3.Pharmaceutical wastewater

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November 15, 2025

A pharmaceutical factory's 5t/h triple-effect evaporator for pharmaceutical wastewater

The "triple-effect countercurrent + TVR thermal pressing" process for treating 5 t/h of high-salt pharmaceutical wastewater can achieve high concentration, salt separation and crystallization, and condensate reuse with low steam and power consumption, resulting in significant economic and environmental benefits. The modular design of the equipment allows for rapid replication at capacities of 3 t/h, 8 t/h, and 10 t/h, making it suitable for treating process wastewater in specific sectors such as antibiotics, vitamins, steroids, and contrast agents. It provides a mature, reliable, and compliant reference paradigm for the green upgrading of the pharmaceutical industry.



5t/h three-effect evaporator for pharmaceutical wastewater in a pharmaceutical factory
5t/h three-effect evaporator for pharmaceutical wastewater
5t/h three-effect evaporator for pharmaceutical plant wastewater

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Specifications

I. Project Overview 

A pharmaceutical raw material plant produces 800 tons of antiviral drugs annually, discharging 120 m³ of high-COD, high-salt process wastewater daily. This wastewater contains 6-8% NaCl, 0.5% methanol, 1000-3000 mg/L of API intermediates, and 20000-35000 mg/L of COD. The original outsourced disposal cost was 380 RMB/ton, with significant transportation and storage risks. In 2023, the company constructed a new 5t/h triple-effect evaporation and crystallization unit (hereinafter referred to as "this unit"), which solves 90% of the wastewater problem in one go, recovers and reuses the condensate, and outsources the resource utilization of by-product industrial wet salt, reducing the overall disposal cost to 85 RMB/ton.


II. Process Route

2.1 Process Overview

The process consists of five stages: pretreatment → triple-effect countercurrent falling film concentration → forced circulation crystallization → centrifugal separation → mother liquor drying. The entire system is constructed of 316L/2205 duplex stainless steel, with a material contact surface Ra≤0.6μm, meeting GMP requirements for easy cleaning.

·  Pretreatment: Wastewater is filtered through a 100μm basket filter → low-temperature vacuum degassing (45℃, -0.085MPa) to recover 95% of methanol → ozone catalytic oxidation, reducing COD to 12000mg/L.

·  First-Effect Falling Film: Live steam at 0.6MPa (158℃) enters the shell side of the first-effect process; wastewater is preheated to 45℃ before entering the tube side, concentrating by 1.5 times; secondary steam at 120℃ serves as the heat source for the second-effect process.

·  Countercurrent operation of Effect II/III: Effect II boiling point 95℃, Effect III 72℃, maintained at -0.075MPa using a vacuum pump; overall specific heat transfer coefficient 1800W/(m²·K), evaporation rate 12kg/(m²·h).

·  Crystallization separation: Effect III discharge concentration 28% (near saturation), pumped into an OSLO type forced circulation crystallizer, operating temperature 82℃, slurry density 20%, centrifuged to obtain wet salt with water content ≤3% and whiteness 80%.

·  Mother liquor drying: Centrifuged mother liquor COD 100000mg/L, dried by a paddle dryer to obtain 0.6t/d of mixed salt with water content 5%, sent for hazardous waste incineration.

2.2 Equipment Configuration

·  Evaporation Capacity: 5t/h (8% salinity in influent)

·  Heat Exchange Area: Effect I 180m², Effect II 160m², Effect III 140m²

·  Steam Consumption: 0.32kg steam/kg water (triple-effect + autoclave pump)

·  Cooling Water Circulation: 60m³/h (28℃→35℃)

·  Vacuum System: Water ring + Roots two-stage, ultimate vacuum -0.085MPa

·  Material: Tube side 2205, shell side 316L


III. Key Technological Highlights

3.1 Thermal Steam Recompression (TVR)

The secondary steam from the first-effect stage, initially at 120℃, is pressurized to 135℃ by a 0.8MPa power steam jet pump before returning to the first-effect shell side, resulting in 18% steam savings and reducing overall steam consumption to 0.32kg/kg water.

3.2 Scale Prevention and CIP

Online CIP uses alternating cleaning with 2% NaOH + 1% HNO₃ at 80℃, with a cycle of 10 days and a cleaning time of 4 hours.

3.3 Salt Quality Control

Through OSLO grading and rinsing, the crystal size D50 is 0.7mm; after centrifugation, rinsing with 2℃ cold deionized water for 5 seconds yields NaCl purity of 97%.

3.4 Deep Condensate Treatment

Secondary condensate with COD 300~500mg/L and methanol ≤5mg/L undergoes catalytic ozone + biological filter treatment, resulting in effluent COD ≤30mg/L, which is then reused in the circulating cooling water system with a reuse rate of 95%.


IV. Operational Results 

The unit successfully started up on the first attempt in November 2023. 72-hour performance evaluation data:

·  Evaporation rate: 5.2 t/h (design 5 t/h)

·  Steam consumption: 0.31 kg/kg water

·  Salt production: 0.42 t/h

·  Condensate recovery rate: 95%

·  Unit availability: >98% (4320 hours of operation over 6 months)


V. Economic and Environmental Benefits

5.1 Economic Indicators

Annual operating cost: approximately RMB 1.28 million (steam RMB 180/t, electricity RMB 0.65/kWh, labor + chemicals). Annual savings in outsourced disposal costs: approximately RMB 12.6 million. After deducting operating costs, the annual net profit is approximately RMB 11.32 million.

5.2 Environmental Indicators

Annual reduction of 36,000 tons of high-salinity wastewater discharge and 1,080 tons of COD emission reduction; 95% methanol recovery and 55 tons of VOCs reduction; 2,800 tons of CO₂ emission reduction per year; and 180 tons of hazardous waste salts are incinerated in compliance with regulations, achieving "reduction and resource utilization".



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