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1766<br />

Generally, mixed linear models of best linear unbiased prediction<br />

(BLUP) in an animal model (AM) are used, and a pedigree of three<br />

or more generations of ancestors is taken into account according<br />

to the model equation:<br />

Y = Xb + Zu + e (1)<br />

where Y is the vector of measured performances, X and Z are<br />

known matrices that relate performance to the systematic effects<br />

of the breeding environment and the animals, b and u are the<br />

estimated vectors of fixed systematic environmental effects and<br />

the random effects of an animal (BV) with the additive numerator<br />

relationship matrix (A), and e is the vector of random error.<br />

Using this model equation, a system of normal equations is<br />

constructed in which the unknown constants (b) and(u) are<br />

estimated. These systems of equations are vast, and special<br />

algorithms are required for their solution. 12<br />

Most of the variability in any measured production trait is<br />

caused by systematic environmental effects. The influence of<br />

the herd–year–season, or herd–test-day, which identifies a<br />

contemporary group of animals kept under the same conditions,<br />

is usually the most important factor.<br />

Evaluations are generally oriented to the MT-AM (multi-trait<br />

animal model), RR-TDAM (random regression test-day animal<br />

model), AM-maternal, and nonlinear methodologies for survival<br />

(kit) analysis. 13–23<br />

It is important to find a method of evaluation that minimises<br />

residual error and simultaneously considers all of the effects that<br />

may influence the performance variable being measured. From<br />

a genetic perspective, it is important to ask: What proportion<br />

of variability is explained by the statistical model used? Is this<br />

proportion different in a model that does not account for genetic<br />

effects? Is this model the best (optimal) of all the possibilities<br />

tested? The proportion of variability explained by the statistical<br />

model used (R 2 ) and other information criteria for testing the<br />

suitability of the model, such as Akaike’s information criterion<br />

(AIC), Bayes information criterion (BIC), Bayes factor (BF) and the<br />

likelihood ratio test (LRT), are very important in answering these<br />

questions. 24–28<br />

Molecular-genetic information can be used to improve selection<br />

programmes. 29 Animals are evaluated more accurately when their<br />

entire genetic value is partitioned into causal factors and withinfamily<br />

genetic components are exploited. The use of moleculargenetic<br />

markers in breeding is the inclusion of additional criteria in<br />

the selection indices. These markers increase selection differences<br />

relativetoexistingtraditionalbreedingprogrammesbydecreasing<br />

the correlation among sib individuals, increasing the accuracy of<br />

animal selection, allowing the utilisation of genetic variability<br />

that is usually included in non-utilisable residuum, and allowing<br />

a shortening of the generation interval (because they may be<br />

analysed in young animals). The use of selection markers is<br />

conditional upon the timely laboratory analysis of the entire<br />

subpopulation subjected to pre-selection (e.g., young bulls) and<br />

rapid application before the determined gene linkages change.<br />

This requires frequent updates of selection indices, as shown<br />

below (Eqn (2)). The consistent application of genomic selection<br />

markedly reduces the cost of a selection programme. 3,30<br />

However, data analysis becomes more complicated, the number<br />

of estimated parameters becomes higher, and a modified<br />

information criterion (mBIC) is necessary for the selection of a<br />

suitable model of evaluation. 31,32<br />

In order to select individuals for breeding, marker-assisted<br />

selection (MAS) may be applied if several genetic markers are to<br />

www.soci.org J Pribyl et al.<br />

be used. Alternatively, genomic selection utilises high numbers of<br />

markers that densely cover the whole genome. 3,33 BV is usually<br />

calculated in two steps. In the first step, the regression coefficients<br />

(v) (substitution effects of the alleles of a considered locus) are<br />

determined in a reference population with known performance<br />

and highly reliable BVs. This reference population usually includes<br />

only a part of the population under selection. From the first step,<br />

quantitative trait loci (QTL) effects are estimated. Subsequently,<br />

BV is determined for all of the young animals in the evaluated<br />

(sub)population by means of a selection index, as described in<br />

Eqn (2). 30<br />

The reference population and the evaluated population are<br />

separated by at least one generation. Therefore, the relationships<br />

between markers and QTLs determined in the older generation<br />

may not be fully applicable to the younger evaluated population,<br />

as the QTLs are not fully covered by study markers. Furthermore,<br />

the influences of selection, mutation, immigration of sires used<br />

intensively in artificial insemination, changes in environment, and<br />

the development of the commercial population under selection<br />

can also affect the applicability of QTL data across generations.<br />

Therefore, it is necessary to periodically redetermine u in Eqn (1),<br />

allele frequencies (q) in Eqn (5), their inherence in the genotypes<br />

of individual animals (T), and regression coefficients (v) in(3)so<br />

that the gap between the reference and the evaluated population<br />

will be as small as possible. 3,30,34<br />

The GEBV of a given trait is calculated based on known loci and<br />

remaining polygenes according to the selection index:<br />

GEBVj = k1 DGVj + k2u ∗ j<br />

where GEBVj is the genomic (total) BV for an individual (j)<br />

determined based on the genomic information at the locus (i)<br />

and remaining polygenic effect. DGVj is the direct genetic value,<br />

calculated as the sum of BVs for a particular loci:<br />

DGVj = �jTijvij<br />

where Tij (with regard to Eqn (9)) is the ith element in the jth row<br />

of the known incidence matrix correlating the genetic effects of<br />

particular alleles to the observed individual, vij is the vector of<br />

genetic marker effects, u ∗ j represents the BV calculated based on<br />

the remaining polygenes, and k1 and k2 are the weights of the<br />

information sources in the index. 35<br />

If the GEBV is calculated for young animals without their own<br />

production records, u ∗ j represents only information about their<br />

parents. In cases where a high density of genetic markers is<br />

available, the u ∗ j in Eqn (2) is frequently omitted.<br />

GENETICALLY CONDITIONED VARIABILITY<br />

OF PERFORMANCE<br />

Reliably determined population-genetic parameters are a precondition<br />

for genetic evaluation. We are usually interested in<br />

phenotype variability (σ 2 P), which can be separated into genetic<br />

additive (σ 2 A), genetic dominant (σ 2 D), genetic epistatic (σ 2 I), and<br />

unpredictable residual (σ 2 E) components, plus covariance caused<br />

by genotype/environment interaction (2σGE). 36 It is generally assumed<br />

that the genotype/environment interaction is negligible.<br />

Therefore:<br />

σ 2 P = σ 2 G + σ 2 E = σ 2 A + σ 2 D + σ 2 I + σ 2 E<br />

The additive effects that are accumulated over successive<br />

generations of selection are used in breeding. Nevertheless, other<br />

www.interscience.wiley.com/jsfa c○ 2010 Society of Chemical Industry J Sci Food Agric 2010; 90: 1765–1773<br />

(2)<br />

(3)<br />

(4)

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