GLN ILE ASN SER ARG TRP TRP CYS ASN ASP GLY ARG THR PRO GLY SER ARG ASN LEU CYS ASN ILE PRO CYS SER ALA LEU LEU SER SER ASP ILE THR ALA SER VAL ASN CYS ALA LYS LYS ILE VAL SER ASP GLY ASN GLY MET ASN ALA TRP VAL ALA TRP ARG ASN ARG CYS LYS GLY THR ASP VAL GLN ALA TRP ILE ARG GLY CYS ARG LEU! In our denaturing medium, at 280 nm εtrp = 5690 M -1 cm -1 and εtyr = 1280 M -1 cm J Biol Chem Aug;238:

16 The experiment! We will determine the concentration of a lysozyme solution indirectly, by first determining the concentration of an aliquot of that solution that we dilute into denaturing conditions. We do that because under denaturing conditions, we can calculate the extinction coefficient because we know the Trp and Tyr content. This extinction coefficient enables us to determine the concentration.! From the dilution factor we will calculate the concentration of the parent native solution.! The calculated concentration and the measured absorbance at 280 nm will then be used to calculate the native protein s extinction coefficient at nm. 32 How we will do it

17 33 Accuracy and precision (Day 1) What you have to do: 1. Use your pipettors to deliver 333 µl, 48µl, and 3µl onto a weighting paper, and report the weight of each drop. 2. Make up a series of standard sample dilutions. 3. Measure absorbance of each. 4. Make a set of identical dilutions. 5. Measure absorbance of each. Step 1a. Use the pipettors in your locker and deionized water from the appropriate faucet near your desk (put some in a beaker). 1b. Go to one of the analytical balances, tare an empty boat then deliver 333 µl water. Record the weight. Repeat for 48 and 3 µl. Accuracy (vs. concentration) Steps 2-3! Your T.A. will provide a concentrated stock solution of Bromophenol blue.! Dilute with water to make the following series of derivative concentrations: 5%, 10%, 20%, 30%, 40%, 60%, 80% (all vol./ vol.).! Measure the absorbance at 590 nm of a cuvette containing only the water used as a diluant.! Rinse the cuvette once with 5% solution and then measure the A590 of this solution.! Repeat for the 10% solution, then the 20%... etc to the highest concentration.! Why should you read from lowest to highest concentration?! Why should you rinse once with solution? 34

18 Accuracy (vs. concentration) Precision! Plot A590 vs. concentration.! Identify the linear regime.! Use the known concentration of the 100% solution to calculate the extinction coefficient based on the linear portion of the plot.! Use the absorbance measured for the 100% solution and the extinction coefficient to calculate the apparent concentration.! How does your apparent concentration compare with the actual concentration?! If you are making a direct determination of concentration and measure an absorbance above 1, what will you do to obtain an accurate value for concentration? Steps 4-5! Make 5 identical 20% solutions by making 5 independent dilutions of 100% solution. In all cases the final volume should be 3 ml.! Measure A590 of each of your solutions and tabulate the results.! Calculate the average value and the standard deviation for your set of readings.! Comment on the results

19 Day 2, Experiment 1: Precautions for Chromogenic assays! The reaction must be limited ONLY by the compound to be measured. (Every molecule of compound is counted.)! A linear relationship must be demonstrated for the absorbance and the reactant that forms the dye.! Conduct the experiment in such a way that the readings corresponding to unknown samples fall within the reading that make up the standard curve.! If necessary, make dilutions of the unknown. Do this BEFORE conducting the reaction. Day 2: juggling two activities. You will be doing two things today: a chromogenic assay and a direct determination. To use your time well you may want to interleave steps of the two activities. A flow chart helps to keep your mind organized as you hop back and forth. Example: Experiment 1 Make series of standard samples Make series of unknown samples Experiment 2 Measure A280 of lysozyme Add dye reagent. Start timing. Add dye reagent. Start timing. Dilute lysozyme w. GuHCl Read and record absorbances. Read and record absorbances. Measure A280 of lysozyme- GuHCl Calculate concentration of initial lysozyme Calculate concentration of diluted lysozyme-guhcl

20 Chromogenic assay What you have to do: 1. Make up standard sample dilutions as per table. 2. Make up unknown sample dilutions as per table. 3. Add 3 ml Bradford reagent to each. Start timer. 4. Gather cuvettes and get in line for spectrophotometer. 5. Once 5 minutes have elapsed read and tabulate A595. (Note how much time had elapsed.) 6. Do not leave without learning from your T.A. what the concentration of the standard is. Chromogenic assay: How to do it The assay conditions! The Bradford concentrate contains methanol and phosphoric acid.! These are potentially hazardous.! How might this formulation be changed for reduced danger?! How will you handle it?! How will you dispose of your reactions?! Standard has a concentration of 2 x 10-2 mm. (Check with your T.A.) 39 40

21 Making standard samples -1 Making standard samples -2! The active ingredient is Coomassie blue G-250, which binds primarily to arginine residues.! The Sigma reagent is used as follows: 3.0 ml reagent ml solution to be tested.! First generate a series of known concentrations of the standard protein solution as follows: Vol. of Protein stdd. soln. (µl) Vol. of buffer (µl)! In your notebook, be sure that you have a name for each sample included in your table and that this name is used to label the corresponding tube.! Make these samples up in test tubes that have sufficient capacity for the addition of 3 ml of the Bradford reagent and subsequent mixing without spilling.! Add 3 ml Bradford reagent to each tube. DO NOT dip a pipette tip into the master bottle, pour a little reagent out of the bottle into a small beaker and pipet from this aliquot. If there is left-over and it is not contaminated, pass it along to a colleague for use

22 Reading the standard samples! Mix each sample and then wait at least 5 min. but no longer than 45 min. (Observe changes in your samples as a function of time, and take photographs.)! Read A595 and record these results. Making the unknown samples! Adapt the protocol detailed above to make a series of five samples of the unknown, plus a null sample.! Your notebook should include a sample table for the unknown that resembles the sample table you made for the standards.! React the unknowns with diluted Bradford reagent as above and read them as above

23 Tips for success Be sure to mix all component thoroughly before taking absorbance measurements The plots of absorbance vs. concentration in the second half of the experiment might not be linear. If so, identify the portion of the plot you will use as the basis for any analysis and explain why. If the color of your unknown tubes is more intense than the known tube with 100 µl of standard, tell the instructor so that the unknown can be remade. Questions! Why do we test a whole series of standard samples instead of just one?! Why do we include a null sample?! Why do we test a whole series of dilutions of our unknown sample instead of just one?! What is a potential pitfall of making a standard curve from one species of protein as a basis for determining the concentration of a different protein?! What are potential hazards of working with the Bradford reagent and why? 46

24 Day 2, Experiment 2: Direct determination of protein concentration! We will determine the concentration of a lysozyme solution under denaturing conditions, because under denaturing conditions, we can calculate the extinction coefficient because we know the Trp and Tyr content. This extinction coefficient enables us to determine the concentration.! From the dilution factor we will calculate the concentration of the parent native solution.! The calculated concentration and the measured absorbance at 280 nm will then be used to calculate the native protein s extinction coefficient ε at 280 nm. Once ε is known the concentration of that protein can be determined without prior denaturation. Direct determination of concentration. What you have to do: 1. Measure A280 of native lysozyme solution using a quartz cuvette. 2. Mix 2.5 ml of the lysozyme with 7.5 ml of guanidinium HCl 3. Rinse cuvette with 3 ml of lysozyme/ GuHCl solution (discard solution used for this). 4. Measure A280 of 3 ml lysozyme/guhcl solution. 5. Measure A280 of another 3 ml lysozyme/guhcl solution

25 Direct determination Protocol: how to do it. (more detail on the steps listed above)! Measure the A280 of a solution of native (folded) lysozyme provided by your T.A. (This will be in 20 mm phosphate buffer at ph 6.5). Use a quartz cuvette for this measurement.! Recover the native lysozyme from the cuvette. Dilute 2.5 ml of the native lysozyme with 7.5 ml of 8 M guanidinium hydrochloride in the same phosphate buffer.! What will be the final concentration of guanidinium hydrochloride?! By what factor will the denatured lysozyme concentration be related to the original concentration of native lysozyme? 49 Questions to be answered in your theory section and pre-lab.! What is the extinction coefficient of denatured lysozyme at 280 nm in our denaturing medium? (Show your work.)! What potential hazards are associated with working with guanidinium HCl?! Does this material contain HCl?! Look at the MSDS for guanidinium HCl available on the course web site and assess this material s toxicity by comparing its LD50 with those of glucose and aspiring, which are also posted.! Why must we use a quartz cuvette? 50

26 Protocol, continued! Transfer 3 ml of denatured lysozyme to the cuvette you just used and then discard this solution. (This step washes away residues of the previous sample.)! Transfer a second 3 ml aliquot of denatured lysozyme to the cuvette and measure its A280.! Discard this solution too and transfer a third 3 ml aliquot of denatured lysozyme to the cuvette and measure its A280 (second measurement). Questions! How do your two readings for the A280 of denatured lysozyme compare?! How does it help to have two readings?! What value should you use and how will you know if it is valid?! Use your calculated extinction coefficient for denatured lysozyme to determine the concentration of denatured lysozyme.! Now calculate the lysozyme concentration of the original native solution of lysozyme based on the dilution factor used.! Use this and the A280 you measured for native lysozyme to calculate the extinction coefficient of native lysozyme

27 Post-lab thoughts! How does the extinction coefficient you determined for native lysozyme compare with published values? (look up at least one, and provide your source. Remember that lysozyme from different sources can have different extinction coefficients, you are looking for hen egg white lysozyme. Hen is also known as Galus galus.! Compare your measured absorbances for the unknown with those measured by a classmate (say who). Discuss the magnitude and possibles causes of any differences.! Also answer questions 2, 3, 4 from our text, experiment 1 (page 24). 53