Designing Packed Bed Wet Scrubbers with Liquid Caustic Soda NaOH 32% for HCl, SO2, HF & Cl2 Acid Fume Abatement (QCVN 19:2024/BTNMT)

Designing Packed Bed Wet Scrubbers with Liquid Caustic Soda NaOH 32% for HCl, SO2, HF & Cl2 Acid Fume Abatement (QCVN 19:2024/BTNMT)
Table of contents

Counter-current Packed Bed Wet Scrubbers circulating Liquid Caustic Soda NaOH 32% are the primary Air Pollution Control (APC) barrier for steel pickling bays, electroplating lines, PCB etching rooms, and boiler flue gas systems. To maintain stack emissions strictly below QCVN 19:2024/BTNMT Column B thresholds (HCl ≤ 50 mg/Nm³, SO₂ ≤ 300 mg/Nm³, HF ≤ 5 mg/Nm³, Cl₂ ≤ 10 mg/Nm³), the scrubber must operate at a superficial gas velocity of 1.2–1.8 m/s, a liquid-to-gas ratio L/G = 1.5–3.0 L/m³, and an automated recirculation setpoint locked at pH 8.5–9.5—achieving over 98.5% acid capture while preventing carbonate scaling across the packing bed.

Actual 25kg jerrycans of Liquid Caustic Soda NaOH 32% at Loc Thien Chemical warehouse


1. Two-Film Mass Transfer Kinetics & Instantaneous Neutralization Stoichiometry

In metal pickling and surface finishing lines using Hydrochloric Acid HCl 32%, Sulfuric Acid H₂SO₄ 98%, or mixed HNO₃ + HF, acid vapors collected by lip-slot hoods enter the bottom of the packed tower and flow upward counter-currently against a downward spray of NaOH liquor distributed over high-surface-area random packing (110–220 m²/m³).

Under Whitman’s Two-Film Mass Transfer Theory, because free hydroxyl ions (OH⁻) in the liquid film react instantaneously and irreversibly with absorbed acid molecules, the equilibrium back-pressure of the acid gas at the gas–liquid interface drops to zero, making the absorption rate entirely gas-film controlled:

  • Hydrochloric Acid Vapor Neutralization: HCl (gas) + NaOH (aq) → NaCl + H₂O (ΔH = -55.8 kJ/mol)
  • Hydrofluoric Acid Vapor Neutralization: HF (gas) + NaOH (aq) → NaF + H₂O
  • Sulfur Dioxide Absorption: SO₂ (gas) + 2NaOH (aq) → Na₂SO₃ + H₂O
  • Free Chlorine Gas Absorption: Cl₂ (gas) + 2NaOH (aq) → NaOCl + NaCl + H₂O
  • Nitrogen Dioxide Absorption: 2NO₂ (gas) + 2NaOH (aq) → NaNO₂ + NaNO₃ + H₂O

Table 1: QCVN 19:2024/BTNMT Emission Limits & Specific Consumption of NaOH 32%

Target Acid Gas PollutantMolar Mass (M, g/mol)Soluble Salt Product in SumpQCVN 19:2024/BTNMT Column B Limit (mg/Nm³)Theoretical NaOH 100% per 1 kg Gas (kg/kg)Practical NaOH 32% Dosing Rate (incl. 1.12 safety factor)
Hydrochloric Acid (HCl)36.46Sodium Chloride (NaCl)≤ 501.097 kg3.84 kg NaOH 32% / kg HCl
Hydrofluoric Acid (HF)20.01Sodium Fluoride (NaF)≤ 51.999 kg7.00 kg NaOH 32% / kg HF
Sulfuric Acid Mist (H₂SO₄)98.08Sodium Sulfate (Na₂SO₄)≤ 350.816 kg2.86 kg NaOH 32% / kg H₂SO₄
Sulfur Dioxide (SO₂)64.06Sodium Sulfite (Na₂SO₃)≤ 3001.249 kg4.37 kg NaOH 32% / kg SO₂
Free Chlorine (Cl₂)70.91NaOCl + NaCl mixture≤ 101.128 kg3.95 kg NaOH 32% / kg Cl₂
Nitrogen Oxides (NOₓ as NO₂)46.01NaNO₂ + NaNO₃ mixture≤ 4000.869 kg3.04 kg NaOH 32% / kg NO₂

2. Hydraulic Sizing, Packing Depth & Mist Elimination Standards

Table 2: Engineering Design Criteria for Counter-Current Packed Bed Wet Scrubbers

Design ParameterUnitStandard Design Range (HCl / HF / SO₂)Engineering Consequence of Improper Sizing
Superficial Gas Velocity (vg)m/s1.2 – 1.8If ≥ 2.2 m/s: liquid flooding and alkaline mist carryover out the stack. If ≤ 0.8 m/s: oversized vessel diameter and poor gas distribution.
Liquid-to-Gas Ratio (L/G)L/m³ gas1.5 – 3.0If ≤ 1.0 L/m³: dry channeling across packing surfaces, allowing unneutralized acid fumes to slip through.
Packed Bed Height (Z = NTU × HTU)m1.5 – 2.5Provides 5–8 Number of Transfer Units (NTU), ensuring 98.5–99.5% removal efficiency.
Random Packing Media—PP Pall Ring / Tellerette D50 – D76 mmHigh void fraction (90–93%), specific surface area 110–190 m²/m³, low pressure drop (150–350 Pa/m).
Demister Pad Thicknessmm150 – 200Knitted PP mesh or Chevron blades capturing 99% of droplets ≥ 15 µm.
Sump Liquid Retention Timeminutes5 – 10Allows complete reaction degassing and prevents pump cavitation.

Engineering Calculation Example: 15,000 m³/h HCl Pickling Exhaust Scrubber

Technical Illustration (Reference Engineering Model): A steel wire pickling bay exhausts Qg = 15,000 m³/h (4.167 m³/s) containing an average inlet HCl concentration Cin = 850 mg/Nm³, targeting stack outlet Cout ≤ 15 mg/Nm³ (η = 98.2%).

  1. Tower Internal Diameter (D): Selecting design velocity vg = 1.5 m/s gives cross-sectional area A = 4.167 ÷ 1.5 = 2.778 m² → Internal diameter D = 1.88 m (select standard fabrication diameter D = 1,900 mm).
  2. Recirculation Pump Flow Rate (QL): Selecting L/G = 2.0 L/m³ gives QL = 15,000 m³/h × 2.0 L/m³ = 30,000 L/h = 30 m³/h.
  3. Hourly NaOH 32% Dosing Rate:
    • Hourly HCl mass load captured: M(HCl) = 15,000 × (850 - 15) × 10⁻⁶ = 12.525 kg HCl/h.
    • Commercial NaOH 32% (d = 1.35 kg/L) dosing rate: 12.525 × 3.84 = 48.10 kg/h (35.6 L/h).

3. Why Locking pH at 8.5–9.5 Prevents Carbonate Scaling (Na₂CO₃ / NaHCO₃)

A widespread operational mistake is manually dumping excessive caustic soda into the scrubber sump until pH reaches 12.5–13.5. Because over 99% of the gas drawn into the hood is ambient factory air containing ~400 ppm Carbon Dioxide (CO₂), running the scrubber above pH 10.8 forces the caustic liquor to scrub CO₂ into sparingly soluble Sodium Bicarbonate (NaHCO₃, solubility only 9.6 g/100 mL at 20 °C):

  • Step 1: CO₂ (gas) + 2NaOH (aq) → Na₂CO₃ (aq) + H₂O
  • Step 2: Na₂CO₃ (aq) + CO₂ (gas) + H₂O → 2NaHCO₃ (solid scale ↓)

Best-Practice Control Protocol from Loc Thien Engineers:

  • Lock the automated pH Controller setpoint at pH = 8.5 – 9.3: Strong acid gases (HCl, HF, H₂SO₄) are still absorbed at > 99% efficiency, while parasitic CO₂ absorption is suppressed—saving 18–25% of NaOH 32% consumption and keeping the packing media scale-free for 6–12 months.
  • Automated Conductivity Blowdown (EC = 65–80 mS/cm): Bleed 15–20% of the concentrated salt brine (~8–10% TDS) to the wastewater neutralization tank whenever EC hits 70 mS/cm.
  • Dual NaOH + Na₂SO₃ Dosing for Chlorine (Cl₂) Scrubbing: When scrubbing Cl₂ gas, maintain ORP ≤ +150 to +250 mV with minor sodium sulfite/thiosulfate addition so intermediate NaOCl cannot re-release toxic Cl₂ gas if pH transiently dips below 7.5.

ZDHC MRSL v3.1 compliant IBC storage at Loc Thien Chemical warehouse


4. ZDHC MRSL v3.1 Level 1 Certified NaOH 32%–50% Supply by Loc Thien Chemical

Loc Thien Investment Development Co., Ltd. (LOC THIEN INVESTMENT DEVELOPMENT COMPANY LIMITED — Tax ID: 0313650856) is a premier commercial supplier and distributor of industrial chemicals across Vietnam:

  1. Official ZDHC MRSL Version 3.1 Conformance Level 1 Certification: NaOH (Sodium Hydroxide) supplied by Loc Thien holds CERTIFICATE (ZDHC MRSL Conformance Level 1) No. ZDHC1 127736 0001 Rev. 00 (Test Report No. 2486017672-Q24VPS-CHM2869) issued by TÜV SÜD Product Service GmbH / TÜV SÜD Vietnam.
  2. 6 Strategic Warehouses (3,000+ tons/month, 5–30-ton specialized tanker fleet): Ba Ria - Vung Tau (Phu My 1 IP), Dong Nai (Long Thanh IP), Binh Duong (Di An City), Da Nang (Hoa Khanh IP), Can Tho (Tra Noc IP), and Bac Ninh (Tien Son IP). Legal Headquarters: 452/6B Tinh Lo 10, Binh Tri Dong Ward, Binh Tan District, Ho Chi Minh City.
  3. Quotation & Delivery SLA: Technical quotation within 15 minutes (unit price structured around 5 factors: 32% vs 50% concentration, order volume, IBC vs 5–30-ton tanker delivery, distance, and contract schedule). Delivery within 4 hours in inner HCMC, 24–48 hours across Southern & Mekong Delta industrial parks, and 2–3 days in Northern & Central Vietnam. Contact hotline 0979 891 929 for detailed delivery procedures.
WeChat B2B

Connect via WeChat B2B

Loc Thien Chemical — Direct Manufacturer & Industrial Chemical Supplier

Loc Thien Chemical Official WeChat B2B QR Code 0979891929

Scan QR code with WeChat on your phone

WeChat ID 0979891929

Tap the copy button above, then open WeChat and paste ID into Search to connect.

Direct Technical & Bulk Quotation Hotline: 📞 0979 891 929