Livestock Research for Rural Development 13 (4) 2001 | Citation of this paper |
Two trials were carried out to compare voluntary intake and digestibility of rice straw which was treated according to a 3 x 3 factorial design using unslaked lime (0, 3, and 6%, w/w) and urea (0, 2, and 4%, w/w). In Trial 1, 27 growing beef bulls were divided into 9 groups to be fed on the 9 types of straw. Voluntary intake was first measured, followed by digestibility determination when a restricted level of straw (47 g OM/kg W0.75/day) was fed. In Trial 2, three rumen-fistulated adult oxen were fed ad libitum (20% in excess) on the same 9 types of straw to determine intake and digestibility concurrently.
It was found that both lime and urea significantly increased straw intake, digestibility, and thus its energy availability. The intake and digestibility of 2% urea-treated straws and especially 4% urea-treated straws were higher than those of untreated straw. A level of 3% lime significantly increased straw intake and digestibility. Treatment with 6% lime continued to increase apparent digestibility, but depressed straw intake compared with 3% lime in Trial 1. In addition, rumen liquor analyses showed that rumen ammonia (NH3) and total volatile fatty acids (VFA) were decreased by the treatments.
The findings suggest that both lime
and urea are effective in increasing straw intake and apparent digestibility.
Treatments of rice straw with lime and/or urea were effective as judged by chemical composition, in-vitro gas production and in-sacco degradability (Nguyen Xuan Trach et al 2001). However, a measure to improve the feeding value of straw, as a roughage, must then result in increased voluntary intake, digestibility and consequently available energy. This is because animal performance is the product of supply, nutrient concentration, intake, digestibility, and metabolism (Mertens 1994). Voluntary intake and digestibility are thus of great importance in evaluating roughage quality. Direct measurements or estimates of them have always been of major interest to nutritionists (Burns et al 1994; Cochran and Galyean 1994; Weiss 1994; Ørskov 1998). Measurements of these properties would provide convincing indicators for evaluation of different treatments to improve rice straw quality.
The present paper reports
two intake-digestion trials, one on growing and the other on adult cattle, to further
evaluate straw treatments using lime and/or urea. In addition, rumen liquor parameters
were measured to provide additional insights into the mechanisms of the treatment effects.
Sun-dried rice straw (90%
DM) in the long form was treated with quick lime (87% CaO) at 0%, 3% or 6% (w/w) in combination with urea (46%
N) at 0%, 2% or 4% (w/w) according to a 3 x 3 factorial design. The treatment chemicals
were dissolved in required amounts of water to attain 50% moisture content for the treated
straw. The respective solution/suspension was then sprayed onto the straw with a watering
can and thoroughly mixed manually. The mixed straw was then placed in polyethylene sacks
(90 cm x 120cm), which each had been put inside another woven plastic sack of the same
size, and sealed after being carefully pressed to remove as much air as possible. The
sacks were then stored in a shed for 3 weeks at an average ambient temperature of around
25oC.
In Trial 1, a total of 27
growing bulls of a tropical beef breed (Bos indicus) at 12-15 months of age with an
average live-weight of 116kg were allocated into the 9 groups to be fed on the straws. All
animals were dewormed prior to commencement of the experiment. The animals underwent a
transition period of 3 weeks to stabilize straw intake and after that voluntary intake
measurements were made for 10 days. For the following 10 days all the animals were fed
straw at a restricted level of 47g OM/kg/W0.75/day (equal to 80% of the
determined voluntary intake of untreated straw) in preparation for a total collection
period of 11 days, during which time the animals remained on restricted intakes. In Trial
2, three fistulated adult yellow oxen of the same breed (251, 269 and 236kg) were fed ad
libitum (20% in excess) in turn on the same 9 types of straw in a random order. For each
type of straw, voluntary intake measurement, faeces collection and rumen liquor sampling
were concurrently made within 11 days following a 15-day adaptation period.
In both trials, animals
were kept in a well-ventilated shed with a cement floor and fed in individual pens. Rice
straw was the sole energy source in the diets, which were supplemented with 1% of bone
meal and 1% of a vitamin-mineral mixture. Urea, 32 g and 16 g/kg straw respectively, was
additionally given to the 0% and 2% urea-treated straws prior to feeding to equalize the
total N level to that of 4% urea-treated straw (20 % urea-N already lost after treatment)
in order to exclude the effect of nitrogen supplementation. The added urea was dissolved
in required amounts of water before spraying to maintain the moisture of untreated straw
similar to that of the treated straws (approximate 50%). Drinking water was freely
supplied at all times.
Voluntary intake of straw
was measured according to Burns et al (1994). Straw was given twice a day at 7 am and 4 pm
with 20% in excess of the average intake of the previous 5 days. All the residues left
from the previous day were removed from the feeding trough in the morning and weighed. A
sample of 100 g was then taken to create a pooled sample for the whole collection period.
Newly fed straw was also sampled from the trough with 100 g taken every day to create a
composite sample for each type of straw. Animal weights were recorded at the beginning and
end of the intake and/or digestion periods. Straw dry matter (DM) and organic matter (OM)
intakes were expressed both as a percentage of live-weight (% LW) and in g per kg
metabolic weight (g kg/W0.75).
Digestibility
determination was organized according to Cochran and Galyean (1994). Representative samples of the straws were taken at
feeding and saved as part of the "running" composite samples for 10 days. Faeces
collection began 1 day following the start of straw sampling. It was quantitatively collected immediately after
excretion and 5% of the bulked faeces were then taken to make a composite sample for 10
days for each type of straw per animal. The running samples of straw and faeces were then
stored at -20oC for subsequent analyses. Before chemical analysis the
representative samples of straws and faeces were thawed and mixed thoroughly. A portion of
each composite sample was taken and pre-dried at 55oC for 72h in a forced air
draught oven, then left to cool for 4 h and ground to pass a 1mm screen.
The
apparent digestibility was calculated according to Cochran and Galyean (1994) for organic
matter (OMD) and neutral detergent fibre (NDFD). The formulae proposed by van Es (1978)
for estimation of metabolisable energy of a low protein roughage was used to estimate rice
straw energy availability, which is ME (MJ) = 15.1 * DOM, where ME is metabolisable energy
in Mega-joule (MJ) and DOM is digestible organic matter. Metabolisable energy of straw in
the present case was calculated particularly on an organic matter (OM) basis to exclude
the differences in the ash content of straw DM due to lime treatment.
Rumen liquor samples were
collected on two consecutive days in the middle of each collection period in Trial 2
between three and four hours after the morning feeding. Samples were taken with a 50 ml
syringe connected to a 50 cm long plastic tube introduced through the fistula. The pH
value of rumen liquor was determined immediately after the sample was taken using a
portable pH meter. Each sample of 25 ml was then placed in a 30ml bottle acidified with 5
drops of concentrated sulphuric acid and then stored at -20oC until analysed
for ammonia (NH3) and total volatile fatty acids (VFA).
Straw and faeces samples
were analysed for dry matter (DM) and crude ash according to AOAC (Cunniff 1997). NDF
content was determined according to Van Soest and Robertson (1985). Ammonia was separated
from rumen liquor by steam distillation, collected in boric acid solution and determined
by titration with standard acid (Preston 1995). Total VFA was also determined by steam
distillation according to AOAC (Cunniff 1997).
Data were analysed using
the GLM (General Linear Model) procedure of the SAS package (1996). For trial 1, a fixed
3x3 factorial model of analysis of variance (ANOVA) was applied. Factor level means were
separated by the Ryan-Einot-Gabriel-Welsch (REGWQ) multiple range test. In addition, the
two levels of urea (2% and 4%) as well as the two levels of lime (3% and 6%) were linearly
combined together to contrast with non-urea or non- lime treated straw, respectively. For
Trial 2, similar procedures were applied, except that the animal factor was included in
the model as a block.
Both lime and urea
increased straw OMI in both trials (Table 1). The intake of 6% lime-treated straw tended
to be lower than that of 3% treated straw in growing cattle and almost the same between
the two lime levels in adult cattle. Growing cattle tended to respond better to straw
treatment in terms of intake. For example, treatment with 2% urea plus 3% lime increased
OMI by 32% in growing cattle compared to 24% in adult cattle. No significant
interaction between lime and urea was found in adult cattle, but it was significant in the
growing cattle of Trial 1. When urea was combined with lime, the differences in OMI
between the two levels of urea (2% and 4%) were no longer apparent.
Table1: Effects of
treatment with lime and/or urea on organic matter intake (OMI) of rice straw by growing
and adult cattle |
|||||||
Treatment |
Chemical input (%) |
Growing cattle (Trial 1) |
Adult cattle (Trial 2) |
||||
Lime |
Urea |
% LW |
g kg/W0.75 |
% LW |
g kg/W0.75 |
||
Means by treatment |
|||||||
I |
0 |
0 |
1.79a |
58.7a |
1.80a |
71.6a |
|
II |
0 |
2 |
2.15b |
70.4bc |
1.96b |
78.2b |
|
II |
0 |
4 |
2.34bc |
77.1c |
2.14c |
85.0c |
|
IV |
3 |
0 |
2.29bc |
77.3c |
2.09bc |
83.3bc |
|
V |
3 |
2 |
2.40c |
77.5c |
2.24c |
88.8c |
|
VI |
3 |
4 |
2.39c |
78.9c |
2.24c |
89.0c |
|
VII |
6 |
0 |
2.13b |
69.4b |
2.13c |
84.6c |
|
VIII |
6 |
2 |
2.32bc |
75.7c |
2.24c |
89.0c |
|
IX |
6 |
4 |
2.25bc |
74.3bc |
2.25c |
89.1c |
|
SEM |
0.07 |
2.0 |
0.05 |
2.0 |
|||
Factorial effects and contrasts |
|||||||
Lime |
** |
*** |
*** |
*** |
|||
Urea |
*** |
*** |
*** |
*** |
|||
Urea x Lime |
* |
** |
Ns |
Ns |
|||
Animal |
- |
- |
Ns |
Ns |
|||
Lime vs. No lime |
*** |
*** |
*** |
*** |
|||
Urea vs. No urea |
*** |
*** |
*** |
*** |
|||
* P<0.05, ** P<0.01, *** P<0.001, Ns:
non-significant; |
It was found in Trial 1
that both lime and urea increased OMD and NDFD (Table 2). When urea was used in
combination with lime no significant difference was found between the two levels of urea.
The differences between 3% and 6% lime were not statistically significant. In Trial 2 (ad
libitum feeding) the OMD and NDFD appeared to be lower than in Trial 1 (restricted
feeding) (Table 3). For instance, 3% lime plus 2% urea increased OMD by 13.0 percentage
points in Trial 1, compared to only 10.5 percentage points in Trial 2. Treatment effects
in Trial 2 were not as clear as in Trial 1. In both trials OMD was significantly
(P<0.001) increased by both lime and urea without any significant interaction found
between the two chemicals. NDFD was also increased (P<0.001) by both lime and
urea with a significant interaction (P<0.05) to reduce their additive effects in Trial
1. In Trial 2 the effect of lime on NDFD was still significant (P<0.01), whereas urea
apparently increased NDFD in absolute terms but the effect was not statistically
significant (P = 0.08).
Table 2: Apparent
digestibility and estimated metabolisable energy (ME) of rice straw treated with lime
and/or urea and fed to growing cattle at a restricted level (Trial 1) |
||||||
Treatment |
Chemical input
(%) |
Apparent
digestibility (%) |
ME |
|||
Lime |
Urea |
OMD |
NDFD |
(MJ
kg/OM) |
||
Means by
treatment |
||||||
I |
0 |
0 |
49.3a |
53.6a |
7.45a |
|
II |
0 |
2 |
55.9b |
58.4b |
8.44b |
|
II |
0 |
4 |
59.5c |
63.5cd |
8.98b |
|
IV |
3 |
0 |
57.8b |
61.4c |
8.73b |
|
V |
3 |
2 |
62.3c |
65.6d |
9.41c |
|
VI |
3 |
4 |
63.2c |
65.4d |
9.54c |
|
VII |
6 |
0 |
58.1b |
62.1c |
8.77b |
|
VIII |
6 |
2 |
62.6c |
66.0d |
9.45c |
|
IX |
6 |
4 |
64.3c |
66.2d |
9.70c |
|
SEM |
0.9 |
0.9 |
0.14 |
|||
Factorial effects and contrasts |
||||||
Lime |
*** |
*** |
*** |
|||
Urea |
*** |
*** |
*** |
|||
Urea x lime |
Ns |
* |
Ns |
|||
Lime vs. No lime |
*** |
*** |
*** |
|||
Urea vs. No urea |
*** |
*** |
*** |
|||
Notes: OMD = organic matter digestibility, NDFD = neutral
detergent fibre digestibility, SEM = standard
error of mean; * P<0.05, ** P<0.01, *** P<0.001, Ns: non-significant; Means
within each column under the same subheading bearing the same superscript (abcd) are not
different at P<0.05. |
||||||
|
||||||
Treatment |
Chemical input (%) |
Apparent
digestibility (%) |
ME |
|||
Lime |
Urea |
OMD |
NDFD |
(MJ
kg/OM) |
||
Means by
treatment |
||||||
I |
0 |
0 |
48.2a |
50.3a |
7.27a |
|
II |
0 |
2 |
53.9b |
54.3a |
8.13b |
|
II |
0 |
4 |
57.1c |
59.8b |
8.63c |
|
IV |
3 |
0 |
55.5bc |
58.3ab |
8.37bc |
|
V |
3 |
2 |
58.7cd |
60.5b |
8.87cd |
|
VI |
3 |
4 |
60.3d |
61.0b |
9.10d |
|
VII |
6 |
0 |
56.6bc |
59.7b |
8.55bc |
|
VIII |
6 |
2 |
60.5d |
61.3b |
9.14d |
|
IX |
6 |
4 |
60.2cd |
60.8b |
9.10d |
|
SEM |
1.0 |
1.5 |
0.15 |
|||
Factorial
effects and contrasts |
||||||
Lime |
*** |
** |
*** |
|||
Urea |
*** |
0.08 |
*** |
|||
Urea x lime |
Ns |
Ns |
Ns |
|||
Animal |
* |
Ns |
* |
|||
Lime vs. No lime |
*** |
** |
*** |
|||
Urea vs. No urea |
*** |
0.06 |
*** |
|||
Notes: OMD = organic matter digestibility, NDFD = neutral
detergent fibre digestibility, SEM = standard
error of mean; * P<0.05, ** P<0.01, *** P<0.001, Ns: non-significant; Means
within each column under the same subheading bearing the same superscript (abcd) are not
significantly different at P<0.05. |
||||||
Straw ME was greatly
increased by lime and/or urea treatment (P<0.001). As a result of higher digestibility
due to restricted feeding, the straw ME values were higher in Trial 1 than in Trial 2.
Compared to untreated straw, the value of ME was increased by 32% and 26% due to the best
treatment in Trial 1 and Trial 2, respectively. In the absolute terms, combination of 6%
lime with 4% urea (in Trial 1) or 2% urea (Trial 2) resulted in the highest values of
straw ME. However, when lime and urea were combined for treatment, the differences in
effect on straw ME between 4% and 2% urea or 6% and 3% lime were not significant.
Rumen pH and NH3 tended
to decline while VFA increased with increasing application rates of urea for treatment,
although the effects of lime and urea on rumen pH were non-significant (Table 4). Rumen NH3
concentration was lowest for diets based on 4% urea-treated straw and highest for
urea-supplemented untreated straw diets. The contrast setting revealed a significant
influence of lime treatment on rumen NH3 concentration (P<0.05). Both lime
and urea significantly increased rumen VFA. However, no significant differences between
the effects of 3% and 6% lime on the three parameters of rumen liquor were detected.
Table 4: Rumen
liquor pH, ammonia (NH3) and total volatile fatty acids (VFA) contents in
cattle fed on rice straw treated with lime and/or urea |
||||||
Treatment |
Chemical input
(%) |
Rumen liquor
parameters |
||||
Lime |
Urea |
pH |
NH3 (mg/litre) |
VFA
(mmol/litre) |
||
Means by
treatment |
||||||
I |
0 |
0 |
7.03 |
297a |
70.6a |
|
II |
0 |
2 |
6.87 |
280ab |
82.1b |
|
II |
0 |
4 |
6.84 |
258b |
93.3c |
|
IV |
3 |
0 |
6.95 |
286a |
84.6b |
|
V |
3 |
2 |
6.82 |
262b |
93.2c |
|
VI |
3 |
4 |
6.78 |
247b |
97.3c |
|
VII |
6 |
0 |
6.85 |
277ab |
86.0bc |
|
VIII |
6 |
2 |
6.86 |
263b |
93.3c |
|
IX |
6 |
4 |
6.81 |
255b |
95.3c |
|
SEM |
0.05 |
9 |
2.9 |
|||
Factorial effects and contrasts |
||||||
Lime |
Ns |
Ns |
*** |
|||
Urea |
Ns |
*** |
*** |
|||
Urea x lime |
Ns |
Ns |
Ns |
|||
Animal |
Ns |
Ns |
* |
|||
Lime vs. No lime |
Ns |
* |
*** |
|||
Urea vs. No urea |
Ns |
*** |
*** |
|||
Notes: * P<0.05, ** P<0.01, *** P<0.001, Ns: non-significant; Means within each column under
the same subheading bearing the same superscript (abc) are not significantly different at
P<0.05. |
||||||
Urea
treatment may increase intake of straw in the range of 15 to 50% as reviewed by Chenost
and Kayouli (1997). Straw intake was increased by urea treatment in the present study in
the lower half of this range. This is probably because in the present study, untreated
straw was supplemented with urea at feeding. In non-supplemented rice straw the crude
protein content is too low to meet the requirement of rumen microbes and thus
supplementation of NPN increases digestion and thus intake due to increased microbial
protein production (Doyle et al 1986; Djajanegara and Doyle 1989). Therefore, it has
usually been uncertain to what extent the increased nutritive value of urea-treated straw
is a result of NPN supplementation and to what extent it is a result of changes in the
structure of the straw due to treatment effects (Schiere and Nell 1993). However, the
increases in straw intake found in the present study were probably due only to treatment
effect because N was no longer a limiting factor in all the straws under comparison owing
to urea supplementation prior to feeding.
The
increased straw intake due to present treatments may thus be explained by virtue of its
increased degradability in the rumen as previously reported (Nguyen Xuan Trach et al
2001). An increase in the outflow of straw cell walls into the abomasum as a result of
alkali treatment has also been reported (Males 1987). These possible effects of alkali
treatment can aid in explaining the increases in straw intake in the present study.
The present findings show
that both lime and urea are effective in increasing OMD and NDFD. In general, the higher
the level of lime and/or urea applied in the present study, the more digestible the
treated straw became. This was in agreement with the increased delignification, in-vitro
gas production and in-sacco degradability of straw due to the treatments (Nguyen
Xuan Trach et al 2001). Increased straw digestibility due to urea treatment has been well
documented previously (Sundstøl and Coxworth 1984; Doyle et al 1986; Schiere and Ibrahim
1989; Chenost and Kayouli 1997; Madrid et al 1997). That lime treatment in the present
study increased apparent digestibility of rice straw is in agreement with Selvendran
et al (1977), Saadullah et al (1981) and Chaudhry
(1998). Improvements in straw apparent digestibility as a result of treatment with lime
and urea in combination have also been reported by Zaman and Owen (1990) and Sahoo et al
(2000).
Since the
rumen is the primary site for fibre digestion, the increases in apparent digestibility of
the treated straws were presumably due to increased rumen degradability resulted from
increased susceptibility of structural carbohydrates of straw cell walls to rumen
fermentation as well as more energy being made available for better growth of rumen
microbes which degrade straw (Silva and Ørskov 1988; Rai and Mudgal 1988). The rumen
retention time is actually not sufficient for the maximal fermentation of the substrate,
thus an increase in degradation rate, as a result of increased straw degradability and
better microbial activity, would cause a substantial improvement in digestibility and also
in voluntary intake (Ørskov 1994).
In the present study,
NDFD was slightly higher than OMD. This may be because measurements of apparent NDF
digestibility over-estimated the digestibility of original cell wall material for treated
straws since the compounds, which are solubilised, are unlikely to be completely digested
(Djajanegara and Doyle 1989). Moreover, the determination of NDF is not confounded with
any endogenous or microbial sources in the faeces.
Although not compared
statistically, the apparent digestibility of straw cell wall components was generally
higher in Trial 1 than in Trial 2. This is in agreement with the finding by Misra et al
(1995) that digestibility of NDF was higher under restricted feeding of wheat straw and
rice straw compared with ad libitum feeding regimes. This may be related to longer
retention time under restricted feeding since the extent of degradation can be increased
if rumen retention time is prolonged (Ørskov 1994).
The general
decreases in rumen liquor pH and increases in VFA (Table 4) due to the treatments were
probably a reflection of the improvements in the ruminal fermentation rate as previously
found (Nguyen Xuan Trach et al 2001), which resulted in increased OMD and NDFD (Tables 2
and 3). Those groups with higher digestibilities showed higher values of VFA and lower
values of pH. This is presumably because VFA was the end product of rumen microbial
degradation of straw, and the more the VFA produced, the lower the resulting rumen pH.
Jayasuriya et al (1987) have concluded that the output of VFA increases with the increase
in feed intake. This explains the increased VFA content in the present observation.
Although the N
level in straw was deliberately equalized prior to feeding, urea-treated straws resulted
in lower rumen NH3 concentrations than urea-supplemented straws. Singh and
Gupta (1988) have also found significant lower ammonia nitrogen concentration in strained
rumen liquor in buffaloes fed on ammonia treated straw compared with untreated straw. The
higher rumen NH3 resulted from supplemented straws may have been due also to
greater part of the urea from the supplemented diets converted to free ammonia than the N
provided by the urea-treated straws (Chermiti
et al 1994). More favourable conditions for rumen microbes to grow and thus capture more
free ammonia in the rumen liquor (Singh and Gupta 1988; Chaudhry 1998) may be another
explanation for the reduced rumen ammonia concentration due to lime and/or urea treatment.
Results of our previous
study (Nguyen Xuan Trach et al 2001) indicated that the effect of lime on in-sacco
degradability and in-vitro fermentability of rice straw was increased with
increasing application level. However, the present in-vivo results showed that 6%
lime was not significantly better than 3% lime in increasing straw intake, digestibility
and VFA. A level of 6% lime even reduced straw intake in growing cattle, compared with 3%
lime. This would suggest some negative responses in-vivo to straw treated with too
high a level of lime. This situation is
similar to that of NaOH treatment as reviewed by Ribeiro (1989) where an application level
above 6% resulted in in-vivo digestibility and voluntary daily intake tending to
level off or even decrease while the IVDMD continued to increase.
The discrepancy between
the in-vivo digestibility and in-vitro or in-sacco results further
indicate that 6% lime is too high a level to maintain favourable rumen conditions for
actual rumen degradation, although it can highly improve degradability/ fermentability of
straw as a substrate. As previously shown (Nguyen Xuan Trach et al 2001), the rate of in-sacco
degradation of hay as a standard substrate was lower when the animals were fed on 6%
compared to 3% lime or urea-treated straws. The similar apparent digestibility and VFA
content that resulted from feeding 6% and 3% lime-treated straws have probably been a
reflection of a compromise between the highly increased degradability of straw and the
less favourable rumen conditions associated with 6% lime. Unpalatability of straw treated
with too high a level of lime (6%) may be a possibility for reduction in voluntary intake
of the straw (Hove personal communication, 2000).
However, a reasonable level of lime may improve straw palatability due to an effect of
lime in reducing oxalates (Mudgal et al 1996).
Information is limited to
elucidate why 6% lime did not have more positive effects on straw intake and in-vivo
digestibility compared to 3% lime. In
general, high concentrations of dietary calcium are tolerated well by cattle (NRC 1996),
and most of the additional calcium is excreted in the faeces (Djajanegara et al 1984). However,
Ammerman et al (1963) have reported that
protein and energy digestibility were reduced when cattle were fed a diet containing 4.4%
Ca. In addition, Alfaro et al (1988) have also found some negative effects of high dietary
Ca (2.35%) on metabolism of phosphorus, magnesium and certain trace elements, although the
changes were relatively small. Although ruminants can tolerate wide Ca: P ratios (Call et
al 1978), a ratio of Ca: P higher than 7:1 has been reported to reduce growth and feed
efficiency (Wise et al 1963; Ricketts et al 1970). Another possible cause for 6% lime
being no better than 3% lime is that a larger effect of a high lime level on straw cell
wall degradability may, at the same time, be offset by a stronger effect on the lignin
molecule to release phenolic acids, which are toxic to rumen microbes (Akin et al 1988;
Chaudhry 2000).
Whatever the reasons may have been, since 6% lime is not superior to 3% lime in increasing straw intake and digestibility and if a maximum tolerable concentration of Ca in feed for beef cattle is 2% as indicated by NRC (1984), a level of 3% lime should be maximum for rice straw treatment. However, further research in this area is needed before a firm conclusion can be made.
Based on the present
study, 3% lime should be used in combination with urea to ensure the overall effectiveness
of straw treatment. The additive effects of lime and urea on apparent digestibility of
straw create the possibility that lime and urea can be used in combination as alkalis for
treatment together with NPN and Ca supplementation of rice straw.
The authors would like to
thank the Norwegian Council of Universities' Committee for Development Research and
Education (NUFU) for the financial support to the present study. Special thanks are
extended to Dr. Frik Sundstøl, Dr. Le Viet Ly, and Dr. Nils Petter Kjos for their
facilitation and advice during the experimentation and manuscript preparation.
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