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* Department of Animal Production, School of Veterinary Medicine, Box 393, Aristotle University of Thessaloniki, GR-54124 Thessaloniki, Greece
Sustainable Livestock Systems Group, Scottish Agricultural College, Bush Estate, Penicuik, Midlothian, EH26 0PH, United Kingdom
School of Biological Sciences, University of Edinburgh, Ashworth Laboratories, Kings Buildings, Edinburgh, EH9 3JT, United Kingdom
1 Corresponding author: banos{at}vet.auth.gr
| ABSTRACT |
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Key Words: maternal effects fertility body condition score milk
| INTRODUCTION |
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The impact of prenatal maternal effects on postnatal development and adult life of the offspring has not been documented as well as that of postnatal nursing environment (Rutledge et al., 1972; Rhees et al., 1999). Pre-natal uterine environment has been shown to have an effect on murine growth, mature size, and morphology (Cowley et al., 1989; Rhees et al., 1999). Barker (1992) speculated that nutrition of the fetus in early gestation may influence its fitness as an adult. In the Netherlands, during the winter of 19441945, humans were subjected to starvation rations and subsequent offspring were found to be at increased risk of coronary heart disease depending on the stage of their mothers pregnancy when restricted nutrition had been imposed (Roseboom et al., 2000). In sheep, the nutritional state of the ewe during gestation seems to have an impact on the offsprings future reproductive performance (Gunn et al., 1995; Borwick et al., 1997). For a review of the intergenerational effects of fetal programming, see Drake and Walker (2004).
In dairy cattle, calves are removed from their dams immediately after calving; hence, any maternal effect on the calf would be a combination of prenatal uterine environment and cytoplasmic inheritance. Maternal lineage, implying cytoplasmic (mitochondrial genetic) effects, may account for a small but significant proportion of the variation in future offspring milk production (Schutz et al., 1992; Albuquerque et al., 1998). Jamrozik et al. (2005) reported sizeable proportions of the total variation in reproduction and fertility traits of Canadian Holsteins being due to overall maternal effects. Small but significant maternal effects on Norwegian heifer performance were reported by A.-Ranberg et al. (2003).
Very few studies have been conducted on the effect of the prenatal uterine environment on adult traits of the calf. Pryce et al. (2002) investigated the effect of maternal diet during gestation on heifer fertility but found no significant associations. However, this was attributed mainly to the lack of sizeable variation in the nutritional status of the pregnant cows raised on the research farm where that study was conducted.
A pregnant cows capacity to care for her embryo is largely determined by the way she partitions nutrients to support fetal development together with her own growth, maintenance, and milk production. Although the energy requirements of a developing embryo at the blastocyst stage may be very small, the maternal uterine environment of a high-yielding cow may create an effect on her offspring via hormonal or other routes that are detectable in the offsprings own life through a number of traits such as milk production, disease resistance, survival, BCS, body energy, and fertility. Conceptually, a dams own energy level may be deduced from her BCS, milk production, and age at calving. These can be viewed as indicators of maternal environment during gestation. For example, BCS is associated with the amount of energy available to sustain growth, production, and fetal development. Milk yield is the main competitor of the fetus for nutrients and energy. Age at calving manifests the state of development of the dam during gestation regarding her own growth. Fuerst-Waltl et al. (2004) reported a significant association of age of the dam with milk production and longevity of the offspring.
The objectives of this study were a) to investigate the impact of the dams age at calving, BCS and milk yield on offspring BCS, fertility, and milk production traits and b) to estimate the maternal variance component for these traits.
| MATERIALS AND METHODS |
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Age of Dam at Calving
Pairs of dams and daughters with validated fertility records were obtained from the UK national database used for fertility genetic evaluations. Daughters were from the first 2 recorded calvings of each dam. There were 13,703 first-calving records in which the average dam age was 27.4 mo (standard deviation = 3.25 mo). Based on its distribution, age at first calving was divided into 3 classes: 1823 mo (early first calvings), 2429 mo (intermediate first calvings), and 3036 mo (late first calvings). There were also 11,269 second-calving records with average dam age of 39.8 mo (standard deviation = 3.83 mo). In this case, age was divided into 4 classes: 3035 mo (early second calvings), 3641 mo (early-intermediate second calvings), 4246 mo (intermediate-late second calvings), and 4755 mo (late second calvings). The impact of age class of the dam on the daughter traits of interest was assessed with the use of the following model; separate analyses were conducted for first and second calvings:
![]() | [1] |
where Yijkm = the first-lactation record (BCS, CI, DFS, NINS, NR56, or MY3) of cow m (daughter) in herd-year of calving i that calved in month j whose dam was in age-class k; HYi = fixed effect of herd-year of calving interaction i, Mj = fixed effect of calving month j (j = 112), Ak = fixed effect of age-class of the dam k, a1 = regression (linear and quadratic) on age at calving of the cow (age), a2 = regression (linear) on percentage of North American Holstein genes of the cow (phol), a3 = regression (linear) on MY3 of the cow (mlkc, for Y = BCS or fertility), a4 = regression (linear and quadratic) on DIM of the cow (dim, for Y = BCS or MY3), a5 = regression (linear) on dam EBV for BCS (bcsd, first-calving analysis) or on dam BCS (bcsd, second-calving analysis), a6 = regression (linear) on dam MY3 (mlkd, for second-calving analysis only), cowm = random effect of cow m (including pedigree genetic relationships among animals), and eijkm = random residual term. Each trait was analyzed separately.
The effect of interest in model [1] was the age-class of the dam (A). Days-in-milk adjusted MY3 of the cow (daughter) was included in the analysis of BCS and fertility to assess the effect of dam age on these traits for constant milk yield. Body condition score and MY3 of the dam (each adjusted for DIM) were added to remove sources of biological variation that might have otherwise masked the age of the dam effect. Because such data were not available for first-calving analysis, the dam EBV for BCS was included as a proxy to her body condition prior to first calving. All other effects fitted in model [1] were as defined in the UK national genetic evaluation model for BCS and fertility traits (Wall et al., 2003a). Furthermore, possible genetic trends affecting the traits of analysis were accounted for by the inclusion of a cow genetic effect and pedigree information.
BCS of Dam During Gestation
Data for this exercise were the 11,269 second-calving records that were considered in the previous analysis. These included first-lactation BCS, CI, DFS, NINS, NR56, and MY3 records of dams and respective daughters from the dams second calvings.
Each cow in the data had a single BCS record. To predict BCS during lactation and gestation, individual cow BCS records were fitted in a random regression model including DIM-adjusted MY3 and DIM when BCS was recorded. The latter was modeled with a fourth-order Legendre polynomial for the fixed curve and a second-order Legendre polynomial for the random deviation of individual cows from the fixed curve. Different fixed curves were calculated for each of the 3 age at first calving classes: early (1823 mo), intermediate (2429 mo), and late (3036 mo) calvings. Cow solutions were obtained by adding the individual random effect to the corresponding fixed curve solution. This model allowed the prediction of adjusted cow BCS across a time trajectory, defined here as d 4 to 400 postpartum. A similar approach to analyzing single records per animal was proposed by Tsuruta et al. (2004). Cow solutions were subsequently de-regressed by first subtracting the appropriate fixed curve solution, then dividing by the estimated reliability and, finally, adding back the fixed curve solution (Wall et al., 2003b). For each cow, de-regressed BCS values corresponding to the last day of each month of gestation were kept.
The entire process was repeated with the analysis of individual cow BCS as single measures with a model including DIM-adjusted MY3, DIM when BCS was recorded, and cow (random). Cow solutions were de-regressed by dividing by their respective reliabilities.
The above exercise involved all cows in the data. Dams with offspring with records in the data set were matched to their own de-regressed BCS solutions. The effect of BCS of the dam on daughter performance was then assessed with the use of the following model:
![]() | [2] |
where Yijm = the first lactation record (BCS, CI, DFS, NINS, NR56, or MY3) of cow m (daughter) in herd-year of calving i that calved in month j, a5 = regression (linear) on BCS of the cow (bcsc, for Y = MY3 or fertility), a6 = regression (linear and quadratic) on de-regressed solutions for BCS of the dam (bscd); HYi, Mj, a1, a2, a3, a4, cowm, and eijm are defined as in model [1].
The regression of interest in model [2] was that of cow (daughter) trait on BCS of the dam (a6). The latter were de-regressed cow effect solutions either from the single measure analysis or for mo 1 to 9 of gestation from fitting a random regression model. In the latter case, 9 consecutive analyses took place for each trait.
In addition, changes in de-regressed dam BCS during gestation were considered as independent variables in model [2] to assess their effect on offspring performance. Changes were expressed either as differences of BCS on each gestation month (1 to 9) from BCS on the day of conception or as regressions of monthly BCS on time. The latter represents the average estimated BCS change during gestation. When model [2] included a BCS change effect, dam BCS level corresponding to day of conception was also fitted. Thus, the effect of BCS change during gestation was assessed for constant BCS level at the onset of gestation.
Body condition score (adjusted for DIM) of the cow (daughter) was included in the analysis of MY3 and fertility to account for the additive genetic BCS effect the dam directly transmits to her daughter and the additive genetic correlation among traits. Hence, the marginal effect estimated for BCS of the dam would describe the noninherited maternal uterine effect associated with her energy level during gestation. In the analysis of BCS of the cow, the effect of BCS of the dam would be a combination of additive genetic and prenatal maternal components.
Milk Yield of Dam During Lactation
For the purposes of this exercise, permanent environment solutions for all cows were obtained from the official UK national genetic evaluation for milk yield. The latter is calculated with a random regression model analysis of repeated test-day records of the first 3 lactations (Mrode et al., 2005). Permanent environment solutions for milk yield represent the noninherited proportion of variation during a cows lactation and were used here to describe maternal environment.
The permanent environment solutions for milk yield on the last day of each month of lactation were extracted for all cows with at least 10 test-day records in the official analysis that also had daughters with validated fertility data. These monthly dam permanent environment solutions were then matched with their daughters first-lactation BCS, fertility, and MY3 data. A total of 19,922 records was considered for this analysis. The effect of the dams permanent environment solution for milk yield on cow (daughter) BCS, fertility, and MY3 was assessed using the following model:
![]() | [3] |
where Yijlm = the first-lactation record (BCS, CI, DFS, NINS, NR56, or MY3) of cow m (daughter) in herd-year of calving i that calved in month j, lcdl = fixed effect of lth lactation of the dam leading to the birth of cow m (l = 1 to 3), a5 = linear regression on monthly permanent environment solution for milk yield in lth lactation of the dam (mlkd); HYi, Mj, a1, a2, a3, a4, cowm, and eijlm are defined as in model [1].
Monthly dam permanent environment solutions for milk yield were also matched with their daughters 305-d milk, fat, and protein yield records. A total of 43,395 records of 19,922 daughters in their first 3 lactations were considered for this analysis. The effect of the dam permanent environment solution for milk yield on daughter 305-d yield was assessed using the following model:
![]() | [4] |
where Yijklm = the record (305-d milk, fat, or protein yield) of cow m (daughter) in lactation k in herd-year of calving i that calved in month j, k = fixed effect of lactation of cow m (k = 1 to 3), pem = permanent environment associated with cow m; HYi, Mj, a1, a2, a5, lcdl, cowm, and eijklm are as defined in model [3].
The regression of interest in models [3] and [4] was that of cow (daughter) performance (BCS, fertility, MY3, or 305-d yield) on milk yield of the dam (a5). The latter were permanent environment solutions for milk yield of the dam, for mo 1 to 10 of her lactation. Their impact was assessed in 10 consecutive analyses for each trait. In the case of 305-d daughter yield, separate coefficients were calculated for each of the 3 daughter lactations. The estimated effects represented the noninherited maternal effect associated with milk production during the dams lactation. Because permanent environment solutions were available only for the first 305 d of lactation, the full gestation of the dam could not be modeled; therefore, associations with milk yield of the dam during gestation were not made.
Variance Due to the Dam
Data for this exercise were obtained from the UK national fertility database comprising first-lactation individual cow records on CI, DFS, NR56, NINS, BCS, and MY3, as described previously. Only dams with multiple daughters having validated fertility records were kept. This data structure ensures proper estimation of variance components including maternal effects (Maniatis and Pollott, 2003). A total of 19,623 cow records from 7,340 dams were analyzed.
The following model was used to estimate variance components:
![]() | [5] |
where Yijkm = the first-lactation record (BCS, CI, DFS, NINS, NR56, or MY3) of cow m (daughter) in herd-year of calving i that calved in month j, damk = the random genetic effect of the dam of cow (including genetic relationships among animals); HYi, Mj, a1, a2, a3, a4, cowm, and eijkm are defined as in model [1].
In model [5], cow represented the direct additive genetic effect and dam was the overall maternal genetic effect. The latter includes both prenatal uterine and cytoplasmic components and might be thought of as any maternal contribution beyond that of the nuclear genome. The percentage of total phenotypic variance accounted for by the maternal effect would determine its importance for the traits in question. Efforts to include a direct by maternal interaction effect were computationally unsuccessful.
| RESULTS AND DISCUSSION |
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The effect of maternal age at first and second calving on first-lactation daughter performance is shown in Tables 2
and 3
, respectively. In both cases, the solution of the first class (early calvings) was set to zero and the effects of the other class solutions were expressed as deviations from the first. All other fixed effects included in model [1], representing sources of systematic variation, were statistically significant (P < 0.05). Some first-calving data examples are presented here to illustrate the point. Regression coefficients for percentage of North American Holstein genes were 0.003 (±0.001), 0.092 (±0.006) kg, 0.171 (±0.051) d, 0.081 (±0.031) d, 0.002 (±0.001), and 0.0009 (±0.0004) for BCS, MY3, CI, DFS, NINS, and NR56, respectively. This suggests that an increase in the percentage of North American Holstein genes was associated with improved milk production but slightly compromised BCS and fertility. Similarly, the regression on cow MY3 that had been included in the analysis of BCS and fertility to ensure assessment of the effect of dam age for constant milk yield, was 0.012 (±0.002) for BCS, 0.560 (±0.085) d for CI, 0.412 (±0.045) d for DFS, 0.007 (±0.002) for NINS, and 0.003 (±0.001) for NR56.
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The significance of this result was corroborated by a side analysis of the same data using model [1], except that age of dam was now fitted as a linear and quadratic regression instead of a class variable. Significantly (P < 0.05) negative linear regressions were observed for BCS, NINS, and MY3, and positive for DFS and NR56. The quadratic regression was significant only for NINS and NR56.
A first-calving cow is frequently a growing cow (Coffey et al., 2006). Therefore, she requires nutrients for both maintenance and her own body development during first lactation. During the pregnancy period leading to this first calving, the fetus may face intense competition for nutrients from its mothers own metabolic needs. As a consequence, early-calving cows may produce calves with difficulties at conceiving as first-lactation cows, as manifested by the adverse impact on NINS and NR56. This is a marginal effect adjusted for the cows own age at calving. These cows seem to mature early, exhibiting the characteristics of high-producing Holsteins, but they can not conceive as easily as cows born to older first-calving dams.
The age of the dam at her second calving had a significant (P < 0.05) effect on all daughter traits except NR56 (Table 3
). Clear trends were observed for increasing CI, DFS, and NINS and decreasing MY3 with the age of the dam. In general, daughters from late-calving dams had longer intervals from calving to first service, meaning they delayed showing evident estrus by up to 8 d (9% of the mean) and needed as many as 7% more inseminations per conception; consequently, they had longer CI. In addition, they produced nearly 6% less MY3 than their early calving (3035 mo) counterparts. They also had lower BCS, although the effect was statistically significant (P < 0.05) only in the case of intermediate-late calvings (4246 mo).
Fitting age at second calving as a linear and quadratic regression instead of a class variable supported these findings as the linear regression was significantly (P < 0.05) negative (unfavorable) for BCS and MY3 and positive (unfavorable) for CI, DFS, and NINS. The quadratic regression was significant only for CI.
Second-calving Holsteins are usually animals that have completed their growth phase. As cows age, the frequency of chromosomal abnormalities increases, with consequences for the offsprings productive and reproductive life. Fuerst-Waltl et al. (2004) reported decreasing milk production, nonreturn rate, and longevity with maternal age in Austrian dual-purpose Simmental cows. Admittedly, their data spanned a wider range of ages, reaching a maximum of 16 yr compared with 4.5 yr in the present study. However, Simmentals mature later than Holsteins. Furthermore, the effect was evident even for early age classes in the Fuerst-Waltl et al. (2004) study; for a maternal age class of 4 to 5 yr, first-lactation ECM yield was reduced by approximately 1% (P < 0.01) and nonreturn rate decreased by 3% (P = 0.24) compared with a maternal age class of 2 to 3 yr (Fuerst-Waltl et al., 2004). No other similar studies on dairy cattle were found in the literature. Wang and vom Saal (2000) reported delayed puberty in mice born to older dams.
BCS of Dam During Gestation
The BCS of a pregnant cow is associated with the amount of energy available to her to sustain growth, maintenance, milk production, and fetal development. In this respect, a cows BCS level and change during gestation can be associated with the proportion of energy expended to cover the needs of the embryo, which can potentially affect the latters future performance as a milk-producing cow.
In the present study, the effect of dam BCS, derived from a single measure analysis, on first-lactation daughter performance is shown in Table 4
. All other fixed effects included in model [2] were statistically significant (P < 0.05). For example, regression coefficients for the percentage of North American Holstein genes were 0.007 (±0.003), 0.023 (±0.008) kg, 0.134 (±0.059) d, 0.039 (±0.020) d, 0.0036 (±0.0017), and 0.0007 (±0.0004) for BCS, MY3, CI, DFS, NINS, and NR56, respectively. Furthermore, the regression on cow MY3 was 0.046 (±0.004) for BCS, 0.591 (±0.139) d for CI, 0.291 (±0.071) d for DFS, 0.007 (±0.003) for NINS, and 0.0009 (±0.0004) for NR56. These effect solutions, which are based on the analysis of cow records from second dam calvings, were similar to those from model [1], as reported earlier, pertaining to cow records from the first calvings of their dams.
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The effect of BCS of the dam at different stages of gestation on daughter NINS, NR56, and MY3 is shown in Figure 1
. These 3 traits were significantly affected by the prenatal environment expressed by the overall body condition of the dam (Table 4
). Results presented in Figure 1
are from 10 separate analyses considering predicted dam BCS at the day of conception and then at 30-d intervals corresponding to the 9 mo of gestation. The effect was more pronounced during the second and third trimesters of gestation. This may be associated with critical phases in the development of the embryo. Thus, cows that maintain high BCS in mid to late gestation appear to produce offspring with improved fertility but slightly reduced test-day milk. The opposing signs for these effects are probably associated with the antagonistic relationship between milk yield and fertility. Furthermore, MY3 was evidently more affected by dam BCS during the last 2 mo of gestation (Figure 1
). The latter coincides with the cows dry period. It can be speculated that cows that build good body condition during this period are likely to have offspring more inclined to reserve energy for the benefit of body condition and fertility rather than expend it to produce milk.
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Milk Yield of Dam During Lactation
Impact on Daughter First-Lactation Traits.
Milk yield is the key competitor to the fetus for nutrients during gestation and may influence the latters development indirectly in early gestation, when fetal nutrient requirements are low, and then directly later in gestation when they are high.
The effect of milk yield of the dam, expressed here as monthly permanent environment solutions, on first-lactation daughter BCS, fertility, and MY3 was nonsignificant (P > 0.05) in all cases. This means that maternal effects (as measured by permanent environmental solutions for milk production) during a dams lactation do not have an impact on first-lactation performance of the offspring that was born during that lactation. In the present study, a cows lactation was defined by the first 305 d. This partially overlaps with her gestation (average number of days open in the data was 112) meaning that the full gestation could not be modeled. However, our results suggest that a maternal environment defined by high milk yield of the dam during conception and the early stages of gestation does not seem to affect future offsprings first-lactation BCS, fertility, and MY3.
In the first instance, permanent environment of the dam during any lactation (first, second, or third) leading to the birth of a particular offspring was considered. It could be argued, however, that animals are still growing during their first lactation, whereas in lactations 2 and 3 they are closer to mature size; therefore, animals might exhibit different behavior regarding partitioning of nutrients and energy in first vs. later lactations. To test this, the entire exercise was repeated considering maternal yield (permanent environment solutions) from the dams first lactation only; results (not shown), however, did not change. In all cases, the impact of maternal yield on first-lactation daughter BCS, fertility, and MY3 was nonsignificant (P > 0.05).
Impact on Daughter Yield in the First Three Lactations.
The overall effect of dam milk yield, expressed as monthly permanent environment solutions, on daughter 305-d yield in their first 3 lactations was significant (P < 0.05) in all cases. Figure 2
depicts the linear regressions of daughter 305-d yield on dam milk permanent environment per month of dams lactation, emanating from 10 consecutive analyses with model [4]. This effect is pooled across the daughters 3 lactations. In general, increasing maternal milk yield was associated with decreasing daughter yield; month 5 of lactation of the dam had the most pronounced effect (Figure 2
). However, although significant, this effect was practically negligible because it amounted to a maximum of 0.17, 0.23, and 0.22% of the average 305-d milk, fat, and protein yields, respectively.
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In general, our results suggest that a favorable maternal yield environment appears to have a very small (<0.3% of the mean) adverse effect on future daughter 305-d production. Because this definition of maternal yield does not include any genetic effects, it can be entirely associated with the maternal environment during lactation, which coincides with the time the offspring was conceived and in early gestation. Negative environmental correlations between dam and offspring performance are not uncommon in livestock (Bijma, 2006). Furthermore, they may often affect the estimation of additive genetic correlation between direct and maternal effects (Bijma, 2006). Although there are studies of the latter in dairy cattle (e.g., Schutz et al., 1992; Albuquerque et al., 1998), reports on nongenetic relationships are largely missing. Van Vleck and Bradford (1965) suggested that they are probably very small, supporting results from the present study. In beef cattle, antagonistic environmental associations between dam and offspring have been reported for some growth traits (Cantet et al., 1988; Dodenhoff et al., 1998).
In this exercise, the effect of milk yield of the dam was described by permanent environment solutions from the UK national genetic evaluation. Such solutions were available throughout the lactation of each cow. Therefore, it was possible to assess the impact of this effect at different stages of lactation. Temporary environmental effects specific to the time when a dam is bearing her offspring might also be important but were not considered in the present study.
Variance Due to the Dam
Table 5
shows the proportion of total phenotypic variance of first-lactation traits accounted for by direct additive and maternal genetic effects. The former, equivalent to narrow sense heritability, was 0.18 and 0.27 for BCS and MY3, respectively, whereas it ranged between 0.01 and 0.04 for the 4 fertility traits. All estimates were significantly greater than zero (P < 0.05) and consistent with those used in the UK national genetic evaluation for fertility (Wall et al., 2003a).
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Maternal genetic effects accounted for just 0.3% of the total variation of MY3 and it was nonsignificant (P = 0.10). This is lower than the 1.1% reported by Albuquerque et al. (1998) for 305-d lactation milk yield.
| CONCLUSIONS |
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Optimal first-calving age is between 24 and 29 mo. Ensuing progeny are then expected to have a better balance of production, BCS, and fertility profiles. On the other hand, calving at an earlier age would produce high-yielding offspring that may later experience difficulties in conceiving as first-lactation cows.
The interval between first and second calving should decrease. Offspring resulting from early second calvings would be associated with increased production and improved BCS and fertility.
A dams BCS during gestation has an impact on the calfs future performance. It is important to avoid BCS losses of the dam especially during the second and third trimester of gestation. Appropriate nutritional strategies at late lactation and the dry period become crucial factors in this respect.
Continuing selection for milk production may be linked to a slightly adverse cross-generational environmental effect, meaning that production of daughters of high-yielding dams can be compromised. However, the very small magnitude of this effect is not expected to seriously influence milk selection and genetic improvement programs.
Finally, maternal genetic effects seem to account for a significant proportion of the total phenotypic variance of calving interval and nonreturn rate. Including such effects in genetic evaluation models is recommended because it would improve variance partitioning and breeding value estimation.
| ACKNOWLEDGEMENTS |
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Received for publication December 4, 2006. Accepted for publication March 20, 2007.
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