Chemical & Agrochemical

Evaporation, concentration and crystallization systems for chemical and agrochemical producers — covering flat-solubility inorganic salts (NaCl, (NH₄)₂SO₄, Na₂SO₄), temperature-sensitive organic acids, and high-COD pesticide / dye mother liquors with TDS from 2% to over 20%.

industries chemical
Process Challenges

Common Process Challenges in Chemical & Agrochemical

Feed composition swings by an order of magnitude across product changeovers; chloride from 0 to 30,000 mg/L, COD from <100 to >50,000 mg/L, and pH from strongly acidic to strongly alkaline — all on the same multi-purpose plant. Equipment must be specified against the worst credible envelope, not the nominal stream.

CHALLENGE 01High COD

High-COD Pesticide & Pharma Intermediate Wastewater

COD typically 10,000–80,000 mg/L with refractory organics (heterocyclics, surfactants, residual solvent). Biological treatment fails above ~3% TDS; direct crystallization yields organic-contaminated salt. Wet-air oxidation or Fenton upstream is usually required before thermal concentration.

COD 10,000–80,000 mg/Ltypical pesticide & pharma intermediate wastewater — biological treatment fails above ~3% TDS
CHALLENGE 02Mixed Salts

Mixed-Salt Systems (NaCl + Na₂SO₄ + Ammonium Salts)

At the NaCl–Na₂SO₄ eutectic (~17.5% Na₂SO₄ at 100°C) achievable salt purity caps near 92–95% regardless of crystallizer type. Selective separation into two sellable fractions requires the NaCl/Na₂SO₄ ratio to sit clearly outside the eutectic band — otherwise a hazardous mixed-salt waste is the only outcome.

92–95%achievable salt purity cap at the NaCl–Na₂SO₄ eutectic (~17.5% Na₂SO₄ at 100°C), regardless of crystallizer type
CHALLENGE 03Corrosion

Corrosive Streams (Chloride / Sulfate / Alkaline)

Above ~200 mg/L Cl⁻ at evaporation temperature, 316L fails by pitting within months. Duplex 2205 covers Cl⁻ to ~1,000 mg/L; above 5,000 mg/L or in acidic service, titanium Grade 2 or Hastelloy C-276 is mandatory. Concentrated NaOH (>30%) above 80°C requires Nickel 200 or Ni-clad construction. Mis-selection surfaces as a through-wall leak within 6–18 months.

6–18 monthstypical time for a mis-selected material to surface as a through-wall leak in corrosive service
CHALLENGE 04Variable Feed

Variable Feed Composition Across Product Changeovers

Campaign-mode chemical production swings TDS (2–25%), COD (<100 to >30,000 mg/L), pH (2–13) and trace metals (Fe, Cu, Ni) within one shift. Heat-transfer coefficients, scaling induction time and crystal PSD all shift with the campaign. Systems are designed around the worst credible envelope, not the average stream.

TDS 2–25%campaign-mode swing within one shift — systems are designed around the worst credible envelope, not the average stream
Typical Process Route

Typical Chemical & Agrochemical ZLD + Salt Separation Route

Indicative process flow for high-salinity chemical wastewater with mixed NaCl / Na₂SO₄ chemistry and residual COD load.

Simplified PFD — Chemical & Agrochemical ZLD
Chemical Wastewater → Pre-treatment → Membrane Concentration → MVR / Multi-Effect Evaporator → FC Crystallizer → Centrifuge → Salt + Condensate Reuse
1

Pre-treatment

COD and hardness removal — wet-air oxidation or Fenton upstream for refractory organics, softening for scaling ions (Ca²⁺, Mg²⁺).

2

Pre-concentration

Membrane or softening pre-concentration delivering a 1–8% TDS lift before thermal concentration.

3

Evaporative Concentration

MVR (15–25 kWh per tonne water) or multi-effect (0.25–0.40 t steam per tonne water) evaporation approaching saturation.

4

FC Crystallization

Forced-circulation crystallization at tube velocity 2–3 m/s, heat exchanger ΔT ≤10°C to suppress wall scaling.

5

Centrifuge & Salt Separation

Centrifuge / pusher separates the crystal magma into salt cake and centrate.

6

Salt + Condensate Reuse

Salt (NaCl / Na₂SO₄) routed to reuse or disposal; condensate recovered.

Simplified PFD for indicative routing only. Actual configuration depends on TDS profile, COD load, anion/cation balance, scaling tendency and site utilities. Mixed-salt separation feasibility requires laboratory solubility and impurity profiling.

Stream Reference

Typical Chemicals & Stream Types

Common feed streams encountered in chemical and agrochemical plants, with the technology route typically considered for first-pass screening.

Chemical / StreamSource / ContextKey BehaviorTypical RouteMaterial Focus
Ammonium sulfate (NH₄)₂SO₄Caprolactam by-product, coke-oven gas, rare earth precipitationSolubility ~70 g/100 mL at 20°C, flat curve → evaporative; crystal target 1–3 mm (fertilizer grade)DTB / FC316L
Adipic acidDicarboxylic acid production (KA oil oxidation)Solubility rises ~10× from 20°C to 70°C; cooling-driven yield >80%Cooling Crystallization316L
Sodium chloride NaClChlor-alkali, ion-exchange resin regenerationSolubility ~26 g/100 mL flat with temperature; scaling-prone as Ca / Mg co-crystallizeFCTitanium (TA2)
Sodium sulfate Na₂SO₄Viscose, lithium battery by-productMirabilite / thenardite transition at 32.4°C complicates operationDTB / FCDuplex 2205
Pesticide mother liquorDichlorvos, glyphosate, atrazine synthesisCOD 20,000–80,000 mg/L; NaCl 5–15%; refractory heterocyclicsFC + Pre-treatmentTitanium / Duplex
Dye & pigment wastewaterReactive / disperse / vat dye productionCOD 5,000–30,000 mg/L; color >1,000 Pt-Co; mixed NaCl + Na₂SO₄FC + AOP + ZLDTitanium / Duplex

Routes shown are for preliminary screening only. Final selection requires solubility data, impurity profiling, crystallization trials and project-specific engineering evaluation.

FAQ

Frequently Asked Questions

Selection questions engineers ask before specifying a chemical or agrochemical system.

How do I identify my wastewater composition before specifying a system?+

Begin with a full characterization: TDS, COD, anion/cation balance (Cl⁻, SO₄²⁻, Na⁺, NH₄⁺), trace heavy metals, pH, viscosity and scaling ions (Ca²⁺, Mg²⁺, SiO₂). TDS above ~5–8% typically indicates the membrane ceiling and the start of evaporative concentration; a COD/TDS ratio above ~0.3 signals pesticide or organic load requiring AOP pre-treatment; mixed-salt separation feasibility requires a NaCl–Na₂SO₄–H₂O phase-equilibrium study at the project’s actual brine composition. Skipping characterization is the single largest cause of failed ZLD projects.

Can mixed NaCl + Na₂SO₄ salts be separated into sellable products?+

Sometimes — it depends on the eutectic composition, COD content of the brine and target product purity. Selective crystallization can produce reusable-grade NaCl in favorable cases; Na₂SO₄ recovery is more sensitive to organics. Laboratory phase-equilibrium testing is required before any recovery claim.

Why does adipic acid use cooling crystallization instead of evaporation?+

Adipic acid solubility rises steeply with temperature, so cooling yields high crystal productivity without thermal degradation. Evaporative routes risk color formation and decomposition. This is a classic solubility-curve-driven technology choice.

How do you handle foaming and scaling in high-COD pesticide brines?+

Forced-circulation evaporators with tube velocity 2–3 m/s suppress wall scaling; heat exchanger ΔT is held ≤10°C to avoid skin-crystallization. Foaming is managed by oversized vapor-liquid separators (residence time ≥6 s), anti-foam dosing at 5–30 mg/L, and advanced oxidation pre-treatment to break surfactants. Each pesticide stream (dichlorvos vs. glyphosate vs. atrazine) requires its own pre-treatment trial — generic recipes fail because the refractory organics differ.

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