table 1 - physical properties of fine and coarse aggregate (astm
TRANSCRIPT
Center for
By-Products
Utilization
DEVELOPMENT OF CLSM USING COAL ASH AND
WOOD ASH, A SOURCE OF NEW POZZOLANIC
MATERIALS
By Tarun R. Naik, Rudolph N. Kraus, Shiw S. Singh, and
Parisha P. Chanodia
Report No. CBU-2000-36
REP-420
January 2001
To be submitted to the ACI Materials Journal.
Department of Civil Engineering and Mechanics
College of Engineering and Applied Science
THE UNIVERSITY OF WISCONSIN - MILWAUKEE
1
CLSM CONTAINING MIXTURES OF COAL ASH AND A NEW POZZOLANIC
MATERIAL
Tarun R. Naik, Rudolph N. Kraus, Shiw S. Singh, Parisha P. Chanodia
ABSTRACT
Significant amount of ash is generated from burning wood with supplementary fuels such as coal,
oil, natural gas, and coke by pulp and paper mills and wood-products manufacturers. Thus, the
ash generated from such facilities is a mixture of wood ash and other ashes generated from such
supplemental fuels. In this investigation, such wood ash is referred to as a combined-fuel ash
(CFA). This investigation was carried out to develop Controlled Low-Strength Materials
(CLSM) mixtures using various sources of CFAs. Three different series of CLSM mixtures were
manufactured using five sources of CFAs. Each series of CLSM mixtures was designed for a
different long-term compressive strength, <0.7 MPa (<100 psi), 0.7 to 3.4 MPa (100 to 500 psi),
and 3.4 to 8.3 MPa (500 to 1,200 psi). All CLSM mixtures were tested for flow, bleedwater,
settlement, shrinkage and cracking, setting characteristics, density, compressive strength, and
permeability. The results revealed that CLSM, meeting ACI 229 requirements, can be
manufactured using substantial amounts of CFAs.
Key words: controlled low-strength materials; flowable fill; CLSM; backfill; wood ash;
combined fuel ash; flowable matter
2
Prof. Tarun R. Naik is Director of the UWM Center for By-Products Utilization, Department of
Civil Engineering and Mechanics at the University of Wisconsin-Milwaukee. He is a member of
ACI Committee 232, "Fly Ash and Natural Pozzolans in Concrete", Committee 228,
"Nondestructive Testing of Concrete", Committee 214, "Evaluation of Results of Strength Tests
of Concrete", and Committee 123, "Research". He was also chairman the ASCE technical
committee "Emerging Materials" (1995-2000).
ACI member Rudolph N. Kraus is Assistant Director, UWM Center for By-Products
Utilization, Milwaukee, WI. He has been involved with numerous projects on the use of by-
product materials including utilization of used foundry sand and fly ash in CLSM (Controlled
Low Strength Materials), evaluation and development of CLSM, evaluation of lightweight
aggregates, and use of by-product materials in the production of dry-cast concrete products.
Dr. Shiw S. Singh is Research Associate, UWM Center for By-Products Utilization, Milwaukee,
WI. He completed his Ph.D. from University of Wisconsin-Madison in biomechanics. His
research interests include solid mechanics, strength and durability of composite materials
including cement-based materials, and remedial investigation of sites contaminated with
hazardous materials.
Parisha P. Chanodia is pursuing her Master of Science degree in Structural Engineering at the
University of Wisconsin-Milwaukee. Her research interests include by-products utilization in
cement-based materials.
3
INTRODUCTION
Wood ash is usually generated by saw mills, pulp mills, and the wood-products industry, by
burning a combination of wood products, such as bark, twigs, knots, chips, etc. with other
supplementary fuels such as coal, oil, natural gas, and coke to generate electricity and/or steam
required for their manufacturing processes. Therefore, the resulting ash is sometimes referred to
as combined-fuel ash (CFA). A majority of such CFAs generated in the USA is either landfilled
or applied on land as a soil supplement. Landfilling is becoming very restrictive and costly while
land application is also restricted because of the presence of undesirable elements and/or high
alkalinity. Some studies [1-8] have been reported toward evaluating physical and chemical
properties of wood ash or CFAs. Based on these properties, a number of constructive use options
such as pollution control [3], land application [9,10,11], construction materials [13,14], have
been reported. However, most of these applications consume very limited amounts of CFAs due
to low-volume uses resulting from environmental restrictions or low economic benefits. More
recently, Naik and his colleagues [8,15] indicated that large amounts of CFAs can be used in
cement-based materials such as CLSM, low and medium-strength concrete, masonry products,
roller-compacted concrete (RCC) pavement, road base materials, blended cements, etc.
However, technology for manufacturer of these materials using CFAs is yet to be established.
Large volumes of CFAs would be consumed in the manufacture of CLSM. Depending upon
intended use, CLSM can be proportioned for compressive strength up to 8.3 MPa (1,200 psi) at
the age of 28 days. CLSM can be used for foundations, bridge abutments, buildings, retaining
4
walls, utility trenches, etc. as backfill; as embankments, grouts, abandoned tunnels and mine
fillings for stabilization of such cavities, etc. CLSM mixture flows like a liquid, and supports
like a solid due to its self-setting and hardening behavior. It can typically harden within a few
hours of placement. For excavatable CLSM, mixtures should be proportioned to attain
compressive strength in the range of 0.4 to 0.7 MPa (50 to 100 psi) at the 28-day age. CLSM can
provide cost-effective alternatives to conventional compacted granular backfill or structural fill
materials (soil or other granular materials). This is primarily due to lower cost of labor and
significantly reduced time required for placement compared to the cost of placing and
compacting conventional granular fill materials. The placement of conventional granular fill
material requires testing after each lift of 305 to 310 mm (12 to 24 in.), while this is not required
for CLSM due to its self-compacting behavior. Since CLSM mixture exhibits very low to
negligible settlement after hardening, it provides better support for overlying structures (and/or
pavements) and avoids the damage associated with the base/support settlement.
Substantial amount of work has been done concerning the use of coal ash in the manufacture of
CLSM [16-20]. However, activities have not been reported concerning the use of CFAs in the
manufacture of CLSM. Therefore, this investigation was carried out to develop CLSM mixtures
for various applications incorporating high volumes of CFAs derived from various sources.
EXPERIMENTAL PROGRAM
Three series (L, M, and H) of experiments were designed and conducted. Each of these series
was developed to obtain a different long-term compressive strength levels at later ages (28 to 91
5
days). CLSM mixtures developed for the project were 0.3 to 0.7 MPa (50 to 100 psi) for Series
L, low-strength mixtures; 0.7 to 3.4 MPa (100 to 500 psi) for Series M, medium-strength
mixtures; and 3.4 to 8.3 MPa (500 to 1200 psi) for Series H, high-strength mixtures.
MATERIALS
Materials utilized for this project consisted of CFA, cement, fine aggregate, coarse aggregate, and
coal fly ash. Each material was characterized for physical and chemical properties in accordance
with the appropriate ASTM standards. The detailed data on properties of these materials are
reported elsewhere [14]. Summary data is provided in Tables 1 and 2.
Five different sources of CFA were used for this project. Each CFA was characterized for
physical properties such as fineness (ASTM C 430), strength activity index with cement (ASTM
C 109), water requirement (ASTM C 109), autoclave expansion (ASTM C 151), and specific
gravity (ASTM C 188). Each CFA was also tested for chemical properties which included
determination of oxides, basic chemical elements, and mineralogy. The physical and chemical
properties of CFA are given in Tables 1 and 2, respectively.
One source of fine aggregate was utilized in this investigation for the high-strength (Series H)
CLSM mixtures. Physical properties of the sand were determined per ASTM C 33 requirements
for the following properties: unit weight (ASTM C 29), specific gravity and absorption (ASTM
6
C 128), fineness (ASTM C 136), material finer than #200 sieve (ASTM C 117), and organic
impurities (ASTM C 40).
Type I cement was used throughout this investigation. Cement was tested per ASTM C 150
requirements for air content (ASTM C 185), fineness (ASTM C 204), autoclave expansion
(ASTM C 151), compressive strength (ASTM C 109), time of setting (ASTM C 191), and
specific gravity (ASTM C 188).
All CLSM mixtures were batched in the laboratory of the UWM Center for By-Products
Utilization. The low-strength CLSM (Series L) mixtures consisted of CFA, ASTM Type I
cement, and water. The medium-strength CLSM (Series 2) mixtures consisted of CFA, an
increased amount of ASTM Type I cement, and water. The high-strength CLSM (Series H)
mixtures consisted of CFA, ASTM Type I cement, sand, and water. These CLSM mixtures were
proportioned to maintain a practical value of flow in the range of approximately 250 mm 50
(10 2 in.).
MANUFACTURING OF CLSM
All CLSM ingredients were manually loaded in a 2.7 m3 (9 ft
3) rotating drum concrete mixer.
The required amount of cement together with one-half the specified quantity of fly ash or sand
was loaded into the mixer and mixed for three minutes. Three-quarters of the specified water
was then added to the mixer and then mixed for an additional three minutes. The remaining CFA
7
or sand, and water was added to the mixer and then mixed for five more minutes. Additional
water was added in the mixture as needed for achieving the desired flow, prior to discharging the
CLSM for testing. Whenever additional water was added to obtain the specified fresh CLSM
characteristics, the CLSM mixture was mixed for an additional five minutes. The resulting
mixture was then discharged into a pan for further testing and evaluation.
SPECIMEN PREPARATION AND TESTING
Fresh CLSM mixtures were tested for properties such as air content (ASTM D 6023), flow
(ASTM D 6103), unit weight (ASTM D 6023), and setting (ASTM D 6024). Ambient air
temperature was also measured and recorded. For each mixture, CLSM test specimens were
prepared for compressive strength (ASTM D 4832), water permeability (ASTM D 5084), and
setting and hardening tests. Compressive strength of 150 x 300-mm (6 x 12-in) cylindrical
specimens was determined at the 3-, 7-, 14-, 28-, and 91-day ages. Permeability was tested at the
ages of 28 and 91 days using 100 x 100-mm (4 x 4-in) cylindrical specimens. The amount of
bleed water and level of the solids (settlement) of CLSM mixtures were also measured in a 150 x
300-mm (6 x 12-in.) cylinder. All test specimens were cast in accordance with ASTM D 4832.
These specimens were typically cured for one day in their molds in the UWM-CBU laboratory at
about 24 2C (75 2F). These specimens were then demolded and placed in a standard
moist-curing room maintained at 100% R.H. and 23 1 C (73 2 F), temperature until the
time of test (ASTM D 4832). The setting characteristics of the CLSM mixtures were determined
using specimens cast in molds, approximately 300 x 300 x 75-mm (12 x 12 x 3-in.). The CLSM
8
was cast directly into the mold and left uncovered for the entire measurement period. The setting
characteristics were determined in accordance with ASTM D 6024. This method measures
diameter of an impression by a spherical steel ball of the Kelly Ball apparatus. Per ASTM D
6024, a CLSM mixture becomes suitable to support load when a maximum diameter of
impression of 76 mm (3 in.) is reached. This value was considered too high for the cylinders to
be safely demolded without damaging the test specimens. Based upon comparing the setting
consistency of the CLSM, as cast in the cylinder molds, a more reasonable value was considered
to be approximately 50 mm (2 in.).
RESULT AND DISCUSSION
Fresh CLSM Properties
Mixture proportions and fresh CLSM properties for Series L CLSM mixtures are given in Table
3. Flow of all the Series L mixtures were approximately 250 mm (10 in.). Unit weight of the
mixtures varied between 1,195 to 1,724 kg/m3 (74.6 to 107.6 lb/ft
3). Mixture 3-L (CFA Source
W-3) had the highest unit weight of 1,726 kg/m3 (107.6 lb/ft
3) while Mixture 2-L (CFA Source
W-2) exhibited the lowest unit weight of 1,195 kg/m3 (74.6 lb/ft
3). The remaining mixtures had
unit weight of approximately 1,323 to 1,371 kg/m3 (82.6 to 85.6 lb/ft
3). The unit weight of the
mixtures agrees with the physical properties of the CFA materials; the mixture containing CFA
with the lowest specific gravity also produced the lowest CLSM unit weight.
9
Mixture proportions and fresh properties for Series M mixtures are shown in Table 4. Similar to
the Series L mixtures, unit weight of the mixtures varied in agreement with the specific gravity of
the CFA material. The water demand for the Series M mixtures was similar to that for the Series
L mixtures. The flow of the Series M mixtures was 265 5 mm (10.5 0.25 in.). The unit
weight followed the same general trend as observed for the Series L mixtures. This was expected
since only the quantity of cement was increased for these mixtures compared to the Series L
mixtures.
Mixture proportions and fresh properties of the Series H mixtures are given in Table 5. These
mixtures contained concrete sand to develop relatively high-strength. The water demand to
obtain the design flow of approximately 250 mm (10 in.) decreased relative to Series L mixtures
which did not contain sand. The required amount of water was approximately 356 to 534 kg/m3
(600 to 900 lb/yd3) for the Series H mixtures, compared to 475 to 712 kg/m
3 (800 to 1,200
lb/yd3) for the Series L or Series M mixtures without fine aggregate. Unit weights of the Series
H mixtures were also significantly higher than the lower-strength mixtures. The values of unit
weight ranged from 1,602 to 1,735 kg/m3 (100 to 127 lb/ft
3) for high-strength mixtures and from
1,602 to 1,762 kg/m3 (75 to 110 lb/yd
3) for the low-strength mixtures. The increase in the unit
weight was attributed to the higher specific gravity of the sand relative to the CFA.
Bleedwater is given as the depth of water present at the top of a 150 x 300 mm (6 x 12 in.)
cylinder filled with CLSM. The bleedwater provides an indication of the cohesiveness of the
CLSM mixture. Minimizing the amount of bleedwater is desirable to minimize potential
10
leaching of elements and escape of bleedwater from the excavation being filled. Bleedwater
measurements of the low-strength, Series L, CLSM mixtures showed that initially, bleedwater
accumulated to a depth of 1.5 to 9.5 mm (1/16 to 3/8 in.), but quickly dissipated after 4 to 8 hours
(Table 6). Table 7 shows that the bleedwater of the medium-strength, Series M, CLSM mixtures.
Bleedwater after one hour ranged from zero to 12.5 mm (1/2 in.) in depth. The bleedwater also
did not dissipate as quickly as for the low-strength CLSM mixtures. Mixtures 1-M, 4-M and 5-
M still had 9.5 to 11.1 mm (1/8 to 7/16 in.) of bleedwater remaining after 24 hours. Except
mixtures 4-H and 5-H, Series H CLSM mixtures did not exhibit any bleedwater beyond 24 hours
(Table 8)
SETTLEMENT
The settlement of the CLSM is the measured level of the solidified CLSM using the top of a 150
x 300 mm (6 x 12 in.) cylinder as the reference point. The settlement measurements would
indicate any potential to shrink or expand and the amount of visible cracking on the surface
which may lead to the inflow of water into the CLSM. The settlement of the low-strength, Series
L CLSM, mixtures showed a slight shrinkage of Mixtures 1-L, and 5-L, while the level of
Mixture 4-L remains relatively constant (Table 9). Two of the mixtures exhibited expansion,
Mixtures 2-L and 3-L. Mixture 3-L showed a slight expansion of approximately 9.5 mm (3/8 in.)
which offset the initial settlement of the CLSM. A large expansion occurred for Mixture 2-L.
Mixture 2-L (CFA Source W-2) visibly expanded as soon as placed into the cylinder molds and
expanded over 25 mm in one hour. Precautions must be taken when using Mixture 2-L due to
11
the significant expansion. Placing this mixture in a confined volume could lead to internal
pressure that would have to be accounted for in the design. However, the expansive
characteristics may be of use when filling a space such as an abandoned tank or pipeline to assure
that no voids remain.
The settlement data of medium-strength CLSM mixtures are given in Table 10. The settlement
or expansion of the medium-strength Series M mixtures was lower compared to the low-strength,
Series L CLSM except for Mixture 2-M, which had increased expansion. This mixture used the
same source of CFA as used in Mixture 2-L, Source W-2. The increased expansion of this
mixture may indicate a reaction with the cement since the cement content of 2-M mixture has
significantly increased over that used for Mixture 2-L.
The settlement data of the high-strength CLSM is given in Table 11. These mixtures show
settlement except for Mixture 2-H, containing CFA Source W-2, which now exhibited a slight
shrinkage rather than expansion. This mixture has a high cement content, 205 kg/m3 (345
lb/yd3), but sand has been introduced into the mixture. The presence of sand in the mixture may
provide a confining effect for the expansion product since the unit weight of the CLSM mixture
has increased over 481 kg/m3 (30 lb/ft
3) from that of Mixture 2-L or 2-M.
Setting and Hardening Characteristics
12
The setting characteristics of the CLSM mixtures are shown in Figs. 1 through 3. Setting of the
CLSM mixtures have been established for two different levels of imprint diameters of 50 mm (2
in.) and 25 mm (1 in.). Setting of the low-strength Series L mixtures (Fig. 1) ranged from
approximately 24 to 96 hours to obtain a diameter of 50 mm (2 in.) to approximately 24 to over
60 hours to obtain a diameter of imprint of 25 mm (1 in.). Mixture 5-L exhibited a significant
delay in setting from the 50 mm (2 in.) to the 25 mm (1 in.) level, almost 200 hours. Other
mixtures set from the 50 mm (2 in.) to the 25 mm (1 in.) imprint diameter in approximately 60
hours. The source of CFA used for Mixture 5-L (Source W-5) seemed to delay the final setting
of the CLSM.
The setting characteristics of the medium-strength Series M mixtures are given in Fig. 2. As
expected, the time of setting of the CLSM to obtain a 50 mm (2 in.) imprint diameter was less
than the Series L mixtures, approximately 12 to 60 hours versus 24 to 96 hours. Similar to the
Series L, the time to reach the 25 mm (1 in.) imprint diameter was much longer for the mixture
containing CFA Source W-5, Mixture 5-M, than for the other medium-strength CLSM mixtures.
The medium-strength Series M mixtures set to the 25 mm (1 in.) diameter in 40 to 75 hours,
while Mixture 5-M set to the same level in over 240 hours. The time of setting for the high-
strength Series H mixtures (Fig. 3) to the 50 mm (2 in.) imprint level was 10 to 20 hours while
setting time to reach the 25 mm (1 in.) imprint level was 24 to 40 hours for Mixtures 1-H through
4-H. Again the CLSM mixture with CFA Source W-5 (Mixture 5-H) had the longest setting time
to reach the 25 mm (1 in.) level, over 72 hours. These setting results indicate that for CLSM
13
incorporating CFA Source W-5, an accelerator should be used to control the final setting time to
acceptable levels.
Compressive Strength of CLSM Mixtures
The compressive strength data for the low-strength CLSM mixtures are given in Table 12. The
compressive strength results at the age of 28 days indicate that four of the mixtures 1-L, 2-L, 3-L,
and 4-L achieved satisfactory strength levels. At 28 days these mixtures had compressive
strengths of 0.2 to 0.3 MPa (35 to 50 psi). Mixture 5-L (CFA Source W-5) exhibited
compressive strength ranging from 0.5 to 1.2 MPa (75 to 170 psi) at 28 days, exceeding the
design strength range of 0.7 MPa (100 psi). This indicates that the amount of cement used for
Mixture 5-L, 95 kg/m3 (160 lb/yd
3), should be reduced for future mixtures to maintain long-term
compressive strengths below 0.7 MPa (100 psi).
The compressive strength data for the medium-strength Series M mixtures are given in Table 13.
These mixtures were designed and proportioned to achieve compressive strengths of
approximately 0.7 to 3.4 MPa (100 to 500 psi). The compressive strengths of all mixtures at the
age of 28 days were in the range of approximately 0.7 to 1.4 MPa (100 to 200 psi). The
compressive strength of mixture 3-M at the age of 91 days increased to 5.3 MPa (765 psi) while
other mixtures had compressive strengths of 1.1 to 2.7 MPa (165 to 390 psi). The strength
increase in Mixture 2-M indicates that a later age reaction occured in the CLSM when using this
source of CFA. This mixture has the same source of CFA (W-2) that exhibited expansion in the
14
settlement tests. This CFA source, when used in CLSM, should be carefully evaluated for
applications where setting and long-term strengths gains are not of concern.
The compressive strength data for the high-strength Series H CLSM mixtures are shown in Table
14. All Series H Mixtures exhibited a significant increase in compressive strength between the
ages of 28 and 91 days. Mixtures 1-H, 3H, 4-H, and 5-H achieved 91-day compressive strengths
that met the design strength range. Mixture 2-H (CFA Source W-2) showed a large increase in
compressive strength between 28 and 91 days, 1.6 to 8.6 MPa (230 to 1250 psi). This
compressive strength exceeded the maximum specified for CLSM and indicates that the amount
of cement could be reduced slightly. Similar to the other Series L and Series M mixtures
containing CFA Source W-2, the long-term increase in compressive strength should be evaluated
and accounted for when designing fill applications.
Water Permeability of CLSM Mixtures
The permeability of the Series L mixtures are shown in Table 15. The permeability value varied
from 15 x 10-6
cm/s to 110 x 10-6
cm/s at the age of 28 days. The permeability data for Series M
CLSM mixtures are shown in Table 16. The permeability values varied from 5 x 10-6
cm/s to
510 x 10-6
cm/s at the age of 28 days. The permeability value decreased substantially at the age
of 91 days due to the increase in the maturity of concrete resulting from increased amount of C-
S-H formation in the CLSM matrix and thus improving the microstructure of the material. At the
15
age of 91 days, permeability varied from 0.1 x 10-6
cm/s to 350 x 10-6
cm/s. Mixtures for 2-M
(CFA Source W-2) exhibited the highest permeability.
The permeability data for the H CLSM Mixtures are shown in Table 17. The permeability
decreased with age due to the densification in the material. Series H CLSM specimens mixtures
attained permeability ranging from 2 x 10-6
cm/s to 120 x 10-6
cm/s at the age of 28 days and
from 1 x 10-6
cm/s to 38 x 10-6
cm/s at the age of 91 days.
CONCLUSION
Based on data collected in this investigation, the following conclusions may be drawn.
The physical and chemical properties of the combined fuel ashes were significantly
influenced by their source.
Although all combined fuel ashes used in this work did not conform to the requirements of
ASTM C 618 Class C or Class F coal fly ash, they are suitable for use as a primary ingredient
of flowable CLSM.
16
Fresh CLSM unit weight generally decreased when CFA content or water to cementitious
materials ratio was increased.
Compressive strength of CLSM mixtures increased with age. CLSM mixtures meeting ACI
229 requirements can be proportioned using large amounts of CFA for strength levels up to
8.3 MPa (1,200 psi) at the age of 28 to 91 days.
The permeabilities of the CLSM mixtures made with CFA decreased with increasing age and
compressive strength. The permeability values of the CLSM mixtures incorporating CFA
was generally lower than that normally observed for compacted clay.
ACKNOWLEDGEMENT
The authors express their deep sense of gratitude to the UWS/RMDB Solid Waste Recovery
Research Program, Madison, WI, and its Program Manager Eileen Norby. Other sponsors of this
research project were: Consolidated Papers, Inc. (Stora Enso North America), Wisconsin
Rapids, WI; National Council for Air and Stream Improvement (NCASI), Kalamazoo, MI;
Weyerhaeuser Company, Rothschild, WI and Tacoma, WA; Wisconsin Electric Power Company,
Milwaukee, WI; and Wisconsin Public Service Corporation, Green Bay, WI. Special
appreciation is expressed to Ms. Lori Pennock and Bruce Ramme for their interest in this project
and monitoring project progress and achievements. Thanks are also due to the UWM Center for
17
By-Products Utilization laboratory staff for their contributions in gathering and analysis of test
data for this project.
The Center was established in 1988 with a generous grant from the Dairyland Power
Cooperative, La Crosse, WI; Madison Gas and Electric Company, Madison, WI; National
Minerals Corporation, St. Paul, MN; Northern States Power Company, Eau Claire, WI;
Wisconsin Electric Power Company, Milwaukee, WI; Wisconsin Power and Light Company
(Alliant Energy), Madison, WI; and, Wisconsin Public Service Corporation, Green Bay, WI.
Their financial support, and support from the Manitowoc Public Utilities, Manitowoc, WI is
gratefully acknowledged.
LIST OF REFERENCES
1. Etiegni, L., “Wood Ash Recycling and Land Disposal,” Ph.D. Thesis, Department of Forest
Products, University of Idaho at Moscow, Idaho, USA, June 1990, 174 pages.
2. Etiegni, L., and Campbell, A. G., “Physical and Chemical Characteristics of Wood Ash,"
Bioresource Technology, Elsevier Science Publishers Ltd., England, UK, Vol. 37, No. 2,
1991, pp.173-178.
18
3. National Council for Air and Stream Improvement, Inc. (NCASI), “Alternative
Management of Pulp and Paper Industry Solid Wastes,” Technical Bulletin No. 655,
NCASI, New York, NY, November 1993, 44 pages.
4. Campbell, A. G., “Recycling and Disposing of Wood Ash,” TAPPI Journal, TAPPI Press,
Norcross, GA, Vol. 73, No. 9, September 1990, pp.141-143
5. Mishra, M. K., Ragland, K. W., and Baker, A. J., “Wood Ash Composition as a Function of
Furnace Temperature,” Biomass and Bioenergy, Pergamon Press Ltd., UK, Vol. 4, No. 2,
1993, pp. 103-116.
6. Steenari, B. M., and Lindqvist, O., “Co-combustion of Wood with Coal, Oil, or Peat-Fly
Ash Characteristics,” Department of Environmental Inorganic Chemistry, Chalmers
University of Technology, Goteborg, Sweden, Report No. ISSN 0366-8746 OCLC
2399559, Vol. No. 1372, 1998, pp. 1-10.
7. Steenari, B. M., “Chemical Properties of BC Ashes,” Report No. ISBN 91-7197-618-3,
Department of Environmental Inorganic Chemistry, Chalmers University of Technology,
Goteborg, Sweden, April 1998, 72 pages.
19
8. Naik, T. R., “Tests of Wood Ash as a Potential Source for Construction Materials,” Report
No. CBU-1999-09, Department of Civil Engineering and Mechanics, University of
Wisconsin-Milwaukee, Milwaukee, August 1999, 61 pages.
9. Meyers, N. L., and Kopecky, M. J., “Industrial Wood Ash as a Soil Amendment for Crop
Production,” TAPPI Journal, TAPPI Press, Norcross, GA, 1998, pp. 123-130.
10. Nguyen, P., and Pascal, K. D., “Application of Wood Ash on Forestlands: Ecosystem
Responses and Limitations,” Proceeding of the 1997 Conference on Eastern Hardwoods,
Resources, Technologies, and Markets, Forest Product Society, Madison, WI, April 21-23,
1997, pp. 203.
20
11. Bramryd, T. and Frashman, B., “Silvicultural Use of Wood Ashes – Effects on the Nutrient
and Heavy Metal Balance in a Pine (Pinus Sylvestris, L.) Forest Soil,” Water, Air and Soil
Pollution Proceeding of the 1995 5th
International Conference on Acidic Deposition:
Science and Policy, Acid Reign ’95, Part 2, Kluwer Academic Publishers, Dordrecht
Netherland, Vol. 85, No. 2, June 26-30, 1995, pp. 1039-1044.
12. Naylor, L. M., and Schmidt, E. J., “Agricultural Use of Wood Ash as a Fertilizer and
Liming Material,” TAPPI Journal, TAPPI Press, Norcross, GA, October 1986, pp. 114-119.
13. Mukherji, S. K., Dan, T. K., and Machhoya, B. B., “Characterization and Utilization of
Wood Ash in the Ceramic Industry,” International Ceramic Review, Verlag Schmid GmbH,
Freiburg, Germany, Vol. 44, No. 1, 1995, pp. 31-33.
14. Kraus, R.N., and Naik, T.R., “Use of Wood Ash for Structural Concrete and Flowable
CLSM,” Report No. CBU-2000-31, UWM Center for By-Products Utilization, University
of Wisconsin– Milwaukee, October 2000, 117 pages.
15. Naik, T. R., Ramme, B. W., and Kolbeck, H. J.,” Filling Abandoned Underground
Facilities with CLSM Fly Ash Slurry”, ACI Concrete International: Design and
Construction, Vol. 12, No. 7, July 1990, pp. 1 - 7.
21
16. Naik, T. R., Sohns, L. E., and Ramme, B. W., "Controlled Low Strength Material Produced
with High-Lime Fly Ash," Proceedings of the Ninth ACAA International Ash Utilization
Symposium, Orlando, FL, January 1991, pp. 9-1 - 9-18.
17. Ramme, B. W., Naik, T. R., and Kolbeck, H. J., "Use of CLSM Fly Ash Slurry for
Underground Facilities," ASCE Proceedings on Utilization of Industrial By-Products for
Construction Materials, October 1993, pp. 41 - 51.
18. Naik, T. R. and Singh, S. S. “Permeability of Flowable Slurry Materials Containing
Foundry Sand and Fly Ash," ASCE Journal of Geotechnical and Geoenvironmental
Engineering, May 1997, pp. 446 - 452.
19
Table 1 - Physical Properties of CFAs
TEST
PARAMETER
W-1
W-2
W-3
W-4
W-5
ASTM C 618
SPECIFICATIONS
CLASS
C
CLASS
F
CLASS
N Retained on
No.325 sieve (%)
23
60
90
40
12
34 max
34 max
34 max
Strength Activity
Index with Cement
(% of Control)
3-day
7-day
28-day
88.4
84.2
88.3
38.4
39.4
33.6
102.0*
83.3*
78.7*
53.8
59.3
59.4
112.3
72.0
67.0
75 min
75 min
75 min
75 min
75 min
75 min Water
Requirement (% of
Control)
115
155
115*
126
130
105
max
105
max
115
Autoclave
Expansion (%)
0.2
0.5
-0.63*
-0.22
0.12
±0.8
±0.8
0.8
max Unit Weight,
kg/m3 (lb/ft3)
545
(34.0)
412
(25.7)
1376
(85.9)
509
(31.8)
162
(10.1)
-
-
-
Specific Gravity
2.26
2.41
2.60
2.26
2.33
-
-
-
Variation from
Mean (%)
Fineness
Specific Gravity
N.A.
0.4
N.A.
0.4
N.A.
N.A.
N.A.
0.7
N.A.
0.1
5 max
5 max
5 max
5 max
5 max
5 max
*Material passing No. 100 (150 um) sieve was used for this test.
20
Table 2 - Analysis for Oxides, SO3, and Loss on Ignition for CFAs
OXIDES, SO3, AND LOSS ON IGNITION ANALYSIS, (%)
Analysis
Parameter
W-1
W-2
W-3
W-4
W-5
ASTM C-618 Requirements
Class C
Class F
Class N
Silicon Dioxide,
SiO2
32.4
13.0
50.7
30.0
8.1
--
--
--
Aluminum
Oxide, Al2O3
17.1
7.8
8.2
12.3
7.5
--
--
--
Iron Oxide,
Fe2O3
9.8
2.6
2.1
14.2
3.0
--
--
--
SiO2 + Al2O3 +
Fe2O3
59.3
23.4
61.0
56.5
18.6
50.0
Min
70 Min
70 Min.
Calcium Oxide,
CaO
3.5
13.7
19.6
2.2
25.3
--
--
--
Magnesium
Oxide, MgO
0.7
2.6
6.5
0.7
4.5
--
--
--
Titanium Oxide,
TiO2
0.7
0.5
1.2
0.9
0.3
--
--
--
Potassium Oxide,
K2O
1.1
0.4
2.8
2.0
2.7
--
--
--
Sodium Oxide,
Na2O
0.9
0.6
2.1
0.5
3.3
--
--
--
Sulfite, SO3
2.2
0.9
0.1
2.1
12.5
5.0
Max
5.0
Max
4.0
Max. Loss on Ignition,
LOI (1000?C)
31.6
58.1
6.7
35.3
32.8
6.0
Max
6.0
Max
10.0
Max.
Moisture
2.4
0.5
0.2
0.4
3.3
3.0
Max
3.0
Max
3.0
Max. Available Alkali,
Na2O,
(ASTM C-311)
0.9
0.4
0.8
1.1
4.2
1.5
Max
1.5
Max
1.5
Max.
21
22
Table 3 - Mixture Proportions for the Series L CLSM Mixtures
Mix No.
1-L
2-L
3-L
4-L
5-L
Laboratory Mixture
Designation
N-1L
DC-1L
R-1L
B4-1L
B5-1L
Fly Ash Source
W-1
W-2
W-3
W-4
W-5
Fly Ash (%)
90
85
90
90
85
Cement, kg/m
3 (lb/yd
3)
77
(130)
89
(150)
53
(90)
56
(95)
95
(160)
Fly Ash, kg/m
3 (lb/yd
3)
641
(1080)
469
(790)
1187
(2000)
662
(1115)
498
(840)
Water, W kg/m
3 (lb/yd
3)
626
(1055)
635
(1070)
481
(810)
656
(1105)
730
(1230)
[W/(C+A)]
0.82
1.14
0.39
0.91
1.23 Air Temperature, C (F)
22.2
(72)
22.2
(72)
22.2
(72)
22.2
(72)
22.2
(72)
Fresh CLSM
Temperature, C (F)
23.3
(74)
23.3
(74)
23.9
(75)
22.8
(73)
24.4
(76)
Flow, mm (in.)
241
(9 ½)
254
(10)
254
(10)
254
(10)
254
(10)
Air Content (%)
2.4
5
3.5
2.8
1.0
Unit Weight, kg/m3
(lb/ft3)
1344
(83.9)
1195
(74.6)
1724
(107.6)
1371
(85.6)
1323
(82.6)
23
Table 4 - Mixture Proportions for the Series M CLSM Mixtures
Mix No.
1-M
2-M
3-M
4-M
5-M
Laboratory Mixture
Designation
N-1
DC-1
R-1
B4-1
B5-1
Fly Ash Source
W-1
W-2
W-3
W-4
W-5
Cement, kg/m
3 (lb/yd
3)
187
(315)
228
(385)
101
(170)
157
(265)
125
(210)
Fly Ash, kg/m
3 (lb/yd
3)
611
(1030)
400
(675)
1133
(1910)
617
(1040)
445
(750)
Water, W kg/m
3 (lb/yd
3)
602
(1015)
596
(1005)
510
(860)
635
(1070)
721
(1215)
[W/(C+A)]
0.75
0.95
0.41
0.82
1.26
Flow, mm (in.)
273
(10 ¾)
260
(10 ¼)
254
(10)
260
(10 ¼)
260
(10 ¼)
Air Content (%)
1.5
5.7
4.4
1.6
1.6
Air Temperature, C (F)
25.5
(78)
25.5
(78)
25.5
(78)
26.1
(79)
26.1
(79)
Fresh CLSM Temperature,
C(F)
22.2
(72)
27.8
(82)
25.5
(78)
31.1
(88)
22.2
(72)
Unit Weight, kg/m
3 (lb/ft
3)
1394
(87)
1234
(77)
1762
(110)
1410
(88)
1298
(81)
24
Table 5 - Mixture Proportions for the Series H CLSM Mixtures
Mix No.
1-H
2-H
3-H
4-H
5-H
Laboratory Mixture
Designation
N-2
DC-2
R-2
B4-2
B5-2
Fly Ash Source
W-1
W-2
W-3
W-4
W-5
Cement, kg/m
3 (lb/yd
3)
169
(285)
205
(345)
196
(330)
175
(295)
157
(265)
Fly Ash, kg/m
3 (lb/yd
3)
427
(720)
205
(345)
537
(905)
392
(660)
353
(595)
Water, W kg/m
3 (lb/yd
3)
418
(705)
430
(725)
359
(605)
484
(815)
540
(910)
[W/(C+FA)]
0.7
1.05
0.48
0.85
1.04
SSD Fine Aggregate, kg/m
3
(lb/yd3)
774
(1305)
828
(1395)
946
(1595)
706
(1190)
611
(1030)
Flow, mm (in.)
273
(10 ¾)
260
(10 ¼)
273
(10 ¾)
260
(10 ¼)
260
(10 ¼)
Air Content (%)
1.4
6.3
1.6
1.3
0.9
Air Temperature, C (F)
25.6
(78)
26.1
(79)
25.6
(78)
25.6
(78)
24.4
(76)
Fresh CLSM Temperature, C
(F)
23.3
(74)
27.8
(82)
28.9
(84)
26.7
(80)
22.8
(73)
Unit Weight, kg/m
3 (lb/ft
3)
1794
(112)
1660
(104)
2035
(127)
1762
(110)
1666
(104)
25
Table 6 - Bleedwater of the Series L CLSM Mixtures
Mixture
No.
Bleedwater mm (in) *
1 hour 4 hour 8 hour 24 hour 2 days 3 days 2 days
1-L
9.5
(3/8)
1.6
(1/16)
0
0
0
0
0
2-L
3.2
(1/8)
1.6
(1/16)
0
0
0
0
0
3-L
9.5
(3/8)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
0
4-L
4.8
(3/16)
3.2
(1/8)
0
0
0
0
0
5-L
1.6
(1/16)
0
0
0
0
0
0
*Average of three readings
Table 7 - Bleedwater of the Series M CLSM Mixtures
Mixture
No.
Bleedwater, mm (in) *
1 hour 4 hour 8 hour 24 hour 2 days 3 days 7 days
1-M
12.7
(½)
9.5
(3/8)
6.4
(1/4)
3.2
(1/8)
1.6
(1/16)
0
0
2-M
0
0
0
0
0
0
0
3-M
3.2
(1/8)
0
0
0
0
0
0
4-M
3.2
(1/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
0
5-M
12.7
(1/2)
11.1
(7/16)
6.4
(1/4)
1.6
(1/16)
0
0
0
*Average of three readings
26
Table 8 - Bleedwater of the Series H CLSM Mixtures
Mixture
No.
Bleedwater, mm (in.) *
1 hour
4 hour
8 hour
24 hour
2 days
3 days
1-H
4.8
(3/16)
3.2
(1/8)
1.6
(1/16)
0
0
0
2-H
9.5
(3/8)
6.4
(1/4)
1.6
(1/16)
0
0
0
3-H
9.5
(3/8)
6.4
(1/4)
3.2
(1/8)
0
0
0
4-H
4.8
(3/16)
7.9
(5/16)
9.5
(3/8)
12.7
(1/2)
9.5
(3/8)
9.5
(3/8)
5-H
6.4
(1/4)
9.5
(3/8)
9.5
(3/8)
6.4
(1/4)
0
0
* Average of three readings
Table 9 - Settlement of the Series L CLSM Mixtures
Mixture
No.
Settlement, mm (in.)*
1 hour
4 hour
8 hour
24 hour
2 days
3 days
7 days
14 days
1-L
9.5
(3/8)
12.7
(1/2)
12.7
(1/2)
7.9
(5/16)
9.5
(3/8)
9.5
(3/8)
--
3/8
2-L
27.0
(1-1/16)*
--
49.2
(1-15/16)**
46.0
(1-13/16)**
46.0
(1-13/16)**
49.2
(1-15/16)
49.2
(1-15/16)*
--
3-L
9.5
(3/8)
1.6
(1/16)
--
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
0
4-L
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
5-L
3.2
(1/8)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
4.8
(3/16)
*Average of three readings
27
**Values indicate CLSM expansion
28
Table 10 - Settlement of the Series M CLSM Mixtures
Mixture
No.
Settlement, mm (in.) *
1 hour
4 hour
8 hour
24 hour
2 days
3 days
7 days
14 days
1-M
12.7
(1/2)
9.5
(3/8)
6.4
(1/4)
6.4
(1/4)
6.4
(1/4)
6.4
(1/4)
6.4
(1/4)
6.4
(1/4)
2-M
42.9
(1-11/16)**
50.8
(2)**
55.6
(2-3/16)**
61.9
(2-7/16)**
61.9
(2-7/16)**
61.9
(2-7/16)**
--
--
3-M
4.8
(3/16)
3.2
(1/8)
0
0
0
0
0
0
4-M
4.8
(3/16)
12.7
(1/2)
12.7
(1/2)
11.1
(7/16)
12.7
(1/2)
12.7
(1/2)
12.7
(1/2)
12.7
(1/2)
5-M
12.7
(1/2)
11.1
(7/16)
9.5
(3/8)
6.4
(1/4)
3.2
(1/8)
6.4
(1/4)
6.4
(1/4)
6.4
(1/4)
*Average of three readings
**Values indicate CLSM expansion
Table 11 - Settlement of the Series H CLSM Mixtures
Mixture
No.
Settlement, mm (in.)*
1 hour
4 hour
8 hour
24 hour
2 days
3 days
7 days
14 days
1-H
4.8
(3/16)
3.2
(1/8)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
1.6
(1/16)
4.8
(3/16)
4.8
(3/16)
2-H
9.5
(3/8)
6.4
(1/4)
1.6
(1/16)
0
0
0
0
0
3-H
9.5
(3/8)
6.4
(1/4)
3.2
(1/8)
0
0
0
0
0
4-H
4.8
(3/16)
6.4
(1/4)
9.5
(3/8)
12.7
(1/2)
12.7
(1/2)
12.7
(1/2)
11.1
(7/16)
11.1
(7/16)
5-H
6.4
(1/4)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
9.5
(3/8)
*Average of three readings
29
Table 12 - Compressive of the Series L CLSM Mixtures
Mixture
No.
Compressive Strength, kPa (psi) *
3-day
7-day
14-day
28-day
91-day
1-L
100
(15)
170
(25)
210
(30)
380
(55)
480
(70)
2-L
70
(10)
140
(20)
140
(20)
240
(35)
380
(55)
3-L
140
(20)
170
(25)
210
(30)
410
(60)
280
(140)
4-L
100
(15)
170
(25)
210
(30)
280
(40)
1170
(70)
5-L
140
(20)
480
(70)
520
(75)
1170
(170)
1790
(260)
*Average of three readings
Table 13 - Compressive of the Series M CLSM Mixtures
Mixture
No.
Compressive Strength, kPa (psi) *
3-day
7-day
14-day
28-day
91-day
1-M
310
(45)
340
(50)
480
(70)
1400
(200)
2840
(390)
2-M
450
(65)
550
(80)
720
(105)
970
(140)
2690
(765)
3-M
450
(65)
660
(95)
760
(110)
1280
(185)
1590
(230)
4-M
210
(30)
660
(95)
900
(130)
1450
(210)
2550
(370)
5-M
170
(25)
340
(50)
620
(90)
720
(105)
1140
(165)
*Average of three readings
30
Table 14 - Compressive of the Series H CLSM Mixtures
Mixture
No.
Compressive Strength, kPa (psi)*
3-day
7-day
14-day
28-day
91-day
1-H
830 (120)
1380 (200)
2340 (340)
3240 (470)
6650 (965)
2-H
720 (105)
1070 (155)
1140 (165)
1590 (230)
8620 (1250)
3-H
1900 (275)
2280(330)
2480 (360)
3100 (450)
4000 (580)
4-H
850 (120)
1520 (220)
2520 (365)
3590 (520)
6960 (1010)
5-H
660 (95)
1480 (215)
2210 (320)
2210 (320)
4240 (615)
*Average of three readings
Table 15 - Permeability of the Series L CLSM Mixtures
Mixture
No.
Permeability (cm/sec)*
28-day
1-L
100 x 10
-6
2-L
54 x 10
-6
3-L
15 x 10
-6
4-L
35 x 10
-6
5-L
110 x 10
-6
*Average of three readings
31
Table 16 - Permeability of Series M CLSM Mixtures
Mixture
No.
Permeability (cm/sec)*
28-day
91-day
1-M
6 x 10
-6
0.1 x 10
-6
2-M
510 x 10
-6
350 x 10
-6
3-M
20 x 10
-6
2.4 x 10
-6
4-M
5 x 10
-6
3.0 x 10
-6
5-M
74 x 10
-6
7.0 x 10
-6
*Average of three readings
Table 17 - Permeability of Series H CLSM Mixtures
Mixture
No.
Permeability (cm/sec)*
28-day
91-day
1-H
12 x 10
-6
4 x 10
-6
2-H
2 x 10
-6
1 x 10
-6
3-H
120 x 10
-6
38 x 10
-6
4-H
19 x 10
-6
14 x 10
-6
5-H
4 x 10
-6
3 x 10
-6
*Average of three readings
30
Fig. 1 - Setting Characteristics for the Series L CLSM Mixtures
0
20
40
60
80
100
120
140
0 24 48 72 96 120 144 168 192 216 240 264 288 312 336Age, hours
Dia
met
er o
f Im
pri
nt,
mm
Mixture 1-L Mixture 2-L
Mixture 3-L Mixture 4-L
Mixture 5-L
ASTM D 6024 Limit 76 mm
Fig. 2 - Setting Characteristics for the Series M CLSM Mixtures
-10
10
30
50
70
90
110
130
150
0 24 48 72 96 120 144 168 192 216 240 264 288 312
Age, hours
Dia
met
er o
f Im
pri
nt,
mm
Mixture 1-M Mixture 2-M
Mixture 3-M Mixture 4-M
Mixture 5-M
ASTM D 6024 Limit 76 mm
31
Fig. 3 - Setting Characteristics for the Series H CLSM Mixtures
0
20
40
60
80
100
120
140
0 24 48 72 96 120 144 168 192 216 240 264
Age, hours
Dia
met
er o
f Im
pri
nt,
in
ches
Mixture 1-H Mixture 2-H
Mixture 3-H Mixture 4-H
Mixture 5-H
ASTM D 6024 Limit 76 mm
Fig. 4 - Compressive Strength for Series L CLSM Mixtures
0
200
400
600
800
1000
1200
1400
1600
1800
2000
3 7 14 28 91
Age, days
Co
mp
ress
ive
Str
eng
th,
KP
a
Mixture 1-L Mixture 2-L
Mixture 3-L Mixture 4-L
Mixture 5-L
32
Fig. 5 - Compressive Strength for the Series M CLSM Mixtures
0
1000
2000
3000
4000
5000
6000
3 7 14 28 91
Age, days
Co
mp
ress
ive
Str
eng
th,
KP
a Mixture 1-M Mixture 2-M Mixture 3-M
Mixture 4-M Mixture 5-M
Fig. 6 - Compressive Strength for the Series H CLSM Mixtures
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
10000
3 7 14 28 91
Age, days
Co
mp
ress
ive
Str
eng
th,
KP
a
Mixture 1-H Mixture 2-H Mixture 3-H
Mixture 4-H Mixture 5-H