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Liquid sedimentation methods for determination of particle size of powders

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.

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1969Edition
Sieves Sieving and other Sizing MethodsCategory
Alternative search terms: IS 5282 PDF, IS 5282 pdf free download, IS 5282 free download pdf, IS5282 PDF, IS-5282 PDF, IS 5282 1969 PDF, IS 5282:1969 PDF, IS 5282-1969 PDF, IS 5282 (1969) PDF, IS 5282 1969 edition PDF, IS 5282 edition 1969 PDF

What This Standard Covers

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.

Who Uses This Standard

  • Materials Engineers
  • Chemical Engineers
  • Quality Control Analysts
  • Powder Metallurgists
  • Pharmaceutical Scientists
  • Civil Engineers
  • Laboratory Technicians

Key Topics Covered

Incremental and cumulative sedimentation methods
Calibration of pipettes and sedimentation vessels
Sample preparation and dispersion techniques
Determination of particle size distribution
Use of dispersing agents and suspension media
Calculation of sedimentation time and particle size
Limits of particle size measurement based on Reynolds number
Correlation factors between different particle size measurement methods
Quantitative and qualitative sedimentation tests
Temperature control during sedimentation
Centrifugal sedimentation method
Shape factors and particle sphericity considerations

Table of Contents

1Scope

Scope of IS 5282: Particle Size and Dispersion of Powders

Key Specifications:

  • Particle Size Limits (Clause 1.00):
    Particle size limits depend on material density (g/cc). For viscosity = 0.01 poise, fluid density = 1.00 g/cc, Reynolds number = 0.2 (upper limit).
MaterialDensity (g/cc)Upper Limit (microns)Lower Limit (microns)
A2723.0
B4502.1
C8371.6
  • Conversion Factors between Particle Diameter Types (Clause 3.1):
Convert FromConvert ToMultiply By
SieveProjected1.40
SieveStokes0.94
ProjectedSieve0.71
ProjectedStokes0.67
StokesSieve1.07
StokesProjected1.50
  • Liquid and Dispersing Agents for Materials (Clause 5.2, Appendix B):
    Examples:
    • Alumina: Water, water with calgon (0.1%), dilute HCl (pH 3)
    • Aluminium powder (sp.gr. 2.5): Isopropanol, chloroform
    • Calcium carbonate: Water, xylene

Summary:

  • Particle size limits vary with density and fluid properties.
  • Use conversion factors for comparing sieve, projected, and Stokes diameters.
  • Select appropriate dispersing agents per material type for accurate testing.
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

2Terms and Definitions

IS 5282: Terms and Definitions - Key Specifications

  1. Reference Standard

    • Terms and definitions as per IS 4124-1967 apply.
  2. 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).

MaterialDensity (g/cc)Upper Limit (μm)Lower Limit (μm)
A2723.0
B4502.1
C8371.6
  1. Liquid & Dispersing Agents (Appendix B)
    Common agents for powders:
MaterialLiquid & Dispersing Agent(s)
AluminaWater; water (calgon 0.1%); sodium tartrate 0.1%; dilute HCl (pH 3); CCl4
Aluminium powderIsopropanol; chloroform
Carbon blackWater (Aerosol OT 1%); gallotannic acid
Calcium carbonateWater; xylene
  1. Calculation Notes (Clause 7.9)
    • Follow procedure in Clause 6.5 for result calculations.

Key Formula for Particle Size Limits

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:

  • (d) = particle diameter
  • (\eta) = fluid viscosity
  • (\rho_s), (\rho_f) = densities of solid and fluid
  • (g) = acceleration due to gravity
  • (v) = settling velocity (related to Re)

flowchart TD
    A[Material Density] --> B[Particle Size Limits]
    B --> C[Upper Limit]
    B --> D[
3Classification of Liquid Sedimentation Methods

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.

Key points from IS 5282 context:

  • It discusses liquid sedimentation methods broadly.
  • Mentions an additional liquid column method with sedimentation accumulation, but this is not covered in the standard.
  • No specific clause on classification or detailed formulas.

General Engineering Insight on Liquid Sedimentation Methods:

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:

    • ( d ) = particle diameter,
    • ( \rho_p ), ( \rho_f ) = densities of particle and fluid,
    • ( g ) = acceleration due to gravity,
    • ( \mu ) = fluid viscosity.
  • Classification often includes:

    • Gravity sedimentation
    • Centrifugal sedimentation
    • Liquid column sedimentation (less common)

Summary Table of Methods

MethodPrincipleApplication
Gravity SedimentationSettling under gravityCoarse to medium particles
Centrifugal SedimentationSettling under centrifugal forceFine particles, faster results
Liquid Column SedimentationSedimentation accumulationRarely used, not in IS 5282

If you need formulas or procedure details for a specific sedimentation method, please specify!

4Suspension and Dispersion

Suspension and Dispersion (IS 5282 Key Points)

1. Suspension Preparation (Clause 4.1)

  • Prepare suspensions with ~2% volume powder in suitable media.
  • Good dispersions settle slowly, with no sharp interface between clear and turbid layers.
  • Sediment in good dispersion: rigid, minimum volume.
  • Flocculated suspension: large, mobile sediment, visible wall deposits on tilting.

2. Selection of Suspending Medium (Clause 4.1, Appendix B)

  • Reynolds number (Re) ≤ 0.2 to limit error within 5%.
  • Use dispersing agents to avoid flocculation (trial and error).
  • Examples of media & agents:
MaterialLiquid & Dispersing Agent
AluminaWater; water + calgon (0.1%); HCl (pH=3)
Alumina dustWater + sodium oxalate
Aluminium powderIsopropanol; chloroform
BarytesWater + sodium pyrophosphate (0.001-0.005 mol/L)
Carbon blackWater + Aerosol OT (1%); gallotannic acid

(See Appendix B for full list)

3. Reynolds Number Formula (Clause 3.3.1)

[ Re = \frac{u d_p}{\nu} \times 10^{-1} \quad \text{where} \quad u = \frac{h}{t} ]

  • (u): settling velocity (height/time)
  • (d_p): particle diameter
  • (\nu): kinematic viscosity of fluid

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:

  • Use suitable liquid + dispersing agent (Appendix B).
  • Ensure
5Preparation of Sample

IS 5282: Preparation of Sample - Key Points

1. Sample Concentration

  • Use ≤ 1% by volume concentration of powder in suspension (Clauses 7.5, 8.4).

2. Sample Weight and Volume

  • Weigh sample accurately to 0.0001 g.
  • Prepare 300 ml suspension volume in chosen sedimentation liquid (Clause 8.4).

3. Sedimentation Liquid Selection (Appendix B)

Choose liquid based on material type for dispersion and sedimentation:

MaterialLiquid & Dispersing Agent(s)
AluminaWater; water + Calgon (0.1%); water + sodium tartrate (0.1%)
Aluminium powder (sp. gr. 2.5)Isopropanol; chloroform
BarytesWater + sodium pyrophosphate (0.001–0.005 mol/litre)
Carbon blackWater + Aerosol OT (1%); gallotannic acid
Calcium carbonateWater; xylene

(Refer full Appendix B for detailed list)

4. Procedure Summary

  • Select sedimentation liquid per material.
  • Accurately weigh sample.
  • Mix to prepare 300 ml suspension.
  • Ensure concentration ≤1% by volume.

Diagram: Sample Preparation Flow

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.

6Apparatus and Calibration

IS 5282: Apparatus and Calibration Key Points

Apparatus (Clauses 6.2, 6.2.3, 7.2)

  • Sedimentation Vessel (Figs. 1 & 2): Main apparatus for sedimentation test.
  • Ancillary Apparatus:
    • Transparent constant temperature bath (≥15 L), immersing sedimentation vessel up to graduation mark.
    • Balance with sensitivity ≤ 0.1 mg.
    • Drying oven with controlled temperature to evaporate suspending liquid without altering material.
    • Wide-mouthed weighing bottle (≥ 20 ml capacity).

Calibration of Pipette (Clause 6.3.1)

  1. Clean and dry the sedimentation vessel and pipette.
  2. Fill sedimentation vessel with water (~20 cm level).
  3. Draw water into pipette bulb to graduation mark using rubber tube.
  4. Drain water into pre-weighed weighing bottle by opening tap.
  5. Blow remaining water from bulb and discharge tube into bottle.
  6. Calculate volume ( V ) of pipette from weight of water collected:

[ V = \frac{W}{\rho} ]

Where:

  • ( W ) = weight of water (g)
  • ( \rho ) = density of water at test temperature (g/ml)

Summary Table: Ancillary Apparatus

ApparatusSpecification
Temperature bathTransparent, ≥ 15 L capacity
BalanceSensitivity ≤ 0.1 mg
Drying ovenTemperature controlled
Weighing bottleWide 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.

7Procedure for Incremental Sedimentation Method

IS 5282: Incremental Sedimentation Method - Key Points

Procedure Summary (Clause 7.7)

  • Clean sedimentation vessel; close outlet with pinch cock.
  • Pour suspension into vessel; rinse beaker with sedimentation liquid to transfer all particles.
  • Fill up to 18 cm mark with sedimentation liquid.
  • Optional: Use pressure pump to bubble air for 3 minutes agitation.
  • Stop air; start stopwatch.
  • Withdraw samples at predetermined depths using pipette.
  • Determine particle size distribution based on sedimentation velocity.

Key Formula (Clause 1.946)

Corrected weight of particles (Wre):

[ W_{re} = W_r \times \rho_l \times \frac{h_0}{h_0 - h_x} ]

Where:

  • (W_r) = observed weight of particles
  • (\rho_l) = density of liquid
  • (h_0) = initial suspension height (e.g., 18 cm)
  • (h_x) = sampling depth from free surface

Example:
[ W_{re} = 0.0037 \times \frac{18}{(18 - 7.13)} = 0.0065 \text{ g} ]

Notes

  • Incremental method measures concentration at a specific depth.
  • Particle size corresponds to settling velocity at sampling time.
  • Clay content and particle size distribution can be correlated with observed weights.

Summary Table: Parameters for Sampling

ParameterTypical Value/Description
Suspension Height ((h_0))18 cm (graduation mark)
Sampling Depth ((h_x))Predetermined depths < 18 cm
Agitation Time3 minutes (air bubbling)
Sample VolumeWithdrawn 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
8Centrifugal Sedimentation Method

Centrifugal Sedimentation Method (IS 5282)

Principle (Clause 8.1)

  • Used for particles < 2 microns; gravity sedimentation is slow and affected by convection/diffusion.
  • Centrifugal acceleration increases settling velocity.
  • Modified Stokes' equation under centrifugal force:

[ d_e = \frac{18 \eta \ln(R_2/R_1)}{(\rho_p - \rho) \omega^2 t} ]

Where:

  • (d_e) = equivalent particle diameter (microns)
  • (\eta) = viscosity of fluid
  • (\rho_p, \rho) = densities of particle and fluid
  • (\omega) = angular velocity (rad/s)
  • (R_1, R_2) = radial distances from axis of rotation
  • (t) = centrifugation time

Procedure

  • Centrifuge suspension for time (t) at angular velocity (\omega).
  • Separate sediment and suspension; dry and weigh both.
  • Plot % sedimented vs. particle size.
  • Draw tangents on curve to get size distribution.

Sedimentation Vessel (Clause 7.2.1)

  • Diameter: ~4.8 cm
  • Length: ~28 cm with graduated scale 0–18 cm (zero at sampling level)
  • Outlet at bottom for draining/air vent
  • Ground glass stopper with air vent at top

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.

9Comparison with Other Particle Size Methods

IS 5282: Comparison with Other Particle Size Methods

Key Points from Clause 9.1 & Appendix F

  • 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 \ ToSieveProjectedStokes
Sieve11.400.94
Projected0.7110.67
Stokes1.071.501
  • Interpretation:
    A particle just passing a 75 µm sieve corresponds to:
    • 106 µm projected diameter (microscope)
    • 70.5 µm Stokes diameter (sedimentation)

Important Formula (Sedimentation Weight Correction)

[ W_{rc} = W_r \rho_l (h_o - h_x) ]

  • (W_r) = observed weight
  • (\rho_l) = liquid density
  • (h_o) = initial column height (18 cm)
  • (h_x) = depth at which particles settle

Tangential Intercept Method (Sedimentation Curve)

  • Plot % sedimented material vs. (1/d^2) (where (d) = particle diameter)
  • Tangents to curve intercept vertical axis → % undersize for corresponding diameter

Summary

  • Use combined methods for wide size ranges.
  • Convert sizes using correlation factors from Table F-3.
  • Apply sedimentation corrections and tangential intercept for accurate size distribution.
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]
Appendix AUpper and Lower Limits of Particle Sizes for Different Densities

IS 5282: Upper and Lower Particle Size Limits for Different Densities

Key Points from Clause 1.00 & Appendix A (Clause 3.3.1)

  • Viscosity (η) = 0.01 poise
  • Fluid density (ρ_f) = 1.00 g/cc
  • Reynolds Number (Re) upper limit = 0.2 (to limit error ≤ 5%)
  • Free-fall velocity ( v = \frac{h}{t} )

Reynolds Number Formula:

[ Re = \frac{u d \rho_f}{\eta} \times 10^{-1} ]

  • ( u ) = velocity of particle
  • ( d ) = particle diameter (microns)
  • ( \rho_f ) = fluid density
  • ( \eta ) = fluid viscosity

Particle Size Limits Table (Diameter in microns)

MaterialDensity (g/cc)Upper LimitLower Limit
A2723.0
B4502.1
C8371.6
  • Lower limit scales with density similarly to upper limit.
  • For density 2 g/cc, lower limit = 3.0 microns.

Notes:

  • Lower limit: particle size unaffected by convection or diffusion.
  • Upper limit: size at which Re ≤ 0.2.
  • Particle size measurement may require multiple methods (Clause 9.1).

Summary Diagram: Particle Size Limits vs Density

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.

Appendix CTests for Dispersion

IS 5282: Tests for Dispersion - Key Points & Formulas


1. Quantitative Test for Dispersion (Clause 5.1)

  • Principle: Reducing powder concentration by half should not significantly increase the proportion of undersize particles.
  • Initial concentration limit:2% by volume.

2. Test Methods (Appendix C, Clause 4.1)

At least two tests must be done to confirm dispersion efficiency:

  • a) Rheological Behaviour:

    • Prepare ~2% volume suspension.
    • Good dispersion → slower settling, no sharp interface, rigid sediment.
    • Flocculated suspension → rapid settling, large sediment volume, sediment moves on tilting.
  • b) Microscopical Examination:

    • Visual check for agglomerates or uniform particle distribution.
  • c) Qualitative Sedimentation:

    • Observation of settling behavior and sediment appearance.
  • d) Quantitative Sedimentation:

    • Measure sediment volume or height over time for dispersion quality.

3. Particle Size Distribution Test (Appendix D, Clause 7.12)

  • Liquid: Water (450 ml)
  • Dispersing agent: Sodium tartrate (0.1%)
  • Powder weight: 0.9 g
  • Pipette volume: 10 ml

4. Dispersing Agents (Clause 1.0)

  • Sodium hexametaphosphate: 0.5 - 1.0 g/L
  • Sodium pyrophosphate: 0.005 mol/L
  • Water + alcohol (1:1)
  • Methyl alcohol + HCl (N/100)

Summary Table: Dispersion Test Criteria

Test TypeKey ObservationGood Dispersion Indicator
Rheological BehaviourSettling rate, sediment rigiditySlow settling, rigid sediment, no wall deposit
MicroscopicalParticle agglomerationUniform particle distribution
Qualitative SedimentationSediment clarity and volumeClear liquid layer, minimal sediment volume
Quantitative SedimentationSediment volume vs. timeConsistent sediment volume, no increase on dilution

Appendix DWorked Example of Particle Size Distribution

IS 5282: Worked Example & Key Data on Particle Size Distribution


1. Particle Size Distribution (Clause 8.3 & Appendix E)

  • Use combined methods (sieving, sedimentation, elutriation, microscope) to cover full size range (1000 µm to 1 µm).
  • Determine smallest particle size by pipette or sedimentation methods.
  • Example in Appendix E illustrates stepwise calculation of weight fractions and particle sizes.

2. Correlation Between Methods (Clause 9.1 & Appendix F)

  • Different methods yield different particle diameters.
  • Use correlation factors (Appendix F) to convert sizes between methods for consistency.

3. Particle Size Limits for Different Densities (Appendix A & Table)

MaterialDensity (g/cc)Upper Limit (µm)Lower Limit (µm)
A2723.0
B4502.1
C8371.6
  • Calculations assume fluid viscosity = 0.01 poise, density = 1 g/cc, Reynolds number = 0.2.

4. Key Formula for Corrected Weight (Clause 1.946)

[ W_{re} = W_r \times \rho_l \times \frac{(h_0 - h_x)}{(h_0 - h_l)} ]

Where:

  • (W_r) = observed weight
  • (\rho_l) = density of liquid
  • (h_0, h_x, h_l) = depths in sedimentation column

Summary Diagram: Particle Size Determination Methods & Range

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

Appendix FCorrelation Factors for Different Methods

IS 5282: Correlation Factors for Different Particle Size Methods

Key Correlation Factors (Clause 3.1, Table F-3)

Convert from → toMultiply by
Sieve → Projected1.40
Sieve → Stokes0.94
Projected → Sieve0.71
Projected → Stokes0.67
Stokes → Sieve1.07
Stokes → Projected1.50
  • These factors convert particle diameters between:
    • Sieve diameter: Nominal aperture size.
    • Projected diameter: Diameter of circle equal to particle's projected area.
    • Stokes diameter: Diameter of sphere with same settling velocity.

Important Notes (Clause 3.2)

  • Use factors cautiously if particles have extreme shapes (e.g., acicular or with cleavage planes).
  • Prefer to establish specific correlation factors for your powder by:
    • Overlapping size classes measured by both methods.
    • Testing a similar sample by both methods.

Practical Example

  • Particles passing a 75 μm sieve correspond approximately to:
    • 106 μm projected diameter
    • 70.5 μm Stokes diameter

Summary Diagram

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.

Popular Questions About IS 5282

?What are the main differences between incremental and cumulative sedimentation methods in IS 5282?

Differences between Incremental and Cumulative Sedimentation Methods (IS 5282):

AspectIncremental Sedimentation MethodCumulative Sedimentation Method
MeasurementConcentration 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.
SamplingParticles 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.
OutputDirect 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 ExamplesPipetting method (withdrawal at fixed depth after time intervals).Measuring total sediment depth or average concentration over depth.
Accuracy ConsiderationRequires stable suspension (~1% volume concentration); flocculation affects accuracy.Less sensitive to local fluctuations but averages over depth.

Key Formula (Stokes' Law for particle diameter (d)):

[ d = \sqrt{\frac{18 \mu h}{(\rho_p - \rho_f) g t}} ]

Where:

  • ( \mu ) = fluid viscosity
  • ( h ) = depth of sampling
  • ( \rho_p, \rho_f ) = particle and fluid densities
  • ( g ) = acceleration due to gravity
  • ( t ) = time elapsed

Loading diagram...

This clarifies how incremental focuses on discrete depths, while cumulative integrates over the sediment column.

?How is the pipette calibrated for accurate volume measurement in the sedimentation process?

Calibration of Pipette as per IS 5282

  • Preparation: Clean and dry the sedimentation tube and pipette thoroughly.
  • Filling: Fill the sedimentation vessel with distilled water (~20 cm level).
  • Sampling: Open the stop cock to the sampling position; water is drawn into the pipette until it just overflows or reaches the 10 ml mark.
  • Discharge: Turn the stop cock to the discharge position; collect water in a tared weighing bottle.
  • Blowing Residual Water: Apply pressure via a rubber tube to ensure all water drains from the bulb and discharge tube into the bottle.
  • Volume Calculation: Calculate the pipette volume ( V ) using:

[ V = \frac{W}{\rho} ]

Where:

  • ( W ) = weight of water collected (g)
  • ( \rho ) = density of water at the test temperature (g/ml)

Key Points:

  • Pipette capacity is nominally 10 ml.
  • Bore diameters: sample withdrawal tube ~2 mm, pipette stem ~1 mm.
  • Allow ~20 seconds to fill pipette fully.
  • Calibration ensures accurate volume for sedimentation testing.
Loading diagram...

This procedure ensures precise volume measurement critical for sedimentation analysis.

?What dispersing agents are recommended for preparing stable suspensions of powders?

Recommended Dispersing Agents for Stable Powder Suspensions (IS 5282)

  • The selection of dispersing agents is empirical, done by trial and error (Clause 4.1).
  • Dispersing agents prevent flocculation and promote stable suspensions.
  • Appendix B of IS 5282 lists suitable liquids and corresponding dispersing agents (refer to the code for specifics).
  • Typical practice:
    • Add a small quantity of dispersing agent to the suspending liquid.
    • Mix thoroughly to form a paste, then a suspension (Clause 5.3).
    • Assess dispersion quality by flow behavior (C-2.1) and sedimentation characteristics (C-4.1).

Qualitative Indicators of Good Dispersion:

  • Flows freely in syrupy threads.
  • Forms a rigid sediment with minimum volume.
  • No visible sediment movement on tube tilting.

Practical Tips:

  • Use dispersing agents compatible with the powder and liquid medium.
  • Stir mechanically or with compressed air; remove entrapped air by reduced pressure.

For exact dispersing agents, consult Appendix B of IS 5282.

?How does IS 5282 address particle size limits based on material density and Reynolds number?

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:

    • ( u = \frac{h}{t} ) (free-fall velocity)
    • ( d_p ) = particle diameter
    • ( \nu ) = kinematic viscosity
  • 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)
2723.0
4502.1
8371.6
  • Lower limits scale proportionally with density.

This ensures sedimentation methods accurately measure particle size within these bounds for different materials.

?What correlation factors are provided to convert particle sizes between sedimentation and sieve methods?

According to IS 5282, Appendix F, Clause 3.1, the correlation factors to convert particle sizes between sedimentation (Stokes diameter) and sieve methods are:

ConversionMultiply by
Sieve to projected1.40
Sieve to Stokes0.94
Projected to sieve0.71
Projected to Stokes0.67
Stokes to sieve1.07
Stokes to projected1.50

Key points:

  • These factors help combine size distributions from different measurement methods.
  • Use with caution for particles with extreme shapes (e.g., acicular or with cleavage planes).
  • Preferably, determine specific correlation factors for the powder by overlapping methods.

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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