PURPOSEIron, an important micronutrient for humans and aquatic organisms but a household (staining capacity) and water treatment problem at high concentrations, is quantitatively determined. Two versions of the lab are presented: a macroscale version and a small scale version.
DESCRIPTIONFerric iron is reduced to ferrous iron and complexed with 1,10-phenanthroline. This complex has a maximum absorbance at 510nm and can be quantified spectrophotometrically or colorimetrically.
TIMEOne 45-minute period.
MATERIALSMacroscale version:
Chemicals
Equipment
Small Scale Version:
Chemicals
Equipment
SAFETY INSTRUCTIONSNormal laboratory safety practice including wearing safety eye protection and aprons should be followed. Care should be exercised when handling concentrated HCl. Adequate ventilation, preferably a hood enclosure, should be provided. Report, neutralize, and clean up any chemical spills.
PROCEDURE
The procedure has been intentionally organized into several modular parts. Because the iron sample must be boiled for a time, its treatment is placed before and after the working standard preparation to save time.
Prepare working standards by adding the following reagents to test tubes labelled A-J as described below.
| A | B | C | D | E | F | G | H | I | J | |
|---|---|---|---|---|---|---|---|---|---|---|
| Hydrazine | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
| sodium acetate | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
| distilled H2O | 70 | 70 | 70 | 70 | 70 | 70 | 70 | 70 | 70 | 70 |
| Phenathroline | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 |
| distilled H2O | 17 | 16 | 15 | 14 | 13 | 12 | 11 | 10 | 9 | 8 |
| Final Fe conc (micrograms) | 10 | 20 | 30 | 40 | 50 | 60 | 70 | 80 | 90 | 100
|
MODIFICATIONS/SUBSTITUTIONSThis experiment is designed for an AP level course. The activity should be sequenced within the course following discussions of spectroscopy, complexation, and redox chemistry.
There is nothing magical about the hydrochloride or hydroxylamine. Other reducing agents will work too. Ascorbic acid will do the trick. When making substitutions remember that the concentration given for using
hydroxylamine (roughly 0.15M) involves 8 Fe+3 for each hydroxylamine molecule used.
In the macroscale experiment, a Bunsen burner may be substituted for the hot plate: DO NOT heat the pyrex test tubes with a Bunsen burner.
Carborundum or other inert material may be used instead of the glass beads.
In the macroscale experiment volumetric flasks aren't absolutely necessary. For example, when diluting the stock solution of Fe, 50mL could be pipeted into a beaker or reagent bottle and 950mL distilled water added to make 1 liter. Note also that graduated cylinders may be substituted for pipets. Some accuracy will be sacrificed. If the glassware used in this experiment has been used with iron compounds it is probably
advisable to rinse it prior to use with concentrated HCl (6M will do a decent job).
DISCUSSIONThis method analyzes total iron. In most natural waters soluble iron will normally be present as Fe+3. Phenanthroline complexes the Fe+2 form. The hydroxylamine is added to reduce Fe+3 to Fe+2 as indicated:
oxidation NH3OH+ + 3H2ONO3- + 10H+ + 8e-
reduction 8Fe+38Fe+2
Net NH3OH- + 3H2O + 8Fe+3NO3- + 10H+ + 8Fe+2
Each molecule of hydroxylamine reduces eight ferric ions to ferrous iron. Iron is also present, depending on the pH, as soluble FeOH+2 complex, Fe(OH)4- complex, solid Fe(OH)3, solid FeCO3, and solid Fe(OH)2. The sample is boiled in acid during the reduction step to ensure complete dissolution of solid or colloidal iron compounds and to protect against the formation of the basic species above, none of which is readily complexed by phenanthroline.
There are several potential interfering substances which will either complex phenanthroline (mostly metals) or oxidize ferrous iron back to ferric iron. The addition of an excess of hydroxylamine eliminates errors caused by excessive concentrations of strong oxidizing agents. The excess phenanthroline replaces that complexed by interfering metal ions.
The sodium or ammonium acetate solution is added for two reasons. Both form buffer solutions which help eliminate precipitates and help complex Fe+2 such that phenanthroline will complex with the iron rather that some interfering species.
Organic material (algae or their excretions, in addition to humic material or other organic material) are possible interferents, but are largely taken into account by using the sample as a reference blank solution.
Sampling bottles should be glass. If a tap water sample is being taken the water should be allowed to run for several minutes before taking the sample. This will flush any iron that has accumulated in the pipes-copper will interfere in the analysis.
The sample size may be greater or less than 50mL (or 50 drops for the small scale method). The only requirement is that the final volume after the boiling step allow addition of reagents and be within the containment volume (100mL for spectrophotometric method or roughly 100 drops for the micro method). It will probably be easier to adjust sample size than remake your standards if the sample falls out of the calibration range.
CALCULATIONSThe concentration of the sample is related by its original volume and absorbance to the calibration standard concentration at that absorbance. Specifically, for an unknown giving an absorbance corresponding to 24 microgram: standard volume (mL).
Sample concentration = standard concentration x (microgram/100mL) sample volume (mL)
std con = std con x microgram per 100mL = / F(20 microgram per 100 x 100mL,50mL) = 40microgram/100mL, which is usually reported as 0.40mg/L Fe.
The concentration (in micrograms/100mL) of the sample will be equal (in micrograms/100mL) to that of the standard which matches in color (assuming equal number of drops of were delivered to the cell well).
DISPOSALFlush all standards and samples down the sink with large quantities of water.
REFERENCESStaff and participants, 1989 Dreyfus Institute on Environmental Chemistry, Princeton University, Princeton, NJ.