IS 12813:1989 is the Indian Standard (BIS) for method of analysis of hydraulic cement by atomic absorption spectrophotometer. This standard details the procedure for chemical analysis of hydraulic cement using an Atomic Absorption Spectrophotometer (AAS). It serves as a rapid instrumental alternative to the classical wet chemical methods for determining major oxide constituents like SiO2, Al2O3, Fe2O3, CaO, and MgO.
Method of analysis of hydraulic cement by atomic absorption spectrophotometer
Key reference values — verify against the current code edition / project specification.
| Reference | Value | Clause |
|---|---|---|
| Method | Atomic absorption spectrophotometry (element-specific) | Scope |
| Best for | Sensitive specific elements — alkalis (Na₂O,K₂O), MgO | Application |
| Key use | Alkali content → alkali-aggregate-reaction risk | Critical |
| Depends on | Complete dissolution + matched standards + interf. control | Critical |
| Not for | Full oxide suite (use XRF / classical) | Caution |
| Referee | Classical IS 4032 for contested results | Cross-ref |
| Drives | Low-alkali cement / SCM (PPC/slag) decision | Application |
IS 12813:1989 is the method for analysis of hydraulic cement by atomic absorption spectrophotometry (AAS) — an instrumental route that determines specific elements in cement (e.g. calcium, magnesium, iron, manganese, alkalis — sodium/potassium) by aspirating a dissolved sample into a flame and measuring light absorption at element-specific wavelengths. It complements the other chemical-analysis methods for element-specific, sensitive determinations.
It sits in the cement chemical-analysis family:
AAS measures one element at a time with high sensitivity: the sample is dissolved, aspirated into a flame, and the absorption at that element's characteristic wavelength gives its concentration against standard solutions. Its niche:
The engineering point: AAS is the method of choice when a *specific element at low level* must be known accurately — notably alkalis for alkali-aggregate-reaction risk — but, like all instrumental methods, its number depends entirely on correct dissolution, interference control and traceable standard solutions.
Scenario: an aggregate is potentially alkali-reactive; the cement's alkali content (Na₂O equivalent) must be known to assess AAR risk.
Step 1 — choose AAS: for sensitive, element-specific Na/K determination, AAS (IS 12813) is well suited.
Step 2 — dissolve correctly: complete sample dissolution per the method — incomplete dissolution undercuts every result.
Step 3 — standards & interference control: matrix-matched standard solutions bracketing the range; add ionisation/interference suppressants as the method requires.
Step 4 — measure & compute: aspirate, read absorption for Na and K, compute the Na₂O-equivalent alkali.
Step 5 — assess AAR: combine the alkali content with the aggregate reactivity assessment to judge alkali-aggregate-reaction risk and the need for low-alkali cement / SCMs (PPC/slag) — a IS 456 durability decision.
AAS delivered the sensitive, element-specific number the durability decision needed — accurate only because dissolution, standards and interference control were right.
1. Incomplete sample dissolution. AAS is solution-based — undissolved analyte simply isn't measured; preparation is decisive.
2. Non-matrix-matched standards / uncontrolled interferences. Chemical and ionisation interferences bias AAS badly without releasing agents/ionisation buffers and matched standards.
3. Using AAS for a full oxide suite. It is element-by-element; for the whole composition fast, XRF or classical [IS 4032] is more appropriate — use AAS for sensitive specific elements.
4. Treating any instrumental result as the referee. Classical IS 4032 adjudicates contested results.
5. Ignoring alkali's durability meaning. The alkali number isn't academic — it drives the alkali-aggregate-reaction risk decision.
IS 12813 is reaffirmed and is the sensitive, element-specific member of the cement chemical-analysis toolkit. Most engineers never run it, but its one durability-critical use is worth knowing: accurate alkali (Na₂O-equivalent) determination underpins the alkali-aggregate-reaction risk assessment — a slow, untreatable concrete disease best avoided by low-alkali cement or SCMs (PPC/slag). As with all instrumental methods, the number is only as good as the dissolution, matrix-matched standards and interference control, and classical IS 4032 remains the referee for contested results. Use AAS for sensitive specific elements (alkalis especially), XRF for fast full-suite control, classical for adjudication — and always tie the alkali figure back to the real IS 456 durability decision it informs.
| Parameter | IS Value | International | Source |
|---|---|---|---|
| Flame for Ca, Mg analysis | Air-acetylene | Air-acetylene | ASTM C114-18 |
| Flame for Si, Al analysis | Nitrous oxide-acetylene | Nitrous oxide-acetylene | ASTM C114-18 |
| Interference suppressant for CaO/MgO | Lanthanum solution | Lanthanum or Strontium salt solution | EN 196-2:2013 |
| Primary Sample Decomposition | Hydrochloric acid (HCl) digestion | HCl digestion or Lithium metaborate (LiBO₂) fusion | ASTM C114-18 |
| Wavelength for Calcium (Ca) | 422.7 nm | 422.7 nm | ASTM C114-18 |
| Wavelength for Silicon (Si) | 251.6 nm | 251.6 nm | ASTM C114-18 |
| Wavelength for Magnesium (Mg) | 285.2 nm | 285.2 nm | EN 196-2:2013 |