IS 5282 (1969) specifies liquid sedimentation methods for determining the particle size distribution of powders, particularly those passing through a 75-micron IS sieve. It covers both incremental and cumulative sedimentation techniques, including apparatus setup, sample preparation, calibration, and calculation procedures. This standard is essential for engineers and scientists involved in powder characterization to accurately measure particle sizes within defined upper and lower limits based on material density and sedimentation principles.
Overview
IS 5282 (1969) specifies liquid sedimentation methods for determining the particle size distribution of powders, particularly those passing through a 75-micron IS sieve. It covers both incremental and cumulative sedimentation techniques, including apparatus setup, sample preparation, calibration, and calculation procedures. This standard is essential for engineers and scientists involved in powder characterization to accurately measure particle sizes within defined upper and lower limits based on material density and sedimentation principles.
Audience
Contents
Structure
Scope of IS 5282: Particle Size and Dispersion of Powders
| Material | Density (g/cc) | Upper Limit (microns) | Lower Limit (microns) |
|---|---|---|---|
| A | 2 | 72 | 3.0 |
| B | 4 | 50 | 2.1 |
| C | 8 | 37 | 1.6 |
| Convert From | Convert To | Multiply By |
|---|---|---|
| Sieve | Projected | 1.40 |
| Sieve | Stokes | 0.94 |
| Projected | Sieve | 0.71 |
| Projected | Stokes | 0.67 |
| Stokes | Sieve | 1.07 |
| Stokes | Projected | 1.50 |
flowchart LR
A[Material Density] --> B[Particle Size Limits]
B --> C[Upper & Lower Limits]
A --> D[Select Dispersing Agent]
E[Particle Diameter Types] --> F[Conversion Factors]
F --> G[Sieve, Projected, Stokes]
This encapsulates the scope related to particle size, measurement
IS 5282: Terms and Definitions - Key Specifications
Reference Standard
Particle Size Limits (Clause 1.00 & 5.2)
Particle size limits depend on material density (g/cc), fluid viscosity (0.01 poise), fluid density (1.00 g/cc), and Reynolds number (0.2).
| Material | Density (g/cc) | Upper Limit (μm) | Lower Limit (μm) |
|---|---|---|---|
| A | 2 | 72 | 3.0 |
| B | 4 | 50 | 2.1 |
| C | 8 | 37 | 1.6 |
| Material | Liquid & Dispersing Agent(s) |
|---|---|
| Alumina | Water; water (calgon 0.1%); sodium tartrate 0.1%; dilute HCl (pH 3); CCl4 |
| Aluminium powder | Isopropanol; chloroform |
| Carbon black | Water (Aerosol OT 1%); gallotannic acid |
| Calcium carbonate | Water; xylene |
Using Reynolds number (Re = 0.2), fluid viscosity (η), and densities (ρ):
[ d \propto \sqrt{\frac{18 \eta v}{(\rho_s - \rho_f) g}} ]
Where:
flowchart TD
A[Material Density] --> B[Particle Size Limits]
B --> C[Upper Limit]
B --> D[
IS 5282 covers Liquid Sedimentation Methods for particle size determination but does not classify these methods explicitly nor provide detailed formulas or tables for classification.
Liquid sedimentation methods classify based on particle settling behavior under gravity or centrifugation, commonly:
Stokes' Law governs settling velocity ( v ):
[ v = \frac{d^2 (\rho_p - \rho_f) g}{18 \mu} ]
where:
Classification often includes:
| Method | Principle | Application |
|---|---|---|
| Gravity Sedimentation | Settling under gravity | Coarse to medium particles |
| Centrifugal Sedimentation | Settling under centrifugal force | Fine particles, faster results |
| Liquid Column Sedimentation | Sedimentation accumulation | Rarely used, not in IS 5282 |
If you need formulas or procedure details for a specific sedimentation method, please specify!
| Material | Liquid & Dispersing Agent |
|---|---|
| Alumina | Water; water + calgon (0.1%); HCl (pH=3) |
| Alumina dust | Water + sodium oxalate |
| Aluminium powder | Isopropanol; chloroform |
| Barytes | Water + sodium pyrophosphate (0.001-0.005 mol/L) |
| Carbon black | Water + Aerosol OT (1%); gallotannic acid |
(See Appendix B for full list)
[ Re = \frac{u d_p}{\nu} \times 10^{-1} \quad \text{where} \quad u = \frac{h}{t} ]
Re ≤ 0.2 ensures laminar flow and accurate sedimentation.
flowchart LR
A[Powder Sample] --> B[Prepare Suspension (~2% vol)]
B --> C[Add Dispersing Agent]
C --> D[Stir Thoroughly]
D --> E[Observe Settling Behavior]
E -->|Good Dispersion| F[Rigid Sediment, Slow Settling]
E -->|Flocculated| G[Mobile Sediment, Wall Deposit]
Summary:
IS 5282: Preparation of Sample - Key Points
Choose liquid based on material type for dispersion and sedimentation:
| Material | Liquid & Dispersing Agent(s) |
|---|---|
| Alumina | Water; water + Calgon (0.1%); water + sodium tartrate (0.1%) |
| Aluminium powder (sp. gr. 2.5) | Isopropanol; chloroform |
| Barytes | Water + sodium pyrophosphate (0.001–0.005 mol/litre) |
| Carbon black | Water + Aerosol OT (1%); gallotannic acid |
| Calcium carbonate | Water; xylene |
(Refer full Appendix B for detailed list)
flowchart TD
A[Select Material] --> B[Choose Sedimentation Liquid (Appendix B)]
B --> C[Weigh Sample (0.0001 g accuracy)]
C --> D[Prepare 300 ml Suspension]
D --> E[Adjust Concentration ≤ 1% by volume]
E --> F[Ready for Analysis]
This ensures uniform dispersion and accurate particle size analysis per IS 5282.
IS 5282: Apparatus and Calibration Key Points
[ V = \frac{W}{\rho} ]
Where:
| Apparatus | Specification |
|---|---|
| Temperature bath | Transparent, ≥ 15 L capacity |
| Balance | Sensitivity ≤ 0.1 mg |
| Drying oven | Temperature controlled |
| Weighing bottle | Wide mouth, ≥ 20 ml capacity |
flowchart LR
A[Start: Clean apparatus] --> B[Fill sedimentation vessel with water]
B --> C[Draw water into pipette bulb to graduation]
C --> D[Drain water into weighing bottle]
D --> E[Blow remaining water into bottle]
E --> F[Weigh bottle to find water weight]
F --> G[Calculate pipette volume: V = W/ρ]
This ensures precise volume calibration critical for sedimentation tests as per IS 5282.
IS 5282: Incremental Sedimentation Method - Key Points
Corrected weight of particles (Wre):
[ W_{re} = W_r \times \rho_l \times \frac{h_0}{h_0 - h_x} ]
Where:
Example:
[
W_{re} = 0.0037 \times \frac{18}{(18 - 7.13)} = 0.0065 \text{ g}
]
| Parameter | Typical Value/Description |
|---|---|
| Suspension Height ((h_0)) | 18 cm (graduation mark) |
| Sampling Depth ((h_x)) | Predetermined depths < 18 cm |
| Agitation Time | 3 minutes (air bubbling) |
| Sample Volume | Withdrawn by pipette in fractions |
| Corrected Weight (W_{re}) | Calculated by formula above |
flowchart TD
A[Prepare sedimentation vessel] --> B[Pour suspension + rinse beaker]
B --> C[Fill to 18 cm mark]
C --> D{Agitate by air bubbling?}
D -- Yes --> E[Bubble air for 3 min]
D -- No --> F[Start stopwatch immediately]
E --> F
Centrifugal Sedimentation Method (IS 5282)
[ d_e = \frac{18 \eta \ln(R_2/R_1)}{(\rho_p - \rho) \omega^2 t} ]
Where:
flowchart TD
A[Prepare Suspension] --> B[Centrifuge at ω for time t]
B --> C[Separate Sediment & Suspension]
C --> D[Dry & Weigh Both Fractions]
D --> E[Plot % Sedimented vs Particle Size]
E --> F[Draw Tangents for Size Distribution]
This method provides rapid, accurate sizing of fine particles using centrifugal acceleration and sedimentation principles.
No single method covers full size range (1,000 to 1 micron).
Combine methods like sieving, sedimentation, elutriation, microscope for full distribution.
Correlation factors convert particle diameters between methods (Appendix F, Table F-3):
| From \ To | Sieve | Projected | Stokes |
|---|---|---|---|
| Sieve | 1 | 1.40 | 0.94 |
| Projected | 0.71 | 1 | 0.67 |
| Stokes | 1.07 | 1.50 | 1 |
[ W_{rc} = W_r \rho_l (h_o - h_x) ]
flowchart LR
A[Sample with wide size range] --> B[Sieving (large particles)]
A --> C[Sedimentation (medium particles)]
A --> D[Microscope (small particles)]
B --> E[Convert sizes using correlation factors]
C --> E
D --> E
E --> F[Combined particle size distribution]
IS 5282: Upper and Lower Particle Size Limits for Different Densities
[ Re = \frac{u d \rho_f}{\eta} \times 10^{-1} ]
| Material | Density (g/cc) | Upper Limit | Lower Limit |
|---|---|---|---|
| A | 2 | 72 | 3.0 |
| B | 4 | 50 | 2.1 |
| C | 8 | 37 | 1.6 |
graph LR
A[Density 2 g/cc] -->|Upper Limit 72 μm| UL2
A -->|Lower Limit 3 μm| LL2
B[Density 4 g/cc] -->|Upper Limit 50 μm| UL4
B -->|Lower Limit 2.1 μm| LL4
C[Density 8 g/cc] -->|Upper Limit 37 μm| UL8
C -->|Lower Limit 1.6 μm| LL8
For detailed dispersion media and liquid agents, refer to Clause 5.2 Appendix B.
IS 5282: Tests for Dispersion - Key Points & Formulas
At least two tests must be done to confirm dispersion efficiency:
a) Rheological Behaviour:
b) Microscopical Examination:
c) Qualitative Sedimentation:
d) Quantitative Sedimentation:
| Test Type | Key Observation | Good Dispersion Indicator |
|---|---|---|
| Rheological Behaviour | Settling rate, sediment rigidity | Slow settling, rigid sediment, no wall deposit |
| Microscopical | Particle agglomeration | Uniform particle distribution |
| Qualitative Sedimentation | Sediment clarity and volume | Clear liquid layer, minimal sediment volume |
| Quantitative Sedimentation | Sediment volume vs. time | Consistent sediment volume, no increase on dilution |
IS 5282: Worked Example & Key Data on Particle Size Distribution
| Material | Density (g/cc) | Upper Limit (µm) | Lower Limit (µm) |
|---|---|---|---|
| A | 2 | 72 | 3.0 |
| B | 4 | 50 | 2.1 |
| C | 8 | 37 | 1.6 |
[ W_{re} = W_r \times \rho_l \times \frac{(h_0 - h_x)}{(h_0 - h_l)} ]
Where:
flowchart LR
A[Sample] --> B[Sieving (>50 µm)]
A --> C[Sedimentation (1-50 µm)]
A --> D[Microscope (<10 µm)]
B --> E[Size Distribution]
C --> E
D --> E
E --> F[Combined Particle Size Distribution]
Use these guidelines and tables for accurate particle size distribution analysis per IS 5282
IS 5282: Correlation Factors for Different Particle Size Methods
| Convert from → to | Multiply by |
|---|---|
| Sieve → Projected | 1.40 |
| Sieve → Stokes | 0.94 |
| Projected → Sieve | 0.71 |
| Projected → Stokes | 0.67 |
| Stokes → Sieve | 1.07 |
| Stokes → Projected | 1.50 |
graph LR
A[Sieve Diameter] -- x1.40 --> B[Projected Diameter]
A -- x0.94 --> C[Stokes Diameter]
B -- x0.71 --> A
B -- x0.67 --> C
C -- x1.07 --> A
C -- x1.50 --> B
Use these correlation factors to convert particle sizes between methods when direct measurement is unavailable or to combine size distributions from different techniques.
Frequently Asked
Differences between Incremental and Cumulative Sedimentation Methods (IS 5282):
| Aspect | Incremental Sedimentation Method | Cumulative Sedimentation Method |
|---|---|---|
| Measurement | Concentration measured at a specific depth (plane section) in the sedimentation vessel. | Mean concentration measured over the entire depth from surface to a known depth or total sediment depth measured. |
| Sampling | Particles extracted incrementally at fixed depths; weight corresponds to particles smaller than diameter settling at that depth/time. | Measures the total unsettled particles or sediment accumulated up to a certain depth. |
| Output | Direct proportion by weight of particles smaller than a certain size at a specific depth/time. | Cumulative weight or concentration of particles smaller than a certain size over the entire sedimentation column. |
| Method Examples | Pipetting method (withdrawal at fixed depth after time intervals). | Measuring total sediment depth or average concentration over depth. |
| Accuracy Consideration | Requires stable suspension (~1% volume concentration); flocculation affects accuracy. | Less sensitive to local fluctuations but averages over depth. |
[ d = \sqrt{\frac{18 \mu h}{(\rho_p - \rho_f) g t}} ]
Where:
Loading diagram...
This clarifies how incremental focuses on discrete depths, while cumulative integrates over the sediment column.
Calibration of Pipette as per IS 5282
[ V = \frac{W}{\rho} ]
Where:
Loading diagram...
This procedure ensures precise volume measurement critical for sedimentation analysis.
Recommended Dispersing Agents for Stable Powder Suspensions (IS 5282)
For exact dispersing agents, consult Appendix B of IS 5282.
IS 5282 sets particle size limits based on material density and Reynolds number as follows:
Reynolds Number (Re) controls the upper particle size limit, ensuring Re ≤ 0.2 to keep measurement error within 5%.
Re is calculated by:
[
Re = \frac{u d_p}{\nu} \times 10^{-1}
]
where:
Lower particle size limit is set to avoid disturbance by convection and diffusion effects.
Appendix A Table gives limits for different densities (fluid viscosity = 0.01 poise, fluid density = 1 g/cc, Re = 0.2):
| Material Density (g/cc) | Upper Limit (µm) | Lower Limit (µm) |
|---|---|---|
| 2 | 72 | 3.0 |
| 4 | 50 | 2.1 |
| 8 | 37 | 1.6 |
This ensures sedimentation methods accurately measure particle size within these bounds for different materials.
According to IS 5282, Appendix F, Clause 3.1, the correlation factors to convert particle sizes between sedimentation (Stokes diameter) and sieve methods are:
| Conversion | Multiply by |
|---|---|
| Sieve to projected | 1.40 |
| Sieve to Stokes | 0.94 |
| Projected to sieve | 0.71 |
| Projected to Stokes | 0.67 |
| Stokes to sieve | 1.07 |
| Stokes to projected | 1.50 |
Key points:
Example: A 75-micron sieve size corresponds roughly to a 70.5-micron Stokes diameter.
Loading diagram...
This helps convert particle size data reliably between sedimentation and sieve methods.
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