| Literature DB >> 34248929 |
Fernando Flores Cardoso1, Oswald Matika2, Appolinaire Djikeng3, Ntanganedzeni Mapholi4, Heather M Burrow5, Marcos Jun Iti Yokoo1, Gabriel Soares Campos1, Claudia Cristina Gulias-Gomes1, Valentina Riggio2,3, Ricardo Pong-Wong2, Bailey Engle6, Laercio Porto-Neto7, Azwihangwisi Maiwashe8, Ben J Hayes6.
Abstract
Ticks cause substantial production losses for beef and dairy cattle. Cattle resistance to ticks is one of the most important factors affecting tick control, but largely neglected due to the challenge of phenotyping. In this study, we evaluate the pooling of tick resistance phenotyped reference populations from multi-country beef cattle breeds to assess the possibility of improving host resistance through multi-trait genomic selection. Data consisted of tick counts or scores assessing the number of female ticks at least 4.5 mm length and derived from seven populations, with breed, country, number of records and genotyped/phenotyped animals being respectively: Angus (AN), Brazil, 2,263, 921/1,156, Hereford (HH), Brazil, 6,615, 1,910/2,802, Brangus (BN), Brazil, 2,441, 851/851, Braford (BO), Brazil, 9,523, 3,062/4,095, Tropical Composite (TC), Australia, 229, 229/229, Brahman (BR), Australia, 675, 675/675, and Nguni (NG), South Africa, 490, 490/490. All populations were genotyped using medium density Illumina SNP BeadChips and imputed to a common high-density panel of 332,468 markers. The mean linkage disequilibrium (LD) between adjacent SNPs varied from 0.24 to 0.37 across populations and so was sufficient to allow genomic breeding values (GEBV) prediction. Correlations of LD phase between breeds were higher between composites and their founder breeds (0.81 to 0.95) and lower between NG and the other breeds (0.27 and 0.35). There was wide range of estimated heritability (0.05 and 0.42) and genetic correlation (-0.01 and 0.87) for tick resistance across the studied populations, with the largest genetic correlation observed between BN and BO. Predictive ability was improved under the old-young validation for three of the seven populations using a multi-trait approach compared to a single trait within-population prediction, while whole and partial data GEBV correlations increased in all cases, with relative improvements ranging from 3% for BO to 64% for TC. Moreover, the multi-trait analysis was useful to correct typical over-dispersion of the GEBV. Results from this study indicate that a joint genomic evaluation of AN, HH, BN, BO and BR can be readily implemented to improve tick resistance of these populations using selection on GEBV. For NG and TC additional phenotyping will be required to obtain accurate GEBV.Entities:
Keywords: beef cattle; genomic selection; host resistance; ticks; tropical adaptation
Year: 2021 PMID: 34248929 PMCID: PMC8261042 DOI: 10.3389/fimmu.2021.620847
Source DB: PubMed Journal: Front Immunol ISSN: 1664-3224 Impact factor: 7.561
Tick resistance data according to population.
| Population | Country of origin | Phenotype available | Number of observations | Mean ± S.D. | Min | Max | Number of genotyped/phenotyped animals1 | Number of animals in validation set |
|---|---|---|---|---|---|---|---|---|
| Angus (AN) | Brazil | Log10 tick counts | 2,263 | 1.54 ± 0.46 | 0.00 | 2.49 | 921/1,156 | 344 |
| Hereford (HH) | Brazil | Log10 tick counts | 6,615 | 1.47 ± 0.50 | 0.00 | 2.78 | 1,910/2,802 | 684 |
| Brangus (BN) | Brazil | Loge tick counts | 2,441 | 4.32 ± 1.20 | 1.00 | 7.69 | 851/851 | 300 |
| Braford (BO) | Brazil | Log10 tick counts | 9,523 | 1.32 ± 0.43 | 0.00 | 2.72 | 3,062/4,095 | 1,267 |
| Trop.Comp. (TC) | Australia | Tick scores | 229 | 2.52 ± 0.93 | 0.00 | 5.00 | 229/229 | 74 |
| Brahman (BR) | Australia | Tick scores | 675 | 0.67 ± 0.74 | 0.00 | 4.00 | 675/675 | 216 |
| Nguni (NG) | South Africa | Averaged loge tick counts2 | 490 | 0.50 ± 0.17 | 0.02 | 0.95 | 490/490 | 157 |
1All genotyped animals had phenotype. 2Animal average solution from log transformed Tick counts.
Figure 1Dispersion of individuals according to the first and second principal components of the G matrix, colored by breed.
Figure 2Heatmap of linkage disequilibrium (r) between adjacent markers of the 332k SNP panel by breed and chromosome.
Average persistence of phase for adjacent markers (above the diagonal) and correlation of allele frequencies (below the diagonal) between different populations.
| Population | Angus | Hereford | Brangus | Braford | Tropical Composite | Brahman | Nguni |
|---|---|---|---|---|---|---|---|
| Angus | 0.81 | 0.81 | 0.77 | 0.81 | 0.63 | 0.27 | |
| Hereford | 0.72 | 0.87 | 0.95 | 0.87 | 0.69 | 0.28 | |
| Brangus | 0.77 | 0.60 | 0.92 | 0.88 | 0.82 | 0.31 | |
| Braford | 0.69 | 0.88 | 0.77 | 0.89 | 0.81 | 0.32 | |
| Tropical Composite | 0.67 | 0.69 | 0.76 | 0.81 | 0.83 | 0.32 | |
| Brahman | 0.21 | 0.15 | 0.60 | 0.54 | 0.55 | 0.35 | |
| Nguni | 0.48 | 0.43 | 0.66 | 0.64 | 0.67 | 0.67 |
Figure 3Heatmap of correlation of phase between adjacent markers among breeds and chromosomes (332k panel by chromosome).
Posterior mean and time series standard errors for genetic correlations (above diagonal) and heritabilities (diagonal) of tick resistance measures across different populations.
| Population | Angus | Hereford | Brangus | Braford | Tropical Composite | Brahman | Nguni |
|---|---|---|---|---|---|---|---|
| Angus | 0.27 ± 0.001 | 0.32 ± 0.03 | 0.65 ± 0.001 | 0.42 ± 0.03 | 0.15 ± 0.04 | 0.17 ± 0.03 | 0.17 ± 0.03 |
| Hereford | 0.05 ± 0.001 | 0.39 ± 0.01 | 0.35 ± 0.01 | 0.22 ± 0.04 | 0.01 ± 0.03 | 0.05 ± 0.06 | |
| Brangus | 0.21 ± 0.003 | 0.87 ± 0.01 | 0.32 ± 0.02 | 0.47 ± 0.01 | 0.29 ± 0.05 | ||
| Braford | 0.17 ± 0.001 | 0.48 ± 0.02 | 0.59 ± 0.01 | 0.14 ± 0.05 | |||
| Tropical Composite | 0.42 ± 0.01 | 0.28 ± 0.02 | -0.01 ± 0.05 | ||||
| Brahman | 0.39 ± 0.01 | 0.18 ± 0.03 | |||||
| Nguni | 0.37 ± 0.02 |
Predictive ability1 [r(y *,û )], regression coefficient (β) and correlation between genomic breeding values (û) predicted from whole (w) and partial2 (p) data using uni and multivariate ssGBLUP population analyses.
| Population |
|
|
| ||||||
|---|---|---|---|---|---|---|---|---|---|
|
|
|
|
|
|
|
|
|
| |
| Angus | 0.15 | 0.16 | 0.07 | 0.92 | 1.06 | 1.06 | 0.50 | 0.58 | 0.22 |
| Hereford | 0.05 | 0.05 | 0.04 | 0.99 | 1.01 | 0.65 | 0.56 | 0.58 | 0.40 |
| Brangus | 0.22 | 0.25 | 0.22 | 0.88 | 0.93 | 1.46 | 0.67 | 0.72 | 0.57 |
| Braford | 0.24 | 0.24 | 0.17 | 1.01 | 1.00 | 1.45 | 0.76 | 0.78 | 0.56 |
| Tropical Composite | -0.06 | 0.00 | 0.21 | 0.32 | 0.53 | 1.74 | 0.14 | 0.23 | 0.35 |
| Brahman | 0.13 | 0.13 | 0.20 | 0.77 | 0.83 | 1.44 | 0.57 | 0.64 | 0.43 |
| Nguni | 0.04 | 0.04 | -0.04 | 0.79 | 1.00 | -2.11 | 0.18 | 0.20 | -0.04 |
1Correlation between phenotypes adjusted for fixed and permanent environmental effects and ûp.
2Partial datasets derived by two strategies: old-young = excluding phenotypes of 1/3 younger animals as validation group; and other-pops = removing all phenotypes of the target population for validation.