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ASTM D4536-96 defines a comprehensive protocol for estimating solid particulate matter concentrations in stationary source stacks using high-volume sampling techniques. The method is carefully bounded by specific velocity ranges and standard conditions to ensure reproducible and legally defensible emission data. It is essential for engineers and environmental compliance officers to understand the method’s specific limitations regarding condensible particulate matter and gas moisture content.
This standard test method is designed for the isokinetic sampling of solid particulate matter from stationary source exhaust streams. It is strictly applicable for stack gas velocities ranging from 4 to 45 meters per second (800 to 8,000 feet per minute), utilizing the specific nozzle geometries cited in the procedure. The standard explicitly states that SI units are to be regarded as the standard for all calculations and reporting.
A critical limitation of this method is that particulate matter present in the gaseous phase at the filtration temperature will not be collected. Therefore, this method may not be suitable for streams with significant quantities of condensible PM. Additionally, if the filter temperature drops below the stream dewpoint, or if moisture is expected to condense between the filter and the metering oriface, the method is not applicable without the addition of a dedicated moisture collection device upstream of the oriface.
Accurately determining emissions relies on strict adherence to standard reference conditions and precise measurement of field variables. The standard defines specific reference conditions for reporting and provides a clear set of symbols for engineering calculations.
| 🟦 Parameter | 📏 Symbol | 📐 Standard Value / Definition |
|---|---|---|
| Standard Pressure | Pstd | 101.32 kPa (29.92 in. Hg) |
| Standard Temperature | Tstd | 298.2 K (537 °R) |
| Molecular Weight of Air | Mo | 29.0 |
| Pitot Tube Factor (Standard-type) | Fp | 1.0 |
| Applicable Stack Velocity | — | 4 to 45 m/s (800 to 8,000 ft/min) |
| Emission Rate | E | kg/h (lb/h) |
| Particulate Concentration | Cg | g/m³ (grains/ft³) |
The proper execution of D4536-96 requires familiarity with several companion standards for velocity measurement, media evaluation, and terminology. The standard specifically references EPA Method 2 for Type S pitot tube velocity determination alongside traditional ASTM methods.
| 🌟 Referenced Standard | 🎯 Purpose in D4536-96 |
|---|---|
| EPA Method 2 (40 CFR 60) | Determination of Stack Gas Velocity and Volumetric Flow Rate (Type S Pitot) |
| ASTM D3154 | Average Velocity in a Duct (Pitot Tube Method) |
| ASTM D1356 | Terminology Relating to Sampling and Analysis of Atmospheres |
| ASTM D2986 | Evaluation of Air Assay Media by the Monodisperse DOP Smoke Test |
| ASTM E1 | Specification for ASTM Thermometers |
The total particulate emission rate (E) depends critically on the stack gas volumetric flow rate (Q), while the concentration (Cg) is calculated from the collected mass and the sampled gas volume corrected to standard conditions. Proper correction for barometric pressure (Pbar) and stack pressure (Pa) is mandatory for accurate results.
This test method is specifically intended to estimate the concentration of solid particulate matter in the exhaust stream of stationary sources. It relies on extracting a representative sample under isokinetic conditions from the stack duct.
The method is strictly validated for stack gas velocities from approximately 4 to 45 m/s (800 to 8,000 ft/min). This velocity range is directly tied to the specified nozzle geometries defined in the standard’s scope.
All emission concentrations and flow rates must be reported on a consistent basis for regulatory compliance. The standard mandates reporting at 101.32 kPa (29.92 in. Hg) and 298.2 K (537 °R) to ensure that results from different testing events are directly comparable.
If significant quantities of PM are in the gaseous phase at the filtration temperature, this test method will not capture them. The standard explicitly warns that this method may not be the method of choice when condensible PM is expected, as only the solid fraction collected on the filter is weighed.