Test methods

Composition, Contaminants and Leachability

Separate what is present from what a procedure releases

Elemental composition, chemical identity, trace contamination, and leachable content
answer different questions. Choose the analytical route by the target constituent, sample
matrix, required reporting limit, and preparation or extraction conditions. An instrument
name alone does not define the result.

Magnifying glass examining powder particles to identify observed process symptoms

Definition

How elemental content, chemical identity, and extractable or leachable content differ.

Clipboard checklist representing practical powder field guides

Selection factors

Define the analyte, sample basis, preparation, required sensitivity, quality controls, and decision criteria.

Interconnected powder mechanisms showing relationships between underlying causes

Test methods

Compare eight routes for solid analysis, solution analysis, chemical identification, and controlled extraction.

Powder measurement instrument and data display representing relevant measurements

Process relevance

Connect results with incoming materials, process contamination, formulation, and release assessment.

Core concept

The preparation defines the claim

Composition describes the constituents measured in a sample. A contaminant is a constituent that matters against a defined product, process, or use requirement. Neither a broad elemental scan nor a spectral library match establishes the absence of every unwanted substance.

Solid analysis, acid digestion, solvent extraction, and leaching do not necessarily access the same material fraction. A digestion may leave resistant phases undissolved. A leaching procedure measures release into a chosen liquid under specified conditions. Elemental analysis generally does not identify oxidation state or chemical species, and an oxide-equivalent result does not prove that the named oxide phase is present.

PowderTechnology.info Insight

Define the measurand before commissioning work: the named analyte or species, sample fraction, preparation method, reporting basis, required quantification limit, and decision criterion. Preserve enough representative material for repeats and independent confirmation.

Key takeaway

Specify the constituent and the material fraction

Use XRF or appropriately prepared ICP analysis for elemental content, a suitable combustion method for selected light elements, FTIR for chemical identification, and validated GC-MS or liquid chromatography for target organic compounds. Use batch extraction or column percolation when the decision concerns release under defined liquid-contact conditions. Require representative sampling, matrix-appropriate calibration, preparation controls, and reporting limits that support the decision. Do not equate an acid-extractable result with total content, a non-detect with absence, or a laboratory leachate concentration with unrestricted field release.

What controls it

Six decisions define a defensible chemical test

Agree on the analytical question and acceptance basis before choosing the instrument.

Target constituent

Specify elements, compounds, or chemical species. Total chromium, for example, does not establish the concentration of an individual oxidation state.

Representative sample

Plan increments and subsampling around segregation, rare contaminant particles, and the lot being assessed. A precise small aliquot can still be unrepresentative.

Preparation and recovery

Select direct solid analysis, digestion, solvent extraction, or leaching. Check losses, incomplete recovery, and contamination from tools, reagents, and vessels.

Sensitivity and selectivity

Set the required quantification limit in the original sample after dilution and recovery effects. Confirm that the method distinguishes the target from matrix effects.

Quality controls

Use appropriate blanks, reference materials, calibration checks, replicates, and recovery studies. A solution spike alone does not prove dissolution of native resistant phases.

Reporting and decision

State dry or as-received basis, units, uncertainty, target list, and method deviations. For leaching, include liquid-to-solid ratio, pH, time, and fraction handling.

Selection and interpretation

Compare the same constituent on the same basis

Separate concentration in the original solid, concentration in an extract, and released mass per solid mass. Converting mg/L to mg/kg requires the appropriate volumes, masses, and corrections. For a column, calculate cumulative release from the individual collected fractions rather than multiplying one concentration by the final volume. A result below the quantification limit is not a measured zero.

Engineering question

Primary route

Useful output

Critical boundary

What elements are present in the prepared solid?XRFElemental or oxide-equivalent compositionMatrix and preparation affect accuracy; no phase identification
How much target element is in a digest or extract?ICP-OES or ICP-MSSolution concentration and calculated sample contentRecovery defines whether the result represents total or extracted content
What is the selected carbon or sulfur content?Combustion analysisElement mass fractionElement coverage and furnace suitability are method-specific
Does the sample match a chemical identity?FTIRSpectrum and supported identificationMixtures and contact effects limit inference; not universal purity
Which suitable organic compounds are present?GC-MSTarget concentrations and qualified identity evidenceExtraction and volatility bound coverage
How much of a suitable dissolved compound is present?Liquid chromatographyCalibrated target concentrationsSeparation and detector selectivity must fit the analyte
What enters a liquid under defined batch conditions?Batch leaching or extractionExtract concentration and method-defined releasepH, liquid ratio, time, and phase separation define the result
How does release evolve with percolation?Column leachingFraction concentrations and cumulative releasePacking, flow, and liquid-to-solid ratio control interpretation

How to measure it

Select the complete analytical route

The preparation, measurement, quality controls, and reporting basis together determine what each result can establish.

Test method 01

X-ray fluorescence

Measurement principle: Characteristic X-ray emission from a prepared solid is measured to determine suitable elemental constituents.

Suitable sample state: A representative powder prepared as a suitable cup, pressed pellet, or fused specimen.

Sample preparation: Control sampling, particle size, homogeneity, moisture, thickness, binder or flux additions, and the calibration matrix. Document preparation that can lose volatile constituents.

Output and interpretation

Typical outputs: Elemental mass fractions or explicitly calculated oxide-equivalent composition within the validated range.

Interpretation: Check calibration and matrix corrections. Oxide-equivalent reporting is a calculation convention, not identification of mineral phases or oxidation states.

Principal limitation: Sensitivity depends on the element, matrix, configuration, and preparation. XRF is not a universal trace-contaminant or organic-compound screen.

Decision and boundaries

Why results may disagree: Particle size, mineralogy, surface condition, dilution by binder or flux, and incomplete dissolution in a comparator method can explain disagreement.

Decision supported: Major and minor elemental comparison, material identity support, and selected contamination checks where sensitivity is adequate.

Relevant standard: Use a validated matrix-specific XRF procedure and suitable reference materials. No single powder XRF standard covers every material, preparation, and analyte range.

Compare solution-based elemental analysis

Test method 02

ICP elemental analysis

Measurement principle: A prepared solution is introduced into an inductively coupled plasma and elements are measured by optical emission or mass spectrometry.

Suitable sample state: A compatible digest, dissolved sample, extract, or leachate with a defined preparation history.

Sample preparation: Choose dissolution appropriate to the matrix and target elements. Control reagent purity, blanks, residual solids, dilution, calibration, internal standards where appropriate, and spectral or matrix interference.

Output and interpretation

Typical outputs: Element concentrations in solution and calculated original-sample concentrations using the stated preparation and mass basis.

Interpretation: Distinguish total, acid-extractable, and leachate results. The illustrated ICP-OES instrument represents one route; ICP-MS uses different detection and interference controls.

Principal limitation: Incomplete decomposition, losses, contamination, and matrix effects can dominate the uncertainty. Routine elemental measurement does not establish chemical speciation.

Decision and boundaries

Why results may disagree: Different digestion chemistries, retained residues, measurement interferences, and wet-versus-dry bases can produce different values without a true lot difference.

Decision supported: Elemental impurity quantification and analysis of digests or leachates when recovery and reporting limits fit the decision.

Relevant standard: EPA 6010D describes ICP-OES and EPA 6020B describes ICP-MS for their respective scopes. Pair the determinative method with a suitable preparation; EPA 3051A does not claim total decomposition.

Distinguish content from extraction

Test method 03

Combustion elemental analysis

Measurement principle: A weighed solid is combusted under controlled conditions and selected evolved gases are quantified.

Suitable sample state: A representative solid suitable for the chosen furnace, element, and concentration range.

Sample preparation: Control sample mass, crucible and accelerator blanks, combustion conditions, calibration, reference materials, and completeness of gas release. Follow the material-specific method.

Output and interpretation

Typical outputs: Mass fractions of the elements supported by the configuration, such as carbon and sulfur in the illustrated system.

Interpretation: State which elements were measured. Total carbon does not by itself distinguish organic carbon, carbonate carbon, and other carbon forms.

Principal limitation: One combustion configuration does not determine every light element. Oxygen and nitrogen in metals may require an inert-gas-fusion route rather than this combustion setup.

Decision and boundaries

Why results may disagree: Incomplete combustion, refractory phases, blank contributions, heterogeneous carbon-bearing particles, and differing carbon definitions can change results.

Decision supported: Selected elemental specifications, carbon or sulfur control, and investigation of material changes within the validated scope.

Relevant standard: Select the applicable material standard and validated furnace method. ISO 15350:2000 is a scoped example for total carbon and sulfur in steel and iron, not a universal powder procedure.

Check whether another analytical route is needed

Test method 04

FTIR chemical identification

Measurement principle: Infrared absorption is recorded from a powder, for example through an ATR accessory, to investigate molecular vibrations.

Suitable sample state: A representative solid with adequate sampling contact and a suitable infrared response.

Sample preparation: Control sampling, accessory, contact pressure, background, contamination, moisture, spectral range, and comparison references. Use multiple sampling locations for heterogeneous material.

Output and interpretation

Typical outputs: An infrared spectrum, characteristic bands, and a supported identification or comparison against references.

Interpretation: Use library matches with chemical and sample context. Overlapping bands and mixtures can make more than one interpretation plausible.

Principal limitation: ATR examines a limited near-contact region. FTIR is not a universal elemental assay, trace-impurity screen, or quantitative purity measurement.

Decision and boundaries

Why results may disagree: Contact, sampling depth, moisture, accessory mode, particle heterogeneity, and reference preparation can alter spectra.

Decision supported: Identification of suitable powders, binders, polymers, or residues and investigation of unexpected chemical differences.

Relevant standard: Use a validated infrared identification procedure with suitable references and confirm ambiguous results by an independent technique.

Consider compound-specific separation

Test method 05

GC-MS organic contaminants

Measurement principle: Suitable compounds are introduced into a gas chromatograph, separated, and examined by mass spectrometry.

Suitable sample state: An appropriate extract, headspace sample, or other validated preparation for the target compounds.

Sample preparation: Choose preparation by volatility and matrix. Control recovery, preservation, blanks, cleanup, internal standards or surrogates, calibration, and carryover. The image shows a liquid-injection configuration.

Output and interpretation

Typical outputs: Identified target compounds and calibrated concentrations, with qualified tentative identifications where the method supports them.

Interpretation: Confirm identity using the required chromatographic and spectral criteria. A library match alone is not quantitative confirmation.

Principal limitation: Coverage depends on extraction, volatility, thermal behavior, separation, and detection. One run does not establish the absence of all organic contaminants.

Decision and boundaries

Why results may disagree: Preparation losses, different target lists, matrix interference, coelution, and reporting limits can explain different reports.

Decision supported: Target organic impurity measurement and appropriately scoped investigation of unexpected organic constituents.

Relevant standard: EPA 8270E is an example for semivolatile compounds within its solid-waste scope. Volatile compounds and other matrices require their applicable introduction, preparation, and determinative methods.

Compare liquid chromatography

Test method 06

Liquid chromatography

Measurement principle: Dissolved constituents are separated on a column and measured with a detector suited to the target analytes.

Suitable sample state: A compatible prepared extract or solution with controlled particulates and matrix loading.

Sample preparation: Specify extraction, filtration compatibility, recovery, column, mobile phase, detection, calibration, blanks, and stability. Check adsorption losses and carryover.

Output and interpretation

Typical outputs: Target-compound concentrations and chromatographic separation or identity evidence supported by the detector.

Interpretation: The illustrated HPLC optical detector has analyte-dependent response. Retention time alone may be insufficient confirmation; use additional evidence where needed.

Principal limitation: A chromatographic peak is not inherently unique, and compounds without suitable detector response can be missed. LC-MS is a distinct configuration with its own matrix effects.

Decision and boundaries

Why results may disagree: Different extraction, separation, detection wavelengths, coelution, and calibration can change apparent concentration or impurity profiles.

Decision supported: Quantification of suitable organic constituents, additives, or contaminants and comparison of prepared extracts.

Relevant standard: Use a validated analyte- and matrix-specific procedure. EPA 8310 is a scoped HPLC example for selected PAHs in groundwater and wastes, not general coverage of every organic compound.

Compare GC-MS scope

Test method 07

Batch leaching and extraction

Measurement principle: A solid contacts a defined liquid under controlled mixing before the liquid phase is separated and analyzed.

Suitable sample state: Representative material prepared to the particle-size and moisture requirements of the selected extraction procedure.

Sample preparation: Specify liquid chemistry, liquid-to-solid ratio, dry-mass basis, particle size, contact time, temperature, agitation, pH, phase separation, preservation, and analytical method. Follow special provisions for volatile analytes.

Output and interpretation

Typical outputs: Extract concentrations and, where appropriate, released mass per dry mass of solid under the stated conditions.

Interpretation: State whether the purpose is compliance extraction, water leaching, pH dependence, or another defined assessment. These procedures are not interchangeable.

Principal limitation: The result depends on the extraction conditions and does not directly predict every exposure or field-release scenario. An ordinary bottle rotator is not sufficient for every volatile-analyte procedure.

Decision and boundaries

Why results may disagree: Liquid chemistry, pH, ratio, contact time, size reduction, filtration, and analytical recovery can produce different extractable fractions.

Decision supported: Comparison of release under specified conditions and preparation of extracts for a clearly defined decision.

Relevant standard: EPA 1311 (TCLP) is a specific waste-mobility procedure; EPA 1316 evaluates liquid-to-solid-ratio dependence by parallel batch extraction. Select the applicable procedure rather than combining their conditions.

Compare successive percolation fractions

Test method 08

Column percolation leaching

Measurement principle: Liquid passes through a packed solid and successive eluate fractions are collected for analysis.

Suitable sample state: A granular solid that can be packed and percolated within the selected method requirements.

Sample preparation: Control particle-size preparation, packing, dry mass, saturation, flow direction and rate, eluent, cumulative liquid-to-solid ratio, collection intervals, pH, preservation, and analysis. Check channeling and blockage.

Output and interpretation

Typical outputs: Constituent concentration by fraction and cumulative release as a function of liquid-to-solid ratio.

Interpretation: Keep fraction concentrations and cumulative mass distinct. Interpret changes with the tested flow, chemistry, and solid structure.

Principal limitation: Channeling, low permeability, particle migration, and altered packing can compromise the test. A laboratory column does not automatically reproduce field hydrology.

Decision and boundaries

Why results may disagree: Batch contact and percolation expose material to different contact histories and liquid renewal, so equal nominal liquid-to-solid ratio need not yield equal concentrations.

Decision supported: Assessment of release evolution under percolation and comparison of granular materials within the method scope.

Relevant standard: EPA 1314 specifies an up-flow percolation procedure for inorganic and nonvolatile organic constituents in granular solids as a function of liquid-to-solid ratio.

Compare batch-contact conditions

Conditional routes

When composition needs a companion method

Add a targeted route when bulk composition does not resolve the identity, location, or decision requirement.

Chemical species or phase is the uncertainty

Total element concentrations do not establish oxidation state or mineral form. Use an appropriate speciation or diffraction method with preparation that preserves the property of interest. Compare solid-state methods.

Oxygen, nitrogen, or hydrogen in metals is the target

Select an appropriate inert-gas-fusion or other validated method for the element and material. Do not assume the illustrated carbon-sulfur combustion analyzer provides these results.

Rare foreign particles or surface residues dominate

Use targeted microscopy and local chemical analysis, such as SEM-EDS where suitable, alongside representative bulk sampling. A local spectrum does not establish whole-lot concentration.

Microbiological quality or a specific compliance decision matters

Add the required microbiological or application-specific testing. Define the jurisdiction, material use, analyte list, and prescribed method before interpreting a result against a limit; this page does not establish universal acceptance thresholds.

Process relevance

Connect the result to the material decision

A useful chemical result states what was measured, which material it represents, and how it informs the specified decision.

01

Incoming materials

Verify the specified constituents with adequate sampling, preparation, and reporting limits.

02

Process contamination

Investigate suspect wear or carryover with a target list and sampling plan that can detect localized contamination.

03

Formulation and identity

Compare appropriate spectral or compound-specific evidence when a binder, additive, or supplied grade changes.

04

Organic residues

Choose extraction and chromatography suited to the target rather than requesting an undefined scan for everything.

05

Recycling and reuse

Separate composition of the recovered solid from release under the liquid-contact conditions relevant to the intended use.

06

Percolation assessment

Follow concentration and cumulative release through successive fractions under controlled column conditions.

Technical FAQ

Common questions about composition and leaching

Keep analyte identity, recovery, reporting limits, and liquid-contact conditions explicit.

No. Some procedures extract only part of the material, leaving resistant phases or causing losses. State the preparation and validate recovery before describing a result as total content.
No. It means the analyte was not detected or quantified under the stated method and reporting limit. Check that the limit, preparation recovery, and target list support the decision.
XRF primarily provides elemental information. Reporting elements as oxide equivalents does not establish mineral phases or oxidation states. Use suitable phase or speciation methods when those are the question.
No. Extraction, analyte stability, separation, detection, calibration, and identification criteria limit coverage. Define the target list or screening scope and distinguish tentative identification from confirmed quantification.
No. Total-content analysis and leaching access different quantities. Release depends on the liquid chemistry, pH, contact history, liquid-to-solid ratio, and phase-separation procedure.
Not generally. Percolation changes liquid renewal and contact history, while field conditions add hydrological and chemical variability. Use the method appropriate to the scenario and justify any interpretation beyond the test conditions.

Go deeper

Continue into contamination and material specifications

These published PTI articles provide process and application context. They are not substitutes for the analytical procedures or leaching references below.

Featured image for Wear of the pneumatic pipeline walls: contaminating the conveyed material

Wear of the pneumatic pipeline walls: contaminating the conveyed material

Consider equipment wear as a source of foreign material entering a conveyed powder.

Featured image for Welding Fumes in Powder Plants: The Hidden Contamination Risk During Maintenance and Hot Work

Welding Fumes in Powder Plants: The Hidden Contamination Risk During Maintenance and Hot Work

Explore maintenance-related deposition as a contamination pathway in powder operations.

Featured image for Copper Powder for Electrification: Why Morphology, Purity, and Packing Density Are Now Engineering Variables

Copper Powder for Electrification: Why Morphology, Purity, and Packing Density Are Now Engineering Variables

Connect chemical requirements with the intended application of a metal powder.

Technical basis

Sources and scope boundaries

These are scoped examples and technical references, not a universal compliance package. Use the complete applicable procedure, current requirements for the intended use, and demonstrated matrix performance. XRF and FTIR also require an appropriate validated preparation and interpretation protocol.

  • EPA 6010D: ICP-OES within its stated scope.
  • EPA 6020B: ICP-MS within its stated scope.
  • EPA 3051A: microwave-assisted acid extraction; not a claim of total decomposition.
  • ISO 15350:2000: a material-specific carbon and sulfur combustion example for steel and iron.
  • EPA 8270E: semivolatile organic compounds by GC-MS.
  • EPA 8310: selected PAHs by HPLC in the specified matrices.
  • EPA 1311: TCLP, a defined waste extraction. EPA identifies it as a method-defined parameter for RCRA use.
  • EPA LEAF methods and guidance: distinguishes pH-dependent, percolation, tank, and batch liquid-to-solid-ratio assessments; these address different release questions.
  • EPA 1314: up-flow percolation for granular materials.

Need the measurement, not just the guidance?

If the remaining uncertainty concerns composition, contamination, or release into a liquid, define the target constituents, matrix, preparation, reporting limits, and decision before commissioning work. Agree the analytical scope and any need for a separate specialist laboratory. For guidance on the appropriate testing route, learn about Delft Solids Solutions and contact the laboratory to confirm capabilities and scope.

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