Estimation of Covariance
Components and Prediction of Additive Genetic Effects for First Lactation 305-d
Milk and Fat Yields in a Thai Multibreed Dairy Population[1]/
Skorn Koonawootrittriron*, Mauricio A. Elzo2/,
Sornthep Tumwasorn and Kovit Nithichai3/
Department of Animal Science,
Faculty of Agriculture,
Kasetsart University, Bangkok
10900, Thailand.
Abstract
Estimates of covariance components and predicted additive
genetic effects for accumulated 305-d milk yield (MY) and accumulated 305-d fat
yields (FY) were obtained by using production records of 610 purebred and
crossbred first lactation cows in a Thai multibreed dairy population. Covariance components were estimated using
average information restricted maximum likelihood procedures and two two-trait
additive genetic animal models with different genetic grouping strategies. The BTBI model accounted for Bos taurus (BT)
and Bos indicus (BI) fractions, whereas the HO model considered Holstein
(H) and Other breeds (O) fractions. Heritability
estimates obtained using the BTBI model were 0.45 for MY and 0.24 for FY, and
those obtained using the HO model were 0.46 for MY and 0.25 for FY. Genetic, environmental, and phenotypic
correlations between MY and FY obtained from these two models were high (0.89 to
0.99). The estimates of BT additive
genetic group effects, as deviations from BI, were 149 kg for MY and -26 kg for
FY. The estimate of H additive genetic
group effects, as deviations from O, were 18 kg for MY and -21 kg for FY. Expected breeding values (EBV) of sires and
dams were evenly spread across BT (BTBI model) and H (HO model) fractions. The top 10% and the bottom 10% of sires for
MY and FY were purebred H sires (91% of all sires were 100% H). The highest dam EBV for MY was from a
crossbred dam (5/8 H) and the lowest one was from a 100% H dam. The EBV here suggest that BT (or H)
crossbred animals can potentially yield better MY and FY than purebred BT or H
animals under Thai tropical conditions.
One drawback of the additive group regression models used here is that
they ignored nonadditive genetic effects.
In particular, interbreed nonadditive genetic effects need to be studied
in Thai dairy cattle populations. To
assess the importance of these genetic effects, multibreed genetic evaluation
procedures that account for additive and nonadditive genetic effects could be
used.
Key words: Dairy cattle, Milk yield, Fat
yield, Multibreed, Genetic group, Genetic evaluation
Introduction
The current Thai dairy cattle population has more than ten
different breeds represented in both purebred and crossbred forms. Most animals in this population are
crossbred, and composed of up to seven different breeds.
A large-scale dairy genetic evaluation program was created
through a collaboration between the Dairy Farming Promotion Organization of
Thailand (DPO) and Kasetsart University in 1996 (D.P.O., 1996). Since that year, genetic predictions of
sires used in the multibreed dairy population controlled by DPO have been
published for milk and fat yield every year.
Currently, genetic predictions are computed based on a best linear
unbiased prediction (BLUP) procedure using a single-trait animal model
(Henderson, 1975; Quaas and Pollak, 1980).
This single-trait animal model includes the components of a contemporary
group as main effects (i.e., interactions among location, year, and season are ignored),
and subclass genetic group effects based on ranges of accumulated Bos taurus
(BT) and Bos indicus (BI) fractions as defined by
Vinther (1974). This model has several
aspects that could be modified to produce genetic predictions of higher
accuracy given the available information supplied by DPO.
Firstly, location in the DPO model is defined as clusters
of herds (amphurs). This definition of
location assumes that sires of all genetic values will be used in all herds
within an amphur. However, this may not
happen if more intensively managed herds use sires of higher predicted genetic
values than more extensively managed herds.
If this happens, the resulting predicted genetic values will
overestimate the genetic value of sires in intensively managed herds by
referring them to the amphur’s lower mean than that of their own herds, and
vice versa. Thus, it seems preferable to
use herds than amphurs as the definition of location.
Secondly, if interactions among location, year, and season
were important in the DPO population ignoring them would cause biases in
genetic evaluations. Further, if
regression procedures could be used to explain genetic group effects, they would
be more accurately estimated because information from all animals in the
population would contribute to their estimation. As with the current DPO model,
genetic evaluations using a model with these modifications can be readily
obtained using available computer packages (e.g., ASREML, Gilmour et al.,
2000).
Thirdly, the genetic basis that genetic predictions are
deviated from could be defined in a way that reflects more closely the breed
composition of the DPO population. The
most represented breed in this population is Holstein (H). In fact, almost every dairy animal in the
DPO multibreed population contains some H fraction. Thus, an alternative genetic grouping strategy to the current DPO
strategy would be to consider H and Other Breed (O) fractions, where O would
include fractions of any other breed (BT or BI) present in an animal.
Consequently, the objectives of this study were: 1) to
develop multiple-trait additive group regression animal models that account for
interactions among contemporary group components, and use regression to
describe either BT and BI fractions (BTBI model), or H and O fractions (HO
model), 2) to estimate covariance components and genetic parameters for these
two models for 305-d milk and 305-d fat yields, and 3) to compare the expected
breeding value (EBV) of sires and dams of all available BT (BTBI model) and H
(HO model) fractions under Thai tropical conditions.
Materials and Methods
Animals and Records
The initial data set used consisted of 12,505 monthly
test-day milk yields and 10,042 monthly test-day fat yields of 921 first
lactation purebred and crossbred cows that calved from 1991 to 2000 provided by
DPO. These records were from 68 farms
in central Thailand. Calving seasons
were classified as winter (November to February), summer (March to June), and
rainy season (July to October).
Breeds represented in this Thai multibreed data set
were Holstein, Brahman, Brown Swiss, Illawarra, Jersey, Red Dane, Red Sindhi,
Sahiwal, Thai Native, and Shorthorn.
However, preliminary descriptive statistical analyses revealed that the
distribution of numbers of sires, dams, and females with records was severely
skewed towards Bos taurus, and in particular, Holstein, and that most of these
breeds were represented only as small fractions in crossbred animals. The small size of the dataset and the
unbalancedness of the breed composition of animals in this DPO dataset made it
impossible to consider all breed groups for genetic analyses. Thus, these ten distinct breeds were
re-defined as Bos taurus (BT) and Bos indicus (BI) breeds
for the analysis using the BTBI model, and Holstein (H) and Other Breeds (O)
for the analysis using the HO model.
The dataset used in the analyses was prepared in two
steps: 1) cow accumulated 305-d milk yields (MY) and 305-d fat yields (FY) were
predicted using monthly test-day milk and fat samples, respectively, and 2)
connectedness was determined by considering the representation of sires across
contemporary groups. Then, the largest connectedness dataset was used for the genetic
evaluation and the estimation of covariance components.
Prediction of
MY and FY
To predict MY and FY, test-day samples that were
collected on months after reaching 305-d in lactation of each animal were
ignored, and animals that did not have consecutive monthly test-day milk and
fat yield records within the first ten months after calving were
discarded.
Monthly production yields (milk and fat) were computed
using two consecutive test day production samples, and then these monthly
production yields were used to compute the accumulated 305-d productions. Unfortunately, the DPO had not recorded
dates of measurement of those monthly test-day samples in the database, and
this information could not be retrieved.
Thus, the number of days between two consecutive production samples
could not be calculated. Monthly
production samples were collected by DPO primarily during the last week of each
month. Thus, it was assumed that these
test-day samples were collected the last day of every month. Consequently, the
new estimation equation was,
[1]
where TPY is the total production yield of an
individual animal, P1 is the test-day production yield sample in the
first month after calving, D1 is the interval between five days
after calving and the last day of the fist sampling month, Pi is the
test-day production yield sample in month i (i = 2, … , k), Di is
the interval between the last day of month i - 1 and i (i = 2, … , k), Pk+1
is the test-day production yield sample in the last month of reaching 305-d in
lactation, and Dk+1 is the interval between the 305-d of lactation
and the last day of the month before reaching 305-d in lactation. To predict MY
and FY in this step, statements in the data step of the SAS program (SAS, 1990)
were used.
Finding the Largest Genetic Connected Dataset
Connectedness between management units or contemporary
groups can influence the accuracy of genetic evaluation or selection when
selection is among animals raised in different environments (Kennedy and Trus,
1993). Preliminary analysis of this
data set reconfirmed that the calving herd ´ year ´ season subclass had important effects (P < 0.01) on milk and fat
production. Thus, contemporary groups
here were defined as groups of cows that calved in the same herd, year, and
season (HYS). A FORTRAN program was
written (Elzo, 2000) to find the largest connected data set using the
connections between sires and contemporary groups. The largest connected data set consisted of 610 MY and 487 FY
from 610 purebred and crossbred cows representing 214 sires from 178
contemporary groups (Table 1).
Table 1. Description
of the largest connected data set
|
Characteristic |
Value |
|
Number of sires |
214 |
|
Number of cows |
610 |
|
Number of animals in the population |
1,319 |
|
Number of contemporary groups |
178 |
|
Number of 305-d milk yield records |
610 |
|
Number of 305-d fat yield records |
487 |
|
Average 305-d milk yield (kg) |
3,925 |
|
Average 305-d fat yield (kg) |
149 |
A description of the largest connected data set in
terms of numbers of sires, dams, and cows with records by BTBI
breed-group-of-sire ´ breed-group-of-dam combination is shown in Table 2, and by HO
breed-group-of-sire ´ breed-group-of-dam combination in Table 3. These tables clearly show the extreme unbalancedness of the
distribution of animals in the DPO population.
Bos taurus sires accounted for 93% of all sires represented in
this data set, and 83% of all dams in this data had a 60% or higher BT
fraction. The vast majority of the BT
sires were H (98%), and 77% of all dams in the 60% or higher BT fraction had H
alleles. This reflects a suggestion of the Thai government to preferably use H
semen on the existing cow population during this period (1991-2000).
Table 2.
Numbers of sires, dams, and calves by BTBI breed-group-of-sire ´
breed-group-of-dam combination
|
|
Breed-group-of-sire |
|
|
Breed-group-of-dam |
Bos taurus |
(0.00-0.99)BT (1.00-0.01)BI 1/ |
|
(0.6-1.0)BT (0.4-0.0)BI |
183 2/ |
15 |
|
|
462 3/ |
36 |
|
|
513 4/ |
36 |
|
(0.4-0.6)BT (0.6-0.4)BI |
32 |
3 |
|
|
37 |
6 |
|
|
43 |
6 |
|
(0.0-0.4)BT (1.0-0.6)BI |
12 |
- |
|
|
12 |
- |
|
|
12 |
- |
1/ BT = Bos taurus (Holstein,
Jersey), BI = Bos indicus: Native, Brahman, Red Sindhi, Sahiwal, Red
Dane;
2/ Number of sires; 3/
Number of dams; 4/ Number of females with records.
Table 3.
Numbers of sires, dams, and calves by HO breed-group-of-sire ´
breed-group-of-dam combination
|
|
Breed-group-of-sire |
|
|
Breed-group-of-dam |
Holstein |
(0.00-0.99)H (1.00-0.01)O 1/ |
|
(0.6-1.0)H (0.4-0.0)O |
158 2/ |
12 |
|
|
356 3/ |
28 |
|
|
394 4/ |
28 |
|
(0.4-0.6)H (0.6-0.4)O |
84 |
6 |
|
|
114 |
8 |
|
|
130 |
8 |
|
(0.0-0.4)H (1.0-0.6)O |
38 |
4 |
|
|
41 |
6 |
|
|
44 |
6 |
1/ H = Holstein, O = Other breeds: Native, Brahman, Red
Sindhi, Sahiwal, Jersey, Red Dane; 2/ Number of
sires; 3/ Number of dams; 4/
Number of females with records.
Estimation of Covariance
Components
Covariance components were estimated by a restricted
maximum likelihood procedure (REML) using the average information (AI)
algorithm (ASREML; Gilmour et al., 2000).
The starting values for the two-trait ASREML analyses were the estimates
of variance components obtained from the initial single-trait genetic analyses
using the same data set.
The models used here were two-trait
(MY and FY) animal models. Each trait
was assumed to have only direct additive genetic effects. Fixed environmental effects were contemporary
group and calving age (mo). Regression
additive genetic group effects were (BT - BI) for the BTBI model and (H - O)
for the HO model. The random effects in
these models were additive animal genetic effects, and residual.
The BTBI and the HO models for two traits can be described
using the following generic matrix notation:
[2]
with
[3]
where
y =
vector of MY and FY ordered by cows within traits.
b = vector of contemporary groups (HYS) and
calving age (mo),
ga = vector of regression additive genetic group
deviations, i.e., (BT - BI) for the
BTBI model and (H - O) for the HO model,
aa = vector of animal additive genetic effects,
e = vector of residuals,
X = matrix of 1’s and 0’s that relates cow records
to elements of b,
Zga = matrix of expected fractions of BT alleles
(BTBI model) and of H alleles (HO model) that relates cow records to elements
of ga ,
Za =
matrix 1’s and 0’s that relates cow records to elements of aa,
subscript 1 = MY, and
subscript 2 = FY.
It was assumed that
[4]
where
Ga = Go
Ä A where Go is the matrix of additive
genetic covariances, A is the numerator relationship matrix (Henderson, 1976),
and Ä represents direct product (Searle, 1982), and
R
= residual covariance matrix.
Prediction of Genetic
Effects
Solutions of genetic effects were obtained by solving the
mixed model equations using the estimated variance components obtained at
convergence. The additive genetic value
(EBV) of animal ij is:
[5]
where
is the
additive genetic value of animal ij,
is the fraction of BT alleles in
the BTBI model, and of H alleles in the HO model for animal ij,
is the regression additive genetic group
effect (BT - BI in the BTBI model, and H - O
in the HO model) , and
is the random additive genetic
effect of animal ij.
Results and Discussion
Regression Additive
Genetic Evaluation Models
The models used here accounted for herd-year-season
subclass effects and used regression to describe differences between BT and BI
genetic effects (BTBI model), and between H and O genetic effects (HO
model). These models were based on the
one used in the DPO genetic evaluations between 1996 and 1999. The BTBI and HO model differ from the DPO
model in the way contemporary groups (i.e., HYS) and genetic group effects are
defined. These differences are
discussed below.
Contemporary
Groups. In dairy genetic evaluations, animals are
compared in groups maintained under similar environmental conditions. These comparison groups are commonly formed
by fitting factors such as herd, year, and season of calving (VanVleck, 1987;
VanBebber et al., 1997). The model used
by DPO included the components of a contemporary group (i.e. location,
year, and season of calving) as main effects, but it ignored the interactions
among them. In that model, herds were
grouped according to administrative locations (amphur), and then amphurs were
used in place of herds in the DPO model.
The mean of an amphur for any trait will be lower than that of the
better-managed herds and higher than that of the poorer managed herds. Assuming that better managed herds bought
semen of higher EBV sires, using groups of herds (amphurs) instead of single
herds as part of a contemporary group may have biased the EBV of genetically
better sires upwards because their daughters were compared to the amphurs’
lower means than those of their herds of origin. Contrarily, lower EBV sires may be biased downwards. To avoid these potential biases, dairy
cattle genetic evaluation models in Thailand should use herds instead of
amphurs.
Ignoring interactions among contemporary group components
may result in biased DPO genetic evaluations.
Dairy cattle genetic evaluation models normally include these
interactions because they have usually been found to be significant (e.g.,
VanVleck, 1987; Schmitz et al., 1991).
Preliminary analyses of the DPO data set here reconfirmed this
fact. Two- and three-way interactions
among herds, years, and seasons were significant (P < 0.01). Thus, HYS subclasses should be used in
genetic evaluation models for the DPO data set.
Genetic
Group Effects. The purpose of genetic group effects in
dairy genetic evaluation is to account for genetic differences among
subpopulations (Quaas and Pollak, 1981).
Genetic group effects in a genetic prediction model can be viewed from a
subclass or a regression viewpoint.
Regression grouping strategies are better suited to multibreed
populations than subclass grouping strategies because regression components
(e.g., Bos taurus) are estimated using information from all animals
containing that component in their genotypes, and they can be used to predict
any subclass genetic group effect, including those not represented in the data
set. Contrarily, subclass-grouping
strategies use only information from a particular subclass to estimate the
genetic group values of that subclass (less accurate than an estimate using
regression group components), and they cannot be used to predict group
subclasses not in the data set. The
1999 DPO model created subclass genetic groups based on ranges of accumulated
fractions of BT and BI as defined by Vinther (1974). If interbreed BT ´ BI nonadditive genetic effects were important for the 1999 genetic
evaluation, they would have been an integral part of the estimated DPO subclass
group effects, and the random portion of the EBV would have been deviated from
a function of additive and nonadditive genetic group components. In the 1999 sire summary, however, DPO
published only the random part of sire EBV, which contained only
additive genetic effects. Thus, the
1999 published EBV permitted unbiased comparisons among sires of the same
BT-BI composition; comparison among bulls of different BT-BI composition would
be biased.
Ideally
additive and nonadditive genetic effects should be estimated separately to help
improve selection and mating decisions in a multibreed population. Unfortunately, the structure and size of the
DPO multibreed data set here prevented a separate estimation of BT ´ BI interbreed nonadditive genetic group effects. Consequently, the genetic value of a sire
was defined here to be the sum of an additive genetic group part and of an
additive random genetic part (equation [5]).
Data-permitting, however, these nonadditive genetic effects must be
included in future larger and more complete Thai multibreed data sets.
The
second regression grouping strategy used here, HO, is a step further in the
development of regression breed oriented multibreed models for Thailand. Holstein was chosen as the identifiable
breed because it is the most popular base breed for dairy crossbreeding
purposes in Thailand. Regression breed
oriented multibreed models are likely to become more feasible in the future as
more data becomes available on a few major breeds in Thailand.
Estimates of
Covariance Components and Genetic Parameters
Additive
genetic and environmental variance components, heritability estimates, and
their standard errors for MY and FY using the BTBI and the HO model are
presented in Table 4. The genetic base
of the BTBI model was the set of BI alleles in the population. On the other hand, the genetic base of the
HO model was the set of non-H alleles in the population. Estimates of additive genetic variances were
similar in the BTBI (327,544 kg2 for MY and 237 kg2 for
FY) and the HO model (335,235 kg2 for MY and 250 kg2 for
FY). Environmental variance estimates
were also similar for MY and FY in these two models. Thus, heritability estimates were almost identical in the BTBI
(0.45 for MY and 0.24 for FY) and the HO model (0.46 for MY and 0.25 for FY). The close similarity of heritability
estimates between the BTBI and the HO model probably occurred because the breed
composition of the base genetic groups for these two models differed very
little. In fact, 88% of the alleles in
this data set were Bos taurus, and 91% of them were from Holstein. As expected, because of the small size of
the multibreed data set, standard errors were large for variances and
heritabilities, particularly for FY additive genetic variances and
heritabilities in both models.
Table 4. Additive genetic and environmental variance
components, and heritabilities for accumulated 305-d milk (MY) and fat yields
(FY) by the BTBI and the HO model
|
Parameters |
MY |
FY |
|
BTBI model |
|
|
|
Genetic variance (kg2) |
327,544 (132,380)1 |
237 (189) |
|
Environmental variance (kg2) |
393,429 (126,913) |
766 (184) |
|
Heritability |
0.45 (0.18) |
0.24 (0.18) |
|
HO model |
|
|
|
Genetic variance (kg2) |
335,235 (148,334) |
250 (195) |
|
Environmental variance (kg2) |
386,998 (134,842) |
747 (190) |
|
Heritability |
0.46 (0.19) |
0.25 (0.19) |
1 Standard error
The
heritability estimates for MY and FY obtained here were similar to others
obtained in tropical environments. Misra et al. (1979) reported MY heritability estimates of 0.48 for
Sahiwal, 0.36 for Red Sindhi, and 0.44 for Friesian ´ BI crossbreds in India. Heritability estimates for Holstein were 0.24 for MY and 0.20 for
FY in Australia (Visscher and Goddard, 1995), 0.28 for MY and 0.26 for FY in
New Zealand (Ahlborn and Dempfle, 1992), 0.25 for MY and 0.22 for FY in Brazil
(Costa et al., 2000), and 0.20 to 0.44 for MY and 0.18 to 0.42 for FY in USA
(Misztal et al., 1992; Dematawewa and Berger, 1998).
Heritability
estimates for MY and FY here were lower than those reported in other Thai
multibreed studies. Differences in the
multibreed field data sets used, editing procedures, and genetic evaluation
models are likely to account for a large portion of these different
estimates. Kanloung et al.
(1999) computed heritability estimates of 0.53 for MY and 0.50 for FY using a
model that considered amphur-year-season subclass as contemporary groups. Kuha (1999) obtained heritability estimates
of 0.55 for MY and was 0.58 for FY using a model that had only year and season
as main effects (i.e., no herds or amphurs), and no contemporary group
subclass. Both studies included a version
of Vinther’s (1974) BT subclass groups.
These two studies are likely to have overestimated the heritability
estimates for both MY and FY. Inclusion
of amphur as part of the definition of a contemporary group may lead to upward
biases in estimates of genetic variances as discussed earlier. Ignoring herds (or amphur) will increase the
likelihood and size of these biases.
Table 5 shows genetic covariances, and genetic,
environmental, and phenotypic correlations between MY and FY using the BTBI and
HO model. The estimated genetic
correlation between MY and FY was high (0.99) for both the BTBI and the HO
model. Estimates of environmental and
phenotypic correlations for MY and FY were also high and positive as additive
genetic correlations. Standard errors
for these correlation estimates were all
Table 5. Genetic covariances, and genetic,
environmental, and phenotypic correlations between accumulated 305-d milk (MY)
and fat yields (FY) for the BTBI and the HO models
|
Parameters |
BTBI model |
HO model |
|
Genetic covariances (kg2) |
8,751 (3,835)1 |
9,076 (5,291) |
|
Genetic correlation |
0.99 (0.09) |
0.99 (0.07) |
|
Environmental correlation |
0.89 (0.04) |
0.93 (0.04) |
|
Phenotypic correlation |
0.90 (0.01) |
0.90 (0.01) |
1 Standard error
low (0.01 to 0.09). High genetic correlations between MY and FY
have been reported in H (0.62 to 0.79; Misztal et al., 1992; Visscher and
Goddard, 1995; Dematawewa and Berger, 1998; Costa et al., 2000). These high genetic correlations between MY
and FY indicated that selection to improve one of these traits (MY or FY) would
also improve the other. They also
reflect the part-whole correlation that exist between MY and FY (FY=MY*Fat
percentage).
Regression Genetic
Group Effects
The
estimate of the MY regression additive genetic group effects was higher in the
BTBI model (149 ± 532 kg) than in the HO model (18 ± 363 kg). It
is unclear why there was such a large difference between the BTBI (149 kg) and
the HO (18 kg). However, these values
should be considered with caution because of their extremely large standard
errors. The small HO difference in MY
might be an indication that non-H alleles performed in similar fashion to H
alleles, but this needs to be reconfirmed with a substantially larger multibreed
data set.
The
estimates for FY regression additive genetic group effects were similar in both
models (BTBI: -26 ± 21; HO: -21 ± 14 kg), and had much smaller standard errors than those for MY. These regression values would suggest
superiority for FY of the Bos indicus breeds represented in this
multibreed population.
Additive Genetic
Predictions
The number and breed composition of sires and dams
represented in the multibreed data set was substantially different. Sires represented only 16% of the evaluated
animals in the data set. Most sires
were straightbred H (91%), whereas the majority of dams (88%) were crossbred
with a high H fraction (5/8 H and higher).
Because of these differences, ranges and figures of EBV were constructed
for both sires and dams.
Table 6 shows the range of EBV for sires, dams, and for
all evaluated animals in the Thai data set.
The range of EBV values for MY was smaller for sires than for dams in
both the BTBI (-567 kg to 1,009 kg for sires, and -1,394 kg to 1,298 kg for
dams) and the HO (-638 kg to 888 kg for sires, and –1,564 kg to 1,248 kg for
dams) models. The same pattern occurred
for FY. The larger range of EBV values
in dams may be a reflection of their larger variability in breed composition as
well as their lower accuracies of genetic predictions compared to those of
sires.
The distribution of EBV for sires and dams by models
(BTBI and HO) is presented in Figure 1 for MY and in Figure 2 for FY. Sires and dams were ordered by EBV value
within BT fraction (BTBI model) and H fraction (HO model). These figures provide a clear depiction of
the predicted additive genetic ability of sires and dams of different breed
composition. Of particular
Table 6. Range of expected breeding values (EBV) for
accumulated 305-d milk (MY) and fat yields (FY) by the BTBI and HO model for
sires and dams
|
Range of EBV (kg) |
BTBI model |
HO model |
|
MY sires |
-567 (332)1 to 1,009 (572) |
-638 (333) to 888 (579) |
|
FY sires |
–45 (9) to –3 (15) |
–39 (9) to 7 (16) |
|
MY dams |
-1,394 (389) to 1,289 (572) |
-1,564 (391) to 1,248 (579) |
|
FY dams |
-67 (11) to 7 (15) |
-65 (10) to 22 (16) |
|
MY all animals |
-1,394 (331) to 1,289 (572) |
-1,564 (333) to 1,248 (579) |
|
FY all animals |
-67 (9) to 7 (15) |
-65 (9) to 22 (16) |
1 Standard error
interest is the comparison
of the additive genetic ability of straightbred or crossbred animals of high H
fraction (7/8 H or 224/256 in the figures) with crossbred animals of H fraction
below 7/8H (i.e., below 224/256 in the figures). The figures clearly show that in this Thai multibreed population
there were animals of high and low EBV across all fractions of BT (BTBI model)
or H (HO model). In fact, the lowest
dam EBV for MY and FY occurred in dams that were 100% H, and the highest dam
EBV were crossbred.




Figure 1. Milk yield (MY) EBV for sires and dams
ordered by EBV within BT (BTBI model) and H (HO model) fraction
Sire EBV showed a similar
pattern for MY and FY (the high FY EBV sires with no H fraction were from three
Jersey sires used between 1992 and 1994).
This pattern of EBV suggests that, under the environmental conditions of
the animals in this multibreed data set, crossbred animals of various BT or H
fractions were as good or better than straightbred H for MY and FY. Purebred BT animals from temperate breeds
like H are known to be less adapted than BT ´ BI crossbred animals in tropical environments. Tropical parasites and insects in Thailand
will cause BT cattle to loose weight and to decrease milk production (Madsen
and Vinther, 1975; Trisanarom et al., 1990; Markvichitr et al., 1995). These known BT adaptability concerns and the
EBV obtained here suggest that BT and H crossbred sires and dams should
continue to be used as the main source of breeding animals for this
population. Thus, straightbred H should
be considered only in herds capable of providing the demanding nutritional,
management, and environmental conditions necessary for the expression of their
MY and FY genetic potential.




Figure 2. Fat yield (FY) EBV for sires and dams
ordered by EBV within BT (BTBI model) and H (HO model) fraction
The additive group regression models used here
provided a reasonable approximation to the underlying set of genetic
effects. Their main drawback was that
they ignored nonadditive genetic effects (group and random), particularly
nonadditive interbreed. However, most
dams in this data set were 75% H or higher and most males were 100% H, thus the
expected fraction of interbreed nonadditive genetic effects was small (25% in
most matings). Thus, group interbreed
nonadditive genetic effect may be large, and ignoring even a small fraction may
cause biases in additive genetic predictions.
Further, ignoring random interbreed nonadditive genetic effects will
increase the size of the standard errors of prediction of additive genetic
evaluations. These two aspects need to
be addressed in future studies, particularly because of the continued use of
crossbred BT ´ BI sires in Thailand. Mating of BT ´ BI crossbred sires (e.g.
50% , 75% BT) to non-BT and BT ´ BI crossbred dams will
guarantee the existence of a substantial number of animals with BT fractions
lower than 50% in Thai dairy cattle populations. Multibreed genetic models that include additive and nonadditive
genetic effects (Elzo, 1983; Elzo and Famula, 1985) will need to be used to
account for both additive and nonadditive genetic effects in such multibreed
populations. The estimates of variance
and covariance components and the genetic evaluations obtained here will serve
as a comparison base for more complex future multibreed genetic evaluation
models and procedures in Thailand.