18-Env-B5 Industrial & Hazardous Waste Management · Undated paper
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams — May 2019 — 18-Env-B5: Industrial & Hazardous Waste Management (3 hours, open book). Marks are indicated beside each question for a total of 100 marks; all ten questions are answered in full below as a complete study resource.
Reference texts: LaGrega, Buckingham & Evans, Hazardous Waste Management (2nd ed.); Nemerow & Dasgupta, Industrial and Hazardous Waste Treatment (2nd ed.); Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery (5th ed.); Davis & Cornwell, Introduction to Environmental Engineering (6th ed.).
Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.
Given. Reduction half-reaction, nitrobenzene → aniline: $E^0_{\text{NB}} = +0.42\ \text{V}$ ($n=6$ electrons). Reduction half-reaction, $\text{Fe}^{3+} + e^- \rightleftharpoons \text{Fe}^{2+}$: $E^0_{\text{Fe}} = +0.77\ \text{V}$.
Find. Whether Fe(II) can reduce nitrobenzene to aniline under standard conditions — the overall cell potential $E^0_{\text{cell}}$ and Gibbs free-energy change $\Delta G^0$.
Approach. For Fe(II) to act as the reducing agent, it must be oxidized to Fe(III) — the printed Fe³♠/Fe²♠ half-reaction must therefore run in reverse, paired with the nitrobenzene half-reaction running forward (as the reduction/cathode reaction). $E^0_{\text{cell}} = E^0_{\text{cathode}} - E^0_{\text{anode}}$ (both written as reductions), and $\Delta G^0 = -nFE^0_{\text{cell}}$.
$E^0_{\text{cell}}$ is negative and $\Delta G^0$ is strongly positive, so the reaction as written is not spontaneous under standard conditions — ferrous iron (Fe2+) alone cannot reduce nitrobenzene to aniline, because the Fe3+/Fe2+ couple is a weaker reducing agent (higher, more positive reduction potential, $+0.77\ \text{V}$) than nitrobenzene is an oxidizing agent ($+0.42\ \text{V}$) requires. This result explains why dissolved ferrous iron is not used as a reductant for nitroaromatic contaminants in practice. By contrast, zero-valent iron, Fe(0), has a much more negative $\text{Fe}^{2+}/\text{Fe}^0$ standard potential (about $-0.44\ \text{V}$, literature value), giving $E^0_{\text{cell}} = 0.42 - (-0.44) = +0.86\ \text{V}$ and a strongly negative $\Delta G^0$ — a thermodynamically favourable reaction. This is the actual basis for permeable reactive barriers (PRBs) using granular zero-valent iron to reduce nitroaromatic and chlorinated contaminants in groundwater: it is the metallic Fe(0) surface, not dissolved Fe(II)/Fe(III) chemistry, that supplies the driving force.
| Quantity | Value |
|---|---|
| $E^0_{\text{cell}}$ (Fe(II) as reductant) | −0.35 V |
| $\Delta G^0$ (Fe(II) as reductant) | +202.6 kJ/mol (non-spontaneous) |
| $E^0_{\text{cell}}$ (Fe(0) as reductant, for contrast) | +0.86 V (spontaneous) |