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Quality Measurement · Quality measurement

Grain Probe Sampling

Also known as: Grain trier sampling, Bulk grain probing

Grain probe sampling draws increments from a bulk with a trier, spear, or pneumatic probe — or, for moving grain, cuts the stream with a diverter sampler — and composites and divides them to a working sample. Sampling determines what value a lot is ultimately assigned, and sampling error usually exceeds the error of whatever instrument later analyses the sample.

Dated referenceLast reviewed: 2026-07-13Updated: 2026-07-13
Illustrative diagram · AgricultureID (original)

Grain probe sampling is the step that draws a working sample from a bulk lot for every downstream test this corpus describes — moisture measurement, foreign material assessment, insect-damage inspection, and mycotoxin analysis all start from a sample this step produced. A probe, which may be a compartmented or open-handle trier, a slotted spear, or a pneumatic or vacuum device, is inserted into a static bulk at points and depths a sampling plan prescribes, and each insertion withdraws an increment. Increments are combined into a single composite sample and then reduced, using a mechanical divider rather than by hand, to the working sample size the downstream test requires. Where grain is moving — being loaded, unloaded, or conveyed — a diverter-type mechanical sampler that cuts the entire stream at intervals is the preferred method and is inherently more representative than probing a static pile from the outside.

The point this entry exists to make is that sampling, not the instrument that later analyses the sample, is usually where the largest source of error in a reported result actually enters. A moisture meter, a laboratory test, or a mycotoxin assay each has its own analytical error, but every one of those results is a statement about the sample handed to it — and it is a statement about the lot only to the extent that the sample genuinely represents the lot. Because grain bulks segregate predictably during filling and are rarely uniform, drawing that representative sample is a harder and more consequential problem than most of the analytical steps that follow it.

How sampling is carried out

A trier or spear-type probe is inserted into a static bulk — a bin, a bag stack, a truck, or a hold — at a series of points and depths a sampling plan sets out, and each insertion withdraws a small increment of grain. Every increment collected across the bulk is combined into a single composite sample. That composite is then reduced to the working sample size a downstream test actually requires using a mechanical divider, which splits the composite systematically rather than by hand-selecting a portion of it.

For grain in motion — being loaded onto or off a vessel, conveyed between stores, or moving on a belt — a diverter-type mechanical sampler that periodically cuts the entire cross-section of the moving stream is the preferred approach wherever it is available. Because it samples the full stream rather than reaching into a static pile from outside, it avoids the segregation problems that probing a settled bulk cannot fully overcome.

Why grain bulks defeat a simple probing pattern

Physical reach compounds the problem. A hand probe often cannot reach the centre or the bottom of a deep bulk, or the far corners of a fully loaded container or ship's hold, and that unreachable volume is frequently the same volume most likely to have spoiled, precisely because it is also the hardest part of the bulk to inspect, turn, or aerate.

Clustered contamination and the composite-and-divide step

Contamination in a bulk lot, mycotoxin above all, is often concentrated in a small number of kernels rather than spread evenly through the mass. This defeats the intuition that a small sample safely represents a large lot: both a genuinely compliant lot and a genuinely failing one can return a clean small sample purely by chance, which is exactly why sampling plans prescribe a specific number of increments rather than a single grab sample — more increments reduce this risk substantially, though they cannot eliminate it entirely.

The composite-and-divide step that follows collection is itself part of the measurement, and it is a common point of failure. Once increments are combined into a composite, reducing that composite to a working sample by scooping out a "representative" handful reintroduces exactly the bias the increment plan was designed to eliminate; a proper mechanical divider is required for the reduction to preserve what the increments achieved.

Sample handling and access hazards

A sample continues to change after it is drawn. Left open to the air, exposed to sun, or held in a warm vehicle cab, a sample exchanges moisture with its surroundings before it ever reaches a meter or a laboratory, so a delayed or poorly handled sample can report its own recent history rather than the true condition of the lot at the moment it was drawn. Good sampling practice seals and protects a sample immediately and analyses it promptly.

Relationships

Evidence-backed connections in the knowledge graph.

Scope & limitations

Geographic scope: Global. Sampling patterns, increment counts, and divider procedures are set by the applicable national or international sampling standard or grading authority and differ by commodity, jurisdiction, and the factor being sampled for; mycotoxin sampling plans are frequently a distinct legal requirement.

  • This entry names no increment counts, sample masses, probing depths, or sampling intervals. The applicable sampling standard or grading authority procedure prescribes these, and they differ by commodity and jurisdiction.
  • This entry gives high-level framing on access hazards only and does not describe a confined-space entry procedure; entry into a bin, silo, or store is governed by facility procedures and applicable occupational safety regulation.
  • This entry does not cover the operating steps for any specific probe, trier, or diverter sampler; consult the applicable official method and equipment documentation.
  • A sample drawn to this method still requires an appropriate downstream test — a moisture meter, a laboratory method, or a mycotoxin assay — to produce a usable result; this entry covers the sampling step only.

Sources

This article draws on the following authoritative sources. See our sources & methodology for how they are selected.

  1. [1]USDA — U.S. Department of Agriculture (opens in a new tab)

    United States Department of Agriculture (USDA)

    Authoritative

    Cited for: United States official grain sampling procedures, probing, compositing, and dividing practice

    Type:
    Government agency
    Jurisdiction:
    United States
    Accessed:
    2026-07-12
  2. [2]FAO — Food and Agriculture Organization (opens in a new tab)

    Food and Agriculture Organization of the United Nations (FAO)

    Authoritative

    Cited for: Post-harvest sampling principles and representativeness in bulk grain lots

    Type:
    Intergovernmental organization
    Jurisdiction:
    Global
    Accessed:
    2026-07-12
  3. [3]EFSA — European Food Safety Authority (opens in a new tab)

    European Food Safety Authority (EFSA)

    Authoritative

    Cited for: Mycotoxin sampling plans and the effect of clustered contamination on sampling reliability

    Type:
    Government agency
    Jurisdiction:
    European Union
    Accessed:
    2026-07-12
  4. [4]AHDB — Agriculture and Horticulture Development Board (opens in a new tab)

    Agriculture and Horticulture Development Board (AHDB)

    High

    Cited for: Grain intake sampling practice and hazards of on-farm and store sampling in the United Kingdom

    Type:
    Government agency
    Jurisdiction:
    United Kingdom
    Accessed:
    2026-07-12