Estimation of additive and dominance genetic variances for - CGIL ...
Estimation of additive and dominance genetic variances for - CGIL ...
Estimation of additive and dominance genetic variances for - CGIL ...
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M.J.R. Pante et al.rAquaculture 204 2002 383–392 387<br />
where s 2 is the <strong>additive</strong> <strong>genetic</strong> variance, s 2 is the <strong>dominance</strong> <strong>genetic</strong> variance, s 2<br />
a d c<br />
is the common environment variance, s 2 is the error variance, A is the <strong>additive</strong> <strong>genetic</strong><br />
e<br />
relationship matrix, D is the <strong>dominance</strong> <strong>genetic</strong> relationship matrix <strong>and</strong> I is an identity<br />
matrix. Note that parental <strong>dominance</strong> variance is one-quarter <strong>of</strong> the <strong>of</strong>fspring <strong>dominance</strong><br />
variance.<br />
Following the algorithm <strong>of</strong> Hoeschele <strong>and</strong> Van Raden Ž 1991 . , inbreeding was<br />
accounted <strong>for</strong> when inverting the A matrix but was ignored when inverting the D matrix.<br />
However, with low levels <strong>of</strong> inbreeding, including the individual inbreeding coefficients<br />
as a covariate in the model may be sufficient to account <strong>for</strong> ignoring inbreeding in<br />
<strong>for</strong>ming the inverse <strong>of</strong> the D relationship matrix Ž Hoeschele <strong>and</strong> Van Raden, 1991 . .<br />
Moreover, the covariance between the <strong>additive</strong> <strong>and</strong> <strong>dominance</strong> <strong>genetic</strong> effects was also<br />
ignored due to the large size <strong>of</strong> the data set.<br />
The estimated variance components were expressed as ratios <strong>of</strong> the total phenotypic<br />
Ž 2 . 2 2 2<br />
variance s <strong>for</strong> each model: the <strong>additive</strong> <strong>genetic</strong> variance ratio as h ss rs , i.e.<br />
t a t<br />
the heritability; the <strong>dominance</strong> <strong>genetic</strong> variance ratio as d 2 ss 2rs 2 d t ; <strong>and</strong> the common<br />
environmental variance ratio as c2 ss 2rs 2 c t .<br />
Log likelihood ratio tests were carried out among the six models to determine the<br />
most suitable <strong>of</strong> the six models. The likelihood ratio is LRsy2logwŽ rNz . rNz Ž .xs<br />
y2wlogŽ rNz . yŽlogŽ Nz .x, where logŽ Nz . is the maximum <strong>of</strong> the likelihood function <strong>for</strong><br />
the full model <strong>and</strong> logŽ rNz . is the maximum <strong>of</strong> the likelihood function <strong>for</strong> the reduced<br />
model subject to r number <strong>of</strong> constrained effects or parameters ŽLynch<br />
<strong>and</strong> Walsh,<br />
Table 3<br />
Ž 2 . Ž 2 . Ž 2 Estimates <strong>of</strong> <strong>additive</strong> h , <strong>dominance</strong> d , <strong>and</strong> common environmental c . <strong>variances</strong> expressed as ratio <strong>of</strong><br />
Ž . Ž 2 total phenotypic variance with their corresponding st<strong>and</strong>ard errors s.e. , <strong>and</strong> the residual variance s . e <strong>for</strong><br />
each <strong>of</strong> the model <strong>for</strong> the three populations <strong>of</strong> rainbow trout<br />
2 2 2 2<br />
Population Model h "s.e. d "s.e c "s.e. s e<br />
1 A 0.366"0.018 0.549<br />
Aq F 0.354"0.018 0.554<br />
AqCE 0.156"0.021 0.041"0.005 0.637<br />
AqCEq F 0.158"0.021 0.038"0.004 0.637<br />
Aq Dq F 0.162"0.023 0.144"0.005 0.635<br />
Aq DqCEq F 0.158"0.020 0.000"0.000 0.038"0.004 0.637<br />
2 A 0.365"0.019 0.559<br />
Aq F 0.344"0.018 0.570<br />
AqCE 0.087"0.018 0.062"0.006 0.681<br />
AqCEq F 0.089"0.017 0.055"0.005 0.681<br />
Aq Dq F 0.083"0.017 0.218"0.005 0.683<br />
Aq DqCEq F 0.082"0.017 0.161"0.013 0.014"0.013 0.684<br />
3 A 0.462"0.020 0.558<br />
Aq F 0.441"0.019 0.572<br />
AqCE 0.180"0.022 0.058"0.006 0.707<br />
AqCEq F 0.185"0.022 0.053"0.005 0.705<br />
Aq Dq F 0.167"0.022 0.216"0.005 0.713<br />
Aq DqCEq F 0.167"0.012 0.215"0.004 0.000"0.000 0.714