Utilization of local feed
resources by dairy cattle
Perspectives of environmentally balanced
production systems
Symposium proceedings
WAGENINGEN INSTITUTE OF ANIMAL SCIENCES (WIAS)
Wageningen, The Netherlands
EAAP Publication No. 84
Ab F. Groen and Jaap Van Bruchem
(Editors)
Optimization of grassland production and herbage feed quality in an
ecological context
Egbert A. Lantinga and Jeroen C.J. Groot
•
•
HカセI@
Wageningen Pers
Wageningen 1996
•
•
Optimization of grassland production and herbage feed quality in an
ecological context
Egbert A. Lantinga 1 and Jeroen C.J. Groot 2
Department of Theoretical Production Ecology, C. T. de Wit Graduate School Production
Ecology, P. 0. Box 430, 6700 AK Wageningen, The Netherlands
Department of Agronomy, C. T. de Wit Graduate School Production Ecology, P. 0. Box
341, 6700 AI! Wageningen, The Netherlands
2
Summary
Improved grassland management and use of better cultivars of perennial ryegrass regarding
feeding quality and persistency can contribute to reduction of concentrate and fertilizer inputs
in grassland based dairy farming systems. Acceptable net energy production levels with
minimal nitrogen losses per unit product can be achieved from grassland fertilized with c.
200 kg N .ha·' .yr·• under integrated grazing and mowing management. Increasing N efficiency
at the animal level through lowering N content in the diet is desirable, as· tong as the supply
of aminogenic nutrients to the intestines is not hampered. In addition, roughage carbohydrate
supply must be enhanced. Prospects of achieving this by increasing cell wall digestibility
(CWD) are marginal, but present. Therefore, more attention is also required to increase the
proportion of water soluble carbohydrates (WSC) in roughages. In the grazing situation this
will not affect rumen pH. Grazing experiments with tetraploid cultivars of perennial ryegrass
show promising perspectives for higher voluntary intake and milk production than from
current diploid cultivars. In comparison with the diploid Wendy, the tetraploid Condesa has
a higher WSC content and the tetraploid Madera has a higher fraction of potentially
degradable CW. Therefore, tetraploids tnight gain in importance, provided their persistence
is sufficient to avoid sward deterioration. Finally, excessive declines in CWD and WSC
content due to ageing and stem elongation must be avoided by appropriate management and
cultivar choice.
Introduction
The forage produced from grassland in the Netherlands supplied about 50% of the estimated
net energy requirement of dairy cows at the end of the 1980's (Ketelaars & Van Vuuren,
1995). Around 1950 this figure was much higher (about 90%). During the last decades, three
major trends have occurred in Dutch dairy farming systems. Firstly, grass and grass products
have been partially replaced by maize silage and concentrates. Secondly, the application of
artificial nitrogen (N) to grassland increased drastically from 50 kg.ha·• in 1950 to 315 kg.ha·•
in 1985 (Van der Meer, 1991). Thirdly, the average milk yield per cow increased from a
national average of 3800 kg.cow·• in 1950 to 7000 kg.cow·' in the early 1990's (LEI-CBS,
1993).
The rate of rumen fermentation of structural carbohydrates in roughages fails to support
the increasing milk production potential of dairy cows. The supply of energy to grazing
animals is insufficient for milk productions above 29 kg.cow· 1 .day· 1 (Van Vuuren, 1993).
Therefore, roughage diets have to be supplemented with concentrates high in nutrient and/or
58
net energy density to support the high milk production potential. However, the production
of concentrates requires large amounts of energy from fossil fuels, and the use of purchased
concentrates introduces a surplus of nutrients into the system.
Enhancing rates of N application result in higher productivity of grass, primarily due to
an increased rate of leaf area expansion after harvest. The grass produced contains a high
proportion of the highly digestible leaf fraction, but is also high in concentration of nitrogen
containing organic and inorganic compounds. Nitrogen con1pounds in fresh and ensiled grass
are released rapidly following ingestion by ruminants (Beever, 1993). The fermentation rate
of carbohydrates, in particular cell walls, by rumen microorganisms is lower. Due to this
desynchronization in digestion and the high level of run1en degradable N, theN incorporation
· in the rumen by the microbial biomass is relatively low. This is only partly con1pensated by
recycling of urea N to the rumen through saliva (De Visser, 1995, personal communication).
Consequently, a high proportion of the ingested N is lost fron1 the rumen as ammonia and
the utilization efficiency of dietary N by cattle is low (between c. 15-30%). The level of
rumen degradable N is lower in hay and artificially dried grass.
Increased environmental awareness imposes detnands on management of grassland and
animal production systems for optimization of fibrous feed quality in an ecological context:
concentrate input has to be reduced and nutrient losses, in particular of N, must be reduced.
In this paper we will discuss the consequences of optimization (i.e. reduction) of the N
input to grassland for herbage production and feeding quality, and the prospects for
in1proving both carbohydrate supply from grass and nitrogen utilization efficiency through
plant breeding.
Effects of nitrogen fertilization on grass productivity and feeding quality
Recommendations of N application rates in the Netherlands are mainly based on economic
cost-benefit analyses of long-term cutling trials in sn1all plots, which at cprrent prices leads
to a marginal profitability of 7-8 kg dry matter per kg N applied. In an experiment by
Deenen & Lantinga (1996) on a sandy soil the calculated economic optimum level of N input
was 420 kg.ha·•.yr' in cutting-only plots, averaged over three years. At the same site the
average N uptake from unfertilized plots was 110 kg.ha·'.yr 1• This non-fertilizer N delivery
capacity of the soil is taken into account in the current N fertilization recommendations
(Unwin & Vellinga, 1994).
At high levels of N input the efficiency of protein utilization by dairy cattle is relatively
low, and consequently a high proportion of ingested nitrogen is excreted in urine and faeces.
This leads to high N losses to the environment. The efficiency with which applied N is used
in herbage production can be illustrated by the ratio between residual inorganic N in the soil
at the end of the growing season and total herbage yield (Figure 1). This ratio reflects the
nitrogen utilization by the crop. At its minin1um value nitrogen losses per unit product are
lowest. From this ecological viewpoint the optin1um level of N input for integrated grazing
and cutting management on the sandy soil was in the order of200 kg.ha·'.yr'.
The question is what the consequences of this reduced N input will be for grassland
productivity and herbage quality. In the experiment of Deenen & Lantinga (1996), the
response to fertilizer N was also estimated under integrated grazing and mowing n1anagement
as the annual sum of herbage intake, and the amount of ensiled herbage from all the
paddocks at each N level together. In Figure 2 this response curve is shown for 1988
together with the one from cutting-only plots. The figure also includes the calculated average
59
net output from grassland of 150 dairy farms on sandy soils in relation to inorganic N input
in 1988 (Daatselaar et a/., 1990; Van der Putten, unpublished data). It is clear from this
figure that the response to N under integrated grazing and mowing management is much
weaker compared to that in the cutting-only plots. The n1ain cause for this phenomenon was
sward deterioration in the grazed paddocks, which increased at higher levels of N
fertilization. The 'gap' between the two response curves represents grazing losses (poached
and scorched grass, losses due to senescence of grazing residues and grass removed by
cleaning cuts) and conservation losses in the field during the wilting period. It may therefore
be concluded that, especially on grassland soils which are susceptible to urine scorching and
poaching, a reduction inN input from 300-400 kg.ha·'.yr·' to about 200 kg.ha·•.yr' will hardly
affect the total net energy yield. This may have been the reason that the grassland output on
the commercial farms was surprisingly low, leaving much scope for improvement of the
efficiency of applied nitrogen.
It has been postulated by Vellinga & VanLoo (1994) and VanLoo et al. (1995) that
breeding and selection work with perennial ryegrass for better N use efficiency could lead
to cultivars which would contribute to reduced nitrogen surpluses. Recovery of applied
nitrogen will be highest in swards with a high tiller density, a low frequency of open patches
and a high leaf expansion rate after harvest. The main criteria in grass breeding should
therefore still be persistency and dry matter yieid under both cutting and grazing
management.
kg· Nres per GJ NE
2
ッKMイLセN@
0
100
200
300
400
500
600
700
kg N ha· 1 yr-1
Figure 1. Relationship benveen fertilizer N application and the amount of residual inorganic
N (kg Nres· ha·') in the soil profile (0-60 em) divided by the total herbage yield
expressed in GJ NE. ha· 1 at the end of the grov.;ing season (mid-October). Data are
from cut-only and grazed-only plots on a sandy soil in 1987. Sources: Deenen &
Lantinga (1996); Van der Putten (unpublished data).
60
QRPセM@
NE yield, GJ per ha
100
cutting-only
80
experimental farm
60
。セM@
__..- a..--
a--
commercial farms
a
40
20
otMセ@
0
200
400
600
800
kg N ha-1 yr1
Figure 2. Relationship between inorganic N input and net energy (NE) yield on an
experimental farm in cutting-only plots and in paddocks as the sum of herbage
intake and ensiled herbage, and Oil commercial dairy famzs as calculated fronz NE
requirements of livestock. One GJ NE corresponds to about 150 kg dry matter. All
data are from grasslands on sandy soils in 1988. Sources: Deenen & Lantinga
(1996); Van der Putten (unpublished data).
Decreasing N fertilization and/or enhanced N use efficiency of grass will lead to
reduction of N content in the dry matter. However, reduction of crude protein content in
grass to levels below approximately 225 g per kg dry matter could lead to negative effects
on the supply of a1ninogenic nutrients (Van Vuuren, 1993). This corresponds to a nitrogen
content of 36 g per kg dry matter, which is still a high value. Oldham (1984) demonstrated
that, in lactating cows, at least 30 g N per kg dry matter must be included in the diet to
avoid negative effects on milk production. From the experiment of Deenen & Lantinga
( 1996) it can be derived that under integrated grazing and mowing management the average
nitrogen content at a fertilizer N rate of about 200 kg.ha· 1.yr 1 will be slightly above 30 g per
kg dry matter. In experiments by Deenen & Lantinga (1993) and Valk & Van Vuuren (1995)
no or only small negative effects on n1ilk production per cow were found from reducing N
fertilization to 250 and 150 kg.ha·'.yr 1 , respectively. Further reductions inN content without
loss of milk yield can only be achieved if the capture of N in the rumen is improved or the
level of run1en degradable N is lowered.
Improving carbohydrate supply from grass
Concentrate feeding to high producing animals and losses of N from the rumen can be
reduced by improving the supply of carbohydrates from roughage. Grass and other roughages
contain water soluble carbohydrates (WSC) and structural, polymerized carbohydrates laid
61
down in cell walls (eW). WSC are released into the rumen after disruption of the cell, e.g.
through n1astication by the ruminant. The sugars are assumed to be fermented rapidly by
rumen microorganisms. CW are more resistant to microbial attack. The ew fraction is not
completely degradable, and the rate of degradation may be too low to assure carbohydrate
supply for microbial growth and N utilization at a desired high level. Potential avenues for
improvement of the fermentation of carbohydrate and the synchronization with N digestion
would be to increase ew digestibility and/or WSC content.
Many researchers have argued that improvement of ew digestibility (CWD) of perennial
ryegrass through breeding would enhance anirnal performance and reduce concentrate
requirement (e.g. Vellinga & VanLoo, 1994), regarding the high correlation between ewD
and organic matter digestibility (Deinum et al., 1996). However, contrary to maize,
prospects for improvement of eWD of per.ennial ryegrass through breeding are limited. Cell
wall content (CWe) in modern grass cultivars is relatively low (below 50% in the DM) and
ewn is generally already high (around 80%). These characteristics have automatically
developed in breeding programmes for higher OM production. A possible improvement
might be found by increasing ewe in organs with fully-degradable CW, for example laid
down in parenchymatic tissue in grass leaves. This is unlikely to be achieved, since ewe
and CWD are negatively correlated (Deinum et al., 1996). Furthermore, extra production
of energeticaJ.ly expensive CW (see e.g. Thornley & Johnson, 1991) would inevitably reduce
grass productivity, which would imply a step backwards in grass breeding. Is there then any
possible advantage from increased CW degradation rates? Hageman et al. ( 1992) observed
large variations in CW degradation rates between cultivars of perennial ryegrass and
throughout the season (approximately 3. 5-8 %. h· 1). However, no correlation at all with
herbage intake, milk production and composition was found. Tamminga & Van Vuuren
(1996) also postulate that effective clearance from the rumen (degradation and passage) is
virtually independent of rate of CW degradation. This would make the scope for
improvements in CW degradation rate limited.
Higher proportions of degradable carbohydrates can also be obtained when the proportion
of easily fermentable WSC is increased. Additionally, this could contribute to a more
balanced C/N ratio in the rumen following ingestion of the feed. This approach is advocated
by Beever (1993) and Beever & Reynolds (1994). In infusion experiments, Rooke et al.
( 1987) observed higher microbial N synthesis and non- ammonia nitrogen flow to the small
intestine and a decline in the ammonia concentration in the rumen of about 50%, as a result
of continuous supply of glucose syrup. This is ascribed to the improved synchronization of
release of C and N compounds.
Ingested WSC are rapidly fermented in the rumen (cf. pulse dose), which could lead to
accumulation of VFA and possibly a decline in pH (Van Vuuren, 1993). This could impair
rumen function (Tamminga & Van Vuuren, 1996) and reduce intake and ruminal outflow of
organic matter, as shown by Henning et al. (1993) and Mansfield et al. (1994) after pulse
dosing of carbohydrates into either the rumen or continuous culture fermenters. In the
grazing situation, Van Vuuren et al. (1986) observed a sharp decrease in rumen pH during
the evening hours. This was associated with a 'bulking period' around
late-afternoon/early-evening, when animals grazed for three hours or longer with short or no
resting periods. It was remarkable in this experiment that the pattern of ruminal pH values
was not influenced by the level of concentrate supplementation (1 vs. 7 kg.cow· 1.d· 1) nor by
intake of easily degradable carbohydrates. In the experiment of Hageman et al. (1992), only
marginal differences in the average values and diurnal patterns of rumen pH were observed
between three grass cultivars. This was also the case in autumn, when a marked difference
62
in WSC content occurred (100 g.kg·• DM in Wendy and Madera, compared to 150 in
Condesa). This leads us to the conclusion that fluctuations in rumen pH may be more
correlated with ingestion rates than with level of WSC intake per se.
WSC content and CWO rapidly decline when stem elongation starts, especially in periods
of high temperatures. In order to shorten the period of stem elongation it may be a wise
decision either not to use cultivars in n1ixtures which differ too much in heading date, or to
simply use monocultures. Besides, stem elongation can be suppressed under intensive
continuous grazing. Since growing conditions and feeding quality of the herbage produced
are best in late spring it is advisable to use cultivars with a rapid early spring growth. By
using such cultivars a high quality first cut silage with a good yield can be obtained more
easily than is the case with late cultivars. In addition, it may be of interest to investigate
whether there are differences between cultivars in the length of the period of stem elongation.
Possibilities for improved intake and n1ilk production
Pron1ising results have been obtained from experiments comparing diploid and tetraploid
cultivars of perennial ryegrass (Hageman et al., 1992, 1993). Tetraploid cultivars of
perennial ryegrass are superior to diploids in terms of animal performance (Castle & Watson,
1971; Vipond et al., 1993). In a grazing experiment, the tetraploid cultivars Condesa and
Madera and one of the most palatable diploids (Wendy) were compared. Herbage intake
tended to be higher for the tetraploids at a herbage allowance of more than 30 kg
OM.cow·'.d·', and a concentrate supplementation of 1-3 kg.cow·'.d·' (Table 1). Although
differences in intake were not significant in this grazing experin1ent, they were reflected in
a higher concentration of volatile fatty acids and the lower pH in the run1en for the
tetraploids (see Robinson et al., 1986). Intake differences might also explain the observed
higher FPCM (fat and protein corrected milk) production on the tetraploids. In the spring of
1990, with a concentrate supplementation of 3 kg .cow·•.d·', there was a difference between
the tetraploids and the diploid of about 2 kg FPCM .cow·'.d·'.
The reasons for the higher intake and milk production from tetraploids are still not fully
understood. It has often been postulated that tetraploids are more palatable than diploids
because of a higher content of WSC in the ingested herbage. However, there were no
differences at all in WSC content on a dry matter basis between the tetraploid. Madera and
the diploid Wendy (Table 1). In the fresh material the content of WSC was even lowest in
Madera due to a higher water content. Despite this, palatability tests in cultivar evaluations
(free choice as in a 'cafeteria') always show a significant preference for the tetraploids. An
alternative explanation might be the lower resistance to physical breakdown during chewing
of tetraploids compared to diploids (Hageman et al., 1992). The rate of mastication has been
identified as an important factor influencing voluntary intake (Moseley & Antuna Manendez,
1989). Notably, in the tetraploid tvladera the fraction of potentially degradable cell walls was
· higher than in Wendy. Taking into account that between 86-89% of the potentially degradable
CW is always digested (Tamn1inga & Van Vuuren, 1996), this n1ight indicate that in fact the
NE content or VEM value of tetraploid perennial ryegrass is somewhat higher than derived
from standard in vitro analyses with an incubation period of 48 hours. These cultivar
differences in potentially degradable CW demonstrate that there is some scope for improving
CW digestibility through breeding.
63
Table 1.
The mean daily herbage allowance and intake (kg OM.cow'.d-'), fat and protein
corrected milk yield (FPCM; kg.colv'.d- 1), milk protein content (%), rumen
fennentation characteristics (VFA,· mmol. l- 1 and pH), in-vitro digestibility of OM
(DOM; %), potentially degradable CW (PDCW; %) and WSC (% in DM) in a
grazing experiment with three cultivars of perennial 1yegrass. D =diploid;
T=tetraploid; VFA =volatile fatty acids. Average values for three 4-weekly grazing
periods in spring, summer and autumn 1990. DOM, PDCW and WSC refer to
ingested grass. Source: Hageman et al. (1992, 1993).
Cultivar
Allow- Intake FPCM Milk VFA pH
ance
4--- protein
DOM PDCW
wsc
Wendy D
Condesa T
Madera T
35.2
33.5
34.3
83.0
83.0
83.6
9.9
12.P
9.9
a
sゥァョヲ」セエャケ@
17.1
17.6
17.7
28.4
29.6
29.3 3
3
3.39
3.48
3.44
129.0 6.02
138.7 5.81
133.9 5.87
88.5
90.4
92.7a
higher than Wendy.
A weak point of the tetraploids is that they generally have a lower tiller density than
diploid cultivars. In Condesa this is also associated with a lower persistency (Neuteboom et
al., 1993). However, based on recent cultivar evaluations (Neuteboom et al., 1992;
Anonymous, 1995), the tetraploid Madera can be seen as a representative of a new
generation of tetraploids, combining high herbage intake with good persistency. Condesa is
no longer present on the Dutch recommended variety list for agricultural crops (Anonymous,
1995).
Acknowledgements
We thank Ir A.H.J. Vander Putten (AB-DLO, Wageningen) for kindly providing the data
on residual inorganic N in Figure 1 and the dairy farms presented in Figure 2.
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