Standard Practice for Preparation of Biomass for Compositional Analysis

SIGNIFICANCE AND USE
4.1 Preparation Method A—Method suitable for the preparation of large quantities (>20 g) of field collected samples into a form appropriate for compositional analysis. Woody samples must first be available as chips of a nominal 5 by 5 by 0.6 cm (2 by 2 by 1/4 in.) or less and twigs not exceeding 0.6 cm (1/4 in.) diameter. Herbaceous materials may be processed as whole straw. It is recommended that wastepaper should be shredded into pieces less then 1 cm (1/2 in.) wide. Furthermore, it is recommended that twigs, straw, and wastepaper should not exceed 61 cm (24 in.) in length to facilitate handling.  
4.2 Preparation Methods B and C—Methods are suitable for very moist feedstocks, samples that would not be stable during prolonged exposure to ambient conditions, or for drying materials when room conditions deviate from the ambient conditions described in 3.1.1. These test methods are also suitable for handling small samples of biomass (  
4.3 Preparation Methods A, B, and C are not intended for materials that will already pass through a 20 mesh sieve or that cannot be dried by the described methods to a total solids content of greater than 85 %, based on an oven dried weight.  
4.4 Preparation Method A will separate the milled material into two fractions, a −20/+80 mesh fraction and a −80 mesh fraction.  
4.4.1 Extraneous inorganic materials will accumulate in the −80 mesh fraction and it should be analyzed independently from the −20/+80 mesh fraction. Weighted results from the two fractions can then be combined to obtain results for materials on an "as received" basis.
Note 1: During analysis, the very fine consistency of the −80 mesh fraction may cause problems in filtering operations and should be handled appropriately.  
4.5 Preparation Method D—Method suitable for cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and cereal grain fermentation residues that are generally stable.  
4.6 Preparation Method E—Method suitable for ce...
SCOPE
1.1 This practice covers a reproducible way to convert hardwoods, softwoods, herbaceous materials (such as switchgrass and sericea), agricultural residues (such as corn stover, wheat straw, and bagasse), wastepaper (such as office waste, boxboard, and newsprint), cellulosic feedstocks pretreated to improve suitability for fermentation, cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and fermentation residues into a uniform material suitable for compositional analysis. This practice is intended for samples that need to be dried prior to analysis.  
1.2 Milling and sieving actions both produce large amounts of dust. This dust can be a nuisance hazard and irritant. Use appropriate respiratory protection as needed. If excessive amounts of dust are allowed to become airborne a potential explosion hazard is possible. Provide appropriate dust control measures as needed.  
1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are provided for information only and are not considered standard.  
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

General Information

Status
Published
Publication Date
31-Mar-2019
Drafting Committee
E48.05 - Biomass Conversion

Relations

Effective Date
01-Apr-2019
Effective Date
01-Oct-2013
Effective Date
01-May-2009
Effective Date
01-May-2004
Effective Date
10-May-2001
Effective Date
10-May-2001
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019
Effective Date
01-Apr-2019

Overview

ASTM E1757-19: Standard Practice for Preparation of Biomass for Compositional Analysis outlines reproducible methods for preparing a wide variety of biomass materials prior to compositional laboratory analysis. This standard, published by ASTM International, provides detailed procedures for reducing raw feedstocks-including hardwoods, softwoods, herbaceous materials, agricultural residues, wastepaper, cereal grains, and fermentation residues-into uniform, analyzable samples. The practice ensures consistency when comparing results and supports accurate bioenergy research, renewable fuel development, and environmental testing.

Key Topics

  • Preparation Methods: Five distinct preparation methods (Methods A-E) tailored to fit different types of biomass and sample sizes, ranging from field-collected wood chips and herbaceous matter to very moist feedstocks and stable or biologically active grains and residues.
    • Method A: Suitable for large, solid biomass quantities; emphasizes air drying, milling, and sieving.
    • Methods B and C: For wet, unstable samples or those sensitive to ambient conditions; use oven drying or freeze-drying.
    • Methods D and E: For cereal grains and related fermentation residues; address both stable and biologically active materials with specific moisture and drying protocols.
  • Sample Handling: Procedures for minimizing contamination, achieving proper sample homogeneity, and preventing sample deterioration during the drying, milling, and sieving processes.
  • Dust Control and Safety: Highlights the hazards associated with dust created during grinding and sieving, recommending appropriate dust control strategies and personal protective equipment to protect workers and reduce explosion risks.
  • Moisture Determination: Emphasizes the importance of drying biomass to specific moisture levels-often below 8% or 85% total solids-to ensure sample integrity and prevent mold growth or spoilage before analysis.
  • Fraction Analysis: Guidance on separating and analyzing different particle size fractions (such as −20/+80 mesh and −80 mesh for Method A) to ensure accurate compositional analysis.

Applications

ASTM E1757-19 is crucial for laboratories, industry professionals, and researchers working in:

  • Bioenergy and Biofuels: Standardizes the preparation of biomass and feedstocks prior to chemical analysis, supporting the development of renewable fuels by enabling consistent assessment of cellulose, hemicellulose, lignin, starch, and other critical components.
  • Agricultural By-products Analysis: Facilitates the evaluation of agricultural and forestry residues, wastepaper, and pretreated cellulosic feedstocks for compositional profiling in bio-industrial processes.
  • Quality Control: Ensures laboratories can accurately compare data across different locations and time periods by following harmonized sample preparation techniques.
  • Environmental and Regulatory Compliance: Helps organizations meet local and international regulations when reporting biomass composition and supports best practices in health, safety, and environmental stewardship.

Related Standards

  • ASTM E11: Specification for test sieve cloth and sieves used in particle size separation.
  • AOAC 935.29: Official method for determing moisture in malt and other biomasses.
  • NFTA 2.2.2.5: Standard procedure for determining dry matter in forage via oven drying.
  • Other ASTM and international biomass characterization standards: These may be used in tandem to cover further analysis of chemical content, ash, and further feedstock processing steps.

By adhering to ASTM E1757-19, laboratories and bioenergy producers ensure the preparation of biomass samples is accurate, repeatable, and safe-contributing to reliable compositional analysis essential for the advancement of bio-based industries and environmental research.

Buy Documents

Standard

ASTM E1757-19 - Standard Practice for Preparation of Biomass for Compositional Analysis

English language (5 pages)
sale 15% off
sale 15% off
Standard

REDLINE ASTM E1757-19 - Standard Practice for Preparation of Biomass for Compositional Analysis

English language (5 pages)
sale 15% off
sale 15% off

Get Certified

Connect with accredited certification bodies for this standard

Control Union Certifications

Global certification for agriculture and sustainability.

RVA Netherlands Verified

ECOCERT

Organic and sustainability certification.

COFRAC France Verified

Rainforest Alliance Certification

Sustainable agriculture and forestry certification.

ANAB United States Verified

Sponsored listings

Frequently Asked Questions

ASTM E1757-19 is a standard published by ASTM International. Its full title is "Standard Practice for Preparation of Biomass for Compositional Analysis". This standard covers: SIGNIFICANCE AND USE 4.1 Preparation Method A—Method suitable for the preparation of large quantities (>20 g) of field collected samples into a form appropriate for compositional analysis. Woody samples must first be available as chips of a nominal 5 by 5 by 0.6 cm (2 by 2 by 1/4 in.) or less and twigs not exceeding 0.6 cm (1/4 in.) diameter. Herbaceous materials may be processed as whole straw. It is recommended that wastepaper should be shredded into pieces less then 1 cm (1/2 in.) wide. Furthermore, it is recommended that twigs, straw, and wastepaper should not exceed 61 cm (24 in.) in length to facilitate handling. 4.2 Preparation Methods B and C—Methods are suitable for very moist feedstocks, samples that would not be stable during prolonged exposure to ambient conditions, or for drying materials when room conditions deviate from the ambient conditions described in 3.1.1. These test methods are also suitable for handling small samples of biomass ( 4.3 Preparation Methods A, B, and C are not intended for materials that will already pass through a 20 mesh sieve or that cannot be dried by the described methods to a total solids content of greater than 85 %, based on an oven dried weight. 4.4 Preparation Method A will separate the milled material into two fractions, a −20/+80 mesh fraction and a −80 mesh fraction. 4.4.1 Extraneous inorganic materials will accumulate in the −80 mesh fraction and it should be analyzed independently from the −20/+80 mesh fraction. Weighted results from the two fractions can then be combined to obtain results for materials on an "as received" basis. Note 1: During analysis, the very fine consistency of the −80 mesh fraction may cause problems in filtering operations and should be handled appropriately. 4.5 Preparation Method D—Method suitable for cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and cereal grain fermentation residues that are generally stable. 4.6 Preparation Method E—Method suitable for ce... SCOPE 1.1 This practice covers a reproducible way to convert hardwoods, softwoods, herbaceous materials (such as switchgrass and sericea), agricultural residues (such as corn stover, wheat straw, and bagasse), wastepaper (such as office waste, boxboard, and newsprint), cellulosic feedstocks pretreated to improve suitability for fermentation, cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and fermentation residues into a uniform material suitable for compositional analysis. This practice is intended for samples that need to be dried prior to analysis. 1.2 Milling and sieving actions both produce large amounts of dust. This dust can be a nuisance hazard and irritant. Use appropriate respiratory protection as needed. If excessive amounts of dust are allowed to become airborne a potential explosion hazard is possible. Provide appropriate dust control measures as needed. 1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are provided for information only and are not considered standard. 1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

SIGNIFICANCE AND USE 4.1 Preparation Method A—Method suitable for the preparation of large quantities (>20 g) of field collected samples into a form appropriate for compositional analysis. Woody samples must first be available as chips of a nominal 5 by 5 by 0.6 cm (2 by 2 by 1/4 in.) or less and twigs not exceeding 0.6 cm (1/4 in.) diameter. Herbaceous materials may be processed as whole straw. It is recommended that wastepaper should be shredded into pieces less then 1 cm (1/2 in.) wide. Furthermore, it is recommended that twigs, straw, and wastepaper should not exceed 61 cm (24 in.) in length to facilitate handling. 4.2 Preparation Methods B and C—Methods are suitable for very moist feedstocks, samples that would not be stable during prolonged exposure to ambient conditions, or for drying materials when room conditions deviate from the ambient conditions described in 3.1.1. These test methods are also suitable for handling small samples of biomass ( 4.3 Preparation Methods A, B, and C are not intended for materials that will already pass through a 20 mesh sieve or that cannot be dried by the described methods to a total solids content of greater than 85 %, based on an oven dried weight. 4.4 Preparation Method A will separate the milled material into two fractions, a −20/+80 mesh fraction and a −80 mesh fraction. 4.4.1 Extraneous inorganic materials will accumulate in the −80 mesh fraction and it should be analyzed independently from the −20/+80 mesh fraction. Weighted results from the two fractions can then be combined to obtain results for materials on an "as received" basis. Note 1: During analysis, the very fine consistency of the −80 mesh fraction may cause problems in filtering operations and should be handled appropriately. 4.5 Preparation Method D—Method suitable for cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and cereal grain fermentation residues that are generally stable. 4.6 Preparation Method E—Method suitable for ce... SCOPE 1.1 This practice covers a reproducible way to convert hardwoods, softwoods, herbaceous materials (such as switchgrass and sericea), agricultural residues (such as corn stover, wheat straw, and bagasse), wastepaper (such as office waste, boxboard, and newsprint), cellulosic feedstocks pretreated to improve suitability for fermentation, cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and fermentation residues into a uniform material suitable for compositional analysis. This practice is intended for samples that need to be dried prior to analysis. 1.2 Milling and sieving actions both produce large amounts of dust. This dust can be a nuisance hazard and irritant. Use appropriate respiratory protection as needed. If excessive amounts of dust are allowed to become airborne a potential explosion hazard is possible. Provide appropriate dust control measures as needed. 1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are provided for information only and are not considered standard. 1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

ASTM E1757-19 is classified under the following ICS (International Classification for Standards) categories: 65.040.20 - Buildings and installations for processing and storage of agricultural produce. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM E1757-19 has the following relationships with other standards: It is inter standard links to ASTM E1757-01(2015), ASTM E11-13, ASTM E11-09e1, ASTM E11-04, ASTM E11-01, ASTM E11-95, ASTM E1755-01(2020), ASTM E1721-01(2020), ASTM E3181-20, ASTM E1821-08(2020), ASTM E1690-08(2021), ASTM E1758-01(2020), ASTM E1756-08(2020). Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E1757-19 is available in PDF format for immediate download after purchase. The document can be added to your cart and obtained through the secure checkout process. Digital delivery ensures instant access to the complete standard document.

Standards Content (Sample)


This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the
Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Designation: E1757 − 19
Standard Practice for
Preparation of Biomass for Compositional Analysis
This standard is issued under the fixed designation E1757; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision.Anumber in parentheses indicates the year of last reapproval.A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 2. Referenced Documents
2.1 ASTM Standards:
1.1 This practice covers a reproducible way to convert
E11Specification forWovenWireTest Sieve Cloth andTest
hardwoods, softwoods, herbaceous materials (such as switch-
Sieves
grass and sericea), agricultural residues (such as corn stover,
2.2 Other Documents:
wheat straw, and bagasse), wastepaper (such as office waste,
AOAC 935.29Moisture in Malt - Gravimetric Method
boxboard, and newsprint), cellulosic feedstocks pretreated to
(AOAC 2005)
improve suitability for fermentation, cereal grains, cereal grain
NFTA 2.2.2.5Dry Matter by Oven Drying for 3 hr at 105
fermentationmash,cerealgrainfermentationbeer,andfermen-
°C
tation residues into a uniform material suitable for composi-
tional analysis. This practice is intended for samples that need
3. Terminology
to be dried prior to analysis.
3.1 Definitions of Terms Specific to This Standard:
1.2 Milling and sieving actions both produce large amounts
3.1.1 ambient conditions, n—a temperature of 20 to 30°C
of dust. This dust can be a nuisance hazard and irritant. Use
(68 to 85°F), less than 50% relative humidity.
appropriate respiratory protection as needed. If excessive
3.1.2 beer, n—the mash after it has undergone fermentation
amounts of dust are allowed to become airborne a potential
and has been deemed complete by virtue of the carbohydrates
explosion hazard is possible. Provide appropriate dust control
being converted into renewable fuel by enzymes and ferment-
measures as needed.
ing organisms.
1.3 The values stated in SI units are to be regarded as
3.1.3 mash, n—a mixture or slurry of water (including
standard. The values given in parentheses after SI units are
recycled water streams) and ground grain.
provided for information only and are not considered standard.
3.1.4 prepared biomass, n—biomass that has been prepared
1.4 This standard does not purport to address all of the
according to this practice.
safety concerns, if any, associated with its use. It is the
3.1.5 predominantly cellulosic, adj—feedstock that has an
responsibility of the user of this standard to establish appro-
averageadjustedcellulosiccontentof75%,measuredonadry
priate safety, health, and environmental practices and deter-
mass basis; furthermore, this “adjusted cellulosic content” is
mine the applicability of regulatory limitations prior to use.
the percent of organic (non-ash) material that is cellulose,
1.5 This international standard was developed in accor-
hemicellulose, or lignin.
dance with internationally recognized principles on standard-
ization established in the Decision on Principles for the
4. Significance and Use
Development of International Standards, Guides and Recom-
4.1 Preparation Method A—Method suitable for the prepa-
mendations issued by the World Trade Organization Technical
rationoflargequantities(>20g)offieldcollectedsamplesinto
Barriers to Trade (TBT) Committee.
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
This practice is under the jurisdiction ofASTM Committee E48 on Bioenergy Standards volume information, refer to the standard’s Document Summary page on
and Industrial Chemicals from Biomass and is the direct responsibility of Subcom- the ASTM website.
mittee E48.05 on Biomass Conversion. Available from AOAC International, 2275 Research Blvd., Suite 300,
Current edition approved April 1, 2019. Published May 2019. Originally Rockville, MD 20850-3250, http://www.aoac.org.
approved in 1995. Last previous edition approved in 2015 as E1757–01(2015). Available from National Forage Testing Association (NFTA), PO Box 1470,
DOI: 10.1520/E1757-19. Stuart, FL 34995, https://www.foragetesting.org/.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E1757 − 19
a form appropriate for compositional analysis.Woody samples 5.5 Sample Mills, for grinding samples.
must first be available as chips of a nominal 5 by 5 by 0.6cm
5.5.1 Sample grinders must be capable of grinding samples
1 1
(2by2by ⁄4in.)orlessandtwigsnotexceeding0.6cm( ⁄4in.)
to a sufficiently fine powder.
diameter. Herbaceous materials may be processed as whole
5.5.1.1 Discussion—Manyanalyticaltestmethodshavespe-
straw. It is recommended that wastepaper should be shredded
cific particle size requirements. For example, when analyzing
into pieces less then 1 cm ( ⁄2 in.) wide. Furthermore, it is
for starch, a particle size of less than 500 µm on average is
recommended that twigs, straw, and wastepaper should not
typically required.
exceed 61 cm (24 in.) in length to facilitate handling.
5.5.2 For materials that are predominantly cellulosic and
fermentation residues from predominantly cellulosic materials
4.2 PreparationMethodsBandC—Methodsaresuitablefor
very moist feedstocks, samples that would not be stable during that have been prepared in accordance with Methods A, B, or
C, a knife cutting style mill is recommended.
prolonged exposure to ambient conditions, or for drying
materials when room conditions deviate from the ambient
NOTE 2—AWiley Mill, size No. 4 with a 2mm screen, is suitable for
conditions described in 3.1.1. These test methods are also
samples >20 g, and the intermediate model, with 1mm screen, is suitable
suitable for handling small samples of biomass (<20 g). The
for samples <20 g that will not be sieved.
dryingstepisdoneinaconvectionovenat45°C(TestMethod
5.5.3 For cereal grains, cereal grain fermentation mash,
B) or by lyophilization (Test Method C).
cereal grain fermentation beer, and cereal grain fermentation
4.3 Preparation Methods A, B, and C are not intended for
residues that have been prepared in accordance with Methods
materialsthatwillalreadypassthrougha20meshsieveorthat
D or E, an impact style mill is recommended.
cannot be dried by the described methods to a total solids
5.6 Drying Oven, capable of maintaining temperatures be-
content of greater than 85%, based on an oven dried weight.
tween 45 and 55 °C (Test Methods B and D).
4.4 Preparation Method A will separate the milled material
5.7 Freeze-Drier—System with vacuum chamber and pump
into two fractions, a −20/+80 mesh fraction and a −80 mesh
capable of maintaining a pressure of <1 torr and a cold finger
fraction.
inthechambercapableofmaintainingatemperatureof−50°C
4.4.1 Extraneous inorganic materials will accumulate in the
(Test Methods C and E).
−80 mesh fraction and it should be analyzed independently
fromthe−20/+80meshfraction.Weightedresultsfromthetwo
6. Procedure: Preparation Method A
fractions can then be combined to obtain results for materials
on an "as received" basis.
6.1 This method is suitable for larger quantities (>20 g) of
biomass as described in 4.1.
NOTE 1—During analysis, the very fine consistency of the −80 mesh
fractionmaycauseproblemsinfilteringoperationsandshouldbehandled
6.2 The raw biomass material should be spread out on a
appropriately.
suitable surface to air dry prior to any milling. Do not pile the
4.5 Preparation Method D—Method suitable for cereal
material deeper then 15 cm. Turn the material at least daily to
grains, cereal grain fermentation mash, cereal grain fermenta-
ensureevendryingandminimizemoldingofmaterialthatmay
tion beer, and cereal grain fermentation residues that are
contain significant amounts of moisture. The material is
generally stable.
considered dried when the change in weight is less than 1% in
24 h.
4.6 Preparation Method E—Method suitable for cereal
grains, cereal grain fermentation mash, cereal grain fermenta-
6.3 The air-dried material is fed into the knife-mill and is
tion beer, and cereal grain fermentation residues that are
milledtopassthrougha2mmscreeninthebottomofthemill.
biologically or enzymatically active.
Milled wastepaper does not need to be sieved and can be used
directly for composition analysis. Milled biomass materials
5. Apparatus
should be sieved as follows.
5.1 Balance, sensitive to 0.1 g.
6.4 The sieving is set up by stacking the sieves in the
following order, starting at the bottom: start with the bottom
5.2 Riffle Sampler with Pans—Amanualsampledividerthat
pan, next stack the 80 mesh sieve, followed by the 20 mesh
splits the milled biomass into a number of alternate elements.
sieve. Milled material is placed no more then 7 cm deep in the
Riffledivisionsshouldbeintherangefrom6.4mmto12.7mm
1 1
20 mesh sieve.
( ⁄4in. to ⁄2 in.) with at least 24 riffle openings across the top.
The feed chute and riffles should have a slope of at least 60°.
6.5 Place the cover on the sieve stack and secure the stack
Three pans are needed, one to pour the sample into the riffler,
in the sieve shaker.
and two to collect the two subsamples.
6.6 Thesievesneedtobeshakenfor15 61min.Attheend
5.3 Sieve Set, No. 20 (850 µm), No. 80 (180 µm) stackable
of the time period remove the sieves. The fraction retained on
sieves with lid and bottom pan. Sieves and bottom pan should
the 20 mesh sieve (+20 mesh fraction) should be reprocessed
be 8.9 cm (3 ⁄2 in.) in height. Sieves conform to Specification
beginning at step 6.3. The fraction retained on the 80 mesh
E11.
sieve (−20/+80 mesh fraction) should be retained for compo-
5.4 Sieve Shaker, provides motion in both horizontal and sitional analysis. The material in the bottom pan is the fines
vertical axes. (−80 mesh). Retain this material for ash analysis.
E1757 − 19
6.7 Repeat6.3–6.6untilallofthemilledmaterialwillpass temperature. Weigh the container and biomass to the nearest
through the 20 mesh sieve. If necessary, combine all of the 0.1 g and record this weight as W.
f
−20/+80 mesh batches. If necessary, combine all of −80 mesh
8.6 For small quantities (<20 g) containing material that
batches. Weigh the combined −20/+80 mesh fraction and the
would not pass through a 20 mesh screen, reduce the particle
combined fines to the nearest 0.1 g. Record the −20/+80 mesh
size of the solid residue by knife-milling the entire sample
fractionweightas Wt andthefinesfractionweightas Wt .
20/80 80
through an intermediate size knife-mill witha1mm screen.
6.8 If multiple sieved samples were combined they must be
8.7 For larger quantities (>20 g) containing material that
uniformlyblendedbacktogetherintoasinglesample.Pourthe
would not pass through a 20 mesh screen, reduce the particle
−20/+80 mesh fraction into the riffle sampler, and then recom-
size for the solids by knife-milling the entire sample and sieve
bine the two subdivided samples in the bottom pans back
according to 6.3 – 6.7.
together. Repeat this division and recombination an additional
8.8 Return the milled sample to the drying oven, maintain-
threetimes.Tocorrectlyusetherifflesampler,thesamplemust
be poured evenly onto all the riffle openings at the same time. ing the temperature at 45 6 3°C. Keep the sample in the
drying oven at 45 6 3°C for at least4h. Allow the samples
A pan, as wide as the riffle opening, should be used. Pour the
tocooltoroomtemperatureinadesiccator.Weigheachsample
sample evenly off the entire side of the pan and not from the
end or the corner, nor from a container such as a jar. to the nearest 0.1 mg and record this mass. After weighing,
return the samples to the drying oven at 45°C for 1 h, cool
6.9 If the total sample needs to be subdivided into smaller
again in the desiccator, and weigh again. Repeat this step until
samples, use the riffler at this time to divide the main sample.
the mass of the samples varies by less than 1% from the
6.10 If the prepared sample is not analyzed immediately
previous weighing.
after sieving and riffling, the sample should be stored in an
air-tight container or sealable polyethylene bag and kept at
9. Report: Preparation Method B
−20°C until needed.
9.1 Calculate the percent of the total solids obtained by
7. Report: Preparation Method A
drying at 45°C:
7.1 Calculate the percent of each fraction in the original,
%T 5 W 2 W / W 2 W 3100% (3)
~ ! ~ !
45 f t i t
whole biomass:
where:
fraction ,% 5 Wt 3100% / Wt 1Wt (1)
~ ! ~ !
20/80 20/80 20/80 80
%T = percent total solids in sample dried at 45°C,
where: W = tare weight of dried container,
t
W = i
...


This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation: E1757 − 01 (Reapproved 2015) E1757 − 19
Standard Practice for
Preparation of Biomass for Compositional Analysis
This standard is issued under the fixed designation E1757; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 This practice covers a reproducible way to convert hardwoods, softwoods, herbaceous materials (such as switchgrass and
sericea), agricultural residues (such as corn stover, wheat straw, and bagasse), wastepaper (such as office waste, boxboard, and
newsprint), cellulosic feedstocks pretreated to improve suitability for fermentation fermentation, cereal grains, cereal grain
fermentation mash, cereal grain fermentation beer, and fermentation residues into a uniform material suitable for compositional
analysis. This practice is intended for samples that need to be dried prior to analysis.
1.2 Milling and sieving actions both produce large amounts of dust. This dust can be a nuisance hazard and irritant. Use
appropriate respiratory protection as needed. If excessive amounts of dust are allowed to become airborne a potential explosion
hazard is possible. Provide appropriate dust control measures as needed.
1.3 The values stated in SI units are to be regarded as the standard. The inch-pound units values given in parentheses are for
information only.after SI units are provided for information only and are not considered standard.
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety safety, health, and healthenvironmental practices and determine the
applicability of regulatory limitations prior to use.
1.5 This international standard was developed in accordance with internationally recognized principles on standardization
established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued
by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
2. Referenced Documents
2.1 ASTM Standards:
E11 Specification for Woven Wire Test Sieve Cloth and Test Sieves
2.2 Other Documents:
AOAC 935.29 Moisture in Malt - Gravimetric Method (AOAC 2005)
NFTA 2.2.2.5 Dry Matter by Oven Drying for 3 hr at 105 °C
3. Terminology
3.1 Definitions of Terms Specific to This Standard:
3.1.1 ambient conditions—conditions, n—a temperature of 20 to 30°C30 °C (68 to 85°F),85 °F), less than 50 % relative
humidity.
3.1.2 beer, n—the mash after it has undergone fermentation and has been deemed complete by virtue of the carbohydrates being
converted into renewable fuel by enzymes and fermenting organisms.
3.1.3 mash, n—a mixture or slurry of water (including recycled water streams) and ground grain.
3.1.4 prepared biomass—biomass, n—biomass that has been prepared according to this practice.
This practice is under the jurisdiction of ASTM Committee E48 on Bioenergy and Industrial Chemicals from Biomass and is the direct responsibility of Subcommittee
E48.05 on Biomass Conversion.
Current edition approved June 1, 2015April 1, 2019. Published July 2015May 2019. Originally approved in 1995. Last previous edition approved in 20072015 as
E1757-01(2007).E1757– 01(2015). DOI: 10.1520/E1757-01R15.10.1520/E1757-19.
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
Available from AOAC International, 2275 Research Blvd., Suite 300, Rockville, MD 20850-3250, http://www.aoac.org.
Available from National Forage Testing Association (NFTA), PO Box 1470, Stuart, FL 34995, https://www.foragetesting.org/.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E1757 − 19
3.1.5 predominantly cellulosic, adj—feedstock that has an average adjusted cellulosic content of 75 %, measured on a dry mass
basis; furthermore, this “adjusted cellulosic content” is the percent of organic (non-ash) material that is cellulose, hemicellulose,
or lignin.
4. Significance and Use
4.1 Preparation Method A—Method suitable for the preparation of large quantities (>20 g) of field collected samples into a form
appropriate for compositional analysis. Woody samples must first be available as chips of a nominal 5 by 5 by 0.6 cm 0.6 cm (2
1 1
by 2 by ⁄4 in.) in.) or less and twigs not exceeding 0.6 cm ( ⁄4 in.) diameter. Herbaceous materials may be processed as whole
straw. It is recommended that wastepaper should be shredded into pieces less then 1 cm ( ⁄2 in.) wide. Furthermore, it is
recommended that twigs, straw, and wastepaper should not exceed 61 cm (24 in.) in length to facilitate handling.
4.2 Preparation Methods B and C—Test methods Methods are suitable for very moist feedstocks, samples that would not be
stable during prolonged exposure to ambient conditions, or for drying materials when room conditions deviate from the ambient
conditions described in 3.1.1. These test methods are also suitable for handling small samples of biomass (<20 g). The drying step
is done in a convection oven at 45°C45 °C (Test Method B) or by lyophilization (Test Method C).
4.3 This practice is Preparation Methods A, B, and C are not intended for materials that will already pass through a 20 mesh
sieve or that cannot be dried by the described methods to a total solids content of greater thenthan 85 %, based on an oven dried
weight.
4.4 This practice Preparation Method A will separate the milled material into two fractions, a −20/+80 mesh fraction and a −80
mesh fraction.
4.4.1 Extraneous inorganic materials will accumulate in the -80−80 mesh fraction and it should be analyzed independently from
the -20/+80−20/+80 mesh fraction. Weighted results from the two fractions can then be combined to obtain results for materials
on an "as received" basis.
NOTE 1—During analysis, the very fine consistency of the -80−80 mesh fraction may cause problems in filtering operations and should be handled
appropriately.
4.5 Preparation Method D—Method suitable for cereal grains, cereal grain fermentation mash, cereal grain fermentation beer,
and cereal grain fermentation residues that are generally stable.
4.6 Preparation Method E—Method suitable for cereal grains, cereal grain fermentation mash, cereal grain fermentation beer,
and cereal grain fermentation residues that are biologically or enzymatically active.
5. Apparatus
5.1 Balance, sensitive to 0.1 g.
5.2 Riffle Sampler with Pans—A manual sample divider that splits the milled biomass into a number of alternate elements. Riffle
1 1
divisions should be in the range from 6.4 mm to 12.7 mm ( ⁄4 in. to ⁄2 in.) with at least twenty-four24 riffle openings across the
top. The feed chute and riffles should have a slope of at least 60°. Three pans are needed, one to pour the sample into the riffler,
and two to collect the two subsamples.
5.3 Sieve Set, No. 20 (850 μm), No. 80 (180 μm) stackable sieves with lid and bottom pan. Sieves and bottom pan should be
8.9 cm (3 ⁄2 in.) in height. Sieves conform to Specification E11.
5.4 Sieve Shaker, provides motion in both horizontal and vertical axes.
5.5 Knife Mill,Sample Mills, for grinding samples.
5.5.1 Sample grinders must be capable of grinding samples to a sufficiently fine powder.
5.5.1.1 Discussion—Many analytical test methods have specific particle size requirements. For example, when analyzing for
starch, a particle size of less than 500 μm on average is typically required.
5.5.2 For materials that are predominantly cellulosic and fermentation residues from predominantly cellulosic materials that
have been prepared in accordance with Methods A, B, or C, a knife cutting style mill is recommended.
NOTE 2—A Wiley Mill, size No. 4 with a 2-mm2 mm screen, is suitable for samples >20 g, and the intermediate model, with 1-mm1 mm screen, is
suitable for samples <20 g that will not be sieved.
5.5.3 For cereal grains, cereal grain fermentation mash, cereal grain fermentation beer, and cereal grain fermentation residues
that have been prepared in accordance with Methods D or E, an impact style mill is recommended.
5.6 Drying Oven, 456 3° (Test Method B only).capable of maintaining temperatures between 45 and 55 °C (Test Methods B
and D).
5.7 Freeze-Drier—System with vacuum chamber and pump capable of maintaining a pressure of <1 torr and a cold finger in
the chamber capable of maintaining a temperature of −50°C−50 °C (Test MethodMethods C only).and E).
E1757 − 19
6. Preparation: TestProcedure: Preparation Method A
6.1 This test method is suitable for larger quantities (>20 g) of biomass as described in 4.1.
6.2 The raw biomass material should be spread out on a suitable surface to air dry prior to any milling. Do not pile the material
deeper then 15 cm. Turn the material at least daily to ensure even drying and minimize molding of material that may contain
significant amounts of moisture. The material is considered dried when the change in weight is less than 1 % in 24 h.
6.3 The air-dried material is fed into the knife-mill and is milled to pass through a 2 mm screen in the bottom of the mill. Milled
wastepaper does not need to be sieved and can be used directly for composition analysis. Milled biomass materials should be sieved
as follows.
6.4 The sieving is set up by stacking the sieves in the following order, starting at the bottom: start with the bottom pan, next
stack the 80 mesh sieve, followed by the 20 mesh sieve. Milled material is placed no more then 7 cm deep in the 20 mesh sieve.
6.5 Place the cover on the sieve stack and secure the stack in the sieve shaker.
6.6 The sieves need to be shaken for 15 6 1 min. At the end of the time period remove the sieves. The fraction retained on the
20 mesh sieve (+20 mesh fraction) should be reprocessed beginning at step 6.3. The fraction retained on the 80 mesh sieve
(−20/+80 mesh fraction) should be retained for compositional analysis. The material in the bottom pan is the fines (−80 mesh).
Retain this material for ash analysis.
6.7 Repeat 6.3 – 6.6 until all of the milled material will pass through the 20 mesh sieve. If necessary, combine all of the
-20/+80−20/+80 mesh batches. If necessary, combine all of -80−80 mesh batches. Weigh the combined −20/+80 mesh fraction and
the combined fines to the nearest 0.1 g. Record the −20/+80 mesh fraction weight as Wt and the fines fraction weight as Wt .
20/80 80
6.8 If multiple sieved samples were combined they must be uniformly blended back together into a single sample. Pour the
−20/+80 mesh fraction into the riffle sampler, and then recombine the two subdivided samples in the bottom pans back together.
Repeat this division and recombination an additional three times. To correctly use the riffle sampler, the sample must be poured
evenly onto all the riffle openings at the same time. A pan, as wide as the riffle opening, should be used. Pour the sample evenly
off the entire side of the pan and not from the end or the corner, nor from a container such as a jar.
6.9 If the total sample needs to be subdivided into smaller samples, use the riffler at this time to divide the main sample.
6.10 If the prepared sample is not analyzed immediately after sieving and riffling, the sample should be stored in an air-tight
container or sealable polyethylene bag and kept at −20°C−20 °C until needed.
7. Report: Preparation Method A
7.1 Calculate the percent of each fraction in the original, whole biomass:
fraction , %5 Wt 3100 % / Wt 1Wt (1)
~ ! ~ !
20/80 20/80 20/80 80
where:
Wt = weight of −20/+80 mesh fraction, g, and
20/80
Wt = weight of fines fraction, g.
fraction , %5 100 %2fraction % (2)
80 20/80
7.2 The mass fraction is used to weigh analytical results when the two fractions differ in composition, but the results are to be
reported on the original, whole biomass.
8. Procedure: Preparation Method B
8.1 This test method is suitable for very wet biomass that is at risk for mold growth during drying, for wet pretreated biomass
or fermentation residues (sludges) that might degrade if allowed to stand for prolonged periods, or for drying biomass when the
prevailing conditions do not meet the ambient conditions defined in 3.1.1.
8.2 Dry a suitable container to hold the biomass at 45 6 3°C3 °C for a minimum of 3 h. Remove the container, place the
container in a dessicatordesiccator, and allow to cool to room temperature. Weigh the container to the nearest 0.1 g and record this
weight as W .
t
8.3 Place the biomass material into the dried container. Do not pile the material deeper than 1 cm. Weigh the container and
biomass to the nearest 0.1 g and record this weight as W .
i
8.4 Place the container into a drying oven ma
...

Questions, Comments and Discussion

Ask us and Technical Secretary will try to provide an answer. You can facilitate discussion about the standard in here.

Loading comments...