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23-Chem-B6 Petroleum Refining and Petrochemicals · May 2015

Question 3 of 6: Crude Refining, Product Specifications and SO₂ Absorption

Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)

Notes on this paper

Paper format: Closed-book, 3 hours; six “Problem” blocks of equal value (20 marks each), of which five constitute a complete paper (the first five in the answer book are marked). Sub-parts (a),(b),(c)… may be treated independently. Most parts call for concise essay answers; several require calculations with all steps shown. All six problems are solved below.

Reference texts: Gary, Handwerk, Kaiser & Geddes, Petroleum Refining: Technology and Economics (5th ed., CRC Press) — refinery processes and product properties; Fahim, Al-Sahhaf & Elkilani, Fundamentals of Petroleum Refining (Elsevier) — hydrogen production, cracking, treating, alkylation; Felder, Rousseau & Bullard, Elementary Principles of Chemical Processes (4th ed., Wiley) — material balances, recycle, combustion and gas-law calculations; supporting property data from Perry’s Chemical Engineers’ Handbook (9th ed.).

Question 3: Crude Refining, Product Specifications and SO₂ Absorption (20 marks — equal value)

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.

(a) Why crude is refined, and how (4 marks)

Crude oil is a complex mixture of thousands of hydrocarbons (plus sulphur, nitrogen, oxygen and metal compounds) with a wide boiling range and, as produced, no direct end use. Refining separates it into fractions with defined, saleable properties (LPG, gasoline, jet/kerosene, diesel, fuel oil, lube base stocks, asphalt, petrochemical feedstocks) and upgrades the low-value heavy ends into more valuable light products while removing contaminants that would poison catalysts or violate fuel specifications.

This is done in three families of process:

(b) Leading specification features by product (6 × 1 mark)

ProductLeading specification feature(s)
i. GasolineOctane number (RON/MON) and volatility (Reid vapour pressure, distillation)
ii. Naphtha & keroseneNaphtha: boiling range and PONA (paraffin/olefin/naphthene/aromatic) for reformer feed; kerosene/jet: smoke point, freeze point and flash point
iii. Gas oils (diesel)Cetane number, cloud/pour point, flash point and sulphur content
iv. Fuel oilsViscosity, sulphur content, pour point and flash point
v. Lubricating oilsViscosity and viscosity index, pour point, flash point
vi. AsphaltsPenetration, softening point (ring-and-ball) and ductility

(c) SO₂ absorption in the packed tower

Given. Gas feed 7380 m³/h at 303 K, 1 bar, 14.8 mol% SO₂ (balance inert); exit gas 1 mol% SO₂; water 1 m³/min. Only SO₂ is absorbed; the inert gas passes through unchanged.

QuantityValue
Inlet gas volume7380 m³/h @ 303 K, 1 bar
Inlet SO₂14.8 mol%
Outlet SO₂1 mol%
Water rate1 m³/min = 60 m³/h

Find. (i) SO₂ concentration in the liquid effluent; (ii) the volumetric flow of the exit gas at 0.95 bar, 293 K.

PackedabsorptiontowerWater 1 m3/min (0% SO2)Gas 7380 m3/h14.8% SO2303 K, 1 barClean gas 1% SO2(6465 m3/h @ 0.95 bar, 293 K)Effluent 43.6 kg SO2/m3
Figure 4 — Countercurrent packed absorber: SO₂-laden gas enters at the bottom, clean water at the top; scrubbed gas leaves at 1% SO₂ and the SO₂-rich water leaves as the bottom effluent.

Approach. Convert the inlet gas to a molar flow (ideal gas), use the inert as a tie to fix the exit gas and the SO₂ absorbed, put the absorbed SO₂ into the water for the effluent concentration, and apply the ideal-gas law again for the exit volume at the new T, P.

  1. Inlet molar flow and SO₂ split. With $R = 8.314$ kPa·m³/(kmol·K),$$\dot n_{in} = \frac{PV}{RT} = \frac{100(7380)}{8.314(303)} = 293.0\ \text{kmol/h}.$$Then SO₂ in $= 0.148(293.0) = 43.36$ and inert $= 249.6$ kmol/h.
  2. Exit gas from the inert tie. Inert is not absorbed, so it is 99% of the exit gas:$$\dot n_{out} = \frac{249.6}{0.99} = 252.1\ \text{kmol/h},\qquad \text{SO}_2\ \text{out} = 0.01(252.1) = 2.52\ \text{kmol/h}.$$SO₂ absorbed $= 43.36 - 2.52 = \boxed{40.84\ \text{kmol/h}}$.
  3. (i) Effluent concentration. The water is $60$ m³/h $= 60{,}000$ kg/h. The absorbed SO₂ mass is $40.84(64) = 2614$ kg/h, so$$C_{SO_2} = \frac{2614\ \text{kg/h}}{60\ \text{m}^3/\text{h}} = \boxed{43.6\ \text{kg/m}^3}\ (\approx 4.17\ \text{wt\%}).$$
  4. (ii) Exit-gas volume at 0.95 bar, 293 K.$$\dot V_{out} = \frac{\dot n_{out} R T}{P} = \frac{252.1(8.314)(293)}{95} = \boxed{6465\ \text{m}^3/\text{h}}.$$
QuantityResult
SO₂ absorbed40.84 kmol/h
(i) Effluent SO₂ concentration43.6 kg/m³ (4.17 wt%)
(ii) Exit-gas volume @ 0.95 bar, 293 K6465 m³/h