Industrial Chemistry
Ostwald Process (Nitric Acid)
Three steps from ammonia to fertilizer — and to TNT
The Ostwald process makes nitric acid by catalytically oxidizing ammonia in three stages: NH₃ → NO → NO₂ → HNO₃. A platinum-rhodium gauze at 850 °C drives the first step at over 95% selectivity. The world makes about 70 million tonnes of HNO₃ a year — most of it for fertilizer.
- InventorWilhelm Ostwald, 1902
- CatalystPt-Rh gauze (90:10)
- Burner temperature~850 °C
- Step-1 selectivity to NO95–98%
- Contact time on gauze~1 ms
- Global output~70 Mt HNO₃/yr
Interactive visualization
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A condensed visual walkthrough — narrated, captioned, under a minute.
How the process works
The Ostwald process turns ammonia into nitric acid in three sequential reactions, each in its own equipment at its own optimal temperature. Step 1 wants high temperature for catalyst activity, step 2 wants low temperature for equilibrium yield, step 3 wants water and a tall absorption column. Real plants run as one heat-integrated train.
┌──────────┐ ┌──────────┐ ┌──────────┐ ┌──────────┐
│ NH₃ │ +O₂ │ NO │ +O₂ │ NO₂ │ +H₂O│ HNO₃ │
│ (g) │ ───► │ (g) │ ───► │ (g) │ ───► │ (aq) │
└──────────┘ Pt └──────────┘ cool └──────────┘ tower└──────────┘
-Rh chamber absorption
gauze oxidation + tail-gas
850 °C ~50–150 °C ~25 °C
~1 ms minutes residence ~30 min
Behind the scenes, this is the same nitrogen that sat as inert N₂ in the atmosphere — fixed by Haber-Bosch into NH₃, then walked up the oxidation ladder by Ostwald. Together the two processes are the chemical engine of the green revolution.
Step 1 — catalytic ammonia burning
4 NH₃(g) + 5 O₂(g) ──Pt-Rh, 850 °C──► 4 NO(g) + 6 H₂O(g)
ΔH = −907 kJ/mol
NH₃ and air (1:9 by volume, 10% NH₃) flow downward through a stack of 10–30 woven Pt-Rh gauzes, each ~80 µm wire diameter, 1024 mesh per cm². Contact time is roughly 1 millisecond — long enough to make NO, too short for NO to back-decompose to N₂. The reaction's own exothermicity holds the gauze at 850 °C; plants pre-heat with a hydrogen flame at startup, then NH₃ + O₂ feed alone sustains temperature.
Selectivity to NO is 95–98% on fresh gauzes. The remaining 2–5% goes to N₂O (greenhouse gas) and N₂ (back where the nitrogen started). Higher temperatures raise NO yield but accelerate Pt evaporation; lower ones risk coking from organic NH₃ contaminants. 850 °C is the sweet spot.
Step 2 — gas-phase NO oxidation
2 NO(g) + O₂(g) ⇌ 2 NO₂(g) ΔH = −114 kJ/mol
Hot exit gas leaves the burner at ~850 °C. Heat exchangers pre-heat absorption-tower air and raise process steam, cooling the stream to ~150 °C and then to ~50 °C. Cooling matters because 2 NO + O₂ → 2 NO₂ is exothermic — high temperature drives it backward.
The reaction needs no catalyst. A few minutes of residence in an "oxidation drum" or the cooler tubing itself converts > 90% of NO to NO₂. The remainder gets re-oxidized by air injected later.
Step 3 — water absorption
3 NO₂(g) + H₂O(l) ⇌ 2 HNO₃(aq) + NO(g) ΔH = −136 kJ/mol
NO₂ contacts water in a packed or sieve-tray tower. Each pass produces 2 HNO₃ per 3 NO₂ plus regenerated NO. Air injected at the bottom re-oxidizes NO back to NO₂, recycling it up the column. 30+ trays push conversion to the equilibrium ceiling.
Dual-pressure plants run absorption at 8–14 bar to push equilibrium toward HNO₃. Output sits at 50–65 wt%; the 95% concentrated-acid explosives grade comes from extractive distillation with H₂SO₄ to break the 68% azeotrope.
Worked numbers — feed to product
Take 1 tonne of NH₃ feed (58 800 mol):
- Step 1 (selectivity 96%): 0.96 × 58 800 = 56 450 mol NO produced. The other 4% becomes ~2350 mol N₂ and ~50 mol N₂O.
- Step 2 (~95% conversion): 53 600 mol NO₂.
- Step 3 (after recycle, ~98% absorption): 35 000 mol HNO₃ (3 NO₂ → 2 HNO₃, with NO recycled).
- Net HNO₃ output: 35 000 × 63 g/mol ≈ 2.2 t HNO₃ per tonne NH₃ — the standard plant ratio.
- Energy: Step 1 generates ~907 kJ/mol NH₃. After heat recovery, plants are net steam exporters by ~0.7 t per tonne HNO₃.
- Pt loss: ~150 mg per tonne HNO₃ at modern recovery rates. A 1000 tpd plant loses ~50 kg of Pt per year.
Full reaction-flow diagram
Haber-Bosch Ostwald (this article)
───────── ─────────────────────────
N₂ ──► NH₃ → NH₃ + air
│
Pt-Rh gauze, 850 °C
│
▼
NO (g) ───┐
│ + O₂, cooler
▼ │
NO₂ (g) ◄──┘
│
│ + H₂O in absorber
▼
HNO₃ (aq)
│
▼
┌─────────────┴─────────────┐
▼ ▼
NH₄NO₃ fertilizer explosives
(75% of output) (TNT, RDX, ANFO,
rocket oxidizer)
Stages compared at a glance
| Step 1: NH₃ → NO | Step 2: NO → NO₂ | Step 3: NO₂ → HNO₃ | Tail-gas treatment | |
|---|---|---|---|---|
| Equipment | Pt-Rh gauze burner | Cooler / oxidation drum | Packed absorption tower | SCR / N₂O abatement bed |
| Temperature | ~850 °C | 50–150 °C | 20–40 °C | 250–400 °C |
| Pressure | 1–10 bar | 1–10 bar | 8–14 bar | 1 bar |
| Residence time | ~1 ms | Minutes | 30+ min | 0.1–1 s |
| Catalyst | Pt-Rh (90:10) gauze | None — gas phase | None — absorption | Fe-zeolite or Co/Ce |
| Conversion | 95–98% to NO | ~90% to NO₂ | ~98% absorbed (recycle) | 70–90% N₂O destroyed |
| What kills it | Pt loss, NH₃ slip | Hot-spot re-equilibration | NO breakthrough at top | SOx poisoning |
Real-world plants and history
- Wilhelm Ostwald, 1902 patent. The German chemist (1909 Nobel Prize) demonstrated the gauze burner in his Leipzig laboratory. His insight: a fast surface reaction at the right temperature beats thermodynamic equilibrium because the reverse decomposition can't keep up.
- Norsk Hydro, Notodden & Rjukan. Norway's giant Birkeland-Eyde plants on cheap hydropower were converted to Ostwald in the 1920s once cheap NH₃ from Haber-Bosch arrived.
- Modern dual-pressure plants. Yara, ThyssenKrupp, KBR license slightly different versions. Burner at low pressure (4–5 bar), absorption at high pressure (10–12 bar) — the compromise between selectivity and absorption.
- Largest single trains. Yara's Porsgrunn (Norway) and CFI's Sluiskil (Netherlands) each push past 2000 tpd. A typical greenfield plant is 500–1500 tpd.
- WWI dual-use chemistry. Germany's nitric-acid supply switched from Chilean saltpetre to synthetic in 1914–1916. The Allied blockade had cut imports; without the NH₃→HNO₃ pipeline German artillery would have run dry.
- Birkeland-Eyde, 1903. Direct N₂ + O₂ → NO via a 3000 °C electric arc. ~60 MWh per tonne HNO₃, only viable on free hydroelectricity. Survived in Norway until ~1940.
Variants and edge cases
- Mono-pressure plants. All steps at one pressure (4 bar low or 10 bar high). Cheaper capex, lower yield. Common in plants < 500 tpd.
- Concentrated nitric acid. Direct-strong-nitric (DSN) variants use cryogenic O₂ and 50% H₂O₂ to push absorption past the 68% water azeotrope without distillation.
- N₂O abatement. Secondary Fe-zeolite or Co/Ce beds downstream of the gauze decompose 2 N₂O → 2 N₂ + O₂. Modern European plants emit < 1 kg N₂O per tonne HNO₃, vs ~10 kg unmitigated.
- SCR tail-gas treatment. Selective catalytic reduction with NH₃ over V-W-Ti destroys remaining NOx in the exhaust to < 25 ppmv.
- Plasma and electrocatalytic alternatives. Active research aims to skip Haber-Bosch + Ostwald entirely by reducing N₂ + H₂O electrochemically to NO₃⁻. Faradaic efficiencies are still in single digits.
Common pitfalls and misconceptions
- "Higher gauze temperature is always better." Selectivity to NO peaks near 850 °C. Beyond ~950 °C, Pt vaporization accelerates and gauze life collapses to weeks.
- "NO₂ absorbs neatly into water." The 3 NO₂ + H₂O ⇌ 2 HNO₃ + NO equilibrium recycles a third of the nitrogen back. Without air re-injection, conversion stalls.
- "Tail gas is just NOx." It also contains N₂O, often the largest CO₂-equivalent emitter in the plant.
- "Ostwald and Haber-Bosch are independent." Almost no Ostwald plant runs alone — they sit adjacent to a Haber-Bosch plant because shipping liquid NH₃ is awkward and heat integration is natural.
- "Pt-Rh gauzes are sintered solid." They're woven wire, not pellets — high surface area, low mass-transfer resistance, and ~99.5% Pt-recoverable when retired.
- "All HNO₃ goes to fertilizer." ~75% does, mostly as ammonium nitrate. The other 25% goes to caprolactam (nylon-6), TNT, plating chemistry, and rocket-oxidizer fuming acid.
Frequently asked questions
Why does the Ostwald process need a platinum-rhodium gauze?
Without a catalyst, NH₃ in air burns straight to N₂ and H₂O — useless for nitric acid. The Pt-Rh gauze (typically 90:10 Pt:Rh, woven at 1024 mesh per cm²) selectively oxidizes NH₃ to NO at >95% yield, but only if the contact time is short enough (~1 ms) that NO doesn't have time to decompose back to N₂. Rhodium toughens the gauze against thermal creep at 850 °C; pure Pt would melt-creep within weeks.
Why does the second-step gas have to cool down before oxidation?
2 NO + O₂ → 2 NO₂ is exothermic and equilibrium-limited — high temperature pushes it back to the left. The hot gas leaving the Pt-Rh gauze is cooled (typically with a heat exchanger that pre-warms the incoming air, recovering most of the energy) to ~150 °C before oxidation, then to ~50 °C for absorption.
Why is N₂O emission a big deal in nitric acid plants?
About 0.3–1.5% of NH₃ feed escapes as nitrous oxide (N₂O) — a 273× more potent greenhouse gas than CO₂. Modern plants install secondary catalysts (Co/Ce or Fe-zeolite beds) downstream of the gauze to decompose N₂O back to N₂ and O₂, cutting emissions by 70–90%. The CDM market has paid plants in India and China to retrofit these for ~$0.50/t-CO₂eq abated.
How does Ostwald compare to Birkeland-Eyde?
Birkeland-Eyde (1903, Norway) ran a 3000 °C electric arc through air to oxidize N₂ directly to NO. It worked, but consumed ~60 MWh per tonne of HNO₃ — only viable next to free hydropower. Ostwald (1902, patented 1908) starts from NH₃ already made by Haber-Bosch and uses ~3 MWh per tonne. Ostwald killed Birkeland-Eyde by the 1930s; Norsk Hydro converted its fjord plants over.
What is concentrated vs dilute nitric acid output?
Standard absorption towers produce "weak" acid at 50–65 wt%. To get concentrated (95–99% white-fuming nitric acid), you have to break the 68 wt% azeotrope — typically by extractive distillation with sulfuric acid or magnesium nitrate brine. Most fertilizer-grade output stays dilute; explosives grade (Pentolite, RDX) needs the concentrated.
What's the catalyst lifetime and what kills it?
A Pt-Rh gauze pack runs 6–12 months between changes. Three things age it. First, Pt vapour pressure at 850 °C is non-negligible — Pt slowly evaporates, and a downstream Pd-Au "catchment gauze" recovers about 70% of it. Second, mechanical creep deforms the wires. Third, sulfur or chloride trace contamination in NH₃ poisons surface sites. A 100-tpd plant loses ~15 g of Pt per day at modern recovery rates.