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Requirements for Biomass Sampling
Guest article by Paul Janze,
Sandwell Engineering
Introduction
With
the current emphasis on the use of biomass for `green’ energy
purposes, the importance of having good quality `hog fuel’, cannot
be over-emphasized. And to ensure good quality fuel, good sampling
procedures must be followed.
Woody biomass in chip form has been
utilized by the pulp and paper industry for many decades and chip
quality has long been recognized as having an important effect on
pulp quality; to make good pulp you need good chips. Likewise for a
biomass-fired plant to operate efficiently, it needs a reliable,
constant supply of consistent quality fuel.
Good quality control relies on proper
sampling, which must be accurate and precise and truly represent the
main body of biomass. Without good sampling, quality control is
based on false information. Bulk materials are difficult to sample
properly on a production basis. Manual sampling can be done but it
is labor intensive, prone to errors and does not easily fit into a
production environment.
Collecting samples of biomass is one
task not always done well, and unless the sample is taken properly,
it will not be a true representation of the main product flow.
Biomass is not easy to sample. It
appears in a myriad of species, forms and sizes; it knits together,
doesn’t flow well, consolidates and packs easily; it can have a wide
range of moisture contents, basic and bulk densities and calorific
values; it will freeze; it is very dusty, catches fire easily and is
self-combustible; it can contain all manner of contaminants; it can
be quite fragile and care must be taken not to degrade the material.
To be of value, biomass samples need
to be unbiased, accurate, precise and representative of the main lot
or consignment of material.
The intent of this paper is to
summarize the requirements that must be met in order to provide
representative chip sampling and to do so in an easily understood
and achievable manner. This paper does not consider chip
classification or analysis.
1. Features of Good Sampling
Accuracy - is the ability to obtain
samples which represent the true nature of the material supply.
Precision - is a statistical term
relating to the number of samples taken from a lot or consignment.
Biomass is a highly variable product
and requires a large number of samples in order to establish
sampling precision. Precision can only be increased by
increasing the number of spot samples.
A single spot sample generally is
less likely to be representative of the main body of biomass than is
a gross sample, which is a mixture of multiple spot samples.
2. Sampling Bias
Poor sampling can induce systematic
errors that skew the results. Two common errors are:
- Spot samples are taken where
certain properties are over-represented. eg. – at tail-gate of a
truck where fines have settled to the bottom.
- The sample device is not capable
of taking a representative sample. eg. – the sample device is
too small and either rejects large pieces or overflows.
Properly designed, operated and
maintained automatic samplers can minimize systematic sampling bias.
Fractionation
Fractionation or particle separation
can occur from the way in which biomass is loaded / stacked and the
way in which it is transported. eg. – fines will settle down to the
bottom of a biomass truck over a long haul.
Additionally, fractionation can be
produced by the sampling device itself; either by rejecting oversize
pieces, failing to pick-up small particles, selectively picking up
small particles, or breaking up particles by the sampling motion
itself.
Stationary material is not uniform
due to fractionation where material stratifies according to size. In
order to get a representative gross sample from stationary material,
a very large number of increment or spot samples are required.
3. Classification of
Sampling Techniques
The quality of the sample depends
upon the amount of human discretion involved, the sampling
conditions, and the sampling location and timing.
- Generally, those samples which
do not involve human discretion are more accurate.
- Accepted sampling conditions,
include:
- Stopped Belt Cut (Laboratory
Reference Method) - taking a full cross-section cut of material
from off of a stopped conveyor belt.
- Full Stream Cut – taking a full
cross-section cut of material from a falling stream.
- Partial Stream Cut – only taking
a part of the cross-section of falling stream.
- Stationary Sampling – taking a
sample from a stationary pile or container.
Generally, the stopped belt cut
provides the best sample but is impractical to use in a
production setting. Full-stream cut and partial-stream cut
samples can produce results which are representative of the main
body of material, depending upon the sampling equipment design.
Stationary sampling produces the poorest sample.
- Sample location and timing
- Systematic – samples are taken
evenly spaced in time or location.
- Random – samples are taken
randomly spaced in time or location.
Systematic spacing generally provides
better results. The challenge is to design a sampling system and
procedure, which repetitively produces the most representative
sample and is easy and practical to use.
4. Establishing Sampling
Procedures and Selecting Sampling Equipment
Establishing
sampling procedures and selecting sampling devices requires an
understanding of the following:
Material Being Sampled
Biomass is highly variable in size,
configuration and moisture content. It is relatively fragile and
size is often an important factor, so care must be taken not to
break the particles unnecessarily during sampling.
Number and Size of Samples
This depends upon the variability of
the biomass and is usually determined by the plant technical
department based on historical statistical results. Where new
sources are coming on line, it can be expected that the number of
samples required will be greater than for established sources, where
historical data is available. Normal sample size required in
the lab is 8-10 litres (~0.35 ft³).
Sample Collection Method
The best practical method should be
used. The `stopped-belt, full-cut’ method is the best, but is not
practical. The `falling stream, full-cut’ or `partial cut’ are
the next best methods.
Sample Distribution Through Lot
Sample increments must be distributed
through the whole volume of the lot, so that any one particle has an
equal chance of being selected. This is particularly important
where `fractionation’ has occurred due to fines segregation to one
part of the lot / consignment.
Characteristics and Movement of
Sampling Device
The opening of the sampling device
must be large enough so as not to reject the largest possible piece
and the capacity must be large enough to completely contain the
sample without spillage. There should be no rejection by size
of material or movement of the device through the material.
There should be no contamination of the sample by the device.
Preferably, the sample device will
pass through the entire cross-section of the stream so that each
particle has an equal chance of being selected; or at least through
a partial section that will contain all particle sizes within the
stream.
Device speed through the flow is
critical as the device must not block the flow of material. The
sampling device shall be non-clogging, self-cleaning and shall be
designed to facilitate inspection and maintenance. Ideally, it
will not be complex or costly to purchase and maintain.
Location of Sampling Equipment
Equipment shall be located where:
- It can effectively take a
representative sample.
- It is convenient and readily
accessible for sample taking.
- It is readily accessible for
maintenance and inspection.
Maintenance of Sampling Equipment
Sampling equipment must be safely and
readily accessible to enable inspection, cleaning and maintenance.
Worn mechanical sampling equipment can produce biased results,
therefore it is imperative that equipment is inspected, repaired
when necessary, and the performance measured regularly.
Preservation of Moisture Content
The sampling device / method shall
neither dry the biomass out or add moisture.
Personnel
Sampling personnel shall be properly
trained and qualified.
Criteria of Sampling Performance
Sampling procedures and equipment
must be routinely monitored to ensure that the samples being
collected are:
- Unbiased
- Accurate
- Provide the degree of precision
required
- Representative of the whole lot
In addition, a constant sampling
ratio should be maintained; ie. – constant volume or weight of
sample as compared to the whole lot.
Sample Handling
Samples once collected must be:
- Clearly labeled and identified
- Sealed in moisture-proof
containers
- Stored in a cool, dry place
Samples properly stored in this
manner can be kept in storage for up to 36 hours with no appreciable
moisture loss.
Gross Sample Size Reduction
Normal increment sample size as
collected will be 8-10 litres (average bucket size); therefore,
combined multiple increments (the gross sample) must be reduced down
to the laboratory sample size in a manner that retains biomass
representative of the whole lot.
Large gross samples shall be
thoroughly mixed before being reduced to laboratory sample size.
Large samples can be reduced in size by mixing thoroughly and coning
and quartering or by the use of an automatic splitter.
5.
Design of Sampling Equipment
There are many `off-the-shelf’
product samplers; most of which were designed for materials other
than biomass. However, it is the author’s experience that the best
sampling equipment is custom designed to meet the specific
requirements of the biomass sampling application considering the
sampling requirements described in this paper, the product being
handled, and the physical and operational constraints.
(Photo: Wood Chip Sampler)
Summary
To be of value, biomass samples need
to be unbiased, accurate, precise and representative of the main lot
or consignment of biomass. Biomass is highly variable in size,
configuration and moisture content and is prone to fractionation and
stratification, which complicate the sampling procedure.
Single spot / increment samples tend
not to be accurate or representative of the main lot / consignment,
particularly those samples taken from stationary loads or piles
where fractionation has occurred.
Two common sampling errors, which
bias results are:
- Spot samples are taken where
certain properties are over-represented. eg. – at the tail-gate
of a truck where fines have settled to the bottom.
- The sample device is not capable
of taking a representative sample. ie. – the sample device is
too small and either rejects large pieces or overflows.
The best, practical sampling
procedures and equipment have the following features:
- Human discretion is minimized.
- Full-stream cut or
partial-stream cut sampling is employed.
- Samples are taken systematically
in time and /or location throughout the whole volume of the main
lot / consignment.
- They do not introduce bias or
contaminants into the sample.
- They are convenient to use.
- Preferably, they automatically
reduce the gross sample to the laboratory sample size.
- Preferably, they have low
capital and maintenance costs.
It is not easy to achieve all of
these objectives, however, the primary goals of accuracy, precision
and representativeness must take precedence. Convenience and
cost, while important, are secondary considerations.
About our author
Paul Janze is a senior material
handling specialist with more than 30 years experience in
engineering, equipment design and manufacture, project management
and plant maintenance, primarily in the forest products industry. He
is a specialist with difficult-to-handle materials such as wood
chips, hog fuel, wastewood and bark, biosolids sludge and wet pulp,
poultry litter and boiler ash which all have differing and unique
handling characteristics.
For more information contact:
Mr. Paul Janze
Material Handling Specialist
Sandwell Engineering Inc.
885 Dunsmuir Street, Suite 600
Vancouver, BC, V6C-1N5
Canada
Telephone: 604-684-9311
Fax: 604-688-5913
Email: pjanze@sandwell.com
Web site:
http://www.sandwell.com/
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