Genetic parameters for various random regression models to describe total sperm cells per ejaculate over the reproductive lifetime of boars

Similar documents
Genetic Parameter Estimation for Milk Yield over Multiple Parities and Various Lengths of Lactation in Danish Jerseys by Random Regression Models

Simulation Study on Heterogeneous Variance Adjustment for Observations with Different Measurement Error Variance

Variance component estimates applying random regression models for test-day milk yield in Caracu heifers (Bos taurus Artiodactyla, Bovidae)

Covariance functions and random regression models for cow weight in beef cattle

Genetic parameters for female fertility in Nordic dairy cattle

Impact of Using Reduced Rank Random Regression Test-Day Model on Genetic Evaluation

Procedure 2 of Section 2 of ICAR Guidelines Computing of Accumulated Lactation Yield. Computing Lactation Yield

Evaluation of Autoregressive Covariance Structures for Test-Day Records of Holstein Cows: Estimates of Parameters

Contrasting Models for Lactation Curve Analysis

Estimates of genetic parameters for total milk yield over multiple ages in Brazilian Murrah buffaloes using different models

Chapter 19. Analysis of longitudinal data -Random Regression Analysis

Quantitative characters - exercises

Longitudinal random effects models for genetic analysis of binary data with application to mastitis in dairy cattle

Genetic Parameters for Stillbirth in the Netherlands

Reaction Norms for the Study of Genotype by Environment Interaction in Animal Breeding Rebecka Kolmodin

Lecture 32: Infinite-dimensional/Functionvalued. Functions and Random Regressions. Bruce Walsh lecture notes Synbreed course version 11 July 2013

RANDOM REGRESSION IN ANIMAL BREEDING

Solving Large Test-Day Models by Iteration on Data and Preconditioned Conjugate Gradient

Prediction of Future Milk Yield with Random Regression Model Using Test-day Records in Holstein Cows

Should genetic groups be fitted in BLUP evaluation? Practical answer for the French AI beef sire evaluation

Maternal Genetic Models

Animal Models. Sheep are scanned at maturity by ultrasound(us) to determine the amount of fat surrounding the muscle. A model (equation) might be

NONLINEAR VS. LINEAR REGRESSION MODELS IN LACTATION CURVE PREDICTION

Animal Model. 2. The association of alleles from the two parents is assumed to be at random.

Multiple random effects. Often there are several vectors of random effects. Covariance structure

Single and multitrait estimates of breeding values for survival using sire and animal models

Multiple-Trait Across-Country Evaluations Using Singular (Co)Variance Matrix and Random Regression Model

RESTRICTED M A X I M U M LIKELIHOOD TO E S T I M A T E GENETIC P A R A M E T E R S - IN PRACTICE

Models with multiple random effects: Repeated Measures and Maternal effects

INTRODUCTION TO ANIMAL BREEDING. Lecture Nr 4. The efficiency of selection The selection programmes

Distinctive aspects of non-parametric fitting

Repeated Records Animal Model

Summary INTRODUCTION. Running head : AI-REML FOR EQUAL DESIGN MATRICES. K. Meyer

Linear Models for the Prediction of Animal Breeding Values

Genotype by environment interaction for 450-day weight of Nelore cattle analyzed by reaction norm models

A MATHEMATICAL MODEL FOR THE LACTATION CURVE OF THE RABBIT DOES

Towards more uniform pig performance. Craig Lewis and Susanne Hermesch

Effects of inbreeding on milk production, fertility, and somatic cell count in Norwegian Red

Genetic relationships and trait comparisons between and within lines of local dual purpose cattle

Estimating Breeding Values

INTRODUCTION TO ANIMAL BREEDING. Lecture Nr 2. Genetics of quantitative (multifactorial) traits What is known about such traits How they are modeled

Contemporary Groups for Genetic Evaluations

The advantage of factorial mating under selection is uncovered by deterministically predicted rates of inbreeding

ASPECTS OF SELECTION FOR PERFORMANCE IN SEVERAL ENVIRONMENTS WITH HETEROGENEOUS VARIANCES

Lecture 9 Multi-Trait Models, Binary and Count Traits

Variance component estimation with longitudinal data: a simulation study with alternative methods

Comparison of computing properties of derivative and derivative-free algorithms in variance component estimation by REML.

INTRODUCTION TO ANIMAL BREEDING. Lecture Nr 3. The genetic evaluation (for a single trait) The Estimated Breeding Values (EBV) The accuracy of EBVs

Bayesian Estimates of Genetic Relationships between Growth Curve Parameters in Shall Sheep via Gibbs Sampling

LINEAR MODELS FOR THE PREDICTION OF ANIMAL BREEDING VALUES SECOND EDITION

Univariate and multivariate parameter estimates for milk production

Genetic assessment of fighting ability in Valdostana cattle breeds

MIXED MODELS THE GENERAL MIXED MODEL

Advances in methodology for random regression analyses

Genotyping strategy and reference population

Genetic Heterogeneity of Environmental Variance - estimation of variance components using Double Hierarchical Generalized Linear Models

Mixed-Model Estimation of genetic variances. Bruce Walsh lecture notes Uppsala EQG 2012 course version 28 Jan 2012

5. Best Linear Unbiased Prediction

Analysis of Longitudinal Data: Comparison between PROC GLM and PROC MIXED.

GENERALIZED LINEAR MIXED MODELS: AN APPLICATION

MULTIBREED ANIMAL EVALUATION AND ITS APPLICATION TO THE THAI ENVIRONMENT. Numbers of Sires. Multibreed Population. Numbers of Calves.

Bayes factor for testing between different structures of random genetic groups: A case study using weaning weight in Bruna dels Pirineus beef cattle

Heterogeneity of variances by herd production level and its effect on dairy cow and sire evaluation

Lecture 24: Multivariate Response: Changes in G. Bruce Walsh lecture notes Synbreed course version 10 July 2013

Alternative implementations of Monte Carlo EM algorithms for likelihood inferences

Lecture 6: Selection on Multiple Traits

3. Properties of the relationship matrix

Analysis of Longitudinal Data: Comparison Between PROC GLM and PROC MIXED. Maribeth Johnson Medical College of Georgia Augusta, GA

Short country report Czech Republic

Comparative Efficiency of Lactation Curve Models Using Irish Experimental Dairy Farms Data

Lecture 5: BLUP (Best Linear Unbiased Predictors) of genetic values. Bruce Walsh lecture notes Tucson Winter Institute 9-11 Jan 2013

Full conjugate analysis of normal multiple traits with missing records using a generalized inverted Wishart distribution

Wiley. Methods and Applications of Linear Models. Regression and the Analysis. of Variance. Third Edition. Ishpeming, Michigan RONALD R.

Supplementary File 3: Tutorial for ASReml-R. Tutorial 1 (ASReml-R) - Estimating the heritability of birth weight

Modification of negative eigenvalues to create positive definite matrices and approximation of standard errors of correlation estimates

G E INTERACTION USING JMP: AN OVERVIEW

STUDY ON DAYS OPEN IN A ROMANIAN BLACK AND WHITE COW POPULATION FROM HE WESTERN ROMANIA

Factor Analytic Models of Clustered Multivariate Data with Informative Censoring (refer to Dunson and Perreault, 2001, Biometrics 57, )

Brief Sketch of Solutions: Tutorial 3. 3) unit root tests

Heritability, Reliability of Genetic Evaluations and Response to Selection in Proportional Hazard Models

Multiple Trait Evaluation of Bulls for Calving Ease

Use of sparse matrix absorption in animal breeding

Step 2: Select Analyze, Mixed Models, and Linear.

Causal Graphical Models in Quantitative Genetics and Genomics

Estimating Variances and Covariances in a Non-stationary Multivariate Time Series Using the K-matrix

Contrasts for a within-species comparative method

Baes, C., Spring, P. Mattei, S., Sidler, X. Ampuero, S., Bee, G. Luther, H., Hofer, A.

Appendix from L. J. Revell, On the Analysis of Evolutionary Change along Single Branches in a Phylogeny

Multivariate Statistical Analysis

Genetic evaluation for large data sets by random regression models in Nellore cattle

This book is dedicated to Professor Dr G. K. Constantinescu, founder of the modern animal husbandry science in Romania, originator of the National

Czech J. Anim. Sci., 50, 2005 (4):

DS-GA 1002 Lecture notes 12 Fall Linear regression

MEXICAN SIMMENTAL-BRAHMAN GENETIC CHARACTERIZATION, GENETIC PARAMETERS AND GENETIC TRENDS

TIME SERIES ANALYSIS AND FORECASTING USING THE STATISTICAL MODEL ARIMA

of the 7 stations. In case the number of daily ozone maxima in a month is less than 15, the corresponding monthly mean was not computed, being treated

The concept of breeding value. Gene251/351 Lecture 5

The use of independent culling levels and selection index procedures in selecting future sires for artificial insemination

Paper Review: NONSTATIONARY COVARIANCE MODELS FOR GLOBAL DATA

Swine: Selection and Mating of Breeding Stock 1

Transcription:

Published December 8, 2014 Genetic parameters for various random regression models to describe total sperm cells per ejaculate over the reproductive lifetime of boars S. H. Oh,* M. T. See,* 1 T. E. Long, and J. M. Galvin 2 *North Carolina State University, Raleigh, NC 27695 and Smithfield Premium Genetics, Roanoke Rapids, NC 27870 ABSTRACT: The objective of this study was to model the variances and covariances of total sperm cells per ejaculate (TSC) over the reproductive lifetime of AI boars. Data from boars (n = 834) selected for AI were provided by Smithfield Premium Genetics. The total numbers of records and animals were 19,629 and 1,736, respectively. Parameters were estimated for TSC by age of boar classification with a random regression model using the Simplex method and DxMRR procedures. The model included breed, collector, and yearseason as fixed effects. Random effects were additive genetic, permanent environmental effect of boar, and residual. Observations were removed when the number of data at a given age of boar classification was <10 records. Preliminary evaluations showed the best fit with fifth-order polynomials, indicating that the best model would have fifth-order fixed regression and fifth- order random regressions for animal and permanent environmental effects. Random regression models were fitted to evaluate all combinations of first- through seventh-order polynomial covariance functions. Goodness of fit for the models was tested using Akaike s Information Criterion and the Schwarz Criterion. The maximum log likelihood value was observed for sixth-, fifth-, and seventh-order polynomials for fixed, additive genetic, and permanent environmental effects, respectively. However, the best fit as determined by Akaike s Information Criterion and the Schwarz Criterion was by fitting sixth-, fourth-, and seventh-order polynomials; and fourth-, second-, and seventh-order polynomials for fixed, additive genetic, and permanent environmental effects, respectively. Heritability estimates for TSC ranged from 0.27 to 0.48 across age of boar classifications. In addition, heritability for TSC tended to increase with age of boar classification. Key words: genetic parameter, pig, random regression, semen 2006 American Society of Animal Science. All rights reserved. J. Anim. Sci. 2006. 84:538 545 INTRODUCTION Artificial insemination plays an important role in animal breeding by allowing greater use of genetically superior sires. It has been shown that there is an opportunity for genetic improvement of male fertility traits (Brandt and Grandjot, 1998; Oh et al., 2006). However, the genetic control of semen traits in pigs has not been extensively studied. Moreover, total sperm cells per ejaculate (TSC) are longitudinal data, i.e., total sperm cells change over age. In previous studies, this type of data was analyzed by multiple trait methods, choosing the most important time points as separate traits. Because of the number of potential observations over a boar s lifetime, it would be difficult to analyze this type 1 Corresponding author: todd_see@ncsu.edu 2 Present address: Halifax Community College, 100 College Drive, Weldon, NC 27890. Received April 29, 2005. Accepted November 4, 2005. of data thoroughly because of computational limits. Semen data have also been analyzed similarly to growth curves, ignoring genetic effects (Morant and Gnanasakthy, 1989), or were considered simple repeated measurements, ignoring time dependency. In many cases, the assumption of a univariate repeated model is not appropriate, and a full multivariate model with the number of traits equal to the number of ages would result in a highly overparameterized analysis. Therefore, a model using the minimum number of traits is required (Meyer and Hill, 1997). Random regression models have been extensively applied to the test-day model analysis of milk yield of dairy cattle (Jamrozik and Schaeffer, 1997; Olori et al., 1999; Strabel and Misztal, 1999). Random regression models have also been fitted to weight data of pigs (Huisman et al., 2002). Random regression models provide a method for analyzing independent components of variation that reveal specific patterns of change over time. The objective of this study was to model the variances and covariances for TSC over the reproductive lifetime of AI boars. 538

Genetic parameters for total sperm cells 539 Table 1. Summary of data structure Number of records 19,629 Year 1998 26 1999 2,875 2000 10,733 2001 5,415 2002 580 Season Spring 5,972 Summer 4,505 Fall 4,080 Winter 5,072 Number of animals in pedigrees 1,736 Number of animals with records 834 Mean of total sperm cells ( 10 9 ) 111.69 SD 42.40 Data MATERIALS AND METHODS Total sperm cell records (n = 19,629) for 834 boars were provided by Smithfield Premium Genetics (Table 1). One thousand seven hundred thirty-six individuals were included in the pedigree file. Boars represented 3 breeds and were housed on 2 farms. Each farm was similar in the numbers of boars of each breed. These data were collected by thirty-four collectors over 5 yr with 4 seasons/yr. Data were collected on farm 1 from 1998 through 2002, and data were recorded on farm 2 only in 2000 and 2001. The TSC were determined by multiplying the total semen volume, measured as the weight of the ejaculate, by the sperm concentration, measured using a self-calibrating photometer. Observations were removed when the number of data at a given age of boar classification time point was <10 records or when the TSC were missing, 0, or <0 (Figure 1). Weights of ejaculates were measured from 1998 to 2002 with approximately one-half recorded in 2000. Data were distributed evenly across seasons (Table 1). Differences between boar collection date and birth date were used to provide each record with a fixed age of boar classification in weeks. When a boar had 2 observations during 1 wk of age, the record closest to the whole week was utilized. The average collection interval of boars was 9 d, and 75% of the records in this study had a collection interval between 6 to 8 d. Collections from boars with <6 dof rest accounted for 5% of the records. The coefficient of determination of regression analysis between the collection interval and the TSC was 0.0034; thus, no relationship between the collection interval and the TSC was assumed here. Figure 1. Number of total sperm cell records by age of boar.

540 Oh et al. Figure 2. Mean of total sperm cells by age of boar. Statistical Analysis Parameters were estimated for TSC by age of boar classification under a random regression model using DxMRR (Meyer, 1998). The model included breed, collector, and year-season as fixed effects and additive genetic effects, permanent environmental effect of boar, and residual as random effects. Random regression models were fitted to evaluate all combinations of firstthrough seventh-order polynomial covariance functions for the fixed effects of age of boar classification, additive genetic, and permanent environmental effects. This resulted in the evaluation of 343 models. Methods to reduce the order of orthogonal polynomials were studied using eigenvalues (Meyer and Hill, 1997; Schaeffer, 2000). However, the absolute standard is ambiguous, and the number of effective eigenvalues was different for every fitted model. Here, all combinations from first to seventh orders for fixed, additive genetic, and permanent environmental effects were analyzed. Goodness of fit for models was tested using Akaike s Information Criterion (AIC) and the Schwarz Criterion (SC): Table 2. Order of fit for fixed (k F ), additive genetic (k A ), and permanent environmental (k P ) effects, number of parameters (p), log likelihood (logl; 77,000), Akaike s Information Criterion (AIC; +154,300), Schwarz Criterion (SC; +154,000), and ranks of log likelihood, AIC, and SC Order of fit k F k A k P p logl Rank AIC Rank SC Rank 6 5 7 44 24.28 1 39.43 4 86.23 52 7 5 7 44 20.44 2 47.11 6 93.92 63 6 4 7 39 20.32 3 37.36 1 44.75 20 5 5 7 44 20.13 4 47.74 8 94.54 65 7 4 7 39 19.51 5 38.99 3 46.38 21 5 4 7 39 16.77 7 44.47 5 51.86 22 4 2 7 32 13.09 10 37.82 2 9.96 1 7 7 2 32 2.69 26 58.61 17 10.83 4 6 7 2 32 2.6 27 58.80 18 11.02 5 5 2 6 25 29.13 46 108.26 34 5.31 2 7 2 6 25 31.29 49 112.59 36 9.63 3

AIC = 2logL + 2 p and SC = 2logL + p log (N r[x]), where p is the number of parameters estimated, N is the sample size, and r(x) is the rank of the coefficient matrix of fixed effects (Meyer, 2001a). The general random regression model was: k F 1 y ij = F ij + n=0 k A 1 β n φ n (w ij )+ α in φ n (w ij ) n=0 k P 1 + δ in φ n (w ij )+ε ij, n=0 where y ij is record j from animal i, F ij is a set of fixed effects, w ij is the standardized ( 1 to 1) age at recording, φ n (w ij is Legendre polynomial of age n, β n represents the fixed regression coefficients that model the population mean, α in represents the random regression coefficients for additive genetic effects, δ in represents the random regression coefficients for permanent environmental effects, and ε ij represents random residuals. The corresponding orders of fit are denoted as k F,k A, and k P. In matrix notation, where y=xb+za+cp+e, y = vector of N observations measured on N D animals, b = vector of fixed effects (including F ij and β n ), a = vector of k A N A additive genetic random regression coefficients, p = vector of k P N D permanent environmental random regression coefficients, e = vector of N residuals, X, Z, and C = design matrices relating elements of y to elements of b, a, and p, respectively, and k A and k P = the order of fit for a and p and corresponding genetic and permanent environmental covariance function G A and E P. Genetic parameters for total sperm cells 541 The variance-covariance matrix of random effects was: a K A A 0 0 V p = 0 K P I 0, e 0 0 R where K A and K P are matrices of coefficients of covariance functions for additive genetic and permanent environmental effects. Matrix A is the numerator relation- Figure 3. Log likelihood, Akaike s Information Criterion (AIC), and the Schwarz Criterion (SC) values by polynomial order of additive genetic effects and polynomial order of permanent environmental (PE) effects. ship matrix, and is an identity matrix. It is assumed that the residuals have a mean of zero and a common variance (σ 2 e).

542 Oh et al. Table 3. Estimates of variances (diagonal), covariances (below diagonal), and correlations (above diagonal) between random regression coefficients and eigenvalues (λ) of the coefficient matrix for models with order of fit of 6, 5, 7; 6, 4, 7; and 4, 2, 7 for fixed, additive genetic, and permanent environmental effects, respectively Order of random regression coefficients 0 1 2 3 4 5 6 λ Additive genetic effect Permanent environmental effect Additive genetic effect Permanent environmental effect Additive genetic effect Permanent environmental effect 747.06 0.48 0.39 0.43 0.64 790.34 113.51 76.14 0.18 0.33 0.37 74.13 70.57 10.45 42.85 0.99 0.29 65.62 75.85 18.60 41.34 40.96 0.20 0.05 84.26 15.46 9.23 6.28 23.13 0.00 361.50 0.23 0.27 0.57 0.36 0.22 0.13 1,194.38 53.91 150.43 0.09 0.03 0.27 0.21 0.05 25.55 38.36 8.59 58.02 0.44 0.61 0.77 0.77 0.00 159.76 4.43 48.81 215.71 0.86 0.82 0.58 154.42 131.94 62.24 88.29 241.18 362.71 0.97 0.64 382.42 94.88 58.13 131.22 270.79 413.82 501.11 0.78 0.01 33.44 8.57 77.69 113.49 161.31 229.73 174.91 67.62 889.06 0.76 0.01 0.00 937.22 202.94 79.33 0.64 0.64 115.93 1.01 31.72 30.94 1.00 0.00 0.29 42.06 40.82 53.86 0.04 314.74 0.15 0.04 0.71 0.45 0.39 0.30 1,381.52 30.38 127.84 0.27 0.28 0.05 0.01 0.20 296.03 7.33 29.92 97.94 0.61 0.72 0.83 0.83 159.65 204.34 51.51 99.02 265.60 0.90 0.87 0.63 0.00 156.03 12.12 140.64 289.81 389.20 0.97 0.62 0.00 160.85 2.37 192.17 332.51 448.67 546.20 0.78 0.00 70.14 29.38 107.16 133.47 160.16 237.95 171.30 75.62 768.06 0.49 795.322 137.47 102.21 74.9486 347.64 0.20 0.61 0.43 0.21 0.13 0.10 857.88 51.66 186.71 0.16 0.32 0.44 0.59 0.24 98.80 91.60 17.38 65.33 0.09 0.12 0.00 0.26 0.00 92.60 51.60 8.58 135.90 0.69 0.58 0.40 12.29 63.62 97.77 16.13 131.79 266.07 0.88 0.52 394.76 49.75 163.44 0.03 137.61 293.47 415.91 0.75 145.25 22.50 39.96 26.24 56.89 103.87 188.48 152.84 61.42 RESULTS AND DISCUSSION The mean and standard deviation of TSC were 111.69 10 9 and 42.40, respectively. The average TSC increased linearly with age. However, fluctuations were observed after approximately 140 wk of age because of decreasing numbers of records. Standard deviations of the average TSC were consistent over time (Figure 2). The random regression model that fitted k F =6,k A = 5, and k P = 7 coefficients for fixed, additive genetic, and permanent environmental effects showed the largest log likelihood value. This model was the fourth bestfitting model based on AIC and the 52nd best-fitting model based on SC. Generally, log likelihood value will increase as the number of parameters in the model increases. Therefore, log likelihood values are less conservative than AIC and SC values, which are weighted by the number of parameters estimated in the model (Table 2). The SC is stricter than AIC. The AIC showed the best fit when k F =6,k A = 4, and k P = 7, and this was the third best-fitting model based on log likelihood and 20th best-fitting model based on SC. The SC showed the best fit when k F =4,k A = 2, and k P = 7, and this model was ranked the 10th best-fitting model by log likelihood and second best-fitting model by AIC. Considering the conservative nature of SC and the relative ranking by AIC, this model may be the best based on overall fit. Log likelihood, AIC, and SC values (Figure 3) for all combinations of k A and k P showed a similar pattern in that their values tended to decrease as the order of the orthogonal polynomials increased. However, second-

Genetic parameters for total sperm cells 543 Figure 4. Heritability estimates of total sperm cells by age of boar. and third-order orthogonal polynomials for additive genetic had the lowest AIC and SC values and, hence, the best fit. Additive genetic and permanent environmental effects and eigenvalues for the 3 best-fitting models are shown in Table 3. Based on the number of nonzero eigenvalues (λ) or eigenvalues relatively closer to zero, 1) the model with k F =6,k A = 5, and k P = 7 could be reduced to 1 with k A = 3 and k P = 5; 2) the model with k F =6,k A = 4, and k P = 7 could be reduced to k A =2 and k P = 4; and 3) the model with k F =4,k A =2,and k P = 7 could be reduced to k A = 2 and k P =6.The methods to reduce the orders of orthogonal polynomials were studied using eigenvalues (Meyer and Hill, 1997; Schaeffer, 2000). However, the absolute standard is ambiguous, and the number of effective eigenvalues was different in every result for each model fitted. This makes it difficult to determine the optimum order of orthogonal polynomials for the models studied here. Heritability estimates over week of age are presented in Figure 4. These values are the means and standard deviations of heritability at each week from all 343 model combinations of first- to seventh-order orthogonal polynomials. Heritability estimates for TSC ranged from 0.27 to 0.48. These values strongly agreed with the estimate of repeatability for this trait (0.37) reported previously by Oh et al. (2006). Standard deviations tended to decrease from 33 wk of age to about 45 wk, maintained consistent intervals until 100 wk of age, and then increased rapidly. Heritability of TSC tended to increase as boars grew older (Figure 4). Huisman et al. (2002) reported a similar increase in heritability estimates in an evaluation of pig BW. Heritability estimates for TSC here were similar to those reported in the literature. Masek et al. (1977) estimated a repeatability of 0.24 using a 2-factorial hierarchical analysis of variance. Du Mesnil du Buisson et al. (1978) reported that the heritability for the number of spermatozoa produced per ejaculate under comparable collection rate conditions was 0.35. Huang and Johnson (1996) estimated repeatability of total number of sperm as 0.26 for 3 collections/wk and 0.16 for daily collections. Brandt and Grandjot (1998) reported a heritability of 0.24 and a repeatability of 0.46 for number of sperm cells. Three-dimensional graphs (Figure 5) showed similar trends for covariance components for models with 1) k F =6,k A = 5, and k P =7;2)k F =6,k A = 4, and k P = 7; and 3) k F =4,k A = 2, and k P = 7. Genetic variances tended to increase with age for each model. Additive genetic covariance estimates between ages decreased as the interval between ages increased. This was in contrast to permanent environmental and phenotypic variances that were relatively consistent over age of boar, and it was linked to the increase in heritability estimates. Graphs of permanent environmental effects for each model were similar, although values differed. Sudden increases in permanent environmental variances and covariances after 140 wk of age may be due to the limited amount of data for those ages. Graphs of phenotypic covariances were similar to those observed for permanent environmental covariances. Residuals were assumed to be homogeneous across ages of boar. However, Meyer (2001b) and Lidauer and Mäntysaari (2001) suggested adjustments be made for heterogeneous residual variances. Genetic correlations, such as genetic covariances, were high between adjacent ages and decreased as the interval between ages increased. The polynomial of order k F =6,k A = 4, and k P = 7 showed the highest genetic correlations even between distant ages. Genetic correlations ranging from 0.4 to 0.5 from the model with

Figure 5. (Co)variance components between ages with different polynomial order of fits for fixed, additive genetic, and permanent environmental effects, respectively. 544 Oh et al.

Genetic parameters for total sperm cells 545 polynomials of order k F =4,k A = 2, and k P = 7 decreased as the intervals of ages increased. These results indicate that later performance may be harder to predict accurately from records at an early age. IMPLICATIONS Genetic variance of total sperm cells per ejaculate increased during the productive life of the boar, resulting in heritability estimates increasing from 0.27 to 0.48. Genetic correlations between total sperm cells per ejaculate at different ages were larger for adjacent ages. Random regression models with comparatively high-order polynomials for fixed, additive genetic, and permanent environmental effects provided the best fit. LITERATURE CITED Brandt, H., and G. Grandjot. 1998. Genetic and environmental effects on male fertility of AI boars. Proc. 6th World Cong. Genet. Appl. Livest. Prod. 23:527 530. Du Mesnil du Buisson, F., M. Paquignon, and M. Courot. 1978. Boar sperm production: Use in artificial insemination A review. Livest. Prod. Sci. 5:293 302. Huang, Y. T., and R. K. Johnson. 1996. Effect of selection for size of testes in boars on semen and testis traits. J. Anim. Sci. 74:750 760. Huisman, A. E., R. F. Veerkamp, and J. A. M. van Arendonk. 2002. Genetic parameters for various random regression models to describe the weight data of pigs. J. Anim. Sci. 80:575 582. Jamrozik, J., and L. R. Schaeffer. 1997. Estimates of genetic parameters for a test day model with random regressions for yield traits of first lactation Holsteins. J. Dairy Sci. 80:762 770. Lidauer, M., and E. Mäntysaari. 2001. A multiplicative random regression model for test-day data with heterogeneous variance. Proc. 2001 Interbull Meeting, Budapest, Hungary. Bulletin 27:167 171. Masek, N., J. Kuciel, J. Masek, and L. Maca. 1977. Genetical analysis of indicators for evaluating boar ejaculates. Acta Universitatis Agriculturae. Facultas Agronomica, Brno. 25:133 139. Meyer, K. 1998. DXMRR A program to estimate covariance functions for longitudinal data by restricted maximum likelihood. Proc. 6th World Cong. Genet. Appl. Livest. Prod. 27:465 466. Meyer, K. 2001a. Estimates of direct and maternal covariance functions for growth of Australian beef calves from birth to weaning. Genet. Sel. Evol. 33:487 514. Meyer, K. 2001b. Estimating genetic covariance functions assuming a parametric correlation structure for environmental effects. Genet. Sel. Evol. 33:557 585. Meyer, K., and W. G. Hill. 1997. Estimation of genetic and phenotypic covariance functions for longitudinal or repeated records by restricted maximum likelihood. Livest. Prod. Sci. 47:185 200. Morant, S. V., and A. Gnanasakthy. 1989. A new approach to the mathematical formulation of lactation curves. Anim. Prod. 49:151 162. Oh, S.-H., M. T. See, T. E. Long, and J. M. Galvin. 2006. Estimates of genetic correlations between production and semen traits in boar. Asian-Australasian J. Anim. Sci. Olori, V. E., W. G. Hill, B. J. McGuirk, and S. Brotherstone. 1999. Estimating variance components for test day milk records by restricted maximum likelihood with a random regression animal model. Livest. Prod. Sci. 61:53 63. Schaeffer, L. R. 2000. Random regression models. Lecture notes. Available: http://www.aps.uoguelph.ca/ lrs/ansc637/lrs14/ Accessed Oct. 31, 2005. Strabel, T., and I. Misztal. 1999. Genetic parameters for first and second lactation milk yields of Polish Black and White Cattle with random regression test-day models. J. Dairy Sci. 82:2805 2810.