5-Step Jar Test SOP to Optimize FeCl3 & PAC Coagulant Dosage | Lộc Thiên

Tóm tắt nội dung
  1. 1. The Role of Jar Test SOP in ETP Operation
  2. 2. Technical Specifications Table for Standard Coagulants Used in Jar Test
  3. 3. Standard 5-Step Jar Test SOP for the Lab
  4. 4. How to Convert Lab Results to Actual Metering Pump Settings
  5. 5. FAQ - Frequently Asked Questions about the Jar Test SOP

The 5-step Jar Test SOP is a standardized laboratory procedure that helps ETP operators precisely determine the optimal coagulant dosage (FeCl3 45%, formula FeCl3, MW 162.20 g/mol, CAS 7705-08-0 or PAC 30%, formula [Al2(OH)nCl6-n]m, CAS 1327-41-9) and polymer flocculant for each batch of industrial wastewater. Applying the standard Jar Test SOP helps treatment plants reduce chemical costs by 20–35%, minimize sludge generation, and ensure effluent quality consistently meets QCVN 40:2011/BTNMT standards.

  • Standardized 5-step SOP: Sample & Stock Solution Preparation → Dosage & Paddle Setup → Rapid Mixing → Slow Mixing → Settling & Measurement.
  • Precise determination of optimal pH range: FeCl3 performs best at pH 5.0–8.5, while PAC operates optimally at pH 6.0–8.0.
  • Cost-effective ETP operation solution that thoroughly resolves issues of floc breakage or sludge floating in settling tanks.

1. The Role of Jar Test SOP in ETP Operation

In industrial wastewater treatment plant operation, dosing chemicals based on intuition or maintaining old dosage records when wastewater characteristics change (turbidity, COD, pH, flow rate) is the leading cause of budget waste and non-compliant effluent. The Jar Test (a coagulation-flocculation simulation using a multi-position stirrer) is an essential technical "compass."

Implementing the Jar Test SOP helps:

Optimize Chemical Costs (Cost-in-Use)
Identify the coagulation saturation point, avoiding overdosing that causes restabilization and re-turbidity of the water.
Reduce Sludge Volume
Optimal dosing creates dense, compact flocs, reducing sludge moisture content and the cost of hiring hazardous sludge treatment services.
Protect Process Equipment
Prevent pipeline corrosion or metering pump clogging caused by excess chemical scaling.

2. Technical Specifications Table for Standard Coagulants Used in Jar Test

Below are the standard technical specifications for the primary coagulants directly supplied by Lộc Thiên for Jar Test experiments:

Technical Parameter FeCl3 45% (Ferric Chloride) PAC 30% (Poly Aluminium Chloride) NaOH 50% (Caustic Soda for pH Adjustment)
Chemical Formula FeCl3 [Al2(OH)nCl6-n]m NaOH
Molecular Weight (MW) 162.20 g/mol Variable Polymer 39.997 g/mol
CAS Number 7705-08-0 1327-41-9 1310-73-2
Physical State & Color Reddish-brown, viscous liquid Fine, lemon-yellow/white powder Clear, viscous liquid
Optimal Working pH Range 5.0 – 8.5 6.0 – 8.0 Increases pH (Alkalization)
Lab Stock Solution Concentration 1.0% w/v (10 g/L) 1.0% w/v (10 g/L) 0.1M or 1.0% w/v

3. Standard 5-Step Jar Test SOP for the Lab

  1. Step 1: Prepare Wastewater Sample & Stock Solutions

    Collect a representative sample (approx. 10–20 liters) from the equalization tank inlet or reaction tank. Measure initial parameters: pH, turbidity (NTU), COD, TSS, temperature. Prepare a 1.0% stock solution of the coagulant (10g of pure chemical dissolved in 1000ml of distilled water). At this concentration, 1ml of stock solution added to a 1000ml sample corresponds to a dosage of 10 mg/L (ppm).

  2. Step 2: Distribute Samples into Jar Test Beakers & Set Dosage Range

    Accurately pour 1000ml of wastewater into each of the 6 glass beakers on the Jar Test apparatus. Set the expected dosage range based on wastewater characteristics (e.g., Beaker 1 = 50 ppm, Beaker 2 = 100 ppm, Beaker 3 = 150 ppm, Beaker 4 = 200 ppm, Beaker 5 = 250 ppm, Beaker 6 = 300 ppm). If the sample pH is outside the working range, adjust it using NaOH 50% or Acid to the optimal range beforehand.

  3. Step 3: Rapid Mixing Phase (Coagulation)

    Lower the paddles into the center of the beakers. Set the rapid mixing speed to 150 – 200 rpm (equivalent to G = 300 s⁻¹). Using a pipette, simultaneously add the calculated volume of coagulant stock solution (FeCl3 45% or PAC 30%) to all 6 beakers. Maintain rapid mixing for 60 – 90 seconds to ensure uniform chemical dispersion and neutralization of colloidal particle surface charges.

  4. Step 4: Slow Mixing Phase (Flocculation)

    Reduce the mixing speed to 30 – 40 rpm (G = 40 s⁻¹) for a duration of 15 – 20 minutes. If needed, add 1–2 ppm of polymer flocculant (Anionic or Cationic) during the 2nd minute of slow mixing. Observe the formation and growth of flocs (micro-floc size, agglomeration rate).

  5. Step 5: Settling Phase & Result Evaluation

    Raise the paddles and allow the beakers to settle undisturbed for 30 minutes. Observe the settling rate (cm/min), the color and clarity of the supernatant, and the volume of accumulated sludge at the bottom. Using a siphon, collect supernatant water from a depth of 2cm below the surface to re-measure: Turbidity (NTU), pH, residual COD, TSS.

4. How to Convert Lab Results to Actual Metering Pump Settings

Formula for converting the optimal lab dosage ($C_{lab}$ mg/L) to the actual chemical pump flow rate ($Q_{chemical}$ Liters/hour) for the ETP plant:

$$Q_{chemical} (L/h) = \frac{Q_{water} (m^3/h) \times C_{lab} (g/m^3)}{C_{stock} (\%) \times 10 \times \rho (kg/L)}$$

Practical Example: Wastewater flow rate $Q_{water} = 50\text{ m}^3\text{/h}$. Optimal Jar Test dosage $C_{lab} = 150\text{ mg/L}$ FeCl3. Using FeCl3 45% solution with specific gravity $\rho = 1.42\text{ kg/L}$.

$$Q_{FeCl3} = \frac{50 \times 150}{45 \times 10 \times 1.42} = \frac{7500}{639} \approx 11.73\text{ Liters/hour}$$

5. FAQ - Frequently Asked Questions about the Jar Test SOP

1. How often should a Jar Test be performed for an ETP plant?

A Jar Test should be performed: (1) Weekly as a routine for stable wastewater sources; (2) Immediately upon any change in the factory's production process; (3) When the wastewater sample shows unusual color or odor; (4) When receiving a new batch of coagulant from the supplier.

2. Why does excessively high FeCl3 dosage cause the wastewater to become turbid and turn dark yellow?

This is the phenomenon of saturation and excess Fe³⁺ ions causing charge reversal (restabilization) of colloidal particles. Simultaneously, residual Fe in the water that cannot precipitate at low pH results in the characteristic turbid yellow color.

3. Should I use PAC or FeCl3 for wastewater with high COD content?

For wastewater with high COD and intense color (e.g., textile dyeing, leachate, food processing), FeCl3 45% provides superior coagulation and color removal due to its ability to form dense, robust iron hydroxide flocs. For water supply or low-COD wastewater, PAC 30% is often more advantageous as it causes less pH depression in the source water.

4. Does Lộc Thiên offer on-site sampling and Jar Test support for factories?

Yes. Lộc Thiên's team of chemical engineers provides free consultation, sampling, and Jar Test services, either at our lab or directly at the customer's ETP plant in the HCMC, Binh Duong, Dong Nai, and Long An areas.

If your wastewater treatment plant is experiencing chemical dosing failures or needs cost optimization, refer to our article: When your chemical dosing system still fails — 8 operational pain points.