RATIONAL METHODS FOR PREDICTING QUALITY
AND DIGESTIBLE ENERGY CONCENTRATION OF
WARM-SEASON FORAGES FOR RUMINANTS
By
Edward J. Golding, III
A DISSERTATION PRESENTED TO THE GRiVDUATE COUNCIL OF
THE UNIVERSITY OF FLORIDA
IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE
DEGREE OF DOCTOR OF PHILOSOPHY
UNIVERSITY OF FLORIDA
1976
, to the future of my family,
Astrid
Nico3.e
Christopher;
and to those who understood.
ACKNOWLEDGMENTS
The author wishes to express his deep appreciation to Dr.
John E. Moore, Chairman of the Supervisory Committee, for his
continued interest, helpful ideas and professional guidance during
the investigations documented in, and during the writing of, this
manuscript. Appreciation is also extended to the Members of the
Supervisory Committee, Dr.s C. B. Ammerman, J. H. Conrad, D. E.
Franke and G. 0. Mott, for willingly sharing their knowledge and
for reviewing this dissertation. The statistical aid provided by
Dr. R. C. Littell and Dr. D. 0. Dixon, and the mathematical assistance
of Dr. K. N. Sigmon are greatly appreciated. Thanks are also ex-
tended to Miss Jan Ferguson and Mrs. Edwina Williams for aid in
conducting chemical and Jji vitro analyses. Help provided the author
by the staff and personnel of the Nutrition Laboratory in solving
the every-day problems is gratefully acknowledged, as is the assistance
and friendship of fellow graduate students.
Financial assistance provided by the Department of Animal Science,
University of Florida, is gratefully acknowledged, as are the efforts
of Dr. Moore and Dr. Conrad in obtaining these funds.
The author wishes to express his appreciation to Mrs. Susan
Weller and Mrs. Pat Beville for typing this manuscript.
TABLE OF CONTENTS
Page
ACKNOWLEDGMENTS
LIST OF TABLES
LIST OF APPENDIX TABLES
LIST OF FIGURES
ABSTRACT
CHAPTER
I INTRODUCTION
II REVIEW OF LITERATURE
Expressions of Forage Quality
Digestible Energy Intake, Digestible Dry Matter Intake
and Digestible Organic Matter Intake
Nutritive Value Index
Retention Time of Organic Matter in the Rumen
Control of Forage Intake by Ruminants
The Distention Mechanism
Site and mechanism of distention control
Relative importance of "fill" and "retention time"
Factors Affecting Retention Time
Factors affecting rates of digestion and passage
Intake vs Rate of Digestion ^ Vitro
Prediction of Forage Nutritive Value
Applicability of Predictors of Nutrient Digestibility
Chemical analyses
In vitro organic matter digestion
Summative equations
Applicability of Predictors of DE Concentration in
Forage DM
In vitro cellulose digestibility
Dry matter digestibility
Crude protein percentage of dry matter
Prediction of Forage Quality
Applicability of Various Techniques for Quality Pre-
diction
Ix
1
3
3
3
7
7
8
8
10
11
12
14
17
18
19
19
19
20
20
20
21
22
22
23
TABLE OF CONTENTS-continued
Page
Chemical analyses and suiuniative equations 23
In vitro techniques 23
The nutritive value index 25
Retention time of organic matter in the rumen 25
Mathematical Modeling of Dynamic Systems 25
III PREDICTION OF DIGESTIBLE ENERGY CONCENTRATION IN FORAGE
FOR PURPOSES OF MARKETING SOUTHERN HAYS 28
Introduction 28
Experimental Procedure 29
Theory Related to Rational Prediction of DE/DM 29
Prediction of DOM 30
Prediction of DE/DM 32
Testing the Procedure 33
Forages and ^IL ^i^o data 33
Laboratory analyses and prediction testing 34
Results and Discussion 35
Chemical Analyses 35
In Vivo and ^H Vitro Determinations 38
NDF digestibility 38
Digestible neutral-detergent fiber and neutral-
detergent solubles 39
OM digestibility 41
Digestible organic matter 41
Metabolic fecal organic matter by calculation 41
Estimation of metabolic fecal organic matter by
regression 42
Prediction of NDFD, DOM and DE/DM 43
Testing of DOM and DE/DM Predictions 47
Acceptability limits for judging the predictions 47
Acceptability of the predictions 48
General Discussion 54
Non-Forage Factors Affecting DE/DM 5 4
Research Needs for Rapid and Accurate DOM Prediction 55
Summary 57
IV ELIMINATION OF ORGANIC SOLVENTS IN THE STUDY OF IN VITRO
NEUTRAL-DETERGENT FIBER DIGESTION 59
Introduction 59
Experimental Procedure 59
TABLE OF CONTENTS-continued
Page
Results and Discussion 61
Summary 66
V A RATIONAL METHOD FOR PREDICTING QUALITY OF WARM-SEASON
FORAGES FOR RUMINANTS 67
Introduction 67
Experimental Procedure 68
Development of Theory Related to Rational Method for
Prediction of Forage Quality 68
Estimation of RTOM 70
Establishing the value of g 71
Estimation of k, 72
Estimation of k 73
Theory relative to 'a', and its estimation 73
Prediction of organic matter digestibility 75
Testing the Procedure 76
Forages and ^ vivo data 76
Laboratory analysis of forages 77
Regression analyses 78
Generation of the prediction equation 78
Testing the acceptability of quality predictions 79
Results and Discussion 82
Laboratory Characteristics of Forages Utilized 82
Actual and Predicted 2ll Vivo Values of Forages Utilized 84
Testing of DOMI and OMI Predictions 90
Acceptability limits for quality and intake predictions 90
Acceptability of quality and intake predictions 92
Utility of Relationships Between Various Measurements
and Analyses 99
Prediction of organic matter digestibility 99
Prediction of intake from neutral-detergent fiber
percentage 100
Prediction of k 101
Prediction of k 103
General Discussion 104
Non-Forage Factors Which Could Override or Modify RTOM 104
Theoretical Methods for Prediction of k 106
Summary 109
APPENDIX 112
LITERATURE CITED 131
BIOGRAPHICAL SKETCH 149
LIST OF TABLES
Table Page
1. MEASURES OF CENTRAL TENDENCY AND DISPERSION OF THE
CHARACTERISTICS OF 52 FLORIDA FORAGES 36
2. GROSS ENERGY, ENERGY DIGESTIBILITY AND ACTUAL AND
PREDICTED DIGESTIBLE ENERGY CONCENTRATIONS IN 10
WARM-SEASON GRASSES 44
3. CONSERVATIVE AND LIBERAL ACCEPTABILITY LLMITS FOR
TESTING PREDICTIONS OF DIGESTIBLE ORGANIC MATTER (DOM)
AND DIGESTIBLE ENERGY (DE) CONCENTRATION 49
4. EFFECT OF ACETONE ON THE DETERMINATION OF ASH-FREE
NEUTRAL-DETERGENT FIBER (NDFA) IN EIGHT HAYS 62
5. EFFECT OF HAY AND STOP-METHOD ON IN VITRO RESIDUAL
ASH-FREE NEUTRAL-DETERGENT FIBER (NT)FA) 64
6. EFFECT OF STOP-METHOD AND REPLICATE (REP) ON IN VITRO
RESIDUAL ASH-FREE NEUTRAL-DETERGENT: FIBER (NDFA) 65
7. MEASURES OF CENTRAL TENDENCY AND DISPERSION OF THE
LABORATORY CHARACTERISTICS OF 31 WARM-SEASON GRASSES 83
8. MEASURES OF CENTRAL TENDENCY AND DISPERSION OF THE
ACTUAL AND PREDICTED IN VIVO VALUES OF 31 WARM-
SEASON GRASSES 85
9. CONSERVATIVE AND LIBERAL ACCEPTABILITY LIMITS FOR
TESTING PREDICTIONS OF DIGESTIBLE ORGANIC MATTER
INTAKE (DOMI) AND ORGANIC MATTER INTAKE (OMI) 93
LIST OF APPENDIX TABLES
Table Page
10. LABORATORY CHARACTERISTICS OF 31 WARM-SEASON GRASSES 113
11. ACTUAL AND PREDICTED IN VIVO VALUES OF 31 WARM-SEASON
GRASSES 118
12. LABORATORY CHARACTERISTICS AND ACTUAL AND PREDICTED
IN VIVO VALUES OF 21 ADDITIONAL FORAGES USED TO TEST
THEORETICAL EQUATION FOR PREDICTION OF DIGESTIBLE
ORGANIC MATTER (DOM) AS PERCENT OF DRY MATTER 123
13. ALGEBRAIC MANIPULATIONS OF EQUATION 9 REQUIRED TO
PRODUCE EQUATION 10 (CHAPTER V) 126
14. DYNAMO COMPUTER PROGRAM FOR PREDICTION OF FORAGE DOMI,
DEI (WITH AND WITHOUT ENERGY SUPPLEMENT) , REPLACEMENT
RATE, OMI, OMD, DOM, DE/DM, DE/OM, NDFD , DNDF, A, B
AND RTOM 127
LIST OF FIGURES
Figure Page
1. TEST OF THEORETICALLY RATIONAL METHOD FOR PREDICTION
OF DIGESTIBLE ORGANIC MATTER AS A PERCENTAGE OF DRY
MATTER. 50
2. COMPARISON OF IN VIVO DIGESTIBLE ENERGY (DE) WITH THAT
PREDICTED FROM ACTUAL IN VIVO DIGESTIBLE ORGANIC MATTER
(DOM) AND CRUDE PROTEIN (CP) BY THE EQUATION: 52
DE = 4.15 DOM + 1.299 CP - 4.59.
100
3. COMPARISON OF IN VIVO DIGESTIBLE ENERGY (DE) WITH THAT
PREDICTED FROM~PREDICTED IN VIVO DIGESTIBLE ORGANIC
MATTER (DOMp) AND CRUDE PROTEIN (CP) BY THE EQUATION: 33
DE = 4.15 DOMp + 1.299 CP - 4.59.
100
4. RELATIONSHIP BETWEEN NEUTRAL -DETERGENT FIBER DIGESTIBILITY
IN VIVO AND IN VITRO FOR EACH OF THREE WARM-SEASON GRASSES
(Data taken from Velasquez, 1974). 86
5. RELATIONSHIP BETWEEN DIGESTIBLE ORGANIC MATTER INTAKE
AND RETENTION TIME OF ORGANIC MATTER IN THE RUMEN FOR
THREE SPECIES OF WARM-SEASON GRASSES. 89
6. RELATIONSHIP BETWEEN ORGANIC MATTER INTAKE AND ACID-
DETERGENT FIBER PERCENTAGE FOR THREE SPECIES OF WARM-
SEASON GRASSES. 91
7. TEST OF RETENTION TIME OF ORGANIC MATTER IN THE RUMEN AS
A RATIONAL PREDICTOR OF DIGESTIBLE ORGANIC MATTER INTAKE. 94
8. TEST OF THEORETICALLY RATIONAL METHOD FOR PREDICTION OF
ORGANIC MATTER INTAKE. 97
9. TEST OF EMPIRICAL PREDICTION OF ORGANIC MATTER INTAKE
FROM ACID-DETERGENT FIBER PERCENTAGE OF DRY MATTER. 98
Abstract of Dissertation Presented to the Graduate Council
of the University of Florida in Partial Fulfillment of the
Requirements for the Degree of Doctor of Philosophy
RATIONAL METHODS FOR PREDICTING QUALITY
AND DIGESTIBLE ENERGY CONCENTRATION OF
WARM-SEASON FORAGES FOR RUMINANTS
By
Edward J. Golding, III
March, 1976
Chairman: Dr. John E. Moore
Major Department: Animal Science
Three separate studies were conducted to (a) devise and test
theoretically rational and acceptably accurate methods for predicting
digestible organic matter (DOM), digestible energy (DE) concentration
and DOM intake (DOMI) of forages; and (b) investigate alternative lab-
oratory methods which eliminate organic solvents in the determination
of ash-free neutral-detergent fiber (NDFA) in hay samples and resi-
dues of in vitro fermentation. These studies included 43 hays from
three species of warm-season grasses (Paspalum notatum Flugge, Cynodon
dactylon (L) Pers. , and Digitaria decumbens Stent) and nine hays of
Medicago sativa L. Conservative and liberal acceptability limits,
which corresponded to the weighted average of the 95 percent confi-
dence interval for means, and plus and minus two weighted average
population standard deviation estimates, respectively, were used to
judge acceptability of DOM, DE and DOMI predictions.
Acceptable predictions of DE for 10 grasses were based on DOM
and digestible crude protein concentrations in forage. Acceptable pre-
dictions of DOM were made for all 52 forages by summing neutral-detergent
solubles (NDS) and in vivo digestible NT)FA, and subtracting a constant
10.3 for metabolic fecal organic matter, all as percentages of dry matter
(DM) . The Van Soest Summative Equation did not accurately predict NDFA
digestibility (NDFD) for warm-season grasses; and discrepancies apparent-
ly exist between alfalfa and grasses with respect to the in vivo NDFD -
in vitro NDFD relationship. The remaining challenge with respect to
DOM and DE prediction, therefore, is development of a rapid procedure
for accurate prediction of digestible NDFA over a wide range of forages.
Acetone washes for determinations of NDFA in hays appeared necess-
ary, but probably could be excluded when analyzing for in vitro residual
NDFA. Terminating fermentation by setting tubes in an ice-water bath
to the level of their contents for 1 hr was an acceptable alternative
to use of toluene. These studies were based on eight hays having a
wide range of NDFA and NDFD.
Ruminal retention time of organic matter (RTOM) was a theoretically
rational independent variable for predicting DOMI. A published equation
for plotting disappearance of cellulose from the rumen through time
was applied to total organic matter (OM) and used to estimate RTOM
values for 31 grasses. For each grass, the value for the rate constant
(k ) for rate of digestion was estimated by in vitro procedures, while
the rate constant (k^) for rate of passage was calculated from known
lignin intake. Estimates of the potentially digestible fraction of
ruminal OM ('a') were made using the formula for 'a' developed in this
study, and the potentially indigestible fraction of ruminal OM was
equal to one minus 'a'. An equation for prediction of DOMI from RTOM
was generated using 15 forages, and the 16 predictions produced by
this equation were acceptable. Actual values of k^, though relatively
invariant, cannot be assumed constant among forages, nor can these
values be predicted accurately at present from predicted values of 'a'.
Rational prediction of OM intake (OMI) was accomplished by divid-
ing predicted DOMI by predicted OM digestibility. This procedure was more
acceptable than empirical prediction of OMI from acid-detergent fiber
or NDFA percentage.
CHAPTER I
INTRODUCTION
In 1972, forages provided some 73 percent of the feed require-
ments for beef cattle, 63 percent for dairy cattle and about 89
percent for sheep and goats in the United States (Wedin et al., 1975).
These figures may be higher today, since grain feeding is less profit-
able in many areas and ruminant production is becoming increasingly
dependent upon grassland farming. Thus, it is becoming imperative
that producers possess accurate information relative to the quantity
and quality of forage available to them. Relatively fast and accurate
estimation of forage production offers little problem to the experienced
practicioner , but rapid and accurate prediction of forage quality
cannot be achieved across a wide range of forage species. Such pre-
dictions of forage quality are required by the objective producer
even if limited grain is to be fed to ruminants. Thus, an important
research area today concerns the rapid and accurate prediction of
quality across a wide range of forages.
Accurate knowledge of forage quality by itself however, may be of
little value to the producer. This is because digestible nutrient
intake may greatly diverge across a number of given situations from
that indicated by laboratory predictions of forage quality. Dynamic
computer modeling is a process which is becoming more widely employed
in today's research in several biological disciplines. Such modeling
may be capable of accurately predicting digestible nutrient intake for
a given situation if the factors which affect this parameter, the
methods by which such factors mediate their influence, and/or the
magnitudes of the effects of these factors can be elucidated over a
wide range of forages. Divulgence and use of such information,
however, requires cooperation by teams of researchers who integrate
their knowledge in order to achieve the rapid, efficient and accurate
solution to a common problem. Such cooperation among researchers is
fast becoming a requirement if the persistence or betterment of man's
present standard of living is to be insured.
In this dissertation, three separate studies were conducted to
(a) devise and test theoretically rational and acceptably accurate
methods for predicting digestible energy concentration and digestible
organic matter intake of forages; and (b) investigate alternative
laboratory methods which eliminate organic solvents in the determination
of ash-free neutral-detergent fiber in hay samples and residues of
in vitro fermentation.
CHAPTER II
REVIEW OF LITERATURE
Expressions of Forage Quality
Moore and Mott (1973) state that when forage availability is not
a limiting factor, and when animal potential is invariant between
treatments, then the best measure of forage quality is output per ani-
mal. Minson (1968) suggested that this output could be in terms of
milk, meat or wool, and also agreed (1971a) that the grazing trial is
the most reliable method of estimating the quality of different forages
or the effect of a management treatment upon quality. Grazing trials
to determine output per animal must be long-term endeavors and they
become costly in terms of resources, time and capital. Thus, an
expression of forage quality which is less expensive to determine,
but which yields equally acceptable results, becomes a necessity if a
large number of forages are to be evaluated.
Digestible Energy Intake, Digestible Dry Matter Intake and Digestible
Organic Matter Intake
According to Heaney (1970) , an expression of the feeding value of
forages, or of forage quality, must have the following inherent charac-
teristics: (1) it must be measurable with a high degree of precision;
(2) observations on a small number of animals under controlled experi-
mental conditions must be applicable to a more general production
situation and animal population; and (3) it must be highly correlated
with animal production when the evaluated feed is fed to animals. This
author also stated that researchers now accept the combination of intake
and digestibility into a single expression, such as digestible energy
intake (DEI), for evaluating forage quality, and that this is the most
effective method ever used. Jones (1972), Milford and Minson (1965a)
and Crampton et al. (1960) agreed that intake and digestibility should
be combined for determining quality, and Heaney (1970) and Ventura
(1973) have reported evidence that neither intake nor digestibility by
themselves can be considered a reliable expression of forage quality.
Why, however, should intake and digestibility qualify as contrib-
utors to an expression of forage quality? In a practical sense, it is
foolish to think of any indicator of forage quality which does not
include some measure of the amount of a forage that animals will
voluntarily eat, for animals will not produce without consuming the
energy and nutrients needed for conversion to livestock products. Minson
et al. (1964), Osbourn et al. (1966) and Milford (1967) reported devia-
tions from a general constant relationship between voluntary intake
and dry matter (DM) digestibility, both among and within forage species.
Thus, a direct and separate estimate of voluntary intake of a forage
must be made for inclusion in an expression of forage quality along with
digestibility (Minson and Haydock, 1971). Some measure of nutritive
value or net energy (NE) (Raymond, 1968; Moore and Mott, 1973) must
also be included in the expression, since consumed nutrients and energy
will not contribute to production unless they are digested and utilized.
Since these functions are not solely under the influence of intake,
the digestibilities of either DM or organic matter (CM) may be used
as expressions of nutritive value (Moore and Mott, 1973) because NE
for maintenance and fattening have been predicted satisfactorily from
energy digestibility, which in turn is well correlated with the
digestibility of either DM or OM (Armstrong et^ al • , 1964). Thus,
digestible dry matter intake (DDMI) or digestible organic matter
intake (DOMI) can be included with DEI as quality expressions. Jones
(1972), Ventura (1973) and Marsh (1974) concurred that DOMI is synonomous
with forage quality.
If DEI, DDMI and DOMI are to be considered expressions of forage
quality, they should be highly correlated with average daily gain of
animals consuming the forage in question. Since an increase in digestible
energy (DE) is associated closely with increases in metabolizable energy
(ME) and NE, it should be expected that increases in DEI, as well as in
other quality expressions, would be well correlated with increases in
NE intake and output per animal. This has been found to be true. Elliott
e_t al . (1961) and Holmes e_^ al^. (1966), working with tropical pastures,
found that liveweight gain of cattle was linearly related to DDMI. Heaney
(1970) observed that forage DEI agreed exceptionally well with growth
rates of lambs fed forages for seven to eight weeks, and Montgomery and
Baumgardt (1965a) found no significant differences between DEI's or
between average daily gains when ruminants consumed high-quality rations .
Thus, as stated by Pfander (1970), probably the most practical measure
of forage quality would be DEI per kilogram of body weight raised to the
.75 power. However, measurements of DDMI or DOMI are probably just as
acceptable where energy determinations cannot be or have not b^en made.
No matter which expression is used to indicate forage quality, the
relative contributions of intake and digestibility to the value of the
expression are not the same. According to Keaney (1970), the range in
recorded values of intake, going from low- to high-quality forages, is
about 2.5 times that of recorded digestibilities. Thus, intake is more
than twice as important as digestibility in determining the value of
forage quality over a range of forages. Crampton (1957), Moore (1968),
Osbourn et al. (1970) and Ventura et, al. (1975) agreed that intake is
the more important factor in determining quality. Milford and Minson
(1965a), working with tropical grasses, found that daily DDMI was
more closely correlated with intake of DM than with its digestibility.
Crampton et^ al^. (1960) reported that variation in intake accounted for
70 percent of the variability in the Nutritive Value Index. Intake
is more important than digestibility in determining quality among forages,
and intake of a given forage is more variable between animals than is
digestibility (Blaxter et^ al. , 1961; Minson et al. , 1964; Heaney et al. ,
1968; Capote, 1975). Therefore, intake should be investigated using
six to ten animals per determination, while three or four will suffice
for digestibility (Heaney, 1970). This variability in intake among
animals on a given forage may be due to animal variation with respect
to (1) weight (Heaney, 1970; Capote, 1975); (2) fatness (Bines et al. ,
1969; Foot, 1972; Capote, 1975); (3) physiological rumen volume (Purser
and Moir, 1966); and/or (4) retention time of DM in the rumen (Campling
et al . , 1961; Phillips £t al. , 1960; Hungate, 1966). This discussion
of intake variability is not to imply, however, that changes in digest-
ibility are insignificant in their influence upon DEI or the other
expressions of quality. Blaxter ^ al • (1961), under ad libitum feeding
conditions, calculated that a change in digestibility of DM from 50 to
55 percent resulted in a 100 percent increase in weight gain.
Nutritive Value Index
The Nutritive Value Index (NVI) was proposed by Crampton e_t al.
(1960) as another expression of forage quality. For temperate forages,
this index was highly correlated with both 12-hour ±n vitro cellulose
digestibility (IVCD) (Donef er et al. , 1960; Johnson et a]^. , 1962b) and
IVCD multiplied by the solubility of forage DM in 1.0 N sulfuric acid
(Johnson and Dehority, 1968). Like the other proposed quality ex-
pressions, it also includes measures of (a) voluntary intake (actually
"relative intake" compared to that of the standard forage proposed by
Crampton et al. (I960)) and (b) digestibility (energy digestibility
(ED)). Minson and Milford (1966) examined NVI in relation to DEI and
found that, though NVI was highly correlated with DEI for the three
forages studied, the regression coefficient for one of the forages was
significantly different from the others. Interpretation of the re-
sults of Johnson et al. (1962a) reveals that for forages consumed in
the fresh state, prediction of an NVI value from 12-hour IVCD would
require different regression equations depending upon the DM percentage
of the in vitro sample. ' This was because of differences between the
12-hour IVCD values of undried versus artificially dried samples. Due
to the absence of a constant caloric value for conversion of NVI to
DEI, and due to the lack of tables of animal requirements for NVI,
Minson and Milford (1966) concluded that the more direct method of
expressing forage quality in terms of DEI per unit of metabolic size
was superior to the NVI system.
Retention Time of Organic Matter in the Rumen
Blaxter (1962) reported that the qualities of different feeds were
proportional to the rates at which they passed through the gut of
ruminants. Thornton and Minson (1972, 1973) and Laredo and Minson (1975)
concluded that the retention time of OM in the rumen (RTOM) was highly
and inversely correlated with DOMI. Thus, if RTOM could be accurately
predicted by means of laboratory analyses, it might prove a method
which could greatly reduce the need for intake and digestion trials in
forage evaluation research. Part of the research in this dissertation
examines this hypothesis.
Control of Forage Intake by Ruminants
Capote (1975) and Golding (1973) have written literature reviews
covering many of the proposed control mechanisms, as well as many of
the factors which interact to control the voluntary intake of ruminants.
Included in these reviews are the effects of the following factors
upon intake: animal breed, weight, size, age, rate of production and
fatness; ration caloric concentration; crude protein percentage of
forage; blood and rumen metabolites; environmental conditions, such
as ambient temperature, humidity and solar radiation; physiological
condition, including lactation and pregnancy; hormones; frequency of
feeding; water deprivation; amino acids; minerals; crude protein
supplementation; and energy supplementation. Thus, these factors will not
be dealt with, or will be touched upon only lightly, in the present
review. This review will attempt to cover the physical or distention
mechanism which has been proposed for control of forage intake by
mminants, as well as the factors which relate to the function of
this mechanism.
The Distention Mechanism
The theoretical distention mechanism for controlling forage intake,
formally proposed by Montgomery and Baumgardt (1965a) and Conrad (1966),
appears to be an extension of the following concepts set forth by
Crampton et ^. (1960) : (1) some specific degree of rumen load reduction
probably is the primary determinant of recurring hunger in ruminants;
(2) the rates of forage cellulose and hemicellulose degradation are
correlated with the rate at which the rumen load is reduced; and (3)
the time period after which the rumen load reaches the degree of
reduction at which hunger recurs is characteristic of the specific
forage involved. Moore and Mott (1973) state that if nitrogen is
not limiting, the mechanism related to the distention theory is that
which most often controls intake of forage-fed animals. Work by
Campling et al. (1962), Egan (1965), Weston (1967) and Minson and Milford
(1968), however, indicated that the distention mechanism may also be
involved in regulating intake, at least in part, when dietary crude
protein (CP) is less than 7 percent of total DM. Baile (1968),
Waldo (1970), Welch (1967) and Weston (1966) all agreed that physical
distention of the rumino-reticulum was an important feedback mechanism
for the regulation of forage intake by ruminants.
The distention control mechanism is generally dominant with long
forages until the digestibility of DM reaches some upper point in the
range of about 65-70 percent. The form in which forage is fed (Blaxter
et al. , 1961; Montgomery and Baumgardt, 1965a) and the physiological
condition of the animal consuming it (Waldo, 1970) have been shown to
change this point. This theory suggests that forage intake and digest-
ibility should be highly correlated. This may be true when forage
quality differences are due to maturity differences, but may not be so
when quality differences are due to forage species (Milford, 1967;
10
Weston and Hogan, 1967; Minson et al. , 1964; Van Soest, 1964) or
cultivars within a species (Osbourn ^ al. , 1966). This possibly is
because chemical and structural differences may exist which cause
differing rates of digestibility, though final digestibilities are
similar, across a given set of forages (Van Soest, 1965a; Demarquilly
et al . , 1965; Milford and Minson, 1965a). Thus, the relationship
between intake and digestibility may be sufficiently accurate for
predictive purposes only when limited to maturity differences within
individual species and/or cultivars.
Site and mechanism of distention control
Earlier work by Blaxter et al . (1956, 1961) and Conrad et al.
(1964) stressed the importance of distention of the entire gastro-
intestinal tract of ruminants in controlling forage intake. Thus, the
rate of passage of digesta through the entire tract was thought important
in limiting consumption. However, fecal DM output varies across the
various forms in which forages are fed (chopped, wafered, ground,
pelleted, etc) (Waldo, 1970), and positive relationships have been
reported between intake ^and amounts of material in sections of the
tract posterior to the rumino-reticulum (Ingalls et al . , 1966). Such
observations led many workers (Ingalls e_t al. , 1966; Ulyatt et al. ,
1967; Waldo, 1970; Ulyatt, 1973) to discount the importance of sections
of the tract posterior to the rumino-reticulum (hereafter referred to
as the rumen) in limiting forage consumption. Thus, most researchers
now agree with the contention of Campling et_ al^. (1961) and Waldo (1970)
that the rumen is that portion of the gastro- intestinal tract in which
distention control over forage intake is exercised. Further, they agreed
that distention control is governed by two main factors: (a) fill, or
11
the amount of digesta in the rumen (Campling and Balch, 1961; Weston,
1966) and (Jj) retention time, or the extent of delay of digesta in the
rumen (Campling, 1965, 1970; Thornton and Minson, 1972). Importance of
the rumen to this mechanism is indicated by receptors sensitive to
ruminal stretch or tension (Bell, 1961; Comline and Titchen, 1961;
Kay, 1963; Leek, 1969), though the nature and location of the sensory
nerve endings have not yet been reported (Campling, 1970). Still, some
evidence indicates that intake of finely ground and pelleted forage
diets may be partly controlled, either directly or indirectly, by
distention of the abomasum and intestines (Campling _et _al. , 1963;
Campling and Freer, 1966).
Relative importance of "fill" and "retention time"
Retention time is probably more important than fill in limiting
forage intake because rumen DM fill per kilogram of metabolic weight
(W, ' ) has been shown relatively constant across a range of forage
kg
quality (Blaxter e_t al . , 1961; Ulyatt et^ al • , 1967; Thornton and Minson,
1972). Campling e^ al. (1961) and Egan (1970), feeding diets of
cereal straws and hays, reported that fill on such diets was low re-
lative to that produced by higher-quality forages. The straw and hay
diets contained less than 1 percent nitrogen. Thus, nitrogen de-
ficiency may have led to the low fill observed with these diets. In
such cases, amount of rumen fill may be more important in controlling
forage intake than when forages of higher quality are considered.
The actual amount of DM fill in the rumen has been reported to vary
from 1.7 percent (Thomas e_t £l. , 1961) to 2.2 percent (Waldo et al. ,
1965) or 2.44 percent (Ingalls et al. , 1966) of body weight. This
12
variation may be due to differences in DM intake across the diets
used in these experiments (Ingalls ^ al. , 1966; Egan, 1970; Thomas
et al. , 1961).
That intake depends to a great extent upon average retention time
of material in the rumen has been shown by many researchers (Ulyatt, 1^ 1;
Oltjen ejt al. , 1971; Elliott and Topps, 1960; Laredo and Minson, 1975;
Thornton and Minson, 1972, 1973). Calculations made in the present
study from data presented by Laredo and Minson (1975) and Thornton
and Minson (1972, 1973) showed that retention time of OM in the rumen
(RTOM) was highly correlated with digestible OM intake per W ' . If
RTOM could be predicted accurately from parameters related to forage
composition and/or structure, accurate predictions of forage quality
might be obtainable from RTOM. This could decrease the necessity of
running intake and digestibility trials with ruminants. Theory and
relationships between various parameters reported by Waldo e^ al. (1972)
may prove useful in attaining this goal.
Factors Affecting Retention Time
For a given forage, RTOM depends upon rate of digestion in the
rumen (Campling, 1965; Jones and Bailey, 1974) and upon the rate at
which undigested residues leave this organ (Campling, 1964, 1965;
Waldo et al. , 1972). This suggests that there are two important rates
to consider, and that there are two types of material in the rumen:
(a) one which leaves the rumen due to digestion (i. e. , by absorption
and eructation), and (b) one which must exit via passage to the lower
gut (Waldo _et al., 1965, 1972). McLeod and Minson (1974a) and de la
Torre (1974) suggest that this latter material contains all the lignified
fractions of the plant cell wall, and hence all the lignin in the diet.
13
However, part of the potentially digestible material must also evacuate
the rumen via passage, since not all of this material is digested in
the rumen. This important fact is included in the model derived by
Waldo et al. (1972) to describe the manner in which cellulose disappears
from the rumen. Also included in this model are the concepts that both
the rate of digestion of digestible material (Gill et al . , 1969; Smith
et al., 1971, 1972) and the rate of passage of indigestible residues
(Meyer &L 3l. , 1967; Alexander et al . , 1969; Brandt and Thacker, 1958)
follow the laws set forth for first-order dynamic processes. That is,
these rates proceed in proportion to the amounts of material undergoing
digestion and passage. Gill et al. (1969) reported that the relative
rate of digestible cellulose digestion (K) in vitro was highly correlated
with the digestible DM intake of cows consuming high-DM legume-grass
silage. Such was not the case when Lechtenberg et al. (1974) fed corn
stover silage from two different corn genotypes to sheep. These authors
postulated that rate of digestion of total cell walls was more important
than K in determining intake. They also reported that rate of digestion
of total cell walls was affected by lignif ication, but that K was not.
A negative relationship between intake and retention time has
been noted by many workers (Thornton and Minson, 1972; Ingalls et al. ,
1966; Waldo et al . , 1965). The decrease in RTOM with increased level
of feeding may be responsible for observed decreases in DM digestibility
(Laredo and Minson, 1975). However, Minson (1966) reported that re-
tention time of DM in the rumen was only slightly influenced by the
level of DM intake of the same diet, since reducing intake by 51 percent
yielded only an 18 percent increase in retention time. Thus, Thornton
14
and Minson (1972) reasoned that among forage diets which exhibited
DM intakes of from 659 to 1355 g/day, intake level could have accounted
for no more than 20 percent of the difference in ruminal retention time,
which varied from 13.3 to 27.1 hours. These investigators concluded
that retention time in the rumen was controlled largely by chemical
composition of forage, particularly neutral-detergent fiber (NDF)
and lignin. Lignin was highly correlated with intake in their study,
however, and such is not always the case (Golding, 1973).
Non-forage factors which may exert important influences upon RTOM
have been reported. Graham and Williams (1962) observed that retention
time of residues in the gut increased as pregnancy advanced in sheep
given a constant amount of feed. Studies by Warren et^ al. (1974)
and Wayman _et al. (1962) indicated that RTOM may increase at high ambient
temperatures. In this latter study, animals were forced-fed at high
ambient temperatures to offset any effect of decreased intake on RTOM,
Factors affecting rates of digestion and passage
Of the many factors which interact to determine rates at which
forage OM digests in and passes from the rumen, probably chemical
composition and organizational structure of cell walls of ingested
forage are the most important (Akin et al. , 1974a; Van Soest, 1965a;
Thornton and Minson, 1972; Laredo and Minson, 1973). That chemical
composition is important in this respect was shown by Campling e_t al.
(1962), Egan (1965) and Weston (1967). These workers increased rate
of digestion and the intake of diets low in CP percentage by supplement-
ing with urea. Such increases would not have occurred unless CP was the
first limiting factor. The fact that lignin can limit rate of digestion
15
was brought out by Lechtenberg et al . (1974) and Crampton (1957).
Thornton and Minson (1972) reported a high correlation between lignin
content of forage and retention time of DM in the rumen. This, at
least in part, was undoubtedly a reflection of the effect of lignin on
rate of digestion of forage cell walls. When forages are supplemented
with energy, rates of DM or cellulose digestibility decline, perhaps
due to mineral imbalances (Burroughs et al, , 1948) or nitrogen competi-
tion (el-Shazley et al, , 1961). Minimum requirements of some rumen
bacteria for phosphorus, magnesium, calcium, sodium and potassium have
been established, and iron, cobalt, copper, manganese and zinc have
been shown to be beneficial to others (Hungate, 1966), Therefore,
deficiencies of these minerals, as well as imbalances concerning their
relative concentrations in the rumen, could cause decreases in rate of
digestion of forage cell walls.
Rate of passage of indigestible OM from the rumen is limited by
the rate at which large particles in this organ are reduced to a size
small enough to pass to the omasum. Rate of breakdown, while certainly
under the influence of composition of feed and animal factors such
as efficiency of chewing and strength and/or frequency of rumlnal
contractions, is regulated to a great extent by organizational structure
of the forage cell wall fraction (Akin e^ al. , 1974a; Ulyatt, 1973),
Further histochemical studies of the nature of those by de la Torre
(1974), Akin £t al, (1974a) and Monson ^ al. (1972) are needed to
elucidate the relationships between cell wall structure and rates of
OM breakdown in, and passage from, the rumen. Perhaps grinding energy,
as proposed by Chenost (1965), deserves more experimental work as a
method for predicting rate of breakdown in the rumen.
16
Other factors which aid in determining rates of digestion and
passage are those related to animal breed, the form in which forages
are fed and supplementation of forages with energy. Phillips (1961)
and Hungate et al. (1960) observed that Zebu cattle demonstrated higher
rates of digestion and passage of forage diets than did steers of
European breeds. In the latter of these studies, the higher rates
correlated well with lower retention times exhibited by Zebu animals,
and it was postulated that the advantage of Zebus relative to European
breeds with respect to rates of digestion and passage would be increased
under conditions of stress and submaintenance feeding. Forages fed in
pelleted form have shown faster rates of digestion and passage and
decreased retention times of digesta in the rumen relative to the same
forages fed in the long or chopped forms (Johnson _et^ al- . 1964; Oltjen
et^ al. , 1971; Laredo and Minson, 1975). The advantage demonstrated
by pellets in this respect seems to be greatest when low-quality forages
are fed (Minson and Milford, 1968). Intake is not always increased by
pelleting, however, if nitrogen is a limiting factor (Minson, 1967;
Minson and Milford, 1968). Supplementation of forage with energy
causes the forage portion of the diet to be retained longer in the rumen
than when forage is fed alone (Montgomery and Baumgardt, 1965b; Campling,
1966; Eng et_ al . , 1964). This appears to be caused by decreased
activity of the cellulolytic microflora in the rumen when forage is
supplemented with starchy energy feeds (Campling, 1970; el-Shazley
et al . , 1961). A lower intake of forage may also contribute to lengthen-
ing its retention time under these conditions.
17
Intake vs Rate of Digestion In Vitro
Since rate of digestion in the rumen has been shown to be instrumental
in determining retention time (Campling, 1965; Jones and Bailey, 1974)
and, therefore, intake, it follows that in vitro rate of digestion should
also be highly correlated with these parameters. Minson and Milford
(1967a) found that 12-hour in vitro DM digestion predicted the voluntary
intake of Rhodes grass (Chloris gayana) , and Crampton et_ al . (1960)
suggested that rate of J:!! vitro cellulose digestion was related to
voluntary intake. Donefer et al. (1960) and Johnson et^ al. (1962b)
reported that 12-hour IVCD was highly correlated with NVI, and Jones
(1972) found that intake of four temperate grasses was highly correlat-
ed with rate of isi vitro DM digestion.
Minson (1971a) described less promising results when correlating
in vitro digestion rate with intake of different varieties of Panicum.
Karn et al. (1967), using temperate grasses and alfalfa, obtained low
correlation coefficients (r values) between intake and ±n vitro rates
of cellulose or DM digestion at various times between five and 11 hours
of fermentation. Laredo and Minson (1973) observed no difference be-
tween mean In vitro rates of digestion of leaf and stem fractions of
five different warm-season grasses, though mean voluntary intake of
leaf was 46 percent higher than that of stem. These authors stated that
this discrepancy was probably due to the fact that all in vitro samples
had been ground to pas5 a one millimeter (mm) screen, thus destroying
the structural differences across samples which had produced the large
difference in in_ vivo intake. This work suggests that high correlations
reported by other workers between intake and rate of in_ vitro digestion
may have been caused by factors other than differences in fiber structure
across forages.
18
Examination of the grasses used by Crampton et^ £l. (1960) and
Minson and Milford (1967a) showed a positive correlation between intake
and nitrogen content of those forages (Laredo and Minson, 1973). These
results suggest that when forage samples are ground to pass a 1 mm
screen prior to determining in vitro rates of digestion, such determin."-
tions will be highly correlated with intake only when intake is related
to chemical composition. High correlations should not be the case when
cell wall structure plays the dominant role in determining intake,
since differences in i^ vivo rates of digestion probably will be masked
in vitro .
Another discrepancy between in vivo and In vitro rates of digestion,
which could cause low correlations between intake and J^ vitro rate of
digestion, could occur with forages of low CP percentage. Glover et al.
(1960) showed that when forages which contained less than 5 percent
CP on a DM basis were fed over prolonged periods of time, a sharp
decrease in in vivo digestibility was likely to occur. This decrease
probably would not appear j^ vitro due to the relatively short fermentation
times, and also because rumen fluid for sample inoculation is normally
drawn from donor animals whose diets are adequate in CP. Thus, low
in vivo rate of digestion and decreased intake of low CP forages which
had been fed for some time might not be reflected by ±n vitro rate of
digestion of that forage.
Prediction of Forage Nutritive Value
Moore and Mott (1973) stated that most forage researchers generally
use ED or apparent digestibility of DM (DMD) or CM (OMD) as expressions
of forage nutritive value. They also concluded, based upon work by
19
Armstrong (1964), Armstrong et^sl. (1964) and Graham (1967) that
digestible energy (DE) per g DM (DE/DM) was a very meaningful and
useful criterion of forage nutritive value for both tropical and
temperate forages.
Applicability of Predictors of Nutrient Digestibility
Chemcial analyses
No chemical determination, whether based upon the Weende proxi-
mate analysis system, the Van Soest method of fiber fractionation or
one of several solubility techniques, will predict 0>ro or DMD with
a high degree of consistent accuracy across a wide range of forage
species (Johnson and Dehority, 1968; Butterworth and Diaz, 1970;
Moore and Mott, 1973; Golding, 1973). Nor will an empirical multiple
regression equation based upon several such chemical determinations
allow accurate prediction of nutritive value over such a range of
forages (Butterworth and Diaz, 1970; Moore and Mott, 1973; Golding,
1973) . Some chemical determinations will exhibit a high degree of
correlation with OMD or DMD over a narrow range of forages if maturity
is the primary determinant of quality. However, when the resultant
regression equation is applied to a different set of forages than
that which produced the equation, digestibility predictions are gener-
ally lacking in accuracy.
In vitro organic matter digestion
The in vitro CM digestion procedure for estimation of in vivo OMD,
while more rational and accurate for this purpose than chemical analyses,
is akin to these analyses in that discrepancies exist in the i^ vivo -
in vitro relationship across forage species (Moore and Mott, 1973;
20
McLeod and Minson, 1974b). Thus, across species, different regression
equations must be utilized in the prediction of O^DD. Weller (1973)
found that the particle-size distribution over 12 warm-season grasses
from three different species did not contribute to this discrepancy.
However, among forages which exhibit true differences in the structur..
make-up of fibrous OM, fine grinding of forages before subjecting
them to fermentation may still influence the degree of an observed
discrepancy (Laredo and Minson, 1973).
Summative equations
Summative equations presented by Van Soest (1965b) and Minson
(1971b) (for prediction of DMD and OMD, respectively) are also not
good predictors of DMD or OMD when applied to a wide range of forage
species. These equations are theoretically rational in that they sum
the various apparently digestible fractions of DM or OM. However, they
include hypothesized cause and effect relationships which are invalid
across forages for estimating digestibilities of various fibrous frac-
tions. If the summative principle could be combined with the Nutritive
Entity concept of Lucas and Smart (1959) , and with some consistent
cause and effect relationship for predicting digestibility of fibrous
OM, the OMD could be more accurately predicted across forages. This
has been shown by Velasquez (1974), who used in vitro NDF digestion to
predict in vivo digestibility of NDF. This procedure, however, is
too time consuming to be employed in routine forage evaluation.
Applicability of Predictors of DE Concentration in Forage DM
In vitro cellulose digestibility
Hershberger ^ al. (1959) found a high correlation (r = ,92)
between kilocalories (kcal) DE/DM and IVCD after 24 hr of fermentation
21
over four temperate grasses and two legumes. Johnson e_t al. (1962b)
reported a high r value (.99) for the relationship between ED of
temperate grasses and IVCD at 24 hr, but when legumes were included
in the analysis, r dropped to .88 after 24 hr, as opposed to .99
after just 12 hr of fermentation. Thus, it appeared to these workers
that 12-hr IVCD compared most favorably with ED across forage species.
Johnson and Dehority (1968), working with temperate species, found
r values of only .79, .54 and .64 within groups of 22 grasses, 25
legumes and 30 mixed forages, respectively, for the relationship be-
tween ED and 12- hr IVCD. Across all 77 forages, the r value for this
relationship was only .64, suggesting that IVCD, after either 12 or
24 hr of fermentation, would not be an accurate predictor of DE/DM.
Also, none of the Van Soest fiber fractions or solubility techniques
studied by Johnson and Dehority (1968) would effectively fill this
role. Across all forages, cellulose solubility in cupriethylenediamine
multiplied by DM solubility in 1.0 N sulfuric acid exhibited the highest
correlation with ED, but r was only .82.
Dry matter digestibility
Moir (1961) reported a highly significant relationship between
DE/DM and DM digestibility (DMD) (r = .98), and proposed that a gen-
eral equation could be used to predict DE/DM from DMD. Butterworth
(1964), however, found an r value of only .86 between these two
parameters for 24 tropical forages. Minson and Milford (1966) stated
that when they used the equation suggested by Moir (1961) to predict
DE/DM, estimates from pastures of low digestibility were in agreement
with actual DE/DM values. With pastures of high digestibility, actual
22
DE/DM values were 7 percent lower than estimated. Therefore, use of
a general equation to predict DE/DM from DMD could lead to inaccurate
results.
Crude protein percentage of dry matter
Glover _et al. (1960) showed that over a wide range of CP, as a
percentage of DM, CP was well correlated with DE concentration in for-
ages. Minson and Milford (1966) also observed a positive correlation
(r = .84) between the caloric value of OM and CP percentage. There-
fore, wide variation in CP may explain part of the discrepancy found
in the relationship between DE/DM and DMD. This would occur because
digestible CP (DCP) , which is highly correlated with CP (Holter and
Reid, 1959; Milford and Minson, 1965b), exhibits a higher caloric value
than does digestible carbohydrate (Maynard and Loosli, 1969). It is
doubtful, however, that CP will be always highly correlated with DE/DM
over a wide range of forages, since CP does not generally exhibit a
strong cause and effect relationship with DMD. Still, some combination
of rational factors related to DMD and CP may produce more accurate
predictions of DE/DM over a wide range of forages than would either
of these factors alone.
Prediction of Forage Quality
The best measure of forage quality is output per animal under
certain conditions (Moore and Mott, 1973). Heaney (1970) and Ventura
(1973) found that neither intake nor digestibility alone could be
considered a reliable expression of forage quality. Thus, most re-
searchers now accept some combination of intake and nutritive value,
such as DEI, DOMI or DDMI , as meaningful expressions of forage quality.
23
Applicability of Various Techniques for Quality Prediction
Chemical analyses and summative equations
Moore and Mott (1973) and Golding (1973) have presented liter-
ature reviews of research to define methods for accurate prediction
of forage quality. Conclusions of these authors will be briefly
summarized in this section, and in those which follow. Quality over
a wide range of forage species defied prediction by single laboratory
chemical analyses, or by empirical multiple regression equations based
upon several such determinations. Digestibility probably could be
accurately predicted by summative equations if these were based upon
the Nutritive Entity concept of Lucas and Smart (1959) and included an
accurate predictor of cell wall digestibility. Accurate summative
equations for digestibility prediction would not insure accurate pre-
diction of forage quality, however, since digestibility and intake
are not highly correlated over a wide range of forage species.
In vitro techniques
In vitro OM digestion (IVOMD) by rumen microorganisms is the best
available predictor of OMD. Across forages, however, discrepancies
have been observed in the in vivo - in vitro relationship, i. e. ,
IVOMD many times will be different at a given level of in vivo OMD
(Moore and Mott, 1973). Even if in vivo OMD could be accurately pre-
dicted from IVOMD with a high degree of consistency, IVOMD would not
be a generally accurate predictor of forage quality due to the frequent
lack of relationship between intake and digestibility. It is possible
that microanatomical studies (Monson et al. , 1972; Akin and Burdick,
1973; de la Torre, 1974) of differences in composition, organization
24
and rates of digestion of structural components of OM may help in
removing discrepancies in the relationships between ±n vivo OMD and
IVOMD, and between intake and digestibility.
In vitro rates of DM or cellulose digestion have been studied
(Cramp ton et al, , 1960; Minson and Milford, 1967a; Karn ^ al . , 1967;
Minson, 1971a; Laredo and Minson, 1973) as possible predictors of
forage quality. Such determinations may be inadequate for this purpose
when structure of fibrous OM fractions is important for control of
forage intake. This is because forage samples are generally ground
to pass a 1 mm screen before being studied by in vitro procedures,
thus greatly removing variation in structure of fibrous OM fractions
among forages. It is possible that studies of ±n vitro rates of OM
digestion which employ more intact forage samples could produce rates
of digestion which would correlate highly with forage quality. Such
samples might also be examined microscopically before being fermented,
and some attribute (s) might correlate highly with rate of OM digestion.
In this case, microscopic examination of a small forage sample would
lead to rapid prediction of forage quality. It is quite probable,
however, that both chemical composition and the structural nature of
fibrous OM must be considered in an attempt to produce a method for
prediction of quality over a wide range of forage species.
The rate constant for rate of cellulose digestion in vitro (K)
was reported by Gill et al. (1969) to be highly correlated with digest-
ible DM intake of high-DM legume-grass silage by cows. This concept
was refuted by Lechtenberg et al. (1974), who fed corn stover silage
to sheep. Thus, it is doubtful that K is highly correlated with
forage quality in a general sense.
25
The nutritive value index
The NVI system (Crampton et^ al. , 1960) for estimation of forage
quality has received wide-spread attention from researchers, as well
as much use in a practical sense. Discrepancies revealed by Minson
and Milford (1966) and Johnson ejt al. (1962a) between actual forage
quality and NVI values may, however, decrease the utility of this system
as a quality estimator over a wide range of forages. Also, the fact
that rapid NVI determination is based upon 12-hr IVCD might cause
errors in quality estimation when structure of fibrous OM is an im-
portant determinant of intake.
Retention time of organic matter in the rumen
Thornton and Minson (1972, 1973) showed that RTOM determined
in vivo was highly and negatively correlated with forage quality. There-
fore, RTOM may ultimately prove to be an accurate predictor of quality
across forages, since it seemingly should be related to both chemical
composition and structural microanatomy of forage OM. Across forages,
values of RTOM may reflect rate and extent of OM digestion in the
rumen which, in turn, should be determined by the microbial and physical
degradability of forage OM.
Mathematical Modeling of Dynamic Systems
Forrester (1968), Joandet and Cartwright (1975) and Blincoe (1975)
presented material which outlined the steps to be followed, types of
information required and benefits to be reaped when mathematical computer
models are employed to simulate the action of a given dynamic system.
Forrester (1968) developed a method for modeling such systems, and
Pugh (1973) presented the computer language, called Dynamo, which makes
26
use of this modeling procedure possible. This procedure has been
employed successfully in such fields as ecology, sociology, plant
sciences, physical sciences and engineering. In the areas of animal
science and agronomy, models utilizing this procedure, as well as
others, have been applied to simulate forage production (Bravo, 1973;
Smith and Williams, 1973; Patten, 1972); forage production under
grazing (Christian et al. , 1972; Paltridge, 1972; Vickery, 1972);
rumen fermentation (Baldwin et al. , 1970); animal energetics (Baldwin
and Smith, 1971a); intermediate metabolites (Baldwin and Smith, 1971b);
energy metabolism of the steer under f eedlot conditions (Paine et al. ,
1972); sheep production (Wright, 1970); the efficiency of nutrient
utilization by different cattle genotypes (Joandet, 1967); and the
utility of different production alternatives from the economic point
of view (Shumway et al. , 1974; Anderson, 1972; Trebeck, 1972). The
relationship between OMI by cattle on pasture and forage production
has been included in the simulation of forage production and pasture
utilization by the animal (Vickery and Hedges, 1974; Donnelly et al. ,
1970; Jones, 1969; Morley and Spedding, 1968). This relationship
has been based upon a relatively simple set of assumptions not con-
sistent with most practical situations (Joandet and Cartwright, 1975).
Thus, proper description of the forage production - OMI relationship
is one problem which must be overcome to achieve accurate simulation
of pasture production and forage utilization by the ruminant animal.
The utility of mathematical models lies in the fact that they
require accurate definition of the structure and function of the system
or process which is being modeled (Forrester, 1968). They also indicate
27
areas where research is needed by means of the degree of sensitivity
which they display to changes in inputs; and they make possible the
study of situations which cannot be achieved experimentally, or which
are too risky or expensive to attempt otherwise (Blincoe, 1975). Per-
haps the greatest attribute of mathematical computer models, however,
is that their construction and use, as well as the interpretation of
results which they generate, generally require the effort of a team of
researchers who integrate their knowledge in trying to solve a common
problem.
CHAPTER III
PREDICTION OF DIGESTIBLE ENERGY CONCENTRATION IN FORAGE
FOR PURPOSES OF MARKETING SOUTHERN HAYS
Introduction
Forages probably would be marketed most fairly on the basis of
their potential to support animal production, i. e. , forage quality.
Estimation of quality for marketing purposes requires a fast, simple
and accurate method which presently is not available over a wide
range of forage species. Thus, marketing of forages must be based
on some other forage attribute. Intake will not serve as this
attribute since lack of a sufficiently accurate method for prediction
of intake (Minson, 1971a) is the main cause of problems encountered
in attempting to predict forage quality. At present, therefore, for-
ages must be marketed on the basis of their nutritive value. This
nutritive value cannot be that which is realized in a given situation,
but must be that which is a basic attribute of a given forage. Digest-
ibility of dry matter (DM) or organic matter (OM) as estimated from
in vitro digestions would satisfy this requirement over narrow ranges
of forages. A rancher probably has little appreciation of such a
parameter, however, and animals' energy requirements are tabulated
on the basis of total digestible nutrients (TDN) or digestible energy
(DE) concentration, not digestibility. Forages should be marketed,
therefore, based on their values of kcal DE/g DM (DE/DM) . This value
is closely related to TDN, since the caloric value of TDN is approximately
28
29
4.4 kcal DE/g TDN (Maynard and Loosli, 1969). If TDN of a forage is
known, DE/DM can be calculated and a bomb calorimeter need not be
employed.
If a prediction method for DE/DM is to be adopted widely for
hay classification and marketing, it should be equally applicable
to grasses, legumes and mixed hays, and must be inexpensive and rapid.
No laboratory chemical analysis, whether used alone or in combination
with other such analyses, will serve for accurate prediction of DE/DM
over a wide range of forages (Johnson and Dehority, 1968; Butterworth
and Diaz, 1970; Moore and Mott, 1973), nor will in vitro digestion of
OM or DM (Minson and Milford, 1966; Moore and Mott, 1973). Summative
equations (Van Soest, 1965b; Minson, 1971b) may be adequate for DE/DM
prediction if they encompass cause and effect relationships which hold
true across forages (Moore and Mott, 1973), and if they include the
Nutritive Entity concept of Lucas and Smart (1959).
The objective of this study was to define and test a theoretically
rational method, based upon use of summative equations, for the accept-
ably accurate prediction of DE/DM over a wide range of Southern hay-
crop forages.
Experimental Procedure
Theory Related to Rational Prediction of DE/DM
Forage digestible OM (DOM), as a percentage of DM, generally con-
tains very little digestible ether extract (DEE) (Glover and Dougall,
1960). Thus, DOM is comprised mainly of digestible crude protein (DCP)
and digestible carbohydrate, both as percentages of DM. The digestible
carbohydrate fraction, in terms of the Weende proximate analysis, is
30
composed of digestible crude fiber (DCF) and digestible nitrogen-free
extract (DNFE) . If forage DOM could be predicted and the caloric
value of its digestible carbohydrate fraction added to that of DCP in
DOM, then an accurate estimation of DE/DM should result.
With most hays, the numerical values of TDN and DOM are nearly
identical. This can be illustrated as follows (values as percentage
of DM) :
TDN = DCP + DCF + DNFE +2.25 (DEE), (1)
and
DOM = DCP + DCF + DNFE + DEE. (2)
Therefore ,
TDN = DOM + 1.25 (DEE). (3)
Since DEE is negligible in most hays, values of TDN and DOM are
numerically equal for all practical purposes. This fact, in itself,
probably will not lead to rapid and accurate prediction of DOM across
a wide range of forages since TDN is not predictable with a high
degree of accuracy over such a range (Butterworth and Diaz, 1970).
The inability to predict TDN accurately among forages may be due to
two facts: (a) crude fiber (CF) and nitrogen-free extract (NFE) are
not Nutritive Entities (Moore and Mott, 1973); and (b) CF and NFE
generally do not conform to their definitions in terms of composition
(Harris et al. , 1972).
Prediction of DOM
The first step in the rational prediction of DE/DM in the laboratory
is the prediction of DOM, as a percentage of DM. Rational laboratory
31
prediction of DOM is probably best approached using the Nutritive
Entity concept of Lucas and Smart (1959) as expressed in terms of a
summative equation (Raymond, 1969; Barnes, 1973; Moore and Mott,
1973). Perhaps the most rational summative equation for DOM prediction
would include the fractions which constitute this parameter (values as
percentages of DM) :
DOM = DNDS + DNDF - MFOM, (A)
where DNDS = digestible ash-free neutral-detergent solubles;
DNDF = digestible ash-free neutral-detergent fiber;
and MFOM = metabolic fecal OM excretion.
The DNDS include readily soluble or digestible carbohydrates,
DCP and whatever digestible lipids may be present. Total ash-free
neutral-detergent solubles (NDS) are, in theory, readily and almost
completely degraded in the rumen, either by direct solution or by
rapid microbial digestion. True digestibility of NDS may be approxi-
mately 100 percent (Van Soest, 1967), and NDS may be considered a
Nutritive Entity which varies as a percentage of DM among forages,
but not in digestibility. Thus, it is possible that replacing DNDS
in equation (4) with NDS would not lead to unacceptable errors in
pr-diction of DOM. This would produce the following rational summative
equation for prediction of DOM (values as percentages of DM):
DOM = NDS + DNDF - MFOM. (5)
Ash-free neutral-detergent fiber (NT)F) varies as a percentage
of DM, and in digestibility, among forages. With forages high in
NDF, such as warm-season grasses, there is not a close relationship
between percentage and digestibility of NDF or its constituents
32
(Velasquez, 1974; Minson, 1971b). Since NDF is not a Nutritive Entity,
both NDF and NDF digestibility (NDFD) must be known to estimate DNDF.
Both NDS and DNDF must be determined for each forage for which
DOM is to be predicted, unless one of them is invariant within a narrow
and well-defined group of forages. Since MFOM in concept is a constant
proportion of DM (Van Soest, 1967), there may be little error associat-
ed with use of one MFOM value for all forages when predicting DOM.
If two of the three right-hand members of equation (5) are not highly
variable across a given group of forages, then values for the third
member should be highly correlated with DOM. Such a situation may
occur within legumes (Tilley et al. , 1969; Johnson and Dehority, 1968).
In such a case, an empirical prediction equation based only on the
third component could predict i^ vivo DOM values which were nearly
identical with those of forages used to generate the equation. This
same equation might not predict DOM accurately within a large group of
forages in which a different component of the equation was more highly
correlated with DOM, or in which two of the three components were highly
variable. Therefore, if a summative equation for prediction of DOM
is to have wide applicability, independent estimates of NDS and DNDF
will probably be required for each forage.
Prediction of DE/DM
The DE value of DOM (DE/DOM) varies among forages due to variation
in DCP as a percentage of DM (Minson and Milford, 1966; Golding, 1973).
Such variation in DE/DOM is due to different average caloric values of
proteins and carbohydrates (5.65 vs 4.15 kcal/g; Maynard and Loosli,
1969). A correction can be made for this difference, and perhaps should
33
be made since DCP may vary widely among forages. A theoretical correction
is indicated by the following equation, under the assumption that DEE
as a percentage of DM = 0 (DE values as kcal/g DM; others as percentages
of DM) :
^„ _ 4.15 (DCF + DNFE) + 5.65 (DCP)
°^ ~ Too • (6)
Since equation (2), for most forages, can be written
DOM = DCP + DCF + DNFE, (7)
then
_„ _ 4.15 (DOM) +1.50 (DCP) .
^^ 100 (8)
Values of DCP can be predicted from CP for most forages (except those
that are heat damaged) by the following equation (N.R.C., 1971) (values
as percentages of DM) :
DCP = .866(CP)-3.06. (9)
The combined theoretical equation for predicting DE/DM from predicted
DOM and determined CP is (DE as kcal/g DM; others as percentages of
DM)
_ 4.15 (DOM) + 1.50 (.866 CP - 3.06).
°^ 100 ' (10)
DE
4.15 (DOM) + (1. 50-. 866) (CP) - (1.50-3.06),
100 (11)
_ 4.15 (DOM) + 1.299 (CP) - 4.59.
^^ - Too (12)
Testing the Procedure
Forages and in vivo data
Fifty- two forages, including 43 warm-season grasses and nine
cuts of 'Florida 66' alfalfa (Medicago sativa L.) were used in this
34
study. The 43 grasses were comprised of 31 which will be described
in Chapter V, and eight additional cuts of Pensacola bahiagrass
(Paspalum no ta turn Flugge) ; one of Suwannee bermudagrass (Cynodon
dactylon (L) Pers.); and three of Pangola digitgrass (Digitaria
decumbens Stent). The latter 12 grasses were fed at less than ad
libitum levels $:estricted-f ed) to sheep when studied i^ vivo , while
alfalfas were fed ad^ libitum. All other details of in vivo trials
involving alfalfas or restricted-fed grasses were as will be described
for 31 grasses in Chapter V.
Laboratory analyses and prediction testing
Procedures relative to (a) laboratory analyses; (b) determinations
of correlation coefficients (r values) and residual standard deviations
(s values) between laboratory analyses and/or in vivo values; (c) pre-
y.x
diction of in vivo parameters; (d) setting of conservative and liberal
acceptability limits (±t(s//n) and ± 2s, respectively); and (e) test-
ing of predictions, were the same as will be described in Chapter V.
In addition, in vivo digestible energies (kcal/g DM) were determined
for 10 grasses. Values of DE/DM (kcal/g) were predicted for these 10
grasses using equation (12) . Predicted values of DOM, as a percentage
of DM, were obtained for all 52 forages from equation (5). Values
of NDS inserted into equation (5) were calculated as CM minus ash-free
NDF (both as percentages of DM) , while DNDF values were those determin-
ed in vivo. Values of MFOM for each hay were calculated as (NDS + DNDF)
minus in vivo DOM, all as percentages of DM.
35
Results and Discussion
Chemical Analyses
Ranges, means and coefficients of variation (CV) resulting from
various laboratory chemical analyses conducted on the nine alfalfas
and 43 grasses are presented in table 1. Values of these parameters
for individual forages can be found in Appendix tables 10 and 12.
Values of CP ranged from 16.8 to 30.6 for alfalfa, with a mean
of 22.5 (table 1), and from 3.8 to 19.5 for grasses, with a mean of
9.3. Though mean alfalfa maturity was less than that of grasses (4.7
vs 7.3 wk, respectively), these data reflect the generally higher CP
percentages of legumes. For all forages, mean CP was 11.6 percent.
Values of ash-free NDS ranged from 39.9 to 50.3 for alfalfa,
and the mean was 46.0 percent. The NDS content of grasses ranged
from 16.1 to 30.5 percent with a mean of 20.7 percent. Mean NDS for
all forages was 25.0 percent. Though differences in average maturity
between alfalfa and gragses may have somewhat influenced these results,
NDS was much higher in legumes than in grasses (Van Soest, 1965a;
Smith et al., 1972). There was much less ash-free NDF present in
legumes than in grasses. Alfalfa contained an average of only 44.0
percent of NDF, while this figure for grasses was 75.1 percent. Again,
differences in average maturity between alfalfa and grasses may have
influenced these results, but grasses are generally considered to
contain more NDF than legumes. For all forages, NDF ranged from 33.2
to 81.3 percent, and averaged 69.7 percent.
36
TABLE 1. MEASURES OF CENTRAL TENDENCY AND DISPERSION OF THE
CHARACTERISTICS OF 52 FLORIDA FORAGES
Item
Alfalfa
Number of forages
Number of species
Crude protein (CP)^
Organic matter (OM)
Neutral-detergent solubles
(ash-free) (N-DS)^
Neutral -detergent fiber
(ash-free) (NDF)^
NDF digestibility (ash-free)
(NDFD)^
Predicted NDFD (ash-free)^
In vitro NDF digestion (ash-free)
(IVNDFD) 72 hr^
Digestible NDF (ash-free) (DNDF)^
OM digestibility (OMD)
Digestible OM (DOM)^
Predicted DOM^
Metabolic fecal OM (MFOM)^
9
1
Mean (CV)^
22.5 (19.9)
Range
16.8-30.6
Mean (CV)
89.9 (3.2)
Range
83.5-92.1
Mean (CV)
46.0 (7.7)
Range
39.9-50.3
Mean (CV)
44.0 (13.5)
Range
33.2-52.1
Mean (CV)
54.9 (11.2)
Range
47.4-64.4
Mean (CV)
-
Range
-
Mean (CV)
43.5 (13.5)
Range
38.5-55.2
Mean (CV)
23.9 (8.8)
Range
20.8-26.9
Mean (CV)
67.1 (5.6)
Range
62.5-72.2
Mean (CV)
60.3 (3.5)
Range
57.6-64.2
Mean (CV)
59.5 (4.6)
Range
56.5-64.6
Mean (CV)
9.5 (11.2)
Range
7.5-10.9
^As % of dry m.atter. In %. Coefficient of variation, in %,
°Restricted-fed. Ad libitum-fed,
37
Table 1 - extended.
d
Grasses
Grasses
Grasses
All
12
31
43
52
3
3
3
4
9.3 (18.8)
5.5-11.9
9.3 (47.1)
3.8-19.5
9.3 (40.9)
3.8-19.5
11.6 (54.8)
3.8-30.6
95.1 (.8)
94.2-96.4
96.0 (1.3)
93.3-97.5
95.7 (1.2)
93.3-97.5
94.7 (2.9)
83.5-97.5
19.5 (6.9)
17.6-21.5
21.1 (21.9)
16.1-30.5
20.7 (19.5)
16.1-30.5
25.0 (41.7)
16.1-50.3
75.6 (2.2)
73.4-78.1
74.9 (7.4)
63.6-81.3
75.1 (6.4)
63.6-81.3
69.7 (18.5)
33.2-81.3
60.4 (12.7)
45.8-68.9
55.3 (17.5)
42.0-76.1
56.7 (16.5)
42.0-76.1
56.4 (15.7)
42.0-76.1
57.6 (16.2)
38.4-68.6
53.3 (18.2)
39.4-71.8
54.5 (17.8)
38.4-71.8
-
54.3 (13.4)
41.3-63.4
52.2 (23.9)
33.9-74.8
52.8 (21.2)
33.9-74.8
51.2 (21.5)
33.9-74.8
45.7 (12.9)
35.3-52.8
40.9 (11.4)
33.1-50.0
42.3 (12.8)
33.1-52.8
39.1 (22.1)
20.8-52.8
11.8 (12.2)
10.3-14.2
9.9 (21.1)
6.9-14.1
10.5 (20.1)
6.9-14.2
10.3 (19.3)
6.9-14.2
56.1 (10.9)
44.9-63.3
54.3 (14.6)
42.8-69.7
54.8 (13.6)
42.8-69.7
57.0 (14.7)
42.8-72.2
53.3 (10.5)
43.3-60.0
52.1 (13.7)
41.7-65.0
52.4 (12.8)
41.7-65.0
53.8 (12.7)
41.7-65.0
54.9 (9.7)
44.4-60.8
51.7 (15.7)
40.2-67.8
52.6 (14.3)
40.2-67.8
53.8 (13.8)
40.2-67.8
38
In Vivo and In Vitro Determinations
Ranges, means and CV's from in vivo and in vitro determinations
conducted using all 52 forages are also presented in table 1. Values
of these parameters for individual forages can be found in Appendix
tables 11 and 12.
NDF digestibility
Mean in vivo NDFD percents were similar for alfalfa and grasses,
though grasses exhibited a wider range in NDFD. The fact that NDFD
percents were similar, though alfalfa was less mature than grasses and
contained considerably less NDF, suggests that NDFD probably is not con-
trolled by NDF concentrations. The similar NDFD percents may have
been due to higher lignin concentrations in alfalfa NDF (Smith et^ al. ,
1972). The wider NDFD range exhibited by grasses was due probably to
a wider range in grass maturity relative to alfalfa maturity (Appendix
tables 11 and 12). Within grasses, NDFD was higher in those which
were restricted-fed (table 1). This effect may have been due to in-
creases in retention time when forages were restricted-fed (Blaxter
et al. , 1956) , but Minson (1966) reported that intake level had a
relatively small effect upon rumen retention time of a given forage.
In the present study, grasses which had been restricted-fed were per-
haps naturally higher in NDFD than grasses which were fed ad libitum.
Support for this hypothesis is drawn from the fact that IVNDFD after
72 hr of fermentation was higher for restricted-fed grasses than for
other grasses.
Mean values of IVNDFD after 72 hr were also lower for alfalfa
than for grasses (43.5 and 52.8 percent, respectively). Since Smith
39
et al. (1972) reported that lignin concentration was higher in legume
NDF than in that of grasses, the lower I VNDFD exhibited by alfalfa
after 72 hr may have been due to the fact that mechanical breakdown of
NDF is not simulated by the in vitro system. Since mechanical break-
down does take place in vivo, lack of this process in vitro could exp!' '.n
the discrepancy shown here between alfalfa and grasses in the in vivo -
in vitro relationship. Whatever the cause of this discrepancy among
forages, different equations would have to be employed for alfalfa and
grasses in predicting in vivo NDFD from IVNDFD after 72 hr of fer-
mentation. Also, the relationship between in vivo NDFD and IVNDFD after
72 hr may not be quite as strong for alfalfa as for grasses. For 31
grasses, this relationship was characterized by an r value of .96
(r^=.92) and an s of 2.71, while for the nine alfalfas these values
y.x
were .91 (.83) and 2.73, respectively.
Digestible neutral-detergent fiber and neutral-detergent solubles
Mean ash-free DNDF was lower for alfalfa than for grasses (23.9
and 42.3 percent, respectively; table 1), since alfalfa contained a
lower percent of ash-free NDF than did grasses. Within alfalfa, the
facts that MFOM is theoretically constant (Van Soest, 1967) and that
DNDF was smaller and less variable in an absolute sense than NDS
raise the possibility that NDS alone would be a good predictor of
alfalfa DOM. Simple linear regression revealed that while the relation-
ship between DOM and DNDF for alfalfa was represented by an r value of
-.10 (r =.01) and an s of 2.30, the relationship between DOM and
y.x
NDS exhibited such values of .77 (.60) and 1.46, respectively. The
40
relationship between DOM and (NDS + DNDF) for alfalfa was represented
2
by an r value of .93 (r =.87) and an s of .85. Thus, (NDS + DNDF)
may be a better predictor of alfalfa DOM than NDS would be alone. This
hypothesis should be investigated in terms of acceptability of alfalfa
DOM predictions. Within grasses, though DNDF was higher and more
variable in absolute terms than was NDS, it also appears that (NDS +
DNDF) would be a better predictor of DOM than DNDF would be alone.
Restricted-fed grasses exhibited higher DNDF than did grasses fed
ad libitum (table 1) , since restricted-fed grasses showed higher NDFD
percents. As pointed out earlier, these higher NDFD percents may not
have been strictly the direct result of lower intake.
It is possible that one reason for failure of the Van Soest
Summative Equation (Van Soest, 1965b) to accurately predict digestibility
of warm-season grasses (Velasquez, 1974) may be that in such grasses
ash-free DNDF is larger and more variable than digestible ash-free
NDS (DNDS), or (ash-free NDS - MFOM) . The Van Soest Summative Equation
was developed on temperate forages, and in these forages DNDF appears
less variable than DNDS' (Tilley e^ al • , 1969). In the present study,
ash-free DNDF for 31 grasses averaged 40.9 percent (table 1), and the
2
variance (s ) associated with this mean was 21.7 units. Ash-free DNDS
2
averaged 11.1 percent and s was 15.2 units. Therefore, the high amount
and variability of DNDF in warm-season grasses may limit the utility
of the Van Soest Summative Equation, per se, for predicting diges-
tibility of such grasses.
41
OM digestibility
Mean OMD was higher for alfalfa than for grasses (67.1 and 54.8
percent, respectively; table 1). This was due to NDS being higher in
alfalfa, and to NDFD being similar between alfalfa and grasses. The
CV for OMD was less for alfalfa (5.6 percent) than for grasses (13.6
percent). This was caused by the higher mean OMD for alfalfa, and
probably also by the lower maturity range among alfalfas than among
grasses. Within grasses, mean OMD was higher for those which had
been restricted-fed. This, however, may not have been directly related
to lower intake of these grasses.
Digestible organic matter
Mean DOM, as a percentage of DM, was also higher for alfalfa
than for grasses (60.3 and 52.4 percent, respectively). This was due
to the much higher NDS in alfalfa more than compensating for higher
DNDF in grasses. Values of CV for DOM were lower for alfalfa than
for grasses, probably due to the same factors which caused this same
response with respect to OMD. Values of DOM for restricted-fed grasses
were similar to those for grasses fed ad libitum because NDS in re-
stricted-fed grasses was slightly lower than in ad libitum- fed grasses
and MFOM was slightly higher.
Metabolic fecal organic matter by calculation
Mean values of MFOM, as a percentage of DM, were 9.5 for alfalfa,
10.5 for grasses and 10.3 for all forages. Thus, a constant value of
10.3 was inserted for MFOM into equation (5) when making DOM predictions.
Within grasses, MFOM means were (as percentages of DM) bahiagrass, 12.2;
42
bermudagrass, 8.3; and Pangola digitgrass, 11.4. The reason that MFOM
for the 12 restricted-fed grasses was higher than the average for all
forages was that eight restricted-fed grasses were bahiagrasses and
three were Pangola digitgrasses. Mean values of MFOM in this study
compare favorably with the 9.5 percent reported by Minson (1971b)
for Panicum species, and the 9.8 and 12.9 percent metabolic fecal DM
for temperate forages found by Colburn et^ al. (1968) and Van Soest
(1967), respectively. Capote (1975) reported that 10 percent could be
used for bermudagrass pellet MFOM. Still, accurate prediction of
MFOM for a given forage, rather than use of a constant value for this
parameter among forages, might produce more accurate DOM predictions
when using equation (5).
Estimation of metabolic fecal organic matter by regression
Velasquez (1974) reported that MFOM for warm-season grasses was
5.4 percent. Actual mean MFOM, as a percentage of DM, for the 40
forages utilized by this worker, however, was 10.4. This discrepancy
possibly arose because the value of 5.4 for MFOM was the ordinate
intercept which resulted when a test for nutritional uniformity (Lucas
and Smart, 1959) was applied to NDS, as a percentage of DM, over a
small range of NDS, i. e. , 15.9 to 30.5 percent. It is true that in
a test for nutritional uniformity of NDS, the ordinate intercept should
approximate MFOM if the slope of the resultant regression line is close
to 1.0, as it should have been in the work by Velasquez (1974) (Van
Soest, 1967; Minson, 1971b). However, the slope of the regression line
was only .75. This low slope probably resulted because Velasquez (1974)
worked with a narrow range of NDS values which, in effect, reduced the
43
sample size from the true population of NDS values for all existing
forages. This small sample size probably did not allow the true
slope of the regression line for all existing forages to express itself,
and resulted in an inaccurate estimation of this slope, which should
have been close to 1.0. Thus, incorrect estimation of the slope for
the true relationship between DNDS and NDS probably caused the ordinate
intercept of 5.4 to inaccurately estimate the true average MFOM value
of 10.4 percent. This hypothesis was tested in the present study.
Using 31 grasses which ranged in NDS from 16.1 to 30.5 percent, the
regression of DNDS on NDS produced a line with a slope of .75, and
an MFOM estimate of 4.7 percent. Actual mean MFOM for these 31 grasses
was 9.9 percent. Repeating this analysis using all 52 forages re-
sulted in an NDS range of from 16.1 to 50.3 percent, or a range which
was 238 percent of that used previously. In this case, regression of
DNDS on NDS produced a line with a slope of 1.00, and an MFOM estimate
of 10.4 percent. Actual mean MFOM for these 52 forages was 10.3 per-
cent (table 1). Thus, if a test of nutritional uniformity is used to
estimate the actual mean value of MFOM, a range of NDS large enough to
allow expression of the true slope of the relationship between DNDS and
NDS must be used.
Prediction of NDFD , DOM and DE/DM
Ranges, means and CV s for predicted values of NDFD and DOM are
presented in table 1. Predicted values of these parameters for indi-
vidual forages appear in Appendix tables 11 and 12. Individual values
for actual and predicted DE/DM for 10 grasses are presented in table 2.
44
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45
For grasses, predicted values of ash-free NDFD ranged from 38.4
to 71.8, and the mean was 54.5 percent (table 1). Predictions of NDFD
were not made for alfalfas since no previously generated prediction
equation was available, and the nine alfalfas used in this study-
were not enough to effectively generate and test such an equation. For
all 43 grasses, simple linear regression of actual NDFD on predicted
NDFD produced an r value of .98 (r =.96) and an s of 2.0 percentage
units. These values were high even within grasses which had been re-
stricted-fed, i. e., r=.98 (r =.96) and s ^=1-5 percentage units. Thus
even when warm-season grasses are restricted-fed, IVNDFD after 72 hr
of fermentation appears to be an excellent independent variable from
which to accurately predict NDFD. Determination of this IVNDFD parameter
in the laboratory, however, requires considerable time and effort, and
development of a more rapid procedure for predicting in vivo NDFD would
accelerate and facilitate forage evaluation. Micro-anatomical studies
of forages (Akin ^ al . , 1974a; Monson et al. , 1972; de la Torre, 1974)
may aid in developing such a procedure.
Another possible reason why the Van Soest Summative Equation (Van
Soest, 1965b) does not apply to warm-season grasses (Velasquez, 1974)
may be that the equation used to predict NDFD is not truly applicable
to such forages. The equation presented by Van Soest (1965b) for NDFD
prediction is
NDFD = 147.8 - 78. 9L, (13)
where L represents the common log of lignin percentage in acid -detergent
fiber. For the 43 warm-season grasses utilized in the present study,
46
simple linear regression of actual NDFD on NDFD predicted using equation
2
(13) produced an r value of only .73 (r =.54) and an s of 6.4 per-
•^ y.x
centage units. Thus, it appears that equation (13), which was develop-
ed on temperate forages, does not possess a high degree of utility for
accurate prediction of NDFD in warm-season grasses.
For alfalfa, predictions of DOM, as a percentage of DM, generated
by equation (5) ranged from 56.5 to 64.6 (table 1), with a mean of 59.5;
and for grasses, predictions ranged from 40.2 to 67.8, with a mean of
52.6. For all forages, DOM predictions ranged from 40.2 to 67.8, and
the mean was 53.8 percent. Using all 52 forages, regression of actual
2
in vivo DOM on predicted DOM produced an r value of .96 (r =.93) and
an s of 1.8 percentage units. Within either grasses or alfalfa
y.x
this relationship was just as strong, with r and s ^ values being
9 2
.96 (r =.93) and 1.8 for grasses, and .94 (r =.88) and .8 for alfalfa,
respectively. These results suggest that equation (5) can be used for
accurate prediction of DOM in alfalfa and warm-season grasses, and
that MFOM can be considered constant at 10.3 percent for these forages.
Before either of these hypotheses can be considered true, however, DOM
predictions must be acceptable when judged by statistically defined
acceptability limits.
Predictions of DE/DM (kcal/g) were generated for 10 warm-season
grasses using equation (12). Two predictions of DE/DM were produced
for each grass: (a) by inserting actual in vivo DOM into equation (12);
and (b) by using predicted values of DOM in this equation. Actual
values of DE/DM ranged from 1.82 to 2.68, with a mean of 2.18 kcal/g
(table 2). Predictions generated by method (a) ranged from 1.78 to
47
2.57, with a mean of 2.11; and for method (b) , from 1.72 to 2.50, with
a mean of 2.15. Regression of actual DE/DM on that predicted by method
2
(a) produced an r value of .99 (r =.99) and an s of .03 kcal/g. This
procedure with respect to method (b) resulted in an r value of .93
2
(r =.87) and an s of .10 kcal/g. These results suggest that equation
y.x
(12) is rational for prediction of DE/DM, and that equation (5) can
be employed in conjunction with equation (12) for accurately predicting
this parameter. As was the case relative to such conjecture concern-
ing DOM prediction, predictions of DE/DM by both method (a) and method
(b) must be acceptable when judged by statistically defined limits
before the above hypotheses can be considered true.
Testing of DOM and DE/DM Predictions
Acceptability limits for judging the predictions
Theory underlying the definition of acceptability limits used in
this study is presented in Chapter V. Differences between actual and
predicted values of DOM or DE/DM were deemed acceptable in a conservative
sense if the absolute values of these differences were less than or equal
to the weighted average of t(s/i/n) when this expression was evaluated at
the .95 confidence level for all 52 or 10 forages, respectively. Such
differences were termed acceptable in a liberal sense when their absolute
values were less than or equal to the weighted average of 2s for the 52
or 10 forages. Though in this study acceptability limits were calculat-
ed for each forage species, only limits applicable to all forages were
used to test predictions. This policy negates the necessity of referring
to such limits for each forage species when qualifying predictions of
48
DOM or DE/DM. Conservative and liberal acceptability limits determined
by applying their respective expressions to the 52 or 10 forages, as
well as to alfalfa, bahiagrass, bermudagrass or Pangola digitgrass
alone, are shown in table 3.
Acceptability of the predictions
Figure 1 shows the test of acceptability of DOM predictions. The
points plotted in this figure are coordinates of actual DOM and pre-
dicted DOM values, and the continuous middle line represents the set of
points where actual DOM equals predicted DOM. The vertical deviation
of any plotted point from the continuous middle line represents the
error in predicting that value of DOM. The inner set of broken lines
represent conservative acceptability limits, and the outer set of
broken, dotted lines mark the liberal acceptability limits. In this
study, all 52 DOM predictions were acceptable when judged by liberal
limits, and 38 predictions were acceptable by conservative standards.
These results confirm the hypotheses that equation (5) can be used to
produce acceptable predictions of DOM for alfalfa and warm-season grasses,
and that MFOM can be considered constant at 10.3 percent among these for-
ages. Forages for which DOM predictions were not acceptable when judged
by conservative limits included one alfalfa, six bahiagrasses , six
bermudagrasses and one Pangola digitgrass. Margins by which DOM pre-
dictions for these forages were unacceptable according to conservative
limits ranged from .1 to 1.3 percentage units, and only five such margins
were greater than .5 percentage units. Since rn vivo DNDF values were
inserted into equation (5) to produce DOM predictions, the absolute
value of a given difference between actual and predicted DOM was equal
49
TABLE 3. CONSERVATIVE AND LIBERAL ACCEPTABILITY LIMITS FOR TESTING
PREDICTIONS OF DIGESTIBLE ORGANIC MATTER (DOM) AND DIGESTIBLE ENERGY
(DE) CONCENTRATION
FORAGE
SPECIES
Item
Alfalfa
Bahia
Bermuda
Pangola
All
DOM, % of dry matter
Conservative [±t(s/v^)]
±2.6
±2.2
±2.5
±3.1
±2.6
Liberal (±2s)
±3.3
±4.3
±5.2
±5.0
±4.7
DE, kcal/g dry matter
Conservative
-
±.12
±.10
±.17
±.13
Liberal
-
±.24
±.20
±.32
±.25
50
40 43 46 49 52 55 58 ^ 61 64 67 70
PREDICTED DIGESTIBLE ORGANIC MATTER (Y) , % OF DRY MATTER
Figure 1. Test of theoretically rational method for prediction
of digestible organic matter as a percentage of dry
matter.
51
to the absolute value of the difference between MFOM for a given
forage and the assumed constant MFOM value of 10.3 percent. Absolute
differences between this constant MFOM value and actual mean MFOM
for bahiagrass and bermudagrass were 1.9 and 2.0 percentage units,
respectively. More accurate estimation of actual mean MFOM for
bahiagrass and bermudagrass would result in a greater number of
conservatively acceptable DOM predictions for these grasses when
using equation (5). For all forages in this study, however, use of
a constant MFOM value of 10.3 percent produced acceptable predictions
of DOM.
Figure 2 shows that prediction of DE/DM (kcal/g) by method (a)
slightly underestimated actual DE/DM for all 10 grasses. This may
have been due to assuming DEE, as a percentage of DM, to be non-
existent in these forages. However, all 10 DE/DM predictions were
acceptable when judged by conservative limits. This result confirms
the hypothesis that equation (12) is rational for prediction of DE/DM
for warm-season grasses. Figure 3 shows that prediction of DE/DM by
method (b) produced predictions which both overestimated and under-
estimated actual DE/DM. Inspection of Appendix tables 11 and 12 and
table 2 shows that actual DE/DM was over-predicted when actual DOM was
over-predicted by equation (5), and vice-versa. The one exception to
this generality may have been due to the possibility that 10-wk Pangola
digitgrass (table 2) contained a small but significant amount of DEE.
Still, figure 3 indicates that all DE/DM predictions resulting from
method (b) were acceptable when judged by liberal limits, and that
52
iVt 178 1.9 2.0 271 272 271 O 273 276 2.7
PREDICTED DE (Y), kcal/g DM
Figure 2. Comparison of in vivo digestible energy (DE) with
that predicted from actual In vivo digestible organic
matter (DOM) and crude protein (CP) by the equation:
DE = 4.15 DOM + 1.299 CP - 4.59.
100
53
2.7 r
2.6 -
2.5 -
2.4 -
2.3 -
2.2
2.1 -
1.7 1.8 1.9 2.0 2.1 2.2 2.3 2.4 2.5 2.6 2.7
PREDICTED DE (Y),kcal/g DM
Figure 3. Comparison of in vivo digestible energy (DE) with
that predicted from predicted iji vivo digestible
organic matter (DOM ) and crude protein (CP) by
the equation:
DE = 4.15 DOM + 1.299 CP - 4.59.
P
100
54
nine predictions were acceptable by conservative limits. That pre-
dicted DE/DM for 4-wk bermudagrass was too low to be acceptable by-
conservative limits, though its actual DOM value was underpredicted
to a lesser extent than that of 8-wk bermudagrass (table 2), may
have been due to a higher amount of DEE in 4-wk bermudagrass. The
results shown in figure 3 confirm the supposition that equation (5)
can be employed effectively together with equation (12) to produce
acceptable predictions of DE/DM.
General Discussion
Non-Forage Factors Affecting DE/DM
When predicted DOM, as a percentage of DM, from equation (5) is
inserted into equation (12) , acceptably accurate predictions of DE/DM
(kcal/g) can be obtained for warm-season grasses. This procedure,
however, predicts DE/DM as an attribute of a given forage, and not as
that which might be realized in a given production situation. This
is because there are many factors influencing forage nutrient digest-
ibility in a given situation which are not taken into account in
existing laboratory procedures used to estimate digestibility. Such
factors generally are related to the animals which consume a given
forage, to environmental conditions or to the management policy under
which forages are fed to ruminants. These factors are termed non-
forage factors, since they are not related directly to chemical compo-
sition or structural organization of forages, per se. Non-forage
factors which have been documented in the literature, and which may
affect DE/DM in a given situation, include
(1) type of ruminant to which forages are fed, i. e. , cattle
or sheep (Cipolloni ejL al . , 1951; Alexander e_t al. , 1962;
Blaxter et al. , 1966) ;
55
(2) breed of ruminant within type (Ashton, 1962; Ledger et al. ,
1970; Riewe and Lippke, 1970; Essig e^ al . , 1975);
(3) the form in which forages are fed, i. e. , long, chopped,
ground or ground and pelleted (Rodrigue and Allen, 1956;
Minson, 1967; Church, 1969; Terry ejt al. , 1972);
(4) energy supplementation of forages (Burroughs e_t al . , 1949;
el-Shazly et al . , 1961; Clanton and Rittenhouse, 1970;
Gelding, 1973);
(5) CP supplementation of low-CP forages (Smith, 1962; Campling
_et al . , 1952; Chapman and Kretschraer, 1964; Ventura, 1973);
(6) level of feeding (Blaxter et al. , 1956; Moe et al. , 1965;
Brown, 1966; Terry e^ al. , 1972);
(7) animal level of internal parasites (Spedding, 1954; cited
by Raymond, 1969) ;
(8) ambient temperature (Blaxter and Wainman, 1961; Bailey,
1964); and
(9) water deprivation (French, 1956; Phillips, 1961).
These non-forage factors, if present at functional levels in a given
production situation, could cause discrepancies between actual and
predicted DE/DM. If effects of these factors upon DE/DM could be
quantified over a wide range of forage quality, then dynamic computer
modeling might allow accurate prediction of DE/DM for given production
situations.
Research Needs for Rapid and Accurate DOM Prediction
Results of this study showed that acceptable predictions of DOM
were obtained when a constant MFOM value of 10.3 percent of DM was
inserted into equation (5) along with actual in vivo DNDF. Thus,
further work on MFOM appears unnecessary in achieving the rapid and
acceptable prediction of DOM for alfalfa and warm-season grasses.
Attention now must be turned toward the rapid, acceptable pre-
diction of DNDF percentage. Percentage of NDF can be determined
56
rapidly in the laboratory (Van Soest and Wine, 1967), but in pre-
dicting DNDF it is not sufficient to measure only NDF, since this
fiber fraction is not a Nutritive Entity (Moore and Mott, 1973).
Digestibility of NDF is predicted best by IVNDFD after a 72-hr
fermentation. Thus, NDFD prediction is laborious and time consuming,
and it is possible that discrepancies exist among forages in this
in vivo-in vitro relationship. In this study, the only chemical
component which correlated highly with NDFD or DNDF in 31 grasses
was lignin (r=-. 89 and -.81, respectively), but these correlations
may not be this high over a wider range of forages (Moore and Mott,
1973). Correlation coefficients between (NDS + DNDF) and lignin or
NDF were -.91 or -.90, respectively, for the 31 grasses, but again
these r values probably will decline over a wider range of forages.
Moir (1972) suggested that DNDF be considered constant among temperate
and tropical grasses at 40 percent of CM, and among legumes at 19.8
percent. In the present study, DNDF ranged from 33.1 to 52.8 percent
of DM for 43 grasses (table 1), and from 20.8 to 26.9 percent for
nine alfalfas. Thus, the suggestion of Moir (1972) appears inaccurate.
Research now must be directed toward development of a rapid, acceptable
procedure for predicting DNDF percentage, or NTDFD percent, as a forage
attribute over a wide range. Results of recent microscopic studies
of NDF degradation by rumen microorganisms suggest that NDF in some
forage tissues is indigestible, whereas NDF in other tissues is digest-
ible (Moore and Mott, 1973; Barnes, 1973; de la Torre e^ al • , 1974).
Therefore, the NT)F fraction may contain two Nutritive Entities, one
57
being potentially digestible NDF with a digestibility near IOC percent,
and the other being potentially indigestible NDF with a digestibility
near 0 percent. This concept has been suggested as the basis for a
model of cellulose digestion (Waldo et al . , 1972), and could be valid
for NDF digestion as well. Thus, microscopic studies to examine
patterns of NDF organization and degradation over a wide range of
forages may aid in development of a procedure for rapid, acceptable
prediction of DNDF among forages.
Summary
Summative equation and Nutritive Entity concepts should serve as
the basis for rational prediction of the digestible energy (DE)/DM
(kcal/g) values of forages. Acceptably accurate predictions of DE/DM
can be obtained by summing the caloric values of the major portions
of forage digestible OM (DOM), i. e. , digestible carbohydrate and
digestible CP. Acceptable predictions of DOM can be obtained by
summing digestible neutral-detergent solubles (DNDS) and digestible
neutral-detergent fiber (DNDF), and subtracting metabolic fecal OM
(MFOM), all as percentages of DM. Use of a constant 10.3 percent for
MFOM and determination of neutral-detergent solubles (NDS) to estimate
DNDS both lend themselves to a rapid and inexpensive procedure for
prediction of DOM. If MFOM is to be predicted for a given group of
forages using a test for nutritional uniformity, care must be taken
to include forages which exhibit a wide range of NDS in the analysis.
Though DNDF is smaller and less variable than NT)S within alfalfa,
this latter parameter by itself may not produce acceptable predictions
58
of alfalfa DOM. Values for neutral-detergent fiber digestibility (NDFD)
can be predicted accurately for grasses from in vitro NDFD after 72 hr
of fermentation. This in vitro procedure is time consuming and laborious,
and discrepancies apparently exist in the iii vivo NDFD - In vitro NDFD
relationship among alfalfas and grasses. Thus, the remaining challer '
with reference to DOM, and ultimately DE/DM, prediction is development
of a rapid procedure for acceptable prediction of DNDF over a wide
range of forages.
The reasons that Van Soest's Summative Equation, which was develop-
ed on temperate forages, does not predict digestibility of warm-season
grasses accurately may be that (a) in warm-season grasses, DNDF appears
larger and more variable than DNDS; and (b) the equation used to pre-
dict NDFD does not predict this parameter accurately for warm-season
grasses.
CHAPTER IV
ELIMINATION OF ORGANIC SOLVENTS IN THE STUDY OF IN VITRO
NEUTRAL-DETERGENT FIBER DIGESTION
Introduction
In vitro studies of forage neutral-detergent fiber (NDF) digestion
will be increasingly important in the future (Chapter III) . Two organic
solvents which may be hazardous to laboratory technicians have been used
in determination of in vitro NDF digestion, e. g., toluene (Goering and
Van Soest, 1970) when contents of fermentation tubes were held for
later analysis; and acetone in the NDF determinations (Van Soest and
Wine, 1967). The effectiveness of toluene may be questionable, since
Meites et al. (1951) reported that cellulolytic activity of rumen micro-
organisms continued for up to 48 hr after addition of toluene.
The objectives of this experiment were (a) to establish whether
acetone washes were required for accurate determination of ash-free
NDF (NDFA) in either hay samples or in residues after ^il vitro fermenta-
tion; and (b) to develop a procedure for terminating in vitro fermentation
which did not require use of toluene.
Experimental Procedure
Artificially dried hays of different quality made from two cuts of
'Florida 66' alfalfa (Medicago sativa L.) (hays 73-B and 73-D, Appendix
table 12), two cuts of Pensacola bahiagrass (Paspalum notatum Flugge)
(47-2A and 47-4C, Appendix tables 10 and 11), two cuts of Suwannee
bermudagrass (Cynodon dactylon (L) Pers.) (65-lA and 65-lF, Appendix
59
60
tables 10 and 11) , and two cuts of Pangola digitgrass (Digitarla decum-
bens Stent) (55- 2A, Appendix tables 10 and 11; 75-2C, Appendix table 12)
were used to examine the necessity of acetone washes in determinations
of NDFA, as a percentage of DM, in hay samples. Treatments used were
(a) the control, in which residues were washed with both boiling water
and acetone (Van Soest and Wine, 1967); and (b) the modification, in
which residues were washed with boiling water alone. Dried residue was
ashed and the difference in weight between dry and ashed residues re-
presented weight of NDFA. Three separate runs, each including all eight
hays, were made for a total of three NDFA observations per treatment.
The experimental design and analysis of variance were those for complete
randomized blocks (Snedecor and Cochran, 1967) , with hays representing
blocks.
The same eight hays were used to investigate the necessity of wash-
ing ^ vitro residual NDF with acetone when determining iii vitro NDFA
digestion, and to determine an alternate stop-method to toluene for
terminating fermentation. Iji vitro fermentations followed the procedure
of Moore and Mott (1974) except that fermentation lasted 28 hr and res-
idual NDFA was determined. Toluene was not used in any stop-method.
The four stop-methods were (a) immediate analysis for residual NDFA
(Goering and Van Soest, 1970); (b) addition to tubes of 25 ml neutral-
detergent (ND) reagent, followed by 40 hr of refrigeration; (c't immersion
of tubes to the level of their contents in an ice-water bath for 1 hr,
followed by 40 hr of refrigeration; and (d) addition to tubes of 6 ml
of 20 percent (v/v) hydrochloric acid (HCl) in 1, 1, 2 and 2 ml increments.
61
followed by 40 hr of refrigeration. Acetone treatments were as describ-
ed earlier for determination of NDFA in hay samples. Treatments were
analyzed in duplicate within run, and two separate runs were made, for
a total of four observations per treatment. The experimental design
consisted of complete randomized blocks, with blocking by hays. Analysis
of variance was done using least-squares procedures described by Harvey
(1960), and interaction means were compared using Duncan's Multiple Range
Test (Duncan, 1955). Due to high precision of in vitro and chemical
determinations, statistical testing was done at the .01 level to reduce
the possibility of claiming differences significant when such differences
were not large in a biological sense.
Results and Discussion
Table 4 shows results of determinations of hay NDFA for the eight
individual hays when the two acetone treatments (+ or -) were applied.
Treatment means for + or - acetone were 68.4 and 69.2 percent, respec-
tively. There was no difference (.01 < P < .05) between these means.
However, the rankings of 4-wk bahiagrass and 13-wk Pangola digitgrass
were reversed between treatments. The largest difference between treat-
ments for an individual hay (2.2 percentage units with 2-wk Pangola
digitgrass) was a positive 3.3 percent of the + acetone value, or
greater than the 3 percent generally accepted for laboratory error. Thus,
though there was no difference (.01 < P < .05) between acetone treatments,
results of this experiment suggest that unacceptable errors in deter-
mination of hay NDFA could result if an acetone wash is not employed.
In the in vitro experiment, acetone was not involved in any two-
way interactions (P>.05). Since the main effect of acetone was not
62
TABLE 4. EFFECT OF ACETONE ON THE DETERMINATION OF ASH-FREE NEUTRAL-
DETERGENT FIBER (NDFA) IN EIGHT HAYS
Hay
TREATMENT
+Acetone
-Acetone
41.3^
41.5
47.2
47.3
67.6
69.8
73.0
74.8
77.3
78.7
78.2
78.5
78.8
79.3
83.6
83.5
73-B (3-wk alfalfa)
73-D (4.5-wk alfalfa)
55-2A (2-wk Pangola digitgrass)
65-lA (2-wk bermudagrass)
47-2A (4-wk bahiagrass)
75-2C (13-wk Pangola digitgrass)
47-4C (mature bahiagrass)
65-lF (12-wk bermudagrass)
Mean
68.4
69.2
Number, weeks of maturity and species. NDFA, % of dry matter.
63
significant (P>.05), results of this experiment suggest that washing
in vitro residues with only boiling water should not produce errors
in determinations of i^ vitro residual NDFA or _in vitro NDFA digestion.
Results differed (P<.01) among in vitro stop-methods. However,
there were interactions (P<.01) between stop-method and hays, and between
stop-method and replications (reps). Table 5 shows the statistical
comparison of stop-method x hays means, and table 6 presents these
comparisons for stop-method x reps means. For all hays, terminating
fermentation with either 25 ml of ND reagent or an ice-water bath,
both followed by 40 hr of refrigeration, produced values for in vitro
residual NDFA which were not different (P>.01) from those produced
by control. Terminating fermentation with 6 ml of HCl, followed by
refrigeration, yielded values for in vitro residual NDFA which were
higher (P<.01) than control values for all hays. These results suggest
that stopping fermentation with either ND reagent or an ice-water bath
could replace toluene in this respect. Table 6 reveals that only the
ice-water stop-method produced results equal (P>.01) to those of the
control for all reps. The ND reagent yielded lower (P<.01) in vitro
residual NDFA than the control in rep 3, and the 6 ml HCl produced re-
sults higher (P<.01) than the control for all reps. Thus, results of
this experiment suggest that only the ice-water method could stop
fermentation effectively in tubes which were to be held for subsequent
in vitro residual NDFA determinations. The ice-water method is also the
easiest of the four methods when large numbers of tubes are involved.
Tubes could be stored in a refrigerator for at least 40 hr between ice-
bath treatment and analysis.
64
TABLE 5. EFFECT OF HAY AND STOP-METHOD ON IN VITRO RESIDUAL ASH- FREE
NEUTRAI.-DETERGENT FIBER (NDFA)
STOP-METHOD
25 ml
6 ml
Hay
Control ND Reagent Ice-water HCl
73-B (3-wk alfalfa)
73-D (4.5-wk alfalfa)
55-2A (2-wk Pangola digitgrass)
65-lA (2-wk bermudagrass)
47-2A (4-wk bahiagrass)
75-2C (13-wk Pangola digitgrass)
65-lF (12-wk bermudagrass)
47-40 (mature bahiagrass)
26.3
34.3^
36.3^
46.0^
57.8^
59.1^
63.8^
64.6*
d,e
25. r
34.0^
35.1^
44.3^
56.8^
58.5*
62.8*
63.8*
26.3
35.1^
37.1^
44.9^
56.8^
58.7^
63.1^
65.0^
28.6
36.7
40.1
49.1
63.6
61.4
67.0
70.6
Mean
48.5
47.6
48.4
52.2
^Number, weeks of maturity and species. In vitro residual NDFA run im-
mediately. *^Neutral-detergent reagent (Goering and Van Soest, 1970).
H e f
In vitro residual NDFA, % of dry matter. ' Means in same row bearing
le superscript are not different (P > .01)
65
TABLE 6. EFFECT OF STOP-METHOD AND REPLICATE (REP) ON IN VITRO RESIDUAL
ASH-
-FREE
NEUTRAL -DETERGENT FIBER (NDFA)
STOP-METHOD
25 ml ^
Reagent Ice-water
6 ml
Rep #
Contro!
ND
HCl
1
48. 8*^'
d
48.5^ 48.8'^
53.5^
2
49.0^
48.1^ 50.3^
54. 1^
3
48.1'^
46.3^ 47.1*^
50.6^
4
48.2*^
47.3^ 47. 2^^
50.3^
Mean
48.5
47.6 48.4
52.1
In vitro
residual NDFA
run
inimediately. Neutral-detergent
reagent
(Goering and Van Soest, 1970). In vitro residual NDFA, % of dry matter,
d e f
' ' Means in same row bearing same superscript are not different
(P > .01).
66
Summary
An experiment which included two hays from each of 'Florida 66'
alfalfa, Pensacola bahiagrass, Suwannee bermudagrass and Pangola
digitgrass was conducted to investigate the necessity of acetone washes
for determinations of ash-free neutral-detergent fiber (NDFA) in hays
or in vitro residues; and to establish an alternate method to toluene
for terminating in vitro fermentation. Acetone washes for determina-
tions of NDFA in hays appeared necessary, but probably could be ex-
cluded when analyzing for in vitro residual NDFA. Fermentation could
be terminated by setting tubes in an ice-water bath for 1 hr, and
tubes can then be stored under refrigeration.
CHAPTER V
A RATIONAL METHOD FOR PREDICTING QUALITY OF
WARM-SEASON FORAGES FOR RUMINANTS
Introduction
Forage quality must be known if intensive high-forage systems
of ruminant production are to be based soundly upon principles of
nutrition and economics. Since determining quality of a large number
of forages by means of grazing trials is an almost impossible task,
forage researchers now generally accept the intake of digestible
energy (DE) , digestible dry matter (DDM) or digestible organic matter
(DOM) by ruminants fed ad_ libitum in confinement as expressions of
forage quality (Heaney, 1970; Holmes et al . , 1966; Jones, 1972). For
prediction of any of these measures of digestible nutrient intake,
digestibility generally can be predicted with acceptable accuracy by
one of several methods, the best of which is probably the two-stage
in vitro fermentation system (Moore and Mott, 1973). Intake is not
always highly correlated with digestibility, especially among forage
species (Minson et al. , 1964; Van Soest, 1964; Milford, 1967). At
present, there appears to be no method which accurately predicts
intake among forages. Therefore, a fast, simple, accurate procedure
for prediction of intake and/or quality is of utmost necessity for
forage evaluation and efficient ruminant production.
The objective of the present investigation was to devise and test
a theoretically rational and acceptably accurate method based upon
laboratory forage analyses for prediction of forage quality over a
wide range of forage species.
67
68
Experimental Procedure
Development of Theory Related to Rational Method for Prediction of
Forage Quality
Forage intake by ruminants is regulated by distention or fill
of some part of their gastro- intestinal tract (Crampton e^ al. , 1960;
Montgomery and Baumgardt, 1965a; Conrad, 1966; Hungate, 1966). The
level of fill at which distention limits intake apparently fluctuates
with such factors as nitrogen status of the animal (Egan, 1970) and
the animal's physiological state (Campling, 1970). Any theory derived
to predict forage quality must center around distention or fill as the
limiting mechanism when forage dry matter (DM) digestibility is less
than approximately 65 to 70 percent. Pelleting of forage may lower
this digestibility figure (Montgomery and Baumgardt, 1965a). Campling
(1965, 1970) concluded that voluntary intake was limited by capacity
of the rumen (including reticulum) and by extent of delay of food in
this organ. Extent of delay of digesta is equivalent to retention
time of digesta in the rumen, so that this latter parameter can be
used with equal success in theoretical considerations.
Thornton and Mlnson (1972) presented an equation for predicting
voluntary DM intake from retention time. Converting this equation
to the organic matter (CM) basis gives
OMI = 24(Q/RTOM), (D
where OMI = voluntary OM intake, g/day;
Q = quantity of OM in the rumen, g; \
and RTOM = retention time of OM in the rumen, hr.
Since (Q/RTOM) is the rate at which OM leaves the rumen, in g/hr,
equation (1) is consistent with the theory developed by Hungate (1966)
69
that rates at. which material flows into and out of the rumen must be
equal when the distention mechanism is limiting intake.
If both sides of equation (1) are divided by animal metabolic
weight (W ' ), the form of the equation is unchanged, but OMI has
Kg
units of g/W ' /day while Q is in g/W " . Since Q is constant
Kg Kg
among forages (Blaxter eX al. , 1961; Ulyatt e_t al . , 1967; Thornton and
Minson, 1972), OMI (g/W * /day) can be considered a function of RTOM
kg
(hr), such that:
OMI = f(RTOM). (2)
Multiplying both sides of equation (2) by apparent digestibility of
OM (OMD) gives the following equation:
DOMI = f (RTOM -OMD), (3)
where DOMI represents digestible OM intake, or forage quality, in
g/Wj^' /day.
The right-hand members of equation (3), i. e. , RTOM and OMD,
are highly correlated among forages (Thornton and Minson, 1973),
Therefore, (RTOM- OMD) should correlate highly with RTOM, and should
be obtained accurately by knowing RTOM and the relationship between
RTOM and OMD. Based upon this theoretical consideration, the follow-
ing equation can be written;
DOMI = f (RTOM) . (4)
This equation is theoretically rational and reflects a high degree
of functional integrity since RTOM should be indicative of both
chemical and structural composition of forage OM. Thus, a procedure
for estimating RTOM, or a value highly correlated with it, from
laboratory analyses was developed and tested for predicting forage
quality.
70
Estimation of RTOM
An equation developed by Waldo et a^. (1972) for plotting
disappearance of cellulose from the rumen through time was used for
estimating RTOM, in hr. This equation is
-(k. + k„)t , , -k t ,
g = ae 1 2 + be 2 , (5)
where g = decimal fraction representing remaining labeled
cellulose in the rumen as a function of time per
unit of labeled cellulose intake;
a = decimal fraction of total ruminal cellulose which
is potentially digestible;
b = one minus 'a', or decimal fraction of total ruminal
cellulose which is potentially indigestible;
k^ = grams of cellulose digested per hour per gram of
digestible cellulose present in the rumen;
k„ = grams of indigestible cellulose passing from the
rumen per hour per gram of indigestible cellulose
present in this organ;
and t = time, in hr.
This equation was applied ^o the total OM present in the rumen. Assuming
that 'a', b, k, and k^ are known, if some rational value for g can be
developed for the time when t is equal to RTOM, then t, and therefore
RTOM, can be found by sequential approximation using Newton's method
for approximating roots of equations (Thomas, 1972). This iterative
procedure must be used in estimating t since equation (5) cannot be
solved in a general way for t.
The equation used to approximate t, or RTOM, in equation (5) by
Newton's sequential method was
-(k, + k„)t , , -k„t (r^
ae 1 2 n + be 2 n - g , (b)
^'^^ " n ^ , ^ -(k. + k^)t , , -k„t
-(k + k )ae 1 2 n - k be 2 n
71
where t = zero initially, and t , , for all subsequent
n . . n+1 ^
approximations;
t ,, = value of each approximation in hr, and RTOM in
n+1 , ^ , ^ . ^ ,
hr after the final approximation;
and 'a', b, k and k„ are as defined for equation (5). Starting with
t equal to zero, four approximations should be sufficient to estimate
the final value of t ,,, or RTOM, to within .1 hr of its actual value.
n+1
Establishing the value of g
Hungate (1966) assumed that rumen digesta was homogenous, and
that rumen evacuation proceeded according to a first-order exponential
decay function. Calculations made in the present study from data
presented by Thornton and Minson (1972, 1973), who worked under the
same assumptions, showed a high correlation (-.94 and -.92 in 1972
and 1973, respectively) between DOMI and RTOM. Per unit of digesta
undergoing partial and continuous removal from the rumen via a first-
order exponential decay function, the fraction still in the rumen
— xt
at time t is equal to e .In this expression, the rate constant
'x' equals the constant rate at which a unit of digesta is removed
from the rumen.
Equation (5) assumes that there are two types of digesta under-
going removal from the rumen, i. e., one which is potentially totally
digestible, and which leaves the rumen by digestion and passage; and
one which evacuates the rumen only by passage, since it is totally
indigestible (Waldo et_ al^. , 1972). Therefore, equation (5) does not
fit exactly the general form of the first-order exponential decay
function. However, the semilog plot of equation (5), which would be
linear if digesta disappeared from the rumen via a true first-order
function, appears only slightly curvilinear (Waldo et al^. , 1972).
72
This fact, plus the success of Thornton and Minson (1972, 1973)
in correlating DOMI with RTOM under the first-order assumption,
suggests that taking this assumption as true might not lead to errors
of appreciable importance in determining an acceptable value of RTOM
from equation (5) .
If the suggestion that rumen evacuation adheres to a first-
order process is acceptable, then .37 can be inserted into equation
(6) for g (Hungate, 1966). Mathematically, this is because, with
reference to a "container" which empties itself via first-order
dynamics, RTOM is equal to 1/x (Waldo et ad . , 1965; Hungate, 1966).
If t, at the time it equals RTOM, is set equal to 1/x in the expression
-xt -1
e , then the value of this expression is e , or .37, Thus, if
assuming that rumen evacuation adheres to first-order dynamics does
not produce major errors, inserting a constant value for g of .37
into equation (6) means that t will equal RTOM when the equation is
solved by sequential approximation with 'a', b, k and k„ known.
Estimation of k.
Values of k, (g/hr/g) for forages in this study were determined
according to the procedure described by Gill e_t a^. (1969) and
Lechtenberg e^ al . (1974). The mathematical basis for estimating k
by this procedure can be appreciated by studying the initial pages of
Chapter 10 in Fruton and Simmonds (1958). In vitro OM digestion
(IVOMD) was measured after 3, 6, 15, 30, 48, 60 and 72 hr of fermenta-
tion, and was calculated for each forage at each time as the mean of
three separate determinations. The percent of OM digested after 72 hr
of ^ vitro fermentation was assumed to represent complete digestion
of a given forage (Akin et al. , 1973, 1974b).
73
Estimation of k
Since no procedure could be found for estimation of k^ from
laboratory analyses, this parameter was calculated from known lignin
intakes of the 31 forages by the following equation presented by
Waldo et al. (1972) :
amount of lignin fed/hr
2 ~ average amount of rumen lignin (7)
The numerator of this equation was calculated by dividing known
lignin intake (g/W "'^/day) by 24. The denominator was estimated
kg
using a simple linear regression equation generated from data re-
ported by Ingalls £t al . (1966):
Rumen lignin (g/W, " ) =
.35 + 1.54 lignin intake (g/\g ' /day). (8)
As described by equation (7), dividing lignin intake (s/\g ' /hr)
by rumen lignin (g/W ^''^) yielded an estimate of k^ (g/hr/g) . In
generating the regression equation from data provided by Ingalls et al.
(1966), values for rumen lignin at 6 hr postprandial were used, this
being the theoretically closest approximation to rumen lignin under
steady-state conditions available from these data.
Theory relative to 'a', and its estimation
Waldo et al. (1972) reported that for cellulose, 'a' was equal
to A , where A was amount of potentially digestible cellulose
A + B ,. -ui
present initially in the rumen, and B was amount of indigestible
cellulose initially present in this organ. This concept was extend-
ed to cover total ruminal OM instead of just cellulose when estimating
74
'a' for grasses utilized in the present investigation. Amount of
ruminal OM depends upon intake (Thomas et al . , 1961; Egan, 1970),
and would be difficult to predict when intake was not known. This,
of course, would be the case in most instances where forage quality
predictions were required. Thus, it was necessary to develop an
equation for estimation of 'a' in which intake was not included.
The rationale behind development of such an equation was based
upon the manner in which amounts of OM designated A and B would occur
in the rumen under steady-state conditions. Given such conditions,
and knowledge that digestible material evacuates the rumen via first-
order kinetics (Waldo etal., 1972), A (g/W^^g"^^) «°^ld equal DOMI
(g/W -^^/day) multiplied by the average number of days which DOMI
kg
would be delayed in the rumen, or retention time of this intake.
,, ^^ ]: » since digestible OM
This retention time would equal 24 (k + k )
leaves the rumen via both digestion and passage. The value of B
(g/W -^^ would equal amount of indigestible OM intake (g/W^^' /day)
multiplied by days of retention time of this indigestible material.
In this case, retention time would be -^ ' since indigestible OM
evacuates the rumen via only passage, which is also a first-order
process. Thus, if forage quality were to be predicted, 'a' would
A ,
be equal to ^ _|_ g or:
^ , , (OMD ) (OMI)
24(k^ + ^) P^ ^ (,)
i (OMD ) (OMI) + T^ (100-OMD ) (OMI)
24 (k, + kj p' 24k P
where OMI is in g/W^ "^^/day. By algebraic manipulation (Appendix
K.g
75
table 13), equation (9) can be reduced to the following equation:
(k„) (OMD ) ,--,
1^. = 2 2 , (10)
^ [(kj (OMD )] + [(k + k„) (100-OMD )]
2 p 12 p
where 'a' = decimal fraction of total ruminal OM which is
potentially digestible;
k^ = rate of digestion rate constant, g/hr/g;
k„ = rate of passage rate constant, g/hr/g;
and OMD = predicted in vivo OMD, in percent.
Since k„ was calculated from previously known J_n vivo data in this
investigation, estimation of 'a' provided no subsequent problems.
Values of b were calculated as one minus 'a'.
Prediction of organic matter digestibility
In equation (10), predicted OMD (OMD ), in percent, was determined
using the following formula:
OMD = NDS -10.3 + (NDF-NDFD), ^^^^
p OM
where NDS = ash-free neutral-detergent solubles (OM
minus NDF) , as percent of DM;
NDF = ash-free neutral-detergent fiber, as per-
cent of DM;
NDFD = decimal fraction representing NDF
digestibility;
OM = organic matter, as decimal fraction o^ DM;
and 10.3 = average value of metabolic fecal OM, as
percent of DM (Chapter III) .
Predictions of digestible OM (DOM), as a percentage of DM, were made
using the numerator of equation (11) .
76
Values for NDFD in equation (11) were estimated as suggested
by Velasquez (1974), and simple linear regression equations for
this purpose were generated from data reported by this author.
These equations were,
for Pensacola bahiagrass, NDFD = 12.69 + .8Sz; (12)
100
for Coastal or Suwannee bermudagrass , NDFD = 15.27 + . 71z; (13)
100
and for Pangola digitgrass, NDFD = -2.69 + l.Oz; (14)
100
where z = in vitro NDF digestion (IVtTDFD) after 72 hr of fermentation,
in percent. In the present investigation, values of z inserted into
equations (12) , (13) and (14) were means of three individual observa-
tions done in separate runs.
Testing the Procedure
Forages and in vivo data
Thirty-one warm-season grasses of known in vivo OliD and OMI by
sheep were utilized for testing the theoretically rational procedure
for prediction of DOMI , or forage quality, from RTOM. These 31 for-
ages included five cuts of Pensacola bahiagrass (Paspalura notatum
Flugge) , 15 cuts of Coastal or Suwannee bermudagrass (Cynodon dactylon
(L) Pers.) and 11 cuts of Pangola digitgrass (Digitaria decumbens
Stent). These forages had been studied previously in seven different
in vivo trials comprising 187 individual animal observations of both
intake and digestibility. In these trials, all grasses were fed
77
ad libitum as chopped, artificially dried hays to yearling or mature
wethers in individual metabolism crates with slatted wooden floors.
Water, salt and def luorinated phosphate were provided ad^ libitum. Each
experimental period consisted of a 14-day preliminary period to allow
sheep to attain voluntary intake, followed by a seven-day total-
collection period for determination of voluntary intake and apparent
nutrient digestibility. Voluntary OMI was calculated on the basis of
grams per kilogram of body weight raised to the .75 power per day
(g/W ■ ), and nutrient digestibility was calculated in percent,
kg
Forage quality, or DOMI in g/W " /day, was determined for each of
kg
the 31 forages by multiplying OMI in g/w * /day by apparent OMD.
kg
Laboratory analysis of forages
Analyses previously determined on all 31 forages were DM, CM
and crude protein (CP) , the latter two being as percentage of DM
(A.O.A.C, 1970); acid-detergent fiber (ADF) and acid-insoluble lignin,
both on the DM basis (Van Soest, 1963); and NDF as a percentage of DM
(Van Soest and Wine, 1967). For this latter determination, dry residue
was ashed and the difference between dry and ashed weights was calculat-
ed as weight of ash-free NDF.
In the present study, ash-free NDS as a percentage of DM was
calculated by subtracting ash-free NDF from OM. Determination of
IVOMD after various periods of fermentation was done according to the
two-stage procedure outlined by Moore and Mott (1974).
Velasquez (1974) determined IVNDFD by employing the procedure of
Moore and Mott (1974) during 72 hr of fermentation. One ml of toluene
per tube followed by refrigeration was used to stop fermentation and
hold residual NTDF for subsequent determination (Goering and Van Soest,
78
1970). Residual ash-free NDF was determined by the method of Van Soest
et^ al . (1966). This procedure was modified slightly for determining
IVNDFD in the present investigation. The modification consisted of
using an ice-water bath for 1 hr instead of 1 ml of toluene to stop
fermentation after 72 hr of incubation. Tubes and their contents
were refrigerated for 40 hr before ash-free residual NDF was determined
(Chapter IV).
Regression analyses
Correlations among laboratory analyses and/or In vivo parameters
were determined using the UFSPL020 linear regression and correlation
program on the University of Florida's IBM 370 digital computer.
Generation of the prediction equation
With both forage quality, in terms of DOMI, and estimated RTOM
known for each of the 31 grasses, 15 grasses were selected as re-
presentative of the entire group in order to generate a simple linear
regression equation for prediction of forage quality from estimated
RTOM, i. e. , (DOMI) = b + b (RTOM). The 15 forages selected covered
the entire maturity range of the 31 grasses (2 to 14 wk) and met the
restriction of containing at least 6 percent CP on a DM basis. This
restriction was imposed so that the relationship between DOMI and
RTOM exhibited by the prediction equation would not be confounded with
other possible effects of low CP upon measurements of forage quality.
For generation of the prediction equation, DOMI values for the 15
selected forages were regressed upon these forages' estimated RTOM
values using a simple linear regression program. Values of DOMI for
the remaining 16 forages were predicted using this equation.
79
Prediction of DOMI for a given forage can be obtained with the
Dynamo computer program shown in Appendix table 14 when values of
constants (C statements) are known.
Testing the acceptability of quality predictions
In testing the utility of the resultant prediction equation, the
question now arises: How much can predicted DOMI deviate from actual
DOMI and still be considered an acceptable prediction? The answer
to this question cannot be supplied by r values or residual standard
deviation (s ^) values unless some criterion of acceptability relative
to the absolute value of prediction error is attached to them. Perhaps
the answer varies depending upon the context in which one is working.
Researchers must work within a policy of error acceptance which is
based upon sound statistical considerations. One such policy would
accept predictions from a given equation if the equation could predict
means within their 95 percent confidence interval 95 percent of the
time. Under this policy, the width of the confidence interval en-
compassing a given mean would be ±t(s//n) , where t is the tabulated
approximation to the normal when the population variance is unknown;
s is the estimate of the population standard deviation; and n is the
number of observations upon which the mean is based. If the value of
t at the 95 percent level of confidence is used in calculating the
value of the above expression, then a prediction which falls within
the resultant range must be acceptable. This is because if the
experiment were repeated it could be stated with 95 percent confidence
that the mean would fall within the calculated range. Thus, if a
prediction falls within this range, it must be acceptable since it
is of the same worth as repeating the experiment. This policy, it
seems, would be the ultimate in judging prediction acceptability.
80
This method of judging prediction acceptability may be too con-
servative for present use. There exists a paucity of literature
relative to (1) manners in which all factors which affect forage
quality mediate their effects; and (2) quantification of effects of
these factors and their interactions upon forage quality over a wide
range of forages. Thus, it is practically impossible to generate
a prediction equation which will yield acceptable predictions of
forage quality in any given situation for any given forage. This
means that either we will do without acceptable prediction equations,
or that we must relax the standards by which we judge such equations.
The standards still must be based, however, upon sound statistical
considerations. Such a set of standards probably v.'ould be produced
by considering mean predictions acceptable if they fall within plus
and minus two population standard deviation estimates (±2s) from
the actual mean. The rationale for postulating this acceptability
range is that the range is still limited by the population standard
deviation, and that according to the statistical Empirical Rule
(Mendenhall, 1971), approximately 95 percent of the individual obser-
vations taken from a normal population will fall into this range. A
prediction in this range may differ at the 95 percent confidence
level from the actual mean, but it should approximate closely at least
some of the individual observations which constitute the mean. There-
fore, acceptability limits at ±2s from the mean would allow use of
a "good" prediction equation, though the equation was not "perfect"
according to limits at±t(s//n) from the mean. The acceptability
range afforded by ±2s would be wider than that provided by ±t(s//ri)
81
but the multiple would not be necessarily great since the number
of observations per treatment in animal experiments is usually small.
Also, if the experiments were conducted well, s may be small and
the difference between the two limits may be minor in absolute term-S.
In comparing two or more prediction equations which appear "good"
when judged by the wider acceptability limits, the number of pre-
dictions from each which fall into the range defined by ±t(s/>/n)
from the mean when t is taken at the 95 percent confidence level
might be taken into account in choosing the equation for predicting
means .
In this study, DOMI predictions were judged with reference to
statistically defined acceptability lim.its around the actual m.ean
DOMI values being predicted. All predictions which fell within the
range defined by acceptability limits were judged acceptable. Since
quality values being predicted were in terms of mean DOMI, a con-
servative set of acceptability limits was defi.ied by a weighted
average of the expression ±t(s/v^) for all 31 forages. This weighted
average was calculated by determining the weighted average of s for
the 31 forages. The weighted average for s was calculated as the
2
square root of the value of the expression Z(n. - l)s. . in this
Z(n. - 1)
1
expression, i defines each individual among the 31 forages. The
value of n in the expression for the weighted 95 percent confidence
interval was taken as the arithmetic mean of the n. for all 31 for-
ages. This average value of n also was used to determine the tabulated
t at the 95 percent confidence level. A liberal set of acceptability
limits also was determined, these being defined by the expression ±2s.
82
Results and Discussion
Laboratory Characteristics of Forages Utilized
Ranges, means and coefficients of variation (CV) for laboratory
characteristics of the 31 wami-season grasses used in this investi-
gation are reported in table 7. Individual values are shown in
Appendix table 10. As percentages of DM, mean CP for all forages was
9.3, while mean ash-free NDF and NDS were 74.9 and 21.1, respectively.
The CV for NDS was about three times that for NDF because the esti-
mated standard deviations (s) for NDS and NDF were similar (4.6 and
5.5 percentage units, respectively). Mean IVOMD increased from
14.6 to 50.9 percent as fermentation time increased from 3 to 72 hr.
As fermentation time became longer, the CV for IVOMD decreased because
the mean increased faster than did s. Thus, it appears that IVOMD
is less variable in a relative sense, though more variable in absolute
terms, after longer periods of fermentation. This may explain results
reported by Velasquez (1974) , who found that IVOMD after 72 hr of
fermentation correlated slightly higher with in vivo OMD than did
IVOMD after 48 hr. This slightly higher correlation probably would
not offset problems encountered in substituting fermentation times of
72 hr for those of 48 hr now used as standard procedure in routine,
large-scale programs of forage analysis.
Values of 'a' averaged .2518 for all forages (table 7), and the
mean for b was .7482. These results indicate that among forages, only
about 25 percent of total ruminal OM would be potentially digestible
at a given point in time.
Estimated kj^ averaged .0557 g/hr/g (table 7), or about 2,5 tim.es
average calculated k2, which was .0227 g/hr/g. The CV for k2 for
83
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84
31 forages was only 5.3 percent, and the range for these values was
only .0047 units. Since at present no laboratory procedure exists
for estimation of k2 , these results suggest that assuming k2 to be
constant among forages at .0227 g/hr/g might not lead to errors of
appreciable importance in estimation of RTOM. Estimated RTOM ranged
from 28.35 to 36.37 hr in this study, with a mean of 33.45 hr and
a CV of only 7 percent for all forages.
Actual and Predicted In Vivo Values of Forages Utilized
Ranges, means and CV's for actual and predicted mean values of
in vivo parameters are presented in table 8. Means for individual
grasses are reported in Appendix table 11. Calculated IIFOM (ash-
free NDS minus ash-free DNDS) averaged 9.9 percent of DM. This is
analogous to the 9.5 percent of DM reported by Minson (1971b), who
worked with three cultivars of each of two Paul cum species, but higher
than the 5.4 percent found by Velasquez (1974) for warm-season grasses.
For temperate forages, metabolic fecal DM has been reported at 12.9
percent (Van Soest, 1967) and 9.8 percent (Colburn e_t al. , 1968;
Deinum and Van Soest, 1969).
Actual in vivo NDFD ranged from 42.0 to 76.1 percent, with a
mean of 55.3 and a CV of 17.5 percent (table 8). Predictions of
this parameter ranged from 39.4 to 71.8 percent, with a mean of 53.3
and a CV of 18.2 percent. The separate regression equations used to
predict NDFD are shown in figure 4. Simple linear regression of
in vivo NDFD on predicted NDFD for all 31 grasses produced an r
2
value of .98 (r'~=.96) and an s of 1.90 percentage units. Thus,
y . X
85
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86
80
75
70
65
60
55
50
45
40
Y = 12.69 + .88X
r = .90; P<.01
3.08
V
/
= 15.27 + .71X
98; P<.01
= 1.33
O Bahia
9 Bermuda
$ Pangola
99; P<.01
= 1.71
35
40
45
50
55
60
65
70 75 80
IN VITRO NEUTRAL-DETERGENT FIBER DIGESTION (ASH-FREE), %
AT 72 hr
Figure 4. Relationship between neutral-detergent fiber
digestibility in vivo and in vitro for each
of three warm-season grasses.
from Velasquez, 1974).
(Data taken
87
ash-free in vitro NDFD after 72 hr of fermentation appears an excellent
predictor of in vivo NDFD. Determinations of in vitro NDFD, however,
require seven working days, which is too slow for rapid estimation
of forage quality. Actual in vivo DNDF ranged from 33.1 to 50.0
percent of DM, with a mean of 40.9 and a CV of 11.4 percent (table 8).
This mean is in accord with the 40 percent of CM found by Moir (1972)
for both temperate and tropical forages, but seems too variable to
be considered constant or to depend upon physiology of ruminant digestion
rather than forage quality, as suggested by that author.
Actual in vivo DOM and predictions of this parameter were quite
similar in range, mean and CV (table 8). Simple linear regression
2
of in vivo DOM on predicted DOM yielded an r value of .97 (r =.94)
and an s ^^ of 1.7 percentage units. Actual in vivo OMD and predicted
OMD V7ere also quite similar, and regression analysis produced an r
2
value of .95 (r =.90) and an s of 2.6 percentage units. Since
y.x ^ *
DOM prediction is based upon estimation of NDFD, which in turn depends
upon in vitro ITOFD after 72 hr of fermentation, IVOMD after 48 hr
would not have to be determined in order to obtain accurate predictions
of in vivo OMD for warm-season grasses. The future challenge is to
develop an accurate predictor of in vivo NDFD which is determined
more quickly and easily in the laboratory than is in vitro 'TOFD after
72 hr of fermentation.
That RTOM might be utilized to obtain accurate predictions of
forage quality over a wide range of forage species has been suggested
by Thornton and Minson (1972, 1973) and Laredo and Minson (1975). In
their studies, RTOM was determined by means of hourly ad libitum
feeding of sheep and complete removal of digesta from the rumen via
a fistula (Minson, 1966). Measuring RTOM by this method does little
to expedite forage quality determinations, since DOMI itself can be
measured in vivo during the same amount of time, and probably at
lower cost. In the present study, actual DOMI ranged from 19.3 to
50.7 g/W " /day for the 31 grasses, with a mean of 31.2 and a CV
of 30.8 percent (table 8). Fifteen of these grasses were used to
generate an equation for prediction of DOMI from estimated RTOM. The
equation, shown in figure 5, was
Y = 169.8 - 4.14 (RTOM), (15)
where Y represents predicted DOMI (g/W * /day) . Use of this equation
Kg
to predict quality for the remaining 16 grasses resulted in DOKI pre-
dictions which ranged from 20.1 to 47.8 g/W * /day, with a mean of
kg
27.9 and a CV of 28.8 percent. Simple linear regression of actual
in vivo DOMI for these 16 grasses on their respective predicted DOMI
2
values produced an r value of .95(r =.90) and an s of 2.4 units.
y.x
Thus, this rational method for predicting forage quality appeared
promising, but the acceptability of predictions generated by equation
(15) remained to be tested by use of appropriate acceptability limits.
Actual (MI by sheep ranged from 39.6 to 84.7 g/W, /day for
kg
all 31 grasses, with a mean of 56.9 and a CV of 21.6 percent ('-able 8).
Predictions of this parameter generated for 16 grasses (predicted
DOMI V predicted OMD) ranged from 38.7 to 76.7 g/W '^^/day, with a
kg
mean of 56.4 and a CV of 20.7 percent. Simple linear regression of
89
15
O Bahia
• Bermuda
^ Pangola
Y = 169.8 - 4.14X
r = -.95; P<.01
= 3.63
y.x
29
30
31
32
33
34
35 36
37
RETENTION TIME OF ORGANIC MATTER IN THE RUMEN, hr
Figure 5. Relationship between digestible organic matter
intake and retention time of organic matter in
the rumen for three species of warm-season
grasses.
90
actual on predicted in vivo OMI for these grasses produced an r of
2
.95 (r =.91) and an s of 3.2 units. Empirical predictions of
y.x
OMI from ADF as a percentage of DM were made as suggested by Weller
(1973). Figure 6 shows the empirical equation used to predict OMI
from ADF:
Y = 169.0 - 2.82 (ADF), (16)
.75
where Y represents predicted OMI (g/W /day) . This equation was
Kg
generated with 15 of the 31 grasses and used to predict OMI for the
other 16. Measures of central tendency and dispersion are shown in
table 8, Regression of ±r\ vivo OMI on OMI predicted from ADF yield-
2
ed an r value of only .77 (r =.59) and an s of 6.6 units. Thus,
y.x
empirical use of ADF to predict OMI appears less promising than use
of (DOMI -^ OMD) when both of these latter parameters are predicted
rationally.
Testing of DOMI and OMI Predictions
Acceptability limits for quality and intake predictions
Differences between actual and predicted values of DOMI (forage
quality) or OMI were deemed acceptable in a conservative sense if
the absolute values of these differences were less than or equal to
the weighted average of the expression t(s//n) at the .95 confidence
level for all 31 grasses utilized in this investigation. Such differ-
ences were termed acceptable in a liberal sense when their absolute
values were less than or equal to the weighted average of 2s for all
31 grasses. Though in this study acceptability limits were calculated
for each grass species, only limits applicable to all grasses were
used to test predictions. This would negate the necessity of referring
85 t-
80
91
75
3
00
70 -
65 -
60 •
55 -
50 -
A5
40
-
\
•
\^
O
o
•
Bahia
Bermuda
• \
&
Pangola
\ O
Y
= 169.0 - 2.82X
\
r
= -.88; P<.01
N.
s •
= 6.87
. 1
32 34 36 38 40 42 44 46
ACID-DETERGENT FIBER, % OF DRY MATTER
48
Figure 6. Relationship between organic matter intake
and acid-detergent fiber percentage for three
species of warm-season grasses.
92
to limits for individual grass species when qualifying predictions of
quality in practice. Conservative and liberal acceptability limits
determined by applying their respective expressions across all forages,
as well as to bahiagrass, bermudagrass or Pangola digitgrass alone,
are shown in table 9.
Acceptability of quality and intake predictions
Figure 7 shows the test of acceptability for forage quality (DOMI)
predictions. The points plotted in this figure are coordinates of
actual DOMI and predicted DOMI values, and the continuous middle line
represents the set of points where actual DOMI equals predicted DOMI.
Thus, the vertical deviation of any plotted point from the continuous
middle line represents error in predicting that value of DOMI. The
inner set of broken lines represent conservative acceptability limits,
and the outer set of broken, dotted lines mark the liberal acceptability
limits. In this study, all DOMI predictions were acceptable when judg-
ed by liberal limits, and 14 of the 16 predictions were acceptable
when judged by conservative limits. Thus, the theoretically rational
prediction of DOMI from RTOM may provide an acceptable method for
prediction of quality for warm-season grasses. Unacceptability in a
conservative sense of quality predictions for two Pangola digitgrass
hays may have been caused by effects of factors not related to RTOM
upon quality measurements for these two hays. These hays exhibited
RTOM values of 29.46 and 30.95 hr, and in vivo OMD ' s of 65.9 and 65.3
percent, respectively. Therefore, it is possible that some chemostatic
regulator- influenced OMI, at least in part, for these two hays as
suggested by Montgomery and Baumgardt (1965a) and Conrad (1966).
93
TABLE 9. CONSERVATIVE AND LIBERAL ACCEPTABILITY LIMITS FOR TESTING
PREDICTIONS OF DIGESTIBLE ORGANIC MATTER INTAKE (DOMI) AND ORGANIC
MATTER INTAKE (OMI)
FORAGE SPECIES
Item
Bahia
Bermuda Paneola
All
DOMI, g/W '^^/day
Kg
Conservative [±t(s//n)] ±2.4
Liberal (±2s) ±5.1
OMI, g/Wj^ '^^/day
Conservative ±4.9
Liberal ±10.3
±3.7 ±5.6
±7.8 ±8.2
±7.0
±14.7
±9.0
±13.2
±3.9
±7.5
±7.1
±13.6
94
PREDICTED DIGESTIBLE ORGANIC MATTER INTAKE (Y), g/W ' /day
kg
Figure 7. Test of retention time of organic matter in the rumen
as a rational predictor of digestible organic matter
intake.
95
Perhaps quality predictions for forages which exhibit such low RTOM
and high OMD values could be improved by including some rational
chemostatic regulating factor along with RTOM in an equation for
predicting quality.
Of the 16 grasses for which quality predictions were made, 10
contained less than 7 percent CP on a DM basis. Egan (1965) and
Weston (1967) indicated that OMI of such forages may be influenced
more by nitrogen status of the animal than by RTOM. If this were
true, it would be expected that quality predictions for such forages
would be too high when determined from RTOM. Such was not the case
in the present study, since quality predictions for all 10 grasses
of low CP percentage were acceptable when judged by conservative
acceptability limits. These results, however, may not invalidate
totally the assumptions of Egan (1965) and Weston (1967), but may be
indicative of the different lengths of in vivo experimental periods
used by these authors compared to those employed with hays used in
the present investigation. Clark and Quin (1951) stated that it
frequently had been found that sheep kept exclusively on a diet of
poor-quality grass hay showed a gradual decline in intake from
about the third week on such a treatment. Data presented by these
workers showed that intake declined after the third, fourth or fifth
week when low-quality forages were fed. Hays employed in the present
study were fed to sheep for three weeks, while Egan (1965) used
7.5 to 11 weeks, and Weston (1967) used 7 to 13 weeks. Thus, hays
studied in the present investigation may have been fed to sheep for
96
periods of time too short to allow animals to achieve a nitrogen status
low enough to override RTOM as the primary determinant of DOMI. In
this case, RTOM still would determine quality of forages low in CP
percentages, as indicated by results reported here.
Figures 3 and 9 show tests of acceptability for OMI predictions
made by rational and empirical methods, respectively. Figure 8
shows that rational prediction of OMI for 16 grasses from predicted
DOMI divided by predicted OMD produced predictions which were all
acceptable when judged by liberal acceptability limits, and 15 which
were acceptable by conservative limits. The one bermudagrass for
which predicted OMI was conservatively unacceptable exhibited a CP
percentage of 5.6 on a DM basis. However, OMI predictions for the
nine other grasses with less than 7 percent CP on a DM basis all fell
within conservative acceptability limits. These results strengthen
the conclusion that in this investigation, nitrogen status of the
animal generally was less important than RTOM in determining in vivo
OMI of grasses with low CP percentages. Figure 9 presents results
of empirical prediction of OMI from ADF as a percentage of DM, as
suggested by Weller (1973). All predictions for the same 16 grasses
used above were acceptable by liberal standards, but five predictions
were unacceptable when judged by conservative limits. Thus, the
rational method for predicting OMI was more promising among grass
species than the empirical prediction method. Also, the high negative
r value (-.88) found in this study for the relationship between OMI
and ADF for 15 forages would not be expected in all cases. Johnson
and Dehority (1968) reported an r value of only -.46 for the relation-
ship between relative intake of 22 temperate grasses and ADF percentage
97
90 K
35 40
80
75
PREDICTED ORGANIC MATTER INTAKE (Y), g/W, " /day
kg
Figure 8. Test of theoretically rational method for prediction
of organic matter intake.
98
PREDICTED ORGANIC MATTER INTAKE (Y) , g/W "'"/day
Figure 9. Test of empirical prediction of organic matter
intake from acid-detergent fiber percentage
of dry matter.
99
of these grasses, and -.31 when legumes and mixed forages were in-
cluded in the analysis. Van Soest (1965a) found r values ranging from
-.88 to .20 between voluntary intake and ADF within seven species of
temperate forages. The value of this statistic was -.53 for all 83
individual forages. This author also reported that the relationship
between voluntary intake and ADF declined as that between voluntary
intake and digestibility decreased. Since this latter relationship
is not always strong, especially over a wide range of forage species,
it is doubtful that the r value between OMI and ADF always would be
as high as found in the present study. Therefore, prediction of OMI
should be undertaken on a rational rather than on an empirical basis.
Utility of Relationships Between Various Measurements and Analyses
Prediction of organic matter digestibility
In this study, OMD was predicted with equation (LI), in which
NDFD was predicted from IVNDFD after 72 hr of fermentation. Since
DOM as a percentage of DM, or the numerator of equation (Ll) , must
be estimated in order to predict DE/g DM (Chapter III) , prediction of
OMD can be achieved simply by dividing DOM by OM as a percentage of
DM. Thus, determination of IVOMD after 48 hr of fermentation is
avoided in predicting 0^ro. This determination apparently can be
avoided in other situations where IVNDFD is measured at 72 hr. For
all 31 grasses, the r value for the relationship between in vivo OMD
and IVNDFD at 72 hr was .96, and s was 2.2 percentage units. The
y.x
relationship between jiTi vivo OMD and IVOMD at 48 hr was characterized
by r and s values of .96 and 2.4 percentage units, respectively.
Weller (1973) reported that in vivo OMD and IVNDFD at 72 hr were highly
100
and positively correlated for 12 warm-season grasses (r = .96;
s =2.0 percentage units). Thus, OMD probably could be predicted
directly, with a high degree of accuracy, from IVNDFD after 72 hr of
fermentation. Measurement of this in vitro parameter, however, re-
quires more time than does determination of IVOMD at 48 hr. There-
fore, changing existing systems of analysis from IVOMD at 48 hr
to IVNDFD at 72 hr of fermentation probably would be unwarranted.
Prediction of intake from neutral-detergent fiber percentage
Van Soest (1965a) suggested that NDF limited intake when this
constituent comprised more than 55 to 60 percent of DM. In the present
investigation, NDF percentage ranged from 63.6 to 81.3 percent on the
DM basis. However, for all 31 grasses, the relationship between OMI
and NDF was characterized by r = -.12 and s =12.4. For bahiagrass
y.x
and bermudagrass individually, these values were only slightly higher ,
i. e. , -.23 and 9.2, or -.47 and 9.5, respectively. With Pangola
digitgrass, r = .91 and s = 5.3. Such a strong relationship, however,
may be more associative than cause and effect in nature. Johnson and
Dehority (1968) reported an r value of only -.21 for the relation-
ship between relative intake and NDF percentage of temperate grasses,
and -.56 for grasses, legumes and mixed forages combined. Van Soest
(1965a) found this value to be -.65 for 83 temperate forages, while
it ranged from -.95 to +.57 within species. Thus, results of these
studies and those of the present investigation strongly indicate that
NDF as a percentage of DM would not be an accurate predictor of OMI
over a wide range of forage species.
101
Prediction of k
In this study, values of k for all 31 grasses were calculated
from their actual in vivo lignin intakes. Estimates of k resulting
from this procedure averaged .0227 g/hr/g, which agrees with the .02
g/hr/g assumed by Waldo ^ al. (1972). This fact and the high degree
of acceptability of forage quality predictions in the present investiga-
tion suggest that the procedure used here for estimation of k is
acceptable. However, for prediction of forage quality in a practical
situation, this procedure is inadequate because intake usually would
not be known. Simple linear regression analysis involving several
in vivo measurements and laboratory determinations revealed that the
relationships between k„ and lignin percentage of either DM or NDF
exhibited r and s values of .82 and .001, or .83 and .001 units,
y.x
respectively. Since only a maximum of 68 percent of the variation in
k„ was explained by these parameters, alternate methods for prediction
of k were sought.
Calculated values for k„ were of low magnitude and were relatively
invariant in this study (table 7). Thus, it was possible that assum-
ing k to be constant among grasses at its mean value, i. e. , .0227
g/hr/g, might not lead to errors in prediction of DOMI. Testing this
assumption with the 16 grasses used throughout this study for predic-
tive purposes, however, resulted in only six quality predictions which
were acceptable when judged by liberal acceptability limits (table 9),
and one which was acceptable by conservative standards. For two for-
ages whose DOMI predictions were in error by only 0.1 g/W ' /day
kg
when predictions were generated using calculated k„ values, prediction
102
errors rose to 6.4 and 7.5 g/W * /day when the mean value of k„ was
Kg 2.
used. The mean underestimated the calculated values by only .0010
and .0011 glhxlg, respectively. For two other forages, DOMI predictions
generated with calculated k values were in error by .8 and 2.8 units,
but prediction errors were 8.5 and 8.3 units, respectively, using
the mean value of k . Calculated k values were underestimated by
X)011 and IX)09 g/hr/g, respectively , by the mean. Therefore, assuming
k to be constant over a wide range of forages does not provide con-
sistently acceptable predictions of forage quality. Since estimates
of k obviously must be quite accurate, it is not surprising that
using the value of .02 g/hr/g (Waldo ^ al • . 1972) produced DOMI
predictions which were too low. Predictions generated under the
assumption that k was constant at .025 g/hr/g were too high.
A second method for prediction of k„ was suggested when simple
linear regression analysis revealed that the relationship between
'a' and (NDS + DNDF) , as a percentage of DM, exhibited an r value of
2
. 88 (r = .78) and s of .034. This relationship, it seems, should
be more than simply associative. The utility of this relationship
would be that, with the value of 'a' known, equation (10) could be
solved for k„ when predicted OMD (OMD ) was expressed as a decimal
2 P
fraction rather than in percent. The resultant formula for determin-
ing k would be as follows:
a(k ) (1-OMD )
k„ = }—■ 2_ . (17)
2 OMD -a ^
P
To test this method for prediction of k , values of 'a' were
first regressed on (NDS + DNDF) , as a percentage of DM, using the same
15 grasses used throughout this study for generation of prediction
equations. The resultant equation was the following:
103
'a'= -.1878 + .0071 (NDS + DNDF) . (18)
2
Values of r and s for equation (18) were .88 (r = .77) and .033,
y.x
respectively. Actual values of 'a' for the 16 remaining grasses,
when regressed upon their respective predicted values from equation
(18), produced a relationship which was characterized by an r value
2
of .87 (r = .77) and s of .036. Predicted values of 'a' were
y.x
inserted into equation (17) , and this equation was solved to predict
values for k . Regressing calculated values of k for the 16 grasses
on their respective k predictions produced an r value of only .58
2
(r = .33) and s of .001 g/hr/g. Therefore, at present, this
y.x
method for prediction of k„ does not appear promising. However, if
some rational method could be developed which would allow more accurate
prediction of 'a', then equation (17) might be useful for accurate
prediction of k .
Prediction of k.
Simple linear regression analysis revealed no laboratory chemical
determination or in vivo measurement which could be used for more
rapid determination of k than is allowed by the in vitro procedures
followed in this study. For all 31 grasses, the relationship between
k and lignin as a percentage of DM exhibited an r value of only
2
.16 (r = .02). This finding agrees with results published by
Lechtenberg et_ al. (1974), who reported that although rate of digestion
of cell walls depended upon lignin as a percentage of DM, k was not
affected by the magnitude of lignin concentration in DM.
104
General Discussion
In this study, quality of warm-season grasses was predictable
with a high degree of accuracy from RTOM when this time period was
longer than about 31 hr. Therefore, RTOM apparently reflects
both chemical composition and structural organization of OM. When
RTOM was below 31 hr, as it was for two Pangola digitgrasses, DOMI
predictions were acceptable when judged by liberal acceptability
limits, but were unacceptable by conservative standards. Therefore,
forage quality may not be always predictable from RTOM alone, since
the distention mechanism and RTOM may be partially or totally over-
ridden by factors related to other DOMI control mechanisms. This
would occur when such factors reach levels at which they become
important as determinants of forage DOMI. In this study, such
factors may have been related to some attribute of the two Pangola
digitgrasses, and may have been chemostatic in nature.
Non-Forage Factors Which Could Override or Modify RTOM
It also is possible that in a given situation where RTOM is
the main determinant of 'forage quality, the j^ vivo value of RTOM
may be modified by non-forage factors (factors which are not related
directly to forage chemical composition or physical structure,
per se) which were not included in the RTOM prediction process. Non-
forage factors also might override RTOM as the main determinant of
forage quality. If RTOM is overridden, or is modified with respect
to its magnitude, the factors responsible need to be identified and
their effects require accurate quantification. If these effects are
not related to forage quality, then the manner (s) in which they are
105
mediated must be elucidated. If such discoveries could be made, forage
DOMI probably could be predicted accurately by dynamic computer model-
ing in situations where RTOM was overridden as the main determinant
of DOMI, or was modified with respect to magnitude in some way that
could not be taken into account in a laboratory procedure for RTOM
prediction.
The number of factors which could override RTOM, or which could
influence its magnitude, is undoubtedly great. Several factors which,
in one of these ways, may affect DOMI of a^ libitum fed animals are
(1) nitrogen status of the animal (Egan, 1965, 1970; Weston,
1967);
(2) environmental conditions, i. e. , ambient temperature, humidity
and solar radiation (Ragsdale e_t a]^. , 1953; Brobeck, 1960;
Wayman et al. , 1962; Warren at al. , 1974; Bhattacharya
and Uwayjan, 1975; Koes and Pfander, 1975);
(3) the physical form in which forages are fed, i. e. , long,
chopped, ground or ground and pelleted (Rodrigue and Allen,
1956; Blaxter and Graham, 1956; Johnson et^ al. , 1964; Minson
and Milford, 1968; Greenhalgh and Reid, 1973);
(4) previous plane of nutrition (Tayler et^ al . , 1957; Tayler,
1959; Heaney, 1970; 0 ' Donovan et al. , 1972; Asplund et al. ,
1975);
(5) the method by which hay is processed, i. e. , artificially
dried, barn-dried, rack-dried or swath-dried in the field
(Shepperson, 1960; Milford and Minson, 1968; Demarquilly
and Jarrige, 1970) ;
(6) physiological state of the animal, i. e. , fatness, stage
of pregnancy and stage of lactation (Reid and Hinks , 1962;
Graham and Williams, 1962; Hutton, 1963; Arnold and Dudzinski,
1966; Ulyatt, 1973; Capote, 1975);
(7) animal type, i. e. , cattle or sheep (Buchman and Hemken,
1964; Blaxter et al. , 1966; Jones et^ al. , 1972);
(8) anim.al breed within type (Hungate et al. , 1960; Phillips,
1961; Kappel et al. , 1972);
106
(9) animal levels of macro- and micro- mineral elements (Under-
wood, 1962; Blaxter, 1962; Preston and Pfander, 1964;
Telle et al. , 1964; Miller et al. , 1966; Weston, 1966;
Patil and Jones, 1970; Chicco et^ al, , 1973; Seoane et al. ,
1975);
(10) CP supplementation of forages which exhibit CP levels of
less than 7 percent on a DM basis (Campling et al. ,
1961; Coombe and Tribe, 1963; Egan, 1965, 1970; Elliott,
1967; Minson and Milford, 1967b; Lourens, 1968; Moore et al. ,
1970; Houser, 1970; Ammerman et al. , 1972; Siebert and
Kennedy, 1972; Fick et al. , 1973; Ventura et^ ail, , 1975);
(11) energy supplementation (Blaxter and Wilson, 1963; Bisschoff
et al . , 1967; Clanton and Rittenhouse, 1970; Tayler and
Wilkinson, 1972; Fick et al . , 1973; Golding, 1973); and
(12) animal levels of certain hormones (Blaxter Bt^ al. , 1949;
Dewar, 1962; Hervey and Hervey, 1964; Wade and Zucker,
1970).
It is important that research to quantify effects upon DOMI of
factors listed above be carried out over a wide range of forage
quality, and that data generated for this purpose be analyzed by
regression procedures. Research must be carried out in this fashion
so that (a) results are applicable to a wide range of forage species;
(b) effects can be predicted continuously over this range instead of
only at a few widely scattered, intermittent points; and (c) efficient
and accurate dynamic modeling can be practiced. Experimental designs
of the central-composite or San Cristobal type require a smaller
number of experimental animals than full-scale factoral designs, and
could be utilized in attaining these goals.
Theoretical Methods for Prediction of k^
Two theoretically possible methods for prediction of k„ remain
to be tested. First, the amount of CM in the rumen per W * has
kg
been found constant among forages when forage CP is greater than
107
7 percent on a DM basis (Blaxter ^ al. , 1961; Ulyatt et al . , 1967;
Thornton and Minson, 1972). If this quantity of OM could be ascertained
for a given set of non-forage factors, then multiplying this quantity
by .63 theoretically should approximate the amount of ruminal OM per
W " which is partially digestible. The other 37 percent would
kg
estimate OM which had been in the rumen for longer than a period of
time equal to RTOM, and this should be mostly indigestible. Multiply-
ing partially digestible ruminal OM per W * by predicted OMD would
kg
approximate ruminal OM which is totally digestible per W * , and
kg
dividing this quantity by the originally assumed amount of ruminal
OM per W * should produce an accurate estimate of 'a'. Inserting
kg
this 'a' value into equation (17) should produce an accurate prediction
of k„. Potential problems to be encountered with this method are,
first, though ruminal OM per W ' has been found statistically constant
kg
among forages this amount of OM does vary numerically. Assuming this
quantity to be constant, therefore, could produce inaccurate estimates
of 'a' over a wide range of forages, and this could result in inaccurate
k predictions. Also, Assuming the 37 percent of total ruminal OM per
W, * which has been in the rumen for longer than RTOM to be totally
kg
indigestible may not always be correct, and this could result in under-
estimation of 'a'. A further difficulty would arise when forage
contains less than 7 percent CP on a DM basis. In such cases, ruminal
OM per W * apparently is not constant (Campling _et al . , 1961; Egan,
kg
1970). Thus, separate estimates of ruminal OM per W ' would have
kg
to be made for such forages. This method for prediction of k deserves
to be tested, however, to see if it would produce acceptable predictions
for this parameter.
108
The second possible method for k prediction is based upon the
fact that rate of passage of OM from the rumen is equal to k multiplied
by the amount of OM undergoing passage. This method would require
measurement of the electrical energy required to grind a known amount
of forage OM in a Wiley mill. Such determinations have been made by
Chenost (1966) and Laredo and Minson (1973).
It is possible that the electrical energy required to grind a
known amount of forage OM may be related to rate of OM breakdown in
(Laredo and Minson, 1973), and rate of OM passage from, the rumen.
If this is true among forages and if the OM undergoing grinding is a
constant percentage among forages of the amount of OM which passes
from the rumen under steady-state conditions, then dividing the energy
required to grind OM by the amount of OM being ground should produce
a value not equal to, but highly correlated with, k . The value of
k^ then could be predicted from a regression equation generated using
a wide range of forages for which k and grinding energy for an amount
of OM highly correlated with rate of OM passage from the rumen divided
by k„ were known.
The difficult part of this procedure would be determination of
the amount of OM which should undergo grinding. This quantity should
be a constant percentage among forages of the amount of OM which under-
goes passage from the rumen under steady-state conditions. At present,
quantification of OM undergoing passage requires knowledge of OMI.
Thus, a method which does not require such knowledge must be devised
for quantifying OM which passes from the rumen. It may be that a
constant relationship exists between grinding energy and amount of OM
being ground. If this were true, then any quantity of OM could be
109
ground. If such a relationship does not exist, however, a mathematician
might be able to aid in quantifying OM which passes from the rumen
under steady-state conditions.
Summary
Thirty-one warm-season grasses of known in vivo intake and digest-
ibility were used to develop and test a theoretically rational method
for prediction of forage quality in terms of digestible organic matter
(OM) intake (DOMI). These grasses included bahiagrasses, bermudagrasses
and Pangola digitgrasses which ranged in maturity from 2 to 14 weeks
of regrowth. Retention time of OM in the rumen (RTOM) was hypothesized
to be a theoretically rational independent variable for prediction of
forage quality. Values of RTOM for all grasses were estimated from
an equation presented by Waldo et^ al. (1972) for plotting disappear-
ance of cellulose from the rumen through time. This equation was
used in reference to OM instead of cellulose for each forage. The
value of the rate constant (k ) for rate of digestion was estimated
using in vitro procedures, while the rate constant (k ) for rate of
passage was calculated from known lignin intake. Estimates of the
potentially digestible fraction of ruminal OM ('a') were made using the
formula for 'a' developed in this study, and the potentially indigest-
ible fraction of ruminal OM was equal to one minus 'a'. Fifteen grass-
es selected as representative of the total of 31 were used to generate
an equation to produce acceptably accurate predictions of forage quality.
Predictions of DOMI were judged acceptable in a conservative sense
if their absolute errors in relation to actual DOMI values were less
than or equal to the value of one side of the 95 percent confidence
interval for the mean weighted across all 31 grasses. Predictions
no
were deemed liberally acceptable if the prediction errors were less
than or equal to the value of two standard deviation estimates
weighted across all grasses.
Fourteen of the 16 DOMI predictions were acceptable when judged
by conservative acceptability limits, while all predictions were
acceptable by liberal standards. Ten of the 16 grasses exhibited
crude protein percentages of less than 7 percent of DM.
Factors not related to RTOM may have influenced the actual quality
of the two Pangola digitgrasses for which DOMI predictions were
conservatively unacceptable. Inclusion in the prediction equation
of some rational factor related to the chemostatic mechanism for
controlling forage intake possibly may increase accuracy of DOMI
predictions in such cases.
Rational prediction of OM intake (OMI) from predicted DOMI
divided by predicted OM digestibility (OMD) appeared a better method
than empirical prediction of OMI from acid-detergent fiber percentage.
Though all predictions generated by this latter method were liberally
acceptable, such success might not be expected over a wider range
of forages which included more genetic diversity. Empirical predic-
tions of OMI from neutral-detergent fiber (NDF) percentage were in-
accurate.
Values of OMD were predicted accurately by dividing predicted
digestible OM (DOM) by OM. Fast and accurate DOM predictions, how-
ever, await development of a rapid, simple laboratory determination
for accurate estimation of digestible NDF or NDF digestibility.
Actual OMD could be predicted as accurately from in vitro NDF digestion
Ill
after 72 hr of fermentation as from in vitro OM digestion after 48 hr.
The former determination, however, requires more time.
Values of k^ , though relatively invariant, cannot be assumed
constant among forages, nor can these values be predicted accurately
at present from predicted values of 'a'. Estimation of k must be
achieved at present by use of in vitro methods. Lignin as a percentage
of DM was not correlated highly with k .
APPENDIX
113
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TABLE 13. ALGEBRAIC MANIPULATIONS OF EQUATION 9 REQUIRED TO
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(OMD )(OMI)
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BIOGRAPHICAL SKETCH
Edward John Golding, III, was born April 11, 1944, in Toledo,
Ohio. In June, 1962, he graduated from DeVilbiss High School in
Toledo. From September, 1962, to June, 1963, he attended North-
western University at Evanston, Illinois. In September, 1963, he
transferred to the University of Idaho, Moscow, Idaho, and received
a Bachelor of Science degree in Forestry (Range Management) in
June, 1967. From September, 1967, to June, 1970, he served as a
Peace Corps Volunteer in Cauquenes , Chile. After his return to
Toledo in June, 1970, he worked for one year at Girkins Welders.
In September, 1971, he enrolled in the Department of Animal Science
at the University of Florida, and received the Master of Science in
Agriculture degree in August, 1973. At present he is a candidate
for the degree of Doctor of Philosophy in the Department of Animal
Science, University of Florida.
He is married to the former Astrid Semler Chipoco, and they have
a daughter, Nicole, and a son, Christopher. The author is a member
of Gamma Sigma Delta, Phi Kappa Phi and Xi Sigma Pi.
149
I certify that I have read this study and that in my opinion
it conforms to acceptable standards of scholarly presentation and
is fully adequate, in scope and quality, as a dissertation for the
degree of Doctor of Philosophy.
tlf
H(r/l
Q-^
Moore, Chairman
or of Animal Science
I certify that I have read this study and that in my opinion
it conforms to acceptable standards of scholarly presentation and
is fully adequate, in scope and quality, as a dissertation for the
degree of Doctor of Philosophy.
C. B. Ammerman
Professor of Animal Science
I certify that I have read this study and that in my opinion
it conforms to acceptable standards of scholarly presentation and
is fully adequate, in scope and quality, as a dissertation for the
degree of Doctor of Philosophy.
H. Conrad
'Professor of Animal Science
I certify that I have read this study and that in my opinion
it conforms to acceptable standards of scholarly presentation and
is fully adequate, in scope and quality, as a dissertation for the
degree of Doctor of Philosophy.
/(.
/V <-
D. E. Franke
Associate Professor of Animal Science
I certify that I have read this study and that in my opinion
it conforms to acceptable standards of scholarly presentation and
is fully adequate, in scope and quality, as a dissertation for the
degree of Doctor of Philosophy.
G. 0. Mott
Professor of Agronomy
This dissertation was submitted to the Graduate Faculty of the
College of Agriculture and to the Graduate Council, and was accepted
as partial fulfillment of the requirements for the degree of Doctor
of Philosophy.
March, 1976
Dean, Graduate School
UNIVERSITY OF FLORIDA
3 1262 08666 929 7