processing cotton gin trash to enhance in vitro dry matter 2005
DESCRIPTION
Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005TRANSCRIPT
![Page 1: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/1.jpg)
Bioresource Technology 96 (2005) 47–53
Processing cotton gin trash to enhance in vitro dry matterdigestibility in reduced time
Lester O. Pordesimo a,*, Samuel J. Ray a, Michael J. Buschermohle a,John C. Waller b, John B. Wilkerson a
a Department of Biosystems Engineering and Environmental Science, The University of Tennessee, 2506 E.J. Chapman Drive Knoxville,
TN 37996-4531 USAb Department of Animal Science, The University of Tennessee, 2505 River Drive, Knoxville, TN, 37996-4500 USA
Received 30 September 2002; received in revised form 23 February 2004; accepted 23 February 2004
Available online 13 April 2004
Abstract
Cotton gin trash (CGT) in the raw form is poorly digested by ruminants due to lignocellulosic complexes. These structures must be
broken down before adequate digestion can occur. This may be performed by physical and/or chemical means. Two methods for
improving digestibility are particle size reduction and/or treatment with sodium hydroxide (NaOH). To evaluate the effectiveness of
each method, three experiments were performed in which different CGT types were tested. Each type represented trash from a
particular cleaning stage in the cotton ginning process. First, each type was ground with a knife-type grinding mill using screen sizes
0.5, 1.0, and 2.0 mm. For the second experiment, particle size was held constant at 2 mm, and all CGT types were treated with 4% and
6% NaOH (w/w) at room temperature. An agitation cycle of 5 min on and 10 min off was used, with the total mixing time being 4 h.
Lastly, particle size and NaOH concentration were held constant, and treatments were performed at room temperature, 40 �C, and50 �C. The total mixing times were 2 and 3 h for 50 and 40 �C, respectively. For all experiments two subsamples of each treatment were
tested for in vitro dry matter digestibility (IVDMD). From grinding alone, digestibility increased as particle size decreased. Grinding
to 0.5 mm resulted in an average IVDMD of 47.8% while grinding to 2.0 mm resulted in an average IVDMD of only 33.8%.
Digestibility also improved with a greater NaOH concentration. An average in vitro digestibility of 70.5% was achieved with 6%
NaOH (w/w) treatment, essentially doubling that of the raw CGT. Increasing the reaction temperature did not result in increased
digestibility because the mixture dried out, with a consequent reduction in chemical distribution and uniformity in heat transfer. There
are still chemical residues in the CGT, and elimination/reduction of these is an issue that needs to be addressed in further research.
� 2004 Elsevier Ltd. All rights reserved.
1. Introduction
Finding an economical and practical method of dis-
posing of the large quantities of cotton gin trash (CGT)
that accumulate during the ginning process remains aproblem for cotton ginning facilities. In the past,
incineration has been a widely used disposal method,
but environmental regulations have practically elimi-
nated this method. Using CGT as a ruminant feed
ingredient is one potential high-value option for dis-
posing of the material in an environmentally friendly
manner. Comparatively, CGT has lower feed value than
alfalfa, but higher than prairie hay, bermuda hay, rice
*Corresponding author. Tel.: +1-865-974-7266; fax: +1-865-974-
4514.
E-mail address: [email protected] (L.O. Pordesimo).
0960-8524/$ - see front matter � 2004 Elsevier Ltd. All rights reserved.
doi:10.1016/j.biortech.2004.02.031
hulls, and sorghum stover, according to Lalor et al.
(1975) (Table 1).
Problems related to utilization of CGT as a livestock
feed/livestock feed ingredient include chemical residues,
digestibility, and nutritive value (Buser, 1999). Whilestill a problem, the issue of chemical residues is not as
severe as in the past. Levels have decreased since the
1970s, and current residues are relatively short-lived
(personal communication from W.D. Mayfield cited by
Thomasson et al. (1998)). All these issues may poten-
tially be addressed and ameliorated with a reduced
processing time by engineering physical, chemical, and
enzymatic pretreatment and nutrient blending processesfor CGT. The strategy is to quickly pre-digest a fraction
of the lignocellulosic material in cotton gin trash to
facilitate a more complete digestion and utilization by
ruminants, and to increase protein content through
![Page 2: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/2.jpg)
Table 1
Nutritive value of cotton gin trash
Nutritional component Analysis
Estimated net energy maintenance (MCa/Cwt) 46
Estimated net energy production (MC/Cwt) 15
TDN ruminant 45
Crude protein (%) 7.0
Crude fat (%) 1.5
Crude fiber (%) 35.0
Ash (%) 10.0
Calcium (%) 0.15
Phosphorous––Total (%) 0.09
Potassium (%) 0.87
Source: Lalor et al. (1975).aMC¼million calories.
48 L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53
blending with other ingredients. Such a strategy requires
characterizing the physico-chemical properties of the ginwaste (broadly classified as picker or stripper trash), and
then investigating the main effects and interactions of
such pretreatment process variables as particle size,
chemical concentrations, cycled agitation, and reaction
time and temperature. While there have been many
studies involving the chemical treatment of crop residues
for enhanced livestock feeding value, there is little
information on the effects of treatment process variablesother than chemical concentration.
Han et al. (1983) stated that in cellulose hydrolysis,
direct physical contact between the hydrolytic agents and
the cellulose molecules is required and that the rate of
hydrolysis is a function of the cellulose surface area
accessible to the hydrolytic agent. This translates to im-
proved digestion of lignocellulosic crop residues with a
decrease in the particle size of the material. Working withrice straw and bagasse, Agrawal et al. (1989) studied the
effect of particle size on the in vitro digestibility. How-
ever, no published research was found that directly
investigated the effects of size reduction of the various
CGTmaterial (and crop residues in general) on ruminant
digestibility. It has also been proven that treating CGT
with sodium hydroxide (NaOH) increases rumen turn-
over (Conner and Richardson, 1987), but there havebeen no reported studies on the chemical pretreatment of
segregated CGT types (materials separated by particular
cleaning stages in the cotton ginning process), much less
the use of agitation and elevated process temperatures to
achieve effective pretreatment over a limited time. Dry
matter digestibilities of crop residues range from 35% to
60%, with corn and sorghum plant material generally
higher than small grain straws (Klopfenstein, 1980).Thomasson (1990) indicated that raw cotton gin trash
had an in vitro digestibility of 34%, which falls in the
lower end of crop residue digestibility range.
The objective of this preliminary study was to deter-
mine the impact of particle size reduction and agitated
treatment with aqueous NaOH solution on the in vitro
dry matter digestibility (IVDMD) of cotton gin trash,
with the goal of reducing treatment time. Both of these
methods should aid in hastening the breakdown of the
lignocellulosic complexes, thereby enhancing ruminant
digestibility. Factors such as convenience, time econ-
omy, effectiveness, and cost are critical for a pretreat-
ment process to be commercially viable for ginners.
Recognizing this, an essentially dry process was studied:
liquid delivery into dry cotton gin trash. More recentstudies concerning the degradation of biomass have
been liquid systems. It is hypothesized that an appro-
priate combination of process variables can result in
acceptable improvement in digestibility over a 4-h
treatment period. The effects of CGT type, particle size,
chemical concentration, and processing temperature
were also investigated.
2. Methods
Various types of CGT from the ginning of stripper-
harvested and spindle-picked cotton were obtained from agin in West Tennessee. Each type represented trash from
a particular cleaning stage in the cotton ginning process. A
consolidated sample of CGT cleaned from stripper-har-
vested cotton was also obtained from Texas. Listed in
Table 2 are different CGT types tested and their moisture
contents, determined following ASTM Standard D 2495
(ASTM, 1987). Types A, B and F, G were mostly non-lint
material whereas types D, E and I, J were mostly lint. Thetest materials were kept in large plastic bags and stored in
an air-conditioned laboratory (�25 �C) before treatment
three months after they were obtained.
Three two-factor experiments were performed in
which all CGT types were tested. The effect of particle
size and CGT type on IVDMD was evaluated in the first
experiment. In the second experiment, the effect of
NaOH concentration and CGT type on IVDMD wasevaluated while maintaining a constant particle size. In
the third experiment, NaOH concentration and particle
size were held constant while testing the effect of dif-
ferent process temperatures and CGT type on IVDMD.
Material, time, and cost constraints limited the studies
to two replicates. IVDMD was evaluated for all samples
using the Moore modification (Moore et al., 1972) of the
Tilley and Terry (1963) two-stage technique. Statisticalanalysis for the effect of the experimental treatment
factors was accomplished through analysis of variance
using the Mixed procedure of the Statistical Analysis
System (SAS Institute, Inc., 1999). Comparison between
treatment means and trend comparisons were investi-
gated using orthogonal contrasts. Specific contrasts
accomplished compared the IVDMD between stripper-
harvested and spindle-picked cotton and high- and low-lint CGT types. The effective trend in IVDMD caused
by a progression in particle size, NaOH concentration,
or process temperature was also evaluated.
![Page 3: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/3.jpg)
Table 2
Cotton gin trash types tested
Code Description MC (% w.b.)
Stripper-harvested cotton––West Tennessee
A First stage cleaning––inclined cleaner (essentially burr and stick separator) 9.60
B Second stage cleaning––inclined cleaner 9.66
C Material underneath gin stand 8.21
D First stage lint cleaner 7.17
E Second stage lint cleaner 5.65
Spindle-picked harvested cotton––West Tennessee
F First stage cleaning––inclined cleaner (essentially burr and stick separator) 8.99
G Second stage cleaning––inclined cleaner 8.75
H Material underneath gin stand 7.26
I First stage lint cleaner 6.64
J Second stage lint cleaner 6.01
Stripper-harvested cotton––Texas
M Mixture of all cleanings 8.76
L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53 49
2.1. Experiment 1
A completely randomized design with split-plot
treatment arrangement was used to study in vitro dry
matter digestibility: CGT type was in the main plot
while particle size was in the sub-plot. The bulk
material of each CGT type procured was split and
randomly designated as replication 1 or 2 [model:y ¼ meanþ typeþ repðtypeÞ þ sizeþ size � typeþsize � repðtypeÞ�. The duplicate samples of each type
were then ground in a knife mill (Model P15, Glen
Mills, Inc., Clifton, N.J., USA) using screen sizes 0.5,
1.0, and 2.0 mm in a randomized manner. Samples
comprising the various type-particle size treatment
combinations were then evaluated for in vitro dry
matter digestibility.
2.2. Experiment 2
CGT types ground through a 2.0 mm screen wereused as the test material for this experiment. Since
greater energy is required to grind material to smaller
particle sizes, it was more practical to undertake chem-
ical treatment testing with the largest of the test material
sizes. Each type was treated with 4% and 6% NaOH
(w/w) on a dry matter basis. These concentrations used
were based on recommendations from Han et al. (1983)
using ryegrass as a test material. Additional support forthese choices came from Klopfenstein (1978), who re-
ported optimum animal response to NaOH at levels
from 3% to 5% of residue dry matter.
Chemical treatment was achieved using a Kitchen
Aid Classic stand mixer (KitchenAid, Greenville, Ohio,
USA) to provide agitation and greater interaction be-
tween the NaOH solution and the CGT. Four mixers
were used simultaneously to reduce the time to accom-plish the chemical treatment experiments. For optimum
mixing effectiveness, a minimum level of fill of material
was required in the mixer bowl. Filling the bowl to one
third of its total depth, approximately 8 cm from the
bowl bottom, provided for effective mixing. Each test
was thereby started by pouring ground CGT up to the
designated fill level. Since the CGT had different densi-
ties, the total mass of material treated was different for
each test. Dry matter of each mixer load was calculated,and the amount of NaOH to produce a 4% or 6%
treatment was then calculated and weighed. The NaOH
was added to the CGT as an aqueous solution. The
amount of water used in the solution was determined by
observing the effectiveness of mixing in several test
mixes. Tests showed that a raw material:water ratio of
1:2 was adequate to homogeneously transport the
NaOH, but not too much as to make the mixture aslurry rather than a moist solid. Thus, a solid to liquid
ratio of 1:2 was set for the experiments to minimize the
amount of water needed for the treatment process and
minimize the amount of wastewater generated in a
possible commercial process. The required amount of
pure NaOH was mixed in a beaker with an amount of
distilled water equal to twice the weight of the CGT
already in the mixer bowl. Since the weight of the solidNaOH was not considered in determining the weight of
water needed, the solid:liquid ratio was actually just
fractionally short of being 1:2. The mixer was set on low,
operated for 4 h using a cycle of 5 min on and 10 min off.
The pretreated samples were transferred to airtight
sample bags and kept in frozen storage ()17 �C) until allexperimental treatments were completed. Samples were
then evaluated for in vitro dry matter digestibility. Theexperiment was conducted as a completely randomized
design with factorial treatments ½model: y ¼ meanþtypeþNaOHþ type � NaOHþ repðtype � NaOHÞ�.In undertaking statistical analysis, the results for CGT
ground to 2 mm in Experiment 1 were used as the no-
chemical control.
![Page 4: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/4.jpg)
50 L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53
2.3. Experiment 3
The 11 CGT types ground through a 2.0 mm screen
were also used as the test material in this experiment.
Each type was treated with 6% NaOH following
Experiment 2 procedures with the use of temperature
during mixing as a treatment variable [ambient
(�25 �C), 40 �C, 50 �C]. Electric rope heaters (OmegaluxFR100, Omega Engineering, Inc., Stamford, Conn.,
USA) were coiled around the base of the mixing bowls
to provide heat. The power for the rope heater was
regulated in order to maintain the targeted elevated
temperatures. To prevent the material from charring on
the bowl surface during processing, heat was applied
only when agitation occurred. Temperature measure-
ments were taken at the end of each mixing/heatingstage with an infrared thermometer (Model no. 39650-
20, Cole-Parmer Instruments, Co., Chicago, Ill., USA)
to verify that the targeted temperatures were achieved.
Since the water evaporation rate increases with tem-
perature, the total mixing time had to be reduced to 3
and 2 h for 40 and 50 �C, respectively. Mixing time was
retained at 4 h for pretreatment at room temperature.
By adjusting the process times at each of the processtemperatures tested, these two factors became con-
founded with each other. The experiment was conducted
following a completely randomized design with factorial
treatments ½model: y ¼ meanþ typeþ tempþ type �tempþ repðtype � tempÞ�. Pretreated samples were
handled as in Experiment 2. Samples comprising the
various type-process temperature treatment combina-
tions were thereafter evaluated for in vitro dry matterdigestibility.
2.4. In vitro dry matter digestibility
Dry matter digestibility was determined using theMoore modification of the Tilley and Terry (1963) two-
stage in vitro technique (Moore et al., 1972). The donor
animal was maintained on a medium quality alfalfa
(Medicago sativa) diet with supplementation of 0.454
kg/d of 48% of soybean meal. The supplementation was
given at 0700 with collection being 2-h post-feeding.
Whole ingesta from the top half of the rumen were re-
moved and transferred to an insulated container thenstrained through four layers of cheesecloth. Fluid was
transported from The University of Tennessee Dairy
Farm to the nutrition laboratory (about 15 min) where it
was flushed with CO2 and then placed into a large glass
bottle in the water bath containing the McDougall’s
saliva (McDougall, 1948). An appropriate quantity of
McDougall’s saliva was prepared prior (40 ml per tube
plus 200 ml extra) and placed into a 13.25 l bottle. Oneml of 4% CaCl2 per liter of McDougall’s saliva was
added to the bottle and then it was placed into a 39 �Cwater bath and CO2 was bubbled gently through the
bottle. The pH of the buffer was adjusted to between 6.9
and 7.0 in order to mimic the natural buffer in the ani-
mal more closely. One part rumen fluid was added to 4
parts buffer and was allowed to mix for 10 min by action
of the bubbling CO2.
Five grams of each sample was weighed and placed
into a numbered centrifuge tube. Two ml of distilled
water were added to each tube to moisten the sample.Each tube was agitated with a test tube mixer. Fifty ml
of media were gently added to each centrifuge tube with
using an automatic pump. The tubes were placed into a
water bath immediately after adding the media and
flushed with CO2 for 15 s. The tubes were sealed quickly
with a rubber stopper fitted with a Bunsen valve. The
tubes were placed in a 39 �C water bath and swirled 1 h
later to ensure that all of the sample particles weresoaked with media. This swirling was repeated twice the
first day and thrice the second day.
After 48 h of incubation, the rubber stoppers were
removed and the sample particles adhering to the stop-
pers were washed into the tubes with distilled water. One
ml of 20% HCl was added to each tube and swirled and
then repeated (total 2 ml per tube). An additional 4 ml
of HCl was added to each tube and then swirled. Two mlof 5% pepsin were then added to each tube followed by
swirling to mix the pepsin with the acid and sample. The
rubber stoppers were replaced and the tubes returned to
the 39 �C incubator. The swirling was repeated twice the
first day and thrice the second day.
Gooch crucibles were then prepared by forming a
glass wool mat in the bottom to serve as a filter. After
46 h of pepsin digestion, the contents of the centrifugetubes were transferred to the Gooch crucibles. All
residual material from the tubes was rinsed out with hot
distilled water and the Gooch crucibles were rinsed with
hot distilled water. The Gooch crucibles were placed
into a drying oven overnight at 105 �C. The following
day they were removed from the drying oven, cooled in
a desiccator, and weighed.
3. Results and discussion
3.1. Particle size
As illustrated in Fig. 1, IVDMD increased as particle
size decreased ðP < 0:01Þ, which was expected. Smaller
particle sizes have a larger total surface area for the
action of the digestive fluids. Grinding to 0.5 mm re-
sulted in the highest IVDMD of the three particle sizes
evaluated, with an average digestibility of 47.8%.
Grinding to 2.0 mm resulted in the lowest digestibility of
33.8%. It should also be noted that there were consid-erable differences in digestibility between the same sizes
for the different CGT types. Generally, regardless of
how the cotton was harvested, the types with higher fi-
![Page 5: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/5.jpg)
0102030405060708090
100
A B C D E F G H I J MCGT Type
IVD
MD
, %
0.5 mm1.0 mm2.0 mm
spindlestripper
Fig. 1. Effect of particle size on in vitro ruminant digestibility.
L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53 51
ber or lint content had lower digestibilities. This result
was highly significant ðP < 0:01Þ. It is also shown in
Fig. 1 that trash from the spindle-harvested cotton
generally had greater digestibilities than trash from the
stripper-harvested cotton ðP < 0:01Þ. For instance, trashfrom spindle-harvested cotton ground through a 0.5 mm
screen had an average digestibility of 58.8%, while that
from stripper-harvested cotton had an average digest-ibility of only 37.8% (both material obtained from West
Tennessee). This result is explained by the makeup of
the foreign material accumulated with the seed cotton
through each harvesting method. Stripper harvesting
includes a higher proportion of heavier and coarser
foreign materials (burrs and stems) that are inherently
less digestible because of their chemical composition.
The CGT from Texas, which was a mixture of all clea-nings, had a digestibility of 44.1%.
3.2. NaOH concentration
Pretreatment of the CGT with NaOH significantly
affected IVDMD ðP < 0:01Þ. It is evident from Fig. 2
that pretreatment of the CGT with either 4% or 6%
NaOH (w/w) improved IVDMD compared to no-
chemical treatment There was a significant type · che-
mical treatment interaction ðP < 0:01Þ. The general
trend in the figure indicates that treating the CGT with
6% NaOH seemed more effective in improving IVDMD
0102030405060708090
100
A B C D E F G H I J MCGT Type
IVD
MD
, % None4% NaOH6% NaOH
spindlestripper
Fig. 2. Effect of sodium hydroxide concentration on in vitro ruminant
digestibility.
than using 4% for all CGT types, with an average IV-
DMD of 70.5% compared to 60.6%. However, a missing
treatment combination prevented a statistical evaluation
of whether the decrease was linear with increasing NaOH
concentration nor could other mean comparisons
through orthogonal contrasts be undertaken. These
digestibility values obtained compare well to the 64%
achieved by submerging the CGT in a caustic solution inwhich a superoxide species, e.g. hydrogen peroxide, is
incorporated (Thomasson, 1990). It can also be seen in
Fig. 2 that high-lint trash types coming from both spin-
dle-picked and stripper-harvested cotton exhibited a
greater positive IVDMD response to NaOH pretreat-
ment than did the non-lint trash types.
3.3. Process temperature
According to chemical reaction kinetics, applying
heat increases chemical reaction rates. Based on this and
also because the starting ratio of CGT to water was keptclose to 1:2, the total time of mixing/chemical pretreat-
ment at elevated temperatures was reduced from the 4 h
used for most of the tests conducted. Preventing char-
ring of the CGT was another reason for this change. It
was presumed that the elevated process temperatures
would counterbalance the reduction in treatment time
thereby resulting in roughly the same IVDMDs achieved
at each temperature–time treatment. The process tem-perature–time treatments significantly affected IVDMD
ðP < 0:05Þ. As shown in Fig. 3, in the study conducted,
agitated NaOH treatment of the CGT at higher tem-
perature–shorter time resulted in a decrease in IVDMD.
However, a missing treatment combination prevented
an evaluation of whether the decrease was linear with
increasing temperature. A probable explanation for this
is the loss of water from the mixtures during the courseof processing. The average moisture content of the CGT
pretreated at �25 (ambient), 40 �C, and 50 �C was
30.51%, 28.34%, and 6.10% d.b., respectively. Water
serves as both the medium for pretreatment chemical
transport and a medium for heat transfer, so treatment
0102030405060708090
100
A B C D E F G H I J MCGT Type
IVD
MD
, % room temp40 °C50 °C
stripper spindle
Fig. 3. Effect of mixing temperature on the effectivity of 6% (w/w)
sodium hydroxide pretreatment.
![Page 6: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/6.jpg)
Table 3
Pretreatment main effects on in vitro ruminant digestibility
Experiment no. Screen size (mm) Pretreatment Agitation time (h) Mean IVDMD (%)
NaOH concentration
(% w/w)
Process temperature
(�C)
1 0.5 0 – – 47.8± 1.15
1.0 0 – – 37.4± 1.15
2.0 0 – – 33.8± 1.15
2 2.0 4 �25 (room) 4 60.6a
2.0 6 �25 (room) 4 70.5± 2.10
3 2.0 6 �25 (room) 4 70.5± 4.18
2.0 6 40 3 65.2a
2.0 6 50 2 55.4± 4.18
a Standard errors could not be calculated due to missing treatment factor combinations.
52 L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53
effectiveness decreases as water evaporates during heat-
ing. This result shows that increased process tempera-
ture did not make up for the loss of water and maybeeven processing time when other process variables were
kept constant. Room temperature samples produced an
IVDMD of 70.5% while samples processed at 50 �Cproduced an IVDMD of only 55.4%. It is likely that in
order for elevated temperatures to effect improved
digestibility, additional water must be continuously ad-
ded to compensate for evaporation during the course of
the chemical pretreatment process.
4. Conclusions
Experiment 1 clearly indicated that size reduction was
effective in enhancing IVDMD of CGT. The effect of
grinding was greatest in the non-lint types. Under
intermittent agitation, a concentration of 6% NaOH
(w/w) was shown in Experiment 2 to be more effective in
improving CGT digestibility than was a 4% concentra-
tion. Lastly, Experiment 3 showed that undertakingagitated chemical pretreatment at elevated temperatures
over a short time did not enhance IVDMD because
water, the medium for chemical transport and heat
transfer, was evaporated. The average IVDMD is shown
in Table 3 for all experiments. For the range of experi-
mental treatment factors studied, the most effective
pretreatment of CGT was to grind the material through
a 0.5 mm screen and then treat the CGT with 6% NaOH(w/w) under agitation at room temperature for 4 h. This
certainly may not be the most efficient method when
considering cost and practicality under commercial
conditions. For instance, the extra power and/or time
required to grind material through a 0.5 mm screen may
not be worth the degree of IVDMD enhancement when
compared to IVDMD levels for CGT ground through a
2.0 mm screen. An optimal target IVDMD needs to bedetermined considering these factors.
This research study has only addressed the problem
of CGT digestibility. The presence of any residual pes-
ticides in the CGT was not investigated. The latter
represents a second hurdle that must be addressed be-
fore the use of CGT as a ruminant feed ingredient can beeffectively moved forward.
Acknowledgements
Support for this research from the Cotton Founda-
tion, the Southern Cotton Ginners Association, and the
Tennessee Agricultural Experiment Station (ProjectNumber TEN 230) is gratefully appreciated. Thanks are
also due to Dr. Arnold Saxton of The University of
Tennessee, Department of Animal Science for assistance
in the statistical analysis.
References
Agrawal, B.D., Verma, L.R., Craig, W.M., 1989. Chemical treatment
of lignocellulosic material for use as ruminant feed. Trans. ASAE
32 (6), 2097–2102.
ASTM Standard D 2495, 1987. Standard test method for moisture in
cotton by oven-drying. Textiles-Yarns, Fabrics, and General Test
Methods 7.01, 688–693.
Buser, M.D., 1999. Update on the extrusion of cottonseed and cotton
gin waste mixtures, In: Proc. Beltwide Cotton Conf., Orlando, FL.
3–7 Jan. 1999. Natl. Cotton Counc. Am., Memphis, TN, pp. 1468–
1472.
Conner, M.C., Richardson, C.R., 1987. Utilization of cotton plant
residues by ruminants. J. Anim. Sci. 65, 1131–1138.
Han, Y.W., Catalano, E.A., Ceigler, A., 1983. Treatments to improve
the digestibility of crop residues. In: Soltes, E.J. (Ed.), Wood and
Agricultural Residues: Research on Use for Feed, Fuels, and
Chemicals. Academic Press, NY, pp. 217–238.
Klopfenstein, T.J., 1978. Chemical treatment of crop residues. J.
Anim. Sci. 46 (3), 841–848.
Klopfenstein, T.J., 1980. Increasing the nutrient value of crop residues
by chemical treatment. In: Huber, J.T. (Ed.), Upgrading Residues
and By-Products for Animals. CRC Press, Boca Raton, FL, pp.
39–60.
Lalor, W.F., Jones, J.K., Slater, G.A., 1975. Cotton gin trash as a
ruminant feed. The Cotton Gin and Oil Mill Press 76 (6), 28–29.
McDougall, E.I., 1948. Studies of ruminant saliva.I. The composition
and output of sheep’s saliva. Biochem. J. 43, 99–109.
![Page 7: Processing Cotton Gin Trash to Enhance in Vitro Dry Matter 2005](https://reader036.vdocuments.net/reader036/viewer/2022081908/552c35784a7959cd7c8b46d4/html5/thumbnails/7.jpg)
L.O. Pordesimo et al. / Bioresource Technology 96 (2005) 47–53 53
Moore, J.E., Mott, G.O., Dunham, D.G., Omer, R.W., 1972. Large
capacity in vitro OM digestion procedure. J. Anim. Sci. 35 (1), 232.
SAS Institute, Inc., 1999. The SAS System Online Doc, Version 8. CD-
ROM. Cary, North Carolina: SAS Institute.
Thomasson, J.A., 1990. A review of cotton gin trash disposal and
utilization. In: Proc. Beltwide Cotton Prod. Res. Conf., Las Vegas,
NV. 9–14 January 1990. Natl. Cotton Counc. Am., Memphis, TN,
pp. 689–705.
Thomasson, J.A., Anthony, W.S., Williford, J.R., Johnson, W.H.,
Gregory, S.R., Calhoun, M.C., Stewart, R.L., 1998. Processing
cottonseed and gin waste together to produce a livestock feed. In:
Proc. Beltwide Cotton Conf., San Diego, CA. 5–9 January 1998.
Natl. Cotton Counc. Am., Memphis, TN, pp. 1695–1698.
Tilley, J.M.A., Terry, R.A., 1963. A two-stage technique for the in
vitro digestion of forage crops. Brit. Grassland Soc. 18 (2), 104–
111.