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Estimation of additive and dominance genetic variances for - CGIL ...

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( )<br />

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

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