Lab: Measuring pH and Trusting the Number
Purpose
Section titled “Purpose”A pH meter is the only instrument in this course that will give you a confident, stable, precise number that is simply wrong, and give it to you all afternoon. It does not squeak, drift visibly or refuse to settle. It reads 7.42 when the truth is 8.1, and it keeps reading it.
This session is therefore not about learning to dip a probe. It is about learning what the number depends on, how to check it against something whose value is known, and how many of the digits on the display you are entitled to copy into a notebook. You will calibrate a meter against two buffer standards, verify it against a third solution it was not calibrated with, predict the pH of six solutions from the chemistry of the two pages before this one, measure them, and account for every disagreement of more than a couple of tenths.
Learning objectives
Section titled “Learning objectives”By the end of this session you will be able to:
- Say what a glass electrode actually measures, and why that makes calibration compulsory rather than optional.
- Perform a two-point calibration, and state what the offset and the slope each correct.
- Predict the pH of a carbonate, a hydrogencarbonate and an equimolar mixture of the two from cited constants, and explain any measured departure.
- Give a pH reading with a defensible number of decimal places and a stated uncertainty.
- Say what an indicator paper can and cannot establish, and name one case where a colour change is the better instrument.
- Recognise the signs of a tired or dying electrode, and store one so that it lasts.
Prerequisites
Section titled “Prerequisites”- Acids, bases and pH, for the scale itself.
- Buffers and buffer capacity, because three of the six samples are buffers and the standards themselves are buffers.
- Measurement and uncertainty, for the treatment of an instrument reading. This session does not re-derive any of it.
- Laboratory safety and protective equipment, for the controls assumed throughout.
- Concentration and dilution, for making up the sample solutions.
Safety classification
Section titled “Safety classification”Level A. The criteria of the classification rubric that decided it, taken in order:
- Substances and quantities. Commercial pH buffer standards at pH 4.01 and 7.00, supplied ready to use; household sodium carbonate and sodium hydrogencarbonate as solutions at about 1 per cent w/v; distilled water; tap water; and white vinegar diluted to about 2 per cent w/v acetic acid. All are aqueous, all are dilute, and the most severe classification among them is eye irritation. Sodium carbonate’s Chemical Safety Card records severe eye irritation and mild skin and respiratory irritation for the substance, and a violent reaction with acids generating heat and carbon dioxide.
- Energy. Nothing is heated. Solutions are used at room temperature and their temperature is recorded, which is the whole of the thermal content of the session.
- Electrical. A purchased, battery-powered meter. Nothing is built, wired or modified.
- Waste. Dilute aqueous solutions of carbonate, hydrogencarbonate and acetic acid, plus small volumes of used buffer standard. Nothing silver-bearing, nothing requiring specialist neutralisation.
What is not a hazard here, and why
Section titled “What is not a hazard here, and why”There is no thiosulfate on this bench, and therefore no sulfur dioxide. The rule that acid samples and thiosulfate samples are never combined in one waste vessel is a real one, because acid on thiosulfate liberates sulfur dioxide — Kodak’s 1928 primer describes the same reaction from the other side, as acid decomposing hypo and precipitating sulfur. That rule does not bite here because no fixer is measured in this session. It will bite in Part XI, and the habit of keeping acid and thiosulfate waste separate is worth forming now, before it matters.
There is no concentrated acid and no caustic alkali. Glacial acetic acid carries H226 and H314 in the aggregated ECHA notifications on PubChem — flammable, and causes severe skin burns and eye damage — and that is a statement about the concentrate. What is handled here is dilute vinegar, which is a food product at the strength it is sold and is diluted further before use. Sodium carbonate is a laundry product handled as a 1 per cent solution. Neither statement transfers to the same substances at strength; the chemical encyclopaedia entries give the difference.
The alkaline buffer standard is deliberately not part of the Level A session. Commercial pH 10 standards are commonly borate-based, and borax as a solid carries H360, may damage fertility or the unborn child, in 93.2 per cent of the aggregated ECHA notifications — a classification that is not among those Level A admits. A supplied dilute standard may well be classified differently, but this course has not verified the safety data sheet of any particular product, so the three-point calibration is placed in Further experiments with the instruction to read your own product’s sheet first and make your own assessment. The two-point session below needs nothing beyond Level A.
What is left is what the Hazards section names: eye irritation from splashes, a fragile glass bulb, and a bench with liquids on it.
Hazards
Section titled “Hazards”Eye irritation from splashes. A 1 per cent sodium carbonate solution is an eye irritant; Chemical Safety Card 1135 records severe eye irritation for the substance. Dilute acetic acid stings. Eye protection is worn from the moment the first cap comes off until the bench is cleared.
Broken glass, and a very expensive small piece of it. The sensing element of a glass electrode is a membrane about 50 micrometres thick — one twentieth of a millimetre. It breaks if it is knocked against the bottom of a beaker, and a broken electrode is both a cut hazard and the end of the session. Support the electrode in a stand or clamp; never let it rest on the bottom of a vessel; never stir with it.
Acid meeting carbonate. Card 1135 records that sodium carbonate solution reacts violently with acids, generating heat and carbon dioxide. At the concentrations here that means fizzing rather than anything dramatic, but it is the reason the acid samples and the carbonate samples are rinsed from the electrode separately and are not poured into one another or into one waste vessel.
Slips and spills. Six samples, three standards, a rinse bottle and a waste beaker is a crowded bench. Everything stands in a tray, and the tray is bigger than the largest vessel on it.
Required PPE
Section titled “Required PPE”- Safety glasses with side protection, to a stated standard, worn throughout. The Level A controls require eye protection whenever solutions are handled, and here the specific reason is the carbonate sample: severe eye irritation is its worst recorded short-term effect, and it is the one that would actually hurt.
- Nitrile gloves. The Level A controls require them whenever solutions are handled. On this page their second job is keeping skin oils and salt off the electrode bulb, which is a measurement control as much as a personal one.
Closed shoes, sleeves clear of the tray, and nothing on the bench that is also food.
Ventilation
Section titled “Ventilation”Ventilation is not among the controls addressing a chemical hazard on this page, because nothing here produces a vapour, a mist, a dust or a gas in any quantity: every solution is aqueous, cold and dilute, and the only volatile component is the acetic acid in dilute vinegar, whose smell is noticeable and whose concentration at this dilution is not the reason for any control on this page.
Work with a window openable all the same, for two reasons that are not chemical. The vinegar smell in a closed room becomes unpleasant enough to make you hurry, and hurrying is the enemy of a calibration. And opening the window is the first item on the laboratory-opening list, rehearsed here so that it is automatic on a day when it does matter.
Materials
Section titled “Materials”| Item | Quantity | Notes |
|---|---|---|
| pH buffer standard, pH 4.01 | 2 sachets or about 100 ml | One for calibration, one kept sealed as a check |
| pH buffer standard, pH 7.00 | 2 sachets or about 100 ml | As above |
| Distilled or deionised water | 1 L | For rinsing, and as sample 1 |
| Tap water | as needed | Sample 2, and run the tap for 30 seconds first |
| Washing soda, or anhydrous sodium carbonate | about 10 g | Samples 3 and 6. Note on your label which form you used |
| Bicarbonate of soda | about 10 g | Samples 4 and 6 |
| White vinegar, with its acidity stated on the label | 100 ml | Sample 5, diluted |
| Narrow-range pH indicator papers | one pack, or two | Ranges covering about 4 to 7 and 7 to 10 are the useful pair |
| Lint-free laboratory tissue | a few sheets | For blotting the electrode, never wiping it |
| Adhesive labels and a waterproof pen | — | Every beaker is labelled before anything goes in it |
Chemicals
Section titled “Chemicals”This session handles buffer standards and household materials only. That is a deliberate departure from the sample list in the course manifest, and the reason is in the callout below.
| Chemical id | Quantity | Form | Notes |
|---|---|---|---|
| sodium-carbonate-anhydrous | about 3 g | solid, then 1 % w/v solution | Sold as washing soda, usually as the decahydrate; Chemical Safety Card 1135 records severe eye irritation |
sodium-carbonate-decahydrate (entry not yet written) |
about 8 g | solid, if that is the form you have | 286.14 g/mol against 105.99 for the anhydrous salt: 37.0 % carbonate by mass |
| sodium-bicarbonate | about 3 g | solid, then 1 % w/v solution | Bicarbonate of soda; 84.01 g/mol |
acetic-acid (entry not yet written) |
about 4 g as vinegar | dilute aqueous solution, about 2 % w/v | Diluted from white vinegar; the concentrate’s H314 classification does not apply at this strength |
| borax | none handled | — | Named because the pH 10 buffer standard is commonly borate-based and appears only in Further experiments |
Potassium chloride is present but is not a chemical this session handles: it is sealed inside the electrode’s reference compartment, and it is the salt added to pH 4 buffer to make the long-term storage solution described under Storage. If you make your own storage solution you will handle it; that is a purchase decision rather than a step in this procedure.
The buffer standards themselves are purchased products, and their composition varies by supplier. Read the safety data sheet supplied with yours before the session — that is the skill reading an SDS exists for, and a buffer sachet is a good first real use of it.
Equipment
Section titled “Equipment”- A pH meter with a combination glass electrode. A pen-type meter is acceptable and its limits are part of what this session teaches. Read its manual before the session, and specifically its calibration procedure, its stated accuracy and its storage instruction.
- A stand or clamp for the electrode, so that it hangs in the solution and does not rest on the bottom.
- Six 100 ml beakers, labelled, plus three more for the standards.
- A wash bottle of distilled water and a waste beaker for rinsings.
- A magnetic stirrer if you own one; otherwise a clean glass rod and the patience to stir gently by swirling the beaker.
- A thermometer, checked at its ice point as the commissioning session taught.
- A balance reading to 0.01 g, a 100 ml graduated cylinder and a 250 ml graduate.
- A timer, the notebook, and the calibration log.
Estimated cost
Section titled “Estimated cost”Cost band ££. The meter and the buffer standards are the whole of it, and both are one-off apart from the standards, which have a shelf life and are consumed. Everything else is Stage 0 equipment or a supermarket item. Dated prices live in the laboratory planner rather than in this page, so that they can be corrected without rewriting the text.
Estimated consumables cost
Section titled “Estimated consumables cost”The meter is an instrument and belongs to the band above. What this session actually consumes is the buffer standards — which have a shelf life and are used up whether or not you use them — a litre of distilled water, and supermarket quantities of three household solids.
| Consumed | This session | Sourced price | Cost this session |
|---|---|---|---|
| pH buffer standards at 4.01 and 7.00 | 2 sachets or about 100 mL of each | None. A named price gap: a pH meter, buffer standards at 4.01 and 7.00, and narrow-range indicator papers | — |
| Narrow-range pH indicator papers | about a dozen strips from two packs | None. A named price gap: a pH meter, buffer standards at 4.01 and 7.00, and narrow-range indicator papers | — |
| Distilled or deionised water | 1 L | None. distilled-water carries a cost band and no dated figure |
— |
| Sodium carbonate, anhydrous | about 10 g as washing soda | £7.20 per 500 g, anhydrous | £0.14 |
| Bicarbonate of soda and white vinegar | about 10 g and 100 mL | Supermarket items; the planner prices neither | — |
| Lint-free laboratory tissue | a few sheets | None. glassware carries a cost band and no dated figure |
— |
The priced rows come to £0.14 for one run of this session, at the retail ranges read on 5 September 2026 and recorded in the laboratory planner. That is a floor, not a total: 4 of the 6 rows carry no dated price, so they are counted as nothing here and are certainly not free. A priced entry is a dated range to plan against, never a quotation.
The electrode itself is the awkward case and is deliberately not in the table: the planner calls it “a consumable measured in months to a couple of years”, which makes it neither a per-session cost nor a one-off purchase. Budget for it once a year or two, not once a session.
Waste streams
Section titled “Waste streams”Three, all dilute and none silver-bearing.
- Alkaline aqueous waste: the carbonate, hydrogencarbonate and mixed-buffer samples, about 400 ml in total, at 1 per cent w/v or less.
- Acidic aqueous waste: the dilute vinegar sample and the pH 4.01 standard, about 200 ml in total.
- Near-neutral rinse water: everything else, including the pH 7.00 standard and the electrode rinsings.
Keep the first two in separate vessels, for the reason Card 1135 gives: carbonate and acid react, generating heat and carbon dioxide. At these concentrations that means fizzing and an overflowing beaker rather than anything worse, and an overflowing beaker of unlabelled liquid is exactly the mistake this course is trying to make impossible.
Preparation
Section titled “Preparation”Read your meter’s manual and your buffer standards’ data sheets. Both, before the session, not during it.
Condition the electrode. If it has been stored dry, or if it is new and arrived dry, soak the bulb in pH 4 buffer or in storage solution for at least eight hours before the session — the Vernier manual gives eight hours as the minimum for a sensor stored dry for a short period. An electrode taken straight from a dry box and used immediately will read slowly, drift, and give you a calibration you cannot trust.
Make up the sample solutions, at least an hour ahead so that they reach room temperature.
| Sample | How to make 100 ml | Predicted pH at 25 °C |
|---|---|---|
| 1. Distilled water | as supplied | see the note below |
| 2. Tap water | run the tap 30 s, then fill | unknown; look up your supplier’s report |
| 3. Sodium carbonate, 1 % w/v | 1.00 g anhydrous, or 2.70 g of the decahydrate, to 100 ml | 11.6 |
| 4. Sodium hydrogencarbonate, 1 % w/v | 1.00 g to 100 ml | 8.35 |
| 5. Acetic acid, about 2 % w/v | dilute white vinegar according to the strength on its label | 2.6 |
| 6. Equimolar carbonate buffer | 1.06 g anhydrous sodium carbonate (or 2.86 g of the decahydrate) and 0.84 g sodium hydrogencarbonate, to 100 ml | 10.33 |
Rule up your tables, from the Data to record section, before you switch the meter on.
Procedure
Section titled “Procedure”Stage 1: understand what you are about to do
Section titled “Stage 1: understand what you are about to do”Inside a combination glass electrode
- pH-sensitive glass membrane — the bulb; about 50 µm thick, and the only part that responds to the sample
- Internal reference — a silver/silver chloride wire in 0.1 mol/L hydrochloric acid: a fixed, known inside
- External reference compartment — a second silver/silver chloride wire in potassium chloride solution
- Liquid junction — a porous wick or frit; the salt bridge to the sample, and the source of a small potential of unknown size
- To the meter — which measures the potential difference between the two wires and converts it to pH using a calibration you supply
The electrode’s response follows a line. At 25 °C, for a good electrode, that line is
E = K + 0.05916 × log₁₀ a(H⁺) volts
where E is the potential the meter measures, a(H⁺) is the hydrogen ion activity of the sample — effectively its concentration, for our purposes — and K is a constant that gathers together the potential of the reference electrode, the asymmetry of the glass membrane and the liquid-junction potential. Harvey’s account is blunt about K: all its contributions are subject to uncertainty, and it may change from day to day and from electrode to electrode. That is why you calibrate. Not to make the meter more accurate, but because without a calibration the meter does not know what K is and cannot convert its millivolts into a pH at all.
Two numbers come out of a calibration. The offset is where the line sits — the potential the electrode gives in a solution of known pH, usually 7. The slope is how steeply it responds: 0.05916 volts, or 59.16 mV, per pH unit at 25 °C for a perfect electrode, and somewhat less for a real or ageing one.
What a calibration measures, and what it misses if you only do one point
- Ideal electrode: 59.16 mV per pH unit, offset 0
- Aged electrode: 52 mV per pH unit, offset +20 mV
Show the numbers behind this plot
| Series | pH of the solution | Electrode potential, mV |
|---|---|---|
| Ideal electrode: 59.16 mV per pH unit, offset 0 | 3.00 | 236.60 |
| Ideal electrode: 59.16 mV per pH unit, offset 0 | 7.00 | 0.00 |
| Ideal electrode: 59.16 mV per pH unit, offset 0 | 11.00 | -236.60 |
| Aged electrode: 52 mV per pH unit, offset +20 mV | 3.00 | 228.00 |
| Aged electrode: 52 mV per pH unit, offset +20 mV | 7.00 | 20.00 |
| Aged electrode: 52 mV per pH unit, offset +20 mV | 11.00 | -188.00 |
Stage 2: calibrate
Section titled “Stage 2: calibrate”- Rinse the electrode with distilled water from the wash bottle, into the waste beaker.
- Blot it dry against lint-free tissue. Do not wipe or rub it: rubbing the bulb builds a static charge on the glass that takes minutes to leak away and makes readings wander in the meantime.
- Place it in the pH 7.00 standard, with the bulb fully covered and clear of the bottom. Stir gently or swirl. Wait for the reading to stop moving — really stop, not slow down — and set the meter’s calibration or standardise control to 7.00. This sets the offset.
- Rinse, blot, and place it in the pH 4.01 standard. Wait again, and set the meter’s slope control to 4.01. This sets the slope. On an automatic meter both steps are prompted; on a manual one they are two separate knobs, and Harvey’s description of the procedure is exactly this order.
- Write down the slope if your meter displays it, as a percentage of theoretical or in mV per unit. That single number is the best health indicator an electrode has, and its history in your calibration log is what will tell you the electrode is dying months before it fails outright.
Stage 3: verify against something you did not calibrate with
Section titled “Stage 3: verify against something you did not calibrate with”Calibration is self-fulfilling: a meter always reads 7.00 in the buffer you just told it was 7.00. The check has to be a solution the calibration did not see.
- Rinse, blot, and measure the second, unopened pH 4.01 sachet — a fresh check standard, not the one you calibrated in, which has now had an electrode in it and a lid off it. Record the reading. If it is not within your meter’s stated accuracy of 4.01, stop and go to Troubleshooting; do not proceed to the samples.
Stage 4: predict, then measure
Section titled “Stage 4: predict, then measure”- Before measuring anything, write your predicted pH for all six samples in the notebook, and sign the line. This is not ceremony: a prediction written after the fact is not a prediction, and the whole value of the exercise is in the disagreements.
- Measure the samples in order of increasing pH — 5, 1, 2, 4, 6, 3 — so that carryover on the electrode always moves the next reading in a known direction and never in the direction that would flatter you.
- For each: rinse with distilled water, blot, immerse, stir gently, wait for a stable reading, and record the pH, the temperature and the time. Take a second reading a minute later without moving anything, and record that too.
- Test the same sample with indicator paper immediately afterwards: dip a fresh strip, compare against the chart in good light, and record the value you would have written down from the paper alone.
Stage 5: close the loop
Section titled “Stage 5: close the loop”- Return to the pH 7.00 standard and measure it as though it were a sample. The difference between this reading and 7.00 is the meter’s drift across the session, and it is a direct measure of how much of your data you can trust.
- Rinse the electrode thoroughly and return it to its storage solution before you write anything up. The electrode comes first; the notebook can wait five minutes.
Expected observations
Section titled “Expected observations”Sample 1, distilled water: the reading will not settle. This is the most instructive result of the session and it is a manufacturer-documented behaviour, not a fault. The Vernier manual states plainly that distilled water can read anywhere from pH 5.5 to 7.0 depending on how much carbon dioxide it has absorbed from the air, and that “due to a lack of ions, the pH values reported with the sensor in distilled water will be erratic.” Two causes, both real: dissolved carbon dioxide makes carbonic acid and genuinely acidifies the water, and the near-absence of ions makes the liquid-junction potential both large and unstable. Watch it wander, record the range you see, and stop treating “pure” as “neutral”.
Sample 2, tap water: somewhere near neutral, and stable, because tap water has ions in it. Where it sits depends on your supply. Thames Water, for instance, publishes hardness bands in milligrams per litre as calcium carbonate — soft up to 100, hard 200 to 300, very hard above 300 — and says all its water is hard because it passes through chalk; carbonate hardness and pH travel together.
Sample 5, dilute vinegar: stable, fast, and close to the predicted 2.6. Acids are the easy end for a glass electrode.
Sample 4, hydrogencarbonate: close to 8.35, and reassuringly independent of exactly how much you weighed.
Sample 6, the equimolar mixture: this should be your best agreement of the day. If your meter reads within 0.05 of 10.33 you have a well-behaved electrode and a good calibration.
Sample 3, 1 per cent carbonate: expect the largest disagreement, and expect the meter to read low. Two effects push the same way. The reading is an extrapolation far beyond the pH 7.00 and 4.01 points you calibrated between. And glass electrodes suffer alkaline error: above about pH 9 the membrane starts responding to sodium and potassium ions as well as to hydrogen ions, so it reports more hydrogen ion than is really there and therefore a lower pH. Harvey works a case at a true pH of 12.7, where the error is −0.5 of a unit. Your carbonate solution at 11.6 is well inside the region where this matters — and it is a sodium carbonate solution, so the interfering ion is the one the classic glass composition responds to most.
The indicator papers: you will find you can place every sample in the right unit and almost none of them in the right tenth.
What is happening chemically
Section titled “What is happening chemically”In the electrode. The pH-sensitive glass is a thin membrane with a hydrated gel layer on each face. Hydrogen ions exchange between the solution and that gel layer, and because the activities on the two sides differ, a potential develops across the membrane. The inside is a solution of fixed composition — Harvey gives 0.1 mol/L hydrochloric acid with a silver/silver chloride wire in it — so the inside contributes a constant, and everything that varies is on the outside. That is the whole principle.
Why the response is 59.16 mV per pH unit. It is not an arbitrary calibration factor. A tenfold change in the activity of a singly charged ion produces a potential change of 2.303RT/F, which at 298 K works out at 0.05916 V. Because it contains T, it changes with temperature — which is what automatic temperature compensation exists for.
In sample 3. Carbonate takes a proton from water, leaving hydroxide behind, which is why a solution of a salt with no hydroxide in it is strongly alkaline.
In sample 6. Both members of the conjugate pair are present in equal amounts, so the mixture sits at the pKa and resists being moved. It is also, note, a buffer of exactly the kind used to calibrate meters — you have made a crude standard, which is why it agrees so well.
In sample 1. Carbon dioxide dissolves and forms carbonic acid, whose first ionisation constant is 4.3 × 10⁻⁷. There is almost nothing else in the water to oppose it, so a very small amount of a very weak acid sets the entire pH — and the amount depends on how long the bottle has been open, which is why the number is not reproducible.
Data to record
Section titled “Data to record”Four tables. Rule them up before the meter goes on.
Table 1. The calibration entry — this goes in the calibration log, not loose in the notebook.
| Field | Value |
|---|---|
| Date and time | |
| Meter and electrode, make and serial or purchase date | |
| Standards used: nominal value, lot or batch, expiry date | |
| Temperature of the standards | |
| Reading in standard 1 before adjustment | |
| Reading in standard 2 before adjustment | |
| Slope reported by the meter (mV/pH or % of theoretical) | |
| Check standard: nominal value and reading after calibration | |
| Reading in the pH 7.00 standard at the end of the session | |
| Drift across the session | |
| Electrode returned to storage solution? |
Table 2. The samples.
| Sample | Predicted pH | Temp °C | Reading 1 | Reading 2, one minute later | Difference | Indicator paper |
|---|---|---|---|---|---|---|
| 5. Acetic acid ~2 % w/v | 2.61 | |||||
| 1. Distilled water | see notes | |||||
| 2. Tap water | your prediction | |||||
| 4. Sodium hydrogencarbonate 1 % | 8.35 | |||||
| 6. Equimolar carbonate buffer | 10.33 | |||||
| 3. Sodium carbonate 1 % | 11.64 |
Table 3. Distilled water, watched.
| Time from immersion | Reading |
|---|---|
| 15 s | |
| 30 s | |
| 1 min | |
| 2 min | |
| 5 min | |
| Range across all five |
Table 4. Your uncertainty budget. One line per contribution, filled in during the Analysis.
| Contribution | Estimate, pH units | How you got it |
|---|---|---|
| Meter’s stated accuracy | from the manual | |
| Calibration error | check-standard reading minus its nominal value | |
| Drift across the session | end-of-session standard reading minus 7.00 | |
| Temperature departure from 25 °C | see the Analysis | |
| Alkaline error, samples above pH 9 | see the Analysis | |
| Combined, for a near-neutral sample | ||
| Combined, for the carbonate sample |
Analysis
Section titled “Analysis”-
Account for every miss of more than 0.2 of a unit. Take the six rows of Table 2 and, for each disagreement between prediction and reading, name the cause: an arithmetic error in the prediction, a weighing error, a temperature departure, calibration extrapolation, alkaline error, or an electrode problem. A miss you cannot account for is a result, and it goes in the notebook as one.
-
Decide how many decimal places you are entitled to. Compare your meter’s display resolution with its stated accuracy. A meter that displays 0.01 and specifies plus or minus 0.2 — the figure Vernier publishes for its teaching-laboratory pH sensor — is showing you two digits it cannot support. Then add your own calibration error and drift from Table 4. Write the number of decimal places your budget justifies at the top of Table 2, and round every reading to it.
-
Separate the two things temperature does. Automatic temperature compensation, where your meter has it, adjusts the slope of the calibration line to the Nernstian value at the measured temperature. It does not correct for the sample’s own chemistry changing with temperature, and it cannot, because it does not know what the sample is. The buffer standards make the difference visible, because their own values are certified against temperature:
The certified pH of three NIST primary standard buffers, against temperature
- 0.05 m potassium hydrogen phthalate (nominal 4)
- Equimolal phosphate (nominal 7)
- 0.01 m sodium tetraborate, borax (nominal 9)
Show the numbers behind this plot
| Series | Temperature, °C | Certified pH of the standard |
|---|---|---|
| 0.05 m potassium hydrogen phthalate (nominal 4) | 0.00 | 4.00 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 5.00 | 4.00 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 10.00 | 4.00 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 15.00 | 4.00 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 20.00 | 4.00 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 25.00 | 4.01 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 30.00 | 4.01 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 35.00 | 4.02 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 40.00 | 4.04 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 45.00 | 4.05 |
| 0.05 m potassium hydrogen phthalate (nominal 4) | 50.00 | 4.06 |
| Equimolal phosphate (nominal 7) | 0.00 | 6.98 |
| Equimolal phosphate (nominal 7) | 5.00 | 6.95 |
| Equimolal phosphate (nominal 7) | 10.00 | 6.92 |
| Equimolal phosphate (nominal 7) | 15.00 | 6.90 |
| Equimolal phosphate (nominal 7) | 20.00 | 6.88 |
| Equimolal phosphate (nominal 7) | 25.00 | 6.87 |
| Equimolal phosphate (nominal 7) | 30.00 | 6.85 |
| Equimolal phosphate (nominal 7) | 35.00 | 6.84 |
| Equimolal phosphate (nominal 7) | 40.00 | 6.84 |
| Equimolal phosphate (nominal 7) | 45.00 | 6.83 |
| Equimolal phosphate (nominal 7) | 50.00 | 6.83 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 0.00 | 9.46 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 5.00 | 9.39 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 10.00 | 9.33 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 15.00 | 9.28 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 20.00 | 9.22 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 25.00 | 9.18 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 30.00 | 9.14 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 40.00 | 9.07 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 45.00 | 9.04 |
| 0.01 m sodium tetraborate, borax (nominal 9) | 50.00 | 9.01 |
-
Estimate your alkaline error. You cannot measure it without a second method, but you can bound it. Compare your carbonate reading with the predicted 11.64, subtract whatever you can attribute to extrapolation and to temperature, and attribute the remainder to alkaline error. Record it as a bound, not a value: “the reading is 0.3 low, of which at most 0.3 is alkaline error.”
-
Judge the papers honestly. For each sample, write down the pH you would have recorded from the paper alone, and the pH the meter gave. Then answer one question in the notebook: for which of the decisions in this course would the paper have been enough? Checking that a developer is somewhere near 10 and not near 7 — yes. Detecting a 0.15 drift in a fixer — no.
-
Write your own summary line for the electrode, into the calibration log: slope, check-standard error, session drift, and a one-word verdict. Next time you will have two lines, and a trend.
Troubleshooting
Section titled “Troubleshooting”The reading will not settle in a buffer standard. Give it two minutes; a slow response is the classic first sign of an electrode that has been stored dry or is nearing the end of its life. If it is still moving, rinse, soak in pH 4 buffer for an hour, and try again. Harvey notes that the average lifetime of a typical glass electrode is several years, so an old one is a plausible diagnosis.
The meter reads 7.00 in the standard, 7.00 in tap water and 7.00 in the stop-bath sample. Work the checks in this order, and note what each rules out.
- Is the electrode actually in the liquid? The bulb must be fully immersed. This rules out the commonest cause and costs five seconds.
- Is the protective cap still on? It rules out the second commonest.
- Measure the pH 4.01 standard. If it also reads 7.00, the electrode is not responding at all and the fault is in the electrode or its connection. If it reads 4.0-something, the electrode is fine and your samples really are all near neutral, which would mean a sample-preparation error.
- Check the connector. A loose or damp BNC connector gives a dead, stable, plausible mid-scale reading.
- Try the shock treatment the Vernier manual describes for a sensor that has been stored dry or responds sluggishly, then recalibrate.
- If it still reads one number everywhere, the electrode is dead. A cracked bulb reads a constant value because the two half-cells are short-circuited through the crack.
The slope is much less than 59 mV per unit. An electrode’s slope falls as it ages, and manufacturers publish an acceptable range for their own products; this course has not verified a specific percentage window and will not invent one, so use your meter’s manual. Falling slope with a good offset usually means an ageing bulb. A large offset with a good slope usually means the reference junction is blocked or the reference solution has been diluted.
Readings drift downwards in every alkaline sample. Suspect carbon dioxide: an alkaline solution standing open absorbs it and genuinely becomes less alkaline. Cover the beakers, and measure the alkaline samples last and promptly.
The reading jumps when you touch the beaker or the bench. Static, usually from wiping the bulb rather than blotting it, or from a synthetic garment. Blot, wait, and keep your hand off the vessel while reading.
Alternative route
Section titled “Alternative route”If you have no meter, this session is still worth doing with indicator papers alone, provided you are precise about what you get.
What papers can establish. That a solution is acid, near neutral or alkaline. That a print developer is in the region of 10 and not of 7 — which is enough to catch a badly mixed batch, a dilution error by a large factor, or a tray that has been contaminated with stop bath. That a stop bath is acid. That a fixer is on the acid side of neutral. ILFORD’s own process-control guidance treats sticks as a real alternative to a meter and names the useful ranges: pH 7 to 10 for developers, pH 4 to 7 for fixers.
What papers cannot establish. A difference of 0.2 of a unit — which is the difference between ILFORD’s published band for ID-11 stock, 8.60 to 8.70, and a batch that is out of specification. The drift of a working bath over its life. Any comparison you intend to make between two dates. The narrowest-range papers claim finer discrimination than the wide-range ones, and this course has not verified a manufacturer’s resolution figure for any of them — which is precisely why step 10 of the Procedure has you determine it for your own papers, on samples whose pH you predicted from chemistry. That comparison is the honest way to find out what your papers can do.
Do all six samples with papers. Predict, test, and record. You will end the session with a calibrated sense of your own strips, which is worth more than a borrowed number.
Clean-up
Section titled “Clean-up”Rinse the electrode thoroughly with distilled water, blot it, and return it to its storage solution before anything else. Empty the sample beakers into the correct waste vessel, keeping acid and alkaline streams apart. Rinse all glassware with tap water and then with a little distilled water, and stand it to drain. Wipe the bench and the tray. Wash hands after gloves come off, not instead of.
Used buffer standard is not returned to the bottle. Nothing that has had an electrode in it goes back into a stock container — the same rule as for any sample aliquot in this course.
Storage
Section titled “Storage”The electrode is the thing that will fail if you get this wrong. The Vernier manual is explicit on all three cases:
- Between measurements and up to 24 hours: stand the electrode in pH 4 or pH 7 buffer. It should never be stored in distilled water. The reference compartment is a concentrated potassium chloride solution, and standing in a solution with no ions in it draws that salt out through the junction.
- Longer than 24 hours: store in a pH 4 buffer and potassium chloride solution — the manual’s own recipe is 10 g of potassium chloride in 100 ml of pH 4 buffer — in the cap or bottle it was supplied in, with the bulb immersed. Harvey gives the general principle: the membrane’s outer surface must stay hydrated.
- If it has dried out: soak for at least eight hours in that storage solution before use, and recalibrate.
One manufacturer, not two. The storage rules above are taken from a single manufacturer’s manual, for a sealed gel-filled combination electrode sold to teaching laboratories, together with Harvey’s general statement that a glass electrode is stored in the storage buffer its manufacturer recommends. This course has not cross-checked a second electrode maker’s instructions, and electrodes differ — refillable ones have a fill hole and a fill solution that this one does not. Your own electrode’s manual governs, and where it disagrees with this page, follow it and note the disagreement in the calibration log.
Buffer standards have a shelf life and a once-opened life, both stated on the packaging. A bottle that has had an electrode dipped in it is contaminated and is no longer a standard. Sachets are better than bottles for occasional use, because each one is opened once.
Store the meter with its battery in and its cap on, somewhere it will not be knocked, and put the calibration log with it.
Disposal considerations
Section titled “Disposal considerations”Three dilute aqueous streams: an alkaline one of sodium carbonate and hydrogencarbonate at 1 per cent w/v or below, an acidic one of dilute acetic acid and used phthalate buffer, and near-neutral rinse water. There is no silver, no thiosulfate, no developing agent and no heavy metal in any of them.
The chemistry is simple: the two named streams are a weak base and a weak acid, and mixing them in a large excess of water gives a near-neutral solution of sodium acetate, carbon dioxide and water. Doing that deliberately, slowly, in a vessel several times the combined volume, is the general practice for reducing a dilute acid and a dilute alkali to something innocuous — and it fizzes, which is why the vessel is oversized and why the two are not simply tipped together in a beaker.
This course does not give a jurisdiction-specific disposal instruction and will not start here. What it gives you is the description you need in order to ask a specific question: about 600 ml of aqueous solution containing sodium carbonate, sodium hydrogencarbonate, sodium acetate and buffer salts, none above 1 per cent w/v, with no silver, no sulfur compounds and no organic developing agent. Take that description to your local authority’s published guidance, or to your water company’s trade-effluent guidance if you are in any doubt, and follow what it says. Check your local regulations. ILFORD’s own guidance for domestic users makes the same point: find out what applies where you live.
Questions
Section titled “Questions”- State the pH of your own tap water to the precision your meter and your calibration actually justify, and defend the number of decimal places you used, citing your Table 4.
- Your meter reads 7.00 in buffer, 7.00 in tap water and 7.00 in the vinegar sample. List the checks in the order you would make them, and say what each rules out.
- Explain, in terms of ions, why the distilled-water reading wandered and the tap-water reading did not.
- You calibrated at 4.01 and 7.00 and then measured a solution at a true pH of 11.6. Name the two separate effects that would make your reading low, and say which one a third calibration point would fix and which one it would not.
- For which of your six samples would an indicator paper have been an adequate instrument, and for which would it not? Answer for a specific decision, not in general.
- Your equimolar carbonate buffer read 10.33 and your 1 per cent carbonate solution read 11.2 against a prediction of 11.64. What does the good agreement on the first tell you about the disagreement on the second?
Further experiments
Section titled “Further experiments”The third calibration point. Obtain an alkaline buffer standard, read its safety data sheet first, and satisfy yourself about its classification before you handle it: commercial pH 10 standards are commonly borate-based, and borax as a solid carries H360 in the aggregated ECHA notifications, which is outside the Level A criteria this session was written to. If you are content to proceed, recalibrate at three points and re-measure sample 3. The difference between the two carbonate readings is your extrapolation error, isolated.
The temperature run. Take the equimolar carbonate buffer, whose predicted pH is exactly the pKa, and measure it at 10, 20 and 30 °C, with automatic temperature compensation on and then off. You are watching two different things move at once: the electrode’s slope, which compensation corrects, and the solution’s own pKa, which it does not.
The exhaustion curve. Make 200 ml of the equimolar buffer, and add 2 ml portions of your dilute vinegar, recording the pH after each. Plot pH against millilitres added. You will draw, by hand and from your own kitchen, the buffered curve from the buffers page — including the moment where it stops being flat.
The unbuffered comparison. Do the same to 200 ml of tap water. Count how many drops it takes to move a unit, then compare with the buffer. That ratio is buffer capacity, measured by you.
The carbon dioxide experiment. Boil 200 ml of distilled water for five minutes, cool it covered, and measure its pH; then leave it open and measure again every ten minutes for an hour. Plot it. What you are watching is atmospheric carbon dioxide dissolving, and it is the same mechanism that quietly acidifies an open tray of print developer overnight.
Check your understanding
Sources for this page
20 cited · checked 2026-09-04
- 01Analytical Chemistry 2.1, section 11.2: Potentiometric MethodsDavid Harvey, DePauw University§ The glass pH electrode: construction of a combination electrode, the 50 micrometre membrane, E = K + 0.05916 log a(H+) valid over about pH 0.5 to 9, the alkaline error worked at pH 12.7, two-point standardisation, automatic temperature compensation as a slope adjustment, storage in the manufacturer buffer, junction potentials, and Table 11.2.6 of NIST primary standard buffer values against temperaturechem.libretexts.org/Bookshelves/Analytical_Chemistry/Analytical_Chemistry_2.1_(Harvey)/11%3A_Electrochemical_Methods/11.02%3A_Potentiometric_Methodstier 2, specialist2026-09-04
- 02pH Sensor (PH-BTA) user manualVernier Science Education§ Specifications - range, accuracy, temperature range, isopotential point; Care and maintenance - short and long term storage and the prohibition on distilled water; Troubleshooting - why distilled water reads erratically; solutions the sensor must not be used invernier.com/manuals/ph-btatier 1, primary2026-09-04
- 03Chemistry 2e, section 14.2: pH and pOHPaul Flowers, Klaus Theopold, Richard Langley and William R. Robinson, for OpenStax§ 14.2 pH and pOH: the definitions and the temperature dependence of neutralityopenstax.org/books/chemistry-2e/pages/14-2-ph-and-pohtier 1, primary2026-09-04
- 04Chemistry 2e, Appendix H: Ionization Constants of Weak AcidsPaul Flowers, Klaus Theopold, Richard Langley and William R. Robinson, for OpenStax§ Appendix H: ionisation constants for acetic acid and carbonic acid at 25 degrees Copenstax.org/books/chemistry-2e/pages/h-ionization-constants-of-weak-acidstier 1, primary2026-09-04
- 05Chemistry 2e, section 14.4: Hydrolysis of SaltsPaul Flowers, Klaus Theopold, Richard Langley and William R. Robinson, for OpenStax§ 14.4 Hydrolysis of Salts: sodium hydrogencarbonate as an amphiprotic salt giving a basic solutionopenstax.org/books/chemistry-2e/pages/14-4-hydrolysis-of-saltstier 1, primary2026-09-04
- 06Chemistry 2e, section 14.6: BuffersPaul Flowers, Klaus Theopold, Richard Langley and William R. Robinson, for OpenStax§ 14.6 Buffers: the Henderson and Hasselbalch equation and the assumption under which it holdsopenstax.org/books/chemistry-2e/pages/14-6-bufferstier 1, primary2026-09-04
- 07Chemistry 2e, section 1.5: Measurement Uncertainty, Accuracy, and PrecisionPaul Flowers, Klaus Theopold, Richard Langley and William R. Robinson, for OpenStax§ 1.5 Measurement Uncertainty, Accuracy, and Precision: significant figures, accuracy against precisionopenstax.org/books/chemistry-2e/pages/1-5-measurement-uncertainty-accuracy-and-precisiontier 1, primary2026-09-04
- 08An Introduction to Film Process ControlHARMAN technology Limited (ILFORD Photo), 2010§ Lab equipment - advanced: pH meter or pH sticks; the ranges of sticks useful for developers and for fixers; monitoring pH as process controlilfordphoto.com/wp/wp-content/uploads/2024/02/FPC-Introduction.pdftier 1, primary2026-09-04
- 09ILFORD Chemical Sundries: ILFOSTOP, ILFOTOL and WASHAID, technical informationHARMAN technology Limited (ILFORD Photo), 2017§ ILFOSTOP: the pH-sensitive indicator dye changing yellow to purple as the bath exhausts; concentrate pH 2.1; capacity per litreilfordphoto.com/amfile/file/download/file/1865/product/669tier 1, primary2026-09-04
- 10ILFORD Powder Film Developers: PERCEPTOL, ID-11 and MICROPHEN, technical informationHARMAN technology Limited (ILFORD Photo), 2024§ pH and specific gravity table, and the note that the figures were obtained under controlled laboratory conditions and that users should make their own control measurementsilfordphoto.com/wp/wp-content/uploads/2024/09/ILFORD-POWDER-CHEM-190824.pdftier 1, primary2026-09-04
- 11ILFORD RAPID FIXER, technical informationHARMAN technology Limited (ILFORD Photo), 2010§ pH at 1+4; correcting a drifted pH with 50 per cent acetic acidilfordphoto.com/amfile/file/download/file/1833/product/711tier 1, primary2026-09-04
- 12Hard water: water quality help and adviceThames Water Utilities Limited§ Hardness of water - the classification bands in mg/L as calcium carbonatethameswater.co.uk/help/water-quality/water-hardnesstier 2, specialist2026-09-04
- 13PubChem compound summary: Borax (B4Na2O7.10H2O) (CID 16211214)National Center for Biotechnology Information§ GHS classification (ECHA C&L Inventory aggregation): Danger, H360 in 93.2 per cent of reportspubchem.ncbi.nlm.nih.gov/compound/16211214tier 1, primary2026-09-04
- 14PubChem compound summary: Sodium Carbonate (CID 10340)National Center for Biotechnology Information§ Computed properties - molecular weight; GHS classificationpubchem.ncbi.nlm.nih.gov/compound/10340tier 1, primary2026-09-04
- 15PubChem compound summary: Sodium Bicarbonate (CID 516892)National Center for Biotechnology Information§ Computed properties - molecular weight; GHS classificationpubchem.ncbi.nlm.nih.gov/compound/516892tier 1, primary2026-09-04
- 16PubChem compound summary: Acetic Acid (CID 176)National Center for Biotechnology Information§ Computed properties - molecular weight; GHS classification of the concentratepubchem.ncbi.nlm.nih.gov/compound/176tier 1, primary2026-09-04
- 17International Chemical Safety Card 1135: Sodium carbonate (anhydrous)Prepared by an international group of experts on behalf of the International Labour Organization and the World Health Organization, with the financial assistance of the European Commission, 2024§ Short-term effects and hazardous reactions: severe eye irritation; violent reaction with acids generating heat and carbon dioxideinchem.org/documents/icsc/icsc/eics1135.htmtier 1, primary2026-09-04
- 18International Chemical Safety Card 1044: Sodium bicarbonatePrepared by an international group of experts on behalf of the International Labour Organization and the World Health Organization, with the financial assistance of the European Commission, 2024§ Physical properties and effects of exposureinchem.org/documents/icsc/icsc/eics1044.htmtier 1, primary2026-09-04
- 19Working with substances hazardous to health: A brief guide to COSHH, INDG136Health and Safety Executive, 2021§ Assessing risk; choosing control measureshse.gov.uk/pubns/indg136.pdftier 1, primary2026-09-04
- 20General health and safety adviceHARMAN technology Limited (ILFORD Photo)§ Safe working practices; waste disposal for photographic productsilfordphoto.com/health-and-safetytier 1, primary2026-09-04
Formulas, hazard statements, historical dates and process descriptions on this page were checked against the sources above on the date shown. Safety data changes: obtain the current safety data sheet for the product you actually buy before you open it.