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Genetic parameters for economically important traits in yellowtail kingfis
Seriola lalandi
Paul Whatmore, Nguyen Hong Nguyen, Adam Miller, Rob Lamont,
Dan Powell, Trent D' Antignana, Erin Bubner, Abigail Elizur, Wayne Knibb
PII: S0044-8486(13)00111-7
DOI: doi: 10.1016/j.aquaculture.2013.03.002
Reference: AQUA 630583
To appear in: Aquaculture
Received date: 1 September 2012
Revised date: 27 February 2013
Accepted date: 3 March 2013
Please cite this article as: Whatmore, Paul, Nguyen, Nguyen Hong, Miller, Adam, Lam-
ont, Rob, Powell, Dan, D'
economically important traits in yellowtail kingfish Seriola lalandi, Aquaculture (2013),doi: 10.1016/j.aquaculture.2013.03.002
This is a PDF file of an unedited manuscript that has been accepted for publication.As a service to our customers we are providing this early version of the manuscript.The manuscript will undergo copyediting, typesetting, and review of the resulting proofbefore it is published in its final form. Please note that during the production processerrors may be discovered which could affect the content, and all legal disclaimers thatapply to the journal pertain.
Knibb, Wayne, Genetic parameters forAntignana, Trent, Bubner, Erin, Elizur, Abigail,
http://dx.doi.org/10.1016/j.aquaculture.2013.03.002http://dx.doi.org/10.1016/j.aquaculture.2013.03.002http://dx.doi.org/10.1016/j.aquaculture.2013.03.002 -
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Genetic parameters for economically important traits in yellowtail kingfish
Seriola lalandi
Paul Whatmorea,b, Nguyen Hong Nguyena, Adam Millerc, Rob Lamonta, Dan Powella, Trent
D'Antignanac, Erin Bubnerd, Abigail Elizura, Wayne Knibba*
aThe University of the Sunshine Coast, Maroochydore, Queensland 4558, Australia
bThe Australian Seafood Cooperative Research Centre.
cClean Seas Tuna Limited, 7 North Quay Boulevard, Port Lincoln, SA 5606, Australia.
dSchool of Biological Science, Lincoln Marine Science Centre, Flinders University, PO Box
2023, Port Lincoln, South Australia 5606, Australia
*Corresponding author: Tel: +61 7 5430 2831; e-mail: [email protected]
ABSTRACT
The aim of the present study was to estimate genetic parameters for body and carcass
traits, visual condition score, and deformity in yellowtail kingfish Seriola lalandi, an
emerging aquaculture species in Australia. These novel data and genetic parameters are
required to solve the problem of how to conduct efficient selection in this and related
species. Analyses were performed on a total of 400 data records collected from a yellowtail
kingfish breeding population at Cleanseas Tuna Ltd. farm. They were progeny of 22 full- and
half-sib families (eight sires and six dams). Six newly developed and four published
microsatellite markers were used to construct the pedigree. Genetic parameters were
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estimated using average information algorithm in ASReml with a multiple trait model. Fixed
effects included sex, seal bite and deformity status. Random effects were the additive
genetics of individual animal, and maternal and common environmental effects (i.e., dam-
tank effect arising from a short period of separate rearing of offspring that came from two
different broodstock tanks). The estimates of heritability for body and carcass traits were
moderate (h2 = 0.15 to 0.30, s.e. ranging from 0.09 to 0.19). Fillet fat content showed an
unusually high heritability (0.940.21) with a standard animal model, but was only moderate
(0.41 0.26) when tank and dam were included as random effects. The estimate for
condition score was 0.15 0.11, whereas the heritability for deformity was close to zero (h2
= 0.02). The genetic correlations between body and carcass (fillet weight and fillet yield)
traits were high and positive (0.57 to 0.94, s.e. 0.05 to 0.46). Genetic correlations between
body traits and condition score were moderate to high and positive (i.e. favourable). These
results suggest that selection for high growth would result in concomitant increase in fillet
weight, a carcass trait of paramount importance. It is concluded that there is substantial
potential for genetic improvement of economically important traits especially growth
performance and fillet weight in the current population of yellowtail kingfish.
Keywords: Seriola lalandi, kingfish; heritability; genetic correlation; fillet; fat content;
selection.
1. IntroductionThe yellowtail kingfish, Seriola lalandi, is an emerging aquaculture finfish species in
Australia, with a current production approaching four thousand tons at a value of 20 million
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dollars/year (Booth et al., 2010) although aquaculture production on Seriola species in Japan
is very large, accounting for most of Japans finfish aquaculture (Statistics Department,
Ministry of Agriculture, Forestry and Fisheries, Japan 2002). In South Australia, where the
majority of production occurs, it is the second most commercially valuable aquaculture
industry (Fernandes and Tanner, 2008). There is increasing demand for the species in both
domestic and export markets with culture technologies being well developed. Yellowtail
kingfish is a premium quality product and is marketed as whole live fish or fresh and frozen
fillets, cutlets and loins. In the Japanese sashimi market yellowtail kingfish is an extremely
valuable product after tuna. However, with steadily reducing catches and quotas for bluefin
tuna, the value and demand for yellowtail kingfish will continue to grow (Love and
Langenkamp, 2003). Up to the present, quantitative genetic basis of these traits are not
known in yellowtail kingfish and there are no reports on genetic associations between body
and carcass traits and flesh quality in this species. Genetic associations between
performance and fitness related traits (condition score and deformity) were also not
available in the literature for this species (Seriola lalandi). As yellowtail kingfish are group
spawners and produce small larvae (about 4mm at hatching), physical tagging of offspring is
unfeasible. DNA markers function as naturally occurring biological tags that can be used in
lieu of physical tags, with the added benefit of enabling other biological observations to be
made, such as management of genetic diversity and inbreeding of stocks (Frost et al., 2006).
The application of genetic markers for parentage allocation and pedigree reconstruction
have been practiced in other aquaculture species (e.g., Ferguson and Danzmann, 1998; Hara
and Sekino, 2003; Sekino et al., 2005; Jerry et al., 2004; Vandeputte et al., 2004; Ninh et al.,
2011). The technology has long been recognized as an effective tool to reconstruct the
pedigrees of group spawned and communally reared aquaculture populations, allowing high
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selection intensity in genetic improvement programmes (Doyle and Herbinger, 1995), to
account for environmental effects common to full-sibs (Rodzen et al., 2004) and to achieve a
high selection responses (Ninh et al., 2011).
In the present study, we used a total of 10 microsatellites to construct the pedigrees for the
breeding population of yellowtail kingfish from which genetic parameters were estimated.
Specifically we report: i) heritability for body and carcass (fillet weight and fillet yield) traits
including fat content, condition score and deformity, and ii) genetic relationships among
traits studied. The main aim of this study was to understand the quantitative genetic basis
of traits in yellowtail kingfish such as whole and fillet weight, traits for which the market
pays for, to start a formal breeding program for this species.
2. Materials and methods2.1Experimental locationThe reproduction, larval rearing, fingerling production and grow-out were conducted at
Clean Seas Tuna Ltd., Arno Bay (33 56.202' S 136 34.500' E), South Australia. Cages were
towed from Arno Bay to Port Lincoln, South Australia (latitude 34 73' S, longitude 135 86'
E) for harvest which is a distance of about 115 km.
2.2Animal materialsThe original broodstock were eight wild males and six wild females, presumed to be 6-10
years old and estimated to be >15kg each, caught in the Spencer Gulf (i.e., are presumed to
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come from the same population) and were held into two broodstock tanks at Arno Bay and
all broodstock contributed to the offspring. The two tanks spawned a daily average of
1,290,000 and 974,000 eggs. Broodstock were kept at a density of 3-5 kg/m3, fed
commercial diets, and mass spawned on several consecutive nights between 19th and 30th
October 2011. The larvae were stocked in hatchery rearing tanks (8 14 m3) at a density of
90/l, and fed rotifers (Artemia) from day 2 until day 15, Artemia was introduced at day 11
and fed until day 25, fish were weaned onto pellet diet around day 22-25. During larval
rearing, water temperature was maintained at about 24.5oC and 12h photoperiod. The
survival rate from hatching to fingerlings varied from 6 to 14%. Fish continued to be reared
in the hatchery until around day 70-80 when they reached 6-8 g when they were transferred
to a sea cage, where they were on-grown to harvest (average body weight of 3.1 kg 0.35;
427 days post spawning) using standard industry practices. At harvest, four hundred fish
were randomly sampled from the sea cage with approximately 40,000 fish and transported
to the processing factory in Port Lincoln in large, ice-filled containers. They were the G1
progeny of 22 full-sibs and half-sibs families. As there were eight sires and six dams,
typically each sire or dam had three to four half-sib groups, ranging from two to 50 offspring
per group.
Phenotyping: Measurements and tissue sampling was completed at the processing factory in
Port Lincoln and at the laboratory at the Lincoln Marine Science Centre. Four hundred
animals were taken for measuring but some data were not available because of seal bites
and availability from the factory. Measurements included weights, lengths (mouth to caudal
fork), and condition score (an arbitrary measure to grade the general appearance of the fish
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on a 1 to 5 scale, with 1 being the poorest condition and 5 the best condition; a fish that
scored 5 had long, wide and deep body shape, appeared to have a heavy body weight for its
length and no deformity, by contrast, a fish that scored 1 had deformity, and short and thin
body shape).
Deformity was visually recorded and categorised as lower jaw, nasal erosion or operculum,
which were the prevalent deformities found in these fish. In the present study, deformity
was defined as a binary trait (coded as 1 for fish which had either low jaw, nasal erosion or
operculum, and coded as 0 if these clinical signs were absent).
Both sides of skinless fillets were weighed and used to calculate total fillet weight and
percent fillet yield (fillet weight/ slaughter weight). Gonads were bagged and placed on ice
for later visual identification of sex. Approximately 20 g of muscle tissue were bagged and
placed on ice for flesh quality assessment (analysis of fat content).
2.3Chemical analysis of fat
The crude fat content of the flesh was determined with an ethyl acetate extraction method
based on the Norwegian Standard method (NS 9402 E) (NSA, 1994). We sampled tissue from
approximately the same region in each animal; approximately 30mm inferior and anterior
from the dorsal fin. This region showed the least seasonal variation and corresponds with
the Mowi cut, which is a standard cut used in examining fat content in salmonids
(Bremner, 2010).
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2.4Marker development2.4.1 Primer design: For this study we used four published microsatellite primer pairs(references following) and developed primers for six additional microsatellite loci from S.
lalandi transcriptome sequences. Primers for 25 published microsatellites from two other
Seriola species (S. quinqueradiata and S. dumerili) were tested on S. lalandibroodstock and
four candidates were selected based on polymorphism and scoring accuracy. These four
microsatellites were Sequ38 (Ohara et al., 2003), Sdu21 (Renshaw et al. 2006), Sdu32 and
Sdu46 (Renshaw et al., 2007). These were tested and validated using the protocols outlined
by Renshaw et al. (2007).
Transcriptome sequences from S. lalandi liver and digestive systems were generated using
the Roche 454 FLX next generation sequencing platform at the Australian Genome Research
Facility. Microsatellite sequences were identified using the QDD pipeline (Meglecz et al.,
2010) which includes primer design using Primer3 (Rozen and Skaletsky, 2000). Of the
41,765 reads generated, 250 contigs containing microsatellites were identified, from which
70 were found to have a suitable number of repeat motifs (over 20) and suitable flanking
regions on which to design primers. Of these 70 microsatellite sequences, 31 candidate
primer pairs with similar Tm (around 60C) and minimal dimer interaction were selected for
further testing. Forward primers for these 31 microsatellites were tagged with the M13(21)
universal sequence 5-TGT AAA ACG ACG GCC AGT -3 to enable two-stage labelling with
the use of an additional fluorescent dye labelled M13(21) primer. Primers were optimised
by testing under a range of thermal and reaction parameters and a final six of the most
specific and polymorphic microsatellites were selected for production. These loci in addition
to the four published microsatellites are Sel001, Sel002, Sel008, Sel011, Sel017 and Sel019.
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A total of six loci developed from our laboratory in addition to four published loci made up a
total of 10 microsatellites for parentage assignments. The thermal parameters for primers
with M13 sequences were: 94C for 3 minutes, 20 cycles of 94C for 30 seconds, 60C for 30
seconds (decreasing by 0.5C for each cycle), 72C for 45 seconds, 20 cycles of 94C for 30
seconds, 50C for 30 seconds, 72C for 45 sec, 72C for 10 minutes. For the primers without
M13 sequences the parameters were: 94C for 3 minutes, 40 cycles of 94C for 30 seconds,
52C for 30 seconds, 72C for 45 seconds, 72C for 10 minutes. Considering all 10 loci, the
average number of alleles detected was 102.10, the average observed heterozygosity was
0.70.05 and the polymorphic information content average was 0.66.06.
2.4.2 DNA extraction and PCR Reactions: DNA was extracted from caudal fin clips frombroodstock and muscle tissue from G1 animals using a Qiagen DNeasy Blood and tissue kit.
Microsatellite markers were amplified using a two-stage touchdown protocol with an initial
20 cycles running at an annealing temperature of 60C reducing by 0.5C every cycle, and
then another 20 cycles run at 50C. This protocol is specifically optimised for M13 tailed
primers. PCR reactions were performed using 1.25 l of 10x reaction buffer, 1 l of 2.5mM
dNTPs, 0.75 l of 25mM MgCl2, 0.05 l of Taq and 1 l of genomic DNA. For reactions using
M13 tailed primers, three primers are included: equimolar reverse primer and M13
fluorescently labelled primers, and a M13 tailed forward primer that has 25% concentration
of the other two primers (Schuelke, 2000). For our reactions this was 0.5 l of both the M13
fluorescently tagged primer and the reverse primer, and 0.125 l of the M13 tailed forward
primer. To reach a final reaction volume of 13 l, 7.825 l of DNAse free water was added.
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2.4.3 Genotyping and analysis: All genotyping was performed at the University of theSunshine Coast on an Applied Biosystems 3500 Genetic Analyzer (Life Technologies). The G5
standard dye set was used on this platform (FAM-blue, NED-yellow, VIC-green, PET-red)
with GeneScan LIZ 600 V2.0 (orange) as the size marker. Samples were prepared for use on
this instrument as per the manufacturers instructions. Genotypes were scored using
Genemarker software (SoftGenetics, USA). Only clear, high quality and easy to score peaks
were accepted, with lower quality results discarded and/or repeated, and accuracy of
markers was further validated by repeat genotyping of 100 samples. Of the 100 genotypes
were that repeated, including a repeated PCR step, all match exactly at all 10 loci which
suggest a high accuracy of scoring. This was done to minimise genotyping error and produce
high confidence results. Validation of individual microsatellite loci was performed by using
MICROCHECKER (van Oosterhout et al., 2004) to check for null alleles, large allele dropout
and scoring errors. Linkage disequilibrium between loci and deviation from Hardy-Weinberg
Equilibrium (HWE) at each locus was calculated using GENEPOP 4.1 (Raymond and Rousset,
1995). Parentage assignment was completed using Cervus software (Kalinowski et al., 2007),
and validated by comparing all broodstock genotypes to designated cohort of 90 G1
individuals known to be offspring from one of the two production broodstock tanks. Over
98% of these G1 animals was correctly assigned to their known parental group. Confidence
scores for parentage assignments were calculated from likelihood-odds ratios and only
assignments scoring over either 80% or 95% confidence were included in the pedigree,
those below 80% were excluded. In total, 84% of parental assignments scored greater than
a 95% confidence, and 8% scored between 80% and 95% confidence, thus 92% scores over
80% confidence. Those scoring between 80% and 95% confidence were confirmed by
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visually scoring individual alleles. The pedigree comprised only one generation of offspring
and parents.
Genotyping and molecular data analysis were conducted at University of the Sunshine Coast
(USC) in Sippy Downs, Queensland, Australia.
2.5Statistical analysis2.5.1 Linear mixed model: Uni- and multi-trait linear mixed models were applied toestimate heritability and correlations for all the traits studied, respectively. The ASReml
package was used (Gilmour et al., 2009). In a matrix notation, the model is written as the
following:
y =Xb +Za + Wc+ e
where yis a vector of observations for traits studied, X,Zand Ware the incidence matrices
related to the fixed, additive genetic and common full-sib effects, and b is the vector of fixed
effects including sex (female and male), seal bite (fish were bitten by seal or not) and
deformity status (yes or no), a is the additive genetic effect of individual animal for traits
studied, and c is the vector of common full-sib effects [i.e., dam nested within spawning
batch (tank), c2]. Due to a short period of about two-week early rearing before communal
grow-out of all families was practised, the c2 effect was included as the second random term
in the model. The c2 effect was however not significant. When it was added to the model,
there were no (or only trivial) changes in logarithmic likelihood (LogL) value to all traits
including fat content. Therefore, all traits observed were also analysed with a model that
omitted the c2 effect.
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Under the full model, heritabilities for traits were calculated as2
22
P
Ah
, where the
phenotypic variance ( 2P
) was the sum of the additive genetic variance ( 2A
), maternal and
common environmental variance ( 2C
) and the residual variance ( 2e
), i.e.
2222
eCAP . The estimated heritability for deformity was transformed from observed
(0, 1) scale to the underlying liability scale using the classical formula of Dempster and
Lerner (1950) as follows.
2
22 )1(
zpphh oL
where 2Lh is the estimate of heritability on the underlying normal scale;2
Oh is the estimate of
heritability from the linear model with binomial observations; p is the fraction of deformity
with observations of 1; and z is the height of the ordinate at the truncation point for an area
ofp under the normal curve.
Genetic and phenotypic correlations were estimated from a series of bivariate and trivariate
linear mixed model with the fixed and random effects as described above. ASReml allows to
specify different random effects for different traits in the model. For traits that had zero c2
estimates (from univariate analysis), this effect was omitted in multi-variate models.
Correlations were calculated as the covariance divided by the product of the standard
deviations of traits:2
2
2
1
12
r where12
was the estimated additive genetic or
phenotypic covariance between the two traits, and 21
and 22
are the additive genetic or
phenotypic variances of traits 1 and 2, respectively.
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2.5.2 Generalized linear mixed model (GLMM): In addition to standard linear mixed modelas described above, deformity was also analysed by GLMM sire model. Under logit model,
the assumption was that the data followed a binomial distribution, and the probability can
be obtained by logistic function ( p = ex /(1 +ex)) where p is the probability of fish deformity
recorded at harvest andxis a linear predictor. The effects fitted in the model included the
effects of sex (j= female and male) and seal bite (the fish were bitten by seal or not). With
GLMM sire model, heritability was calculated using the variance of the logit link function,
which implies that residuals have a mean of 0 and a variance of2/3.
3
42
22
22
es
sh
where 12 e
The mathematical form of the generalized linear mixed model with a logit link function used
to estimate variance components for deformity is as the followings:
)1
log(ijklm
ijklm
p
p
= + Bi+ Sk+ al+ eijklm
where Bi, and Skare the fixed effects of seal bite and sex respectively, al is the random effect
of sire and eijkl is the error term of the model, and p is the probability of fish deformity
recorded at harvest.
Deformity was also analysed using probit threshold model. The statistical model was the
same as described for logit model. However, the probit link function )(1 ip is used,
with inverse link
dxe
x
i2
2
2
1)( , where is the cumulative normal density
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function, and pi denotes the probability of deformity for fish i. Under the probit threshold
model, the heritability was calculated as
1
42
22
s
sh
3. Results3.1Descriptive statisticsThe number of actual observations, means, standard deviations and coefficients of variation
for traits studied is given in Table 1. The body weight of the fish at harvest averaged 3.1 kg,
corresponding to a fillet weight of 1.8 kg and fillet yield of 61%. The fillet fat content of
yellowtail kingfish fillet sampled from approximately the same region (about 30mm inferior
and anterior from the dorsal fin) was 4.9%. The coefficient of variation (CV) for fat content
was 43.3%, markedly greater than that for body and fillet traits (10-15%). The proportion of
deformities in this population was about 20%.
3.2Fixed effectsThe fixed effects included in statistical models for the analysis of traits studied were sex,
seal bite and deformity. The least square means for sex, seal bite and deformity status are
shown in Table 2. Of particular interest is that in yellowtail kingfish sex dimorphism does not
exist at the size evaluated (3.1 kg). Between-sex differences were not statistically significant
for all traits studied.
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The effect of seal bite was statistically significant for carcass traits only (i.e., fillet weight,
fillet yield and fat content). On the other hand, deformity had significant effect ( P < 0.05 to
0.001) on the majority of growth and carcass performance traits in yellowtail kingfish,
except for fillet yield (Table 2). Deformed fish grew slower and had smaller fillet weights and
lower visual condition score than normal (non-deformed) counterparts.
3.3HeritabilitiesSingle trait analysis of heritabilities, and maternal and common environmental variances in
proportion to phenotypic variances (c2) is presented in Table 3. The estimates of heritability
for body and carcass traits including fillet fat content were moderate (0.15 to 0.41).
Condition score was heritable (0.15). Overall, the estimates for heritability for all traits were
associated with high standard errors (0.03 to 0.26), likely due to the limited sample size and
shallowness of the pedigree. Heritability for deformity obtained from both nonlinear
(generalized) mixed model using logit and probit link functions and standard animal mixed
were low, close to zero.
The c2 were low, only 5% for body weight, but were essentially zero for other traits. One
exception was the moderate c2 for fat content. The heritability of 0.94 for fat content from
the model without maternal and common environmental effect hence may be
overestimated.
Among body and carcass traits, multivariate analyses increased albeit marginally heritability
estimates for body and fillet weight relative to single trait models, 0.30 vs. 0.26 and 0.34 vs.
0.31, respectively (results not shown). However these differences were not significant.
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3.4Correlations among body and fillet traits
Table 4 presents phenotypic and genetic correlations among body and carcass traits.
Measurements of body traits (weight and length) were genetically highly correlated (rg=
0.57 0.28). The genetic correlations between fillet weight and body measurements were
also very high (close to unity, 0.91 to 0.96), indicating that both growth and fillet weight can
be simultaneously improved. Fillet weight showed slightly greater correlations with body
weight than with fork length (0.96 vs. 0.91), suggesting that harvest weight is the most
effective selection criterion to improve both growth and fillet weight in practical breeding
programs. The genetic correlation of fillet yield with body weight were moderate (0.57), but
those with fork length were not significant different from zero (-0.19 and 0.24, respectively).
There was also a moderate and positive genetic correlation between fillet yield and fillet
weight (rg = 0.72). Breeding objectives for increased fillet weight are thus expected to result
in improvement in fillet yield.
Overall, condition score show favourable phenotypic and genetic correlations with body and
carcass traits.
3.5Correlations between fillet fat content and body and carcass traitsPhenotypic and genetic correlations of body and carcass traits with muscle fat content are
shown in Table 5. At both phenotypic and genetic levels, all the estimates were moderately
positive and significant, except for the genetic correlations between length and fillet yield
with fat content that were not significant due to their high standard errors.
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4. Discussion4.1Carcass characteristics of yellowtail kingfishThe fillet yield of yellowtail kingfish Seriola lalandiin our study (61%) falls in the high range
reported for marine species in the literature, from 43 to 69% (e.g. Navarro et al., 2009). In
the present study we report skinless fillet yield which is higher than the average value of the
same species reported in other studies (Burke, 2011), and remarkably higher than other
fishes such as tilapia (Nguyen et al., 2010b; Gjerde et al., 2012) or equivalent to rainbow
trout and Atlantic salmon (Kause et al., 2007; Powell et al., 2008; Le Boucher et al., 2011).
The fat content of 4.9% in the yellowtail kingfish population in our present study is generally
in line with other reports for Seriola lalandi(e.g., Bowyer et al., 2012). Several studies (e.g.,
Tobin et al., 2006) report that fat content varies largely with fish tissues (fillet cuts, adipose
and intestinal tissues, viscera or liver). Within a fillet, the distribution of fat also differs, that
is, higher fat content in anterior ventral than posterior dorsal sections (Burke, 2011). The
muscle tissue sampled in the present study showed the least variation in fat content.
4.2HeritabilitiesThe extent of genetic variation in body traits and fillet weight for yellowtail kingfish in our
study is also consistent with those reported for sea bream (Knibb, 2000), rainbow trout
(Kause et al., 2005), Atlantic salmon (Gjerde and Gjedrem, 1984), tilapias (Nguyen et al.,
2007; Ponzoni et al., 2011; Bentsen et al., 2012), common carp (Ninh et al., 2011) and
crustaceans species (Gitterleet al., 2005; Kenway et al., 2006; Jurezet al., 2007; Hung, D.,
pers. comm.). The high standard errors associated with our estimates were likely due to the
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limited sample size, single generation data, mass spawning practices as well as impacts of
other environmental factors during rearing and growout. Though the data were somewhat
limited (n = 400), the animals did come from a number of half-sib families and the genetic
parameters estimates were usually statistically significant. Overall, our estimates together
with the moderate to high heritabilities across farmed aquaculture species indicates that
improvement for body traits can be achieved through conventional selection in properly
designed breeding program.Our current estimate of heritability for fillet yield in yellowtail kingfish was 0.19 0.11, in
good agreement with the results reported by Nguyenet al. (2010b) in GIFT tilapia where h2
for fillet yield was at 0.250.07. Some other studies, however, showed low heritability
estimates for fillet yield or carcass ratio traits (0.03-0.05) such as in striped catfish
Pangasianodon hypophthalmus (Sang et al., 2012), gilthead seabream (Navarro et al., 2009),
rainbow trout and Atlantic salmon (Gjerde and Gjedrem, 1984).
In the present population of yellowtail kingfish fillet fat content is highly heritable, showing
potential for genetic improvement of this trait. The estimates of heritability for fat content
range from 0.17 to 0.33 in salmonids (Gjerde and Schaeffer, 1989; Iwamoto et al., 1990; Rye
and Gjerde 1996; Kause et al., 2002; Tobin et al., 2006; Niera et al., 2004; Quinton et al.,
2005; Viera et al., 2007; Powell et al., 2008) and from 0.06 to 0.48 in tilapia (Nguyen et al.,
2010a and b; Hamzah, A. per. comm.). The number of fillet samples analysed for fat content
in our study is generally comparable with those studies reported in the literature (e.g., n=
514 in tilapia reported by Nguyen et al., 2010a).
On both observed and underlying liability scales, the heritability for deformity is not
significantly different from zero. Perhaps since our measures of deformity include a range of
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traits, a low or negligible heritability is expected. The heritability on the underlying scale for
skeletal deformities is 0.25 0.03 for European seabass (Bardon et al., 2009; Karahan et al.,
2012), 0.36 0.14 for Atlantic salmon (Gjerde et al., 2005), 0.64 for sire and 0.36 for dam
components of variance on the underlying liability scale in another salmon study (McKay
and Gjerde, 1986), and 0.27 in cod (Kolstad et al., 2006). These results show that there is
additive genetic component for deformity which would allow scope for selection and
improvement through conventional selective breeding approach.
4.3Common environmental effectsThe common environmental differences between full-sib and half-sib families had significant
effects on growth performance on farmed aquaculture species (e.g., Winkelman and
Peterson, 1994). The extent of common environmental effects on body traits generally
depend on mating strategy, rearing environment, data and family structure, and they are
not easily separated from maternal genetic and non-genetic components unless there is a
good depth in the pedigree and ideal data structure. In our present study we demonstrated
that by the application of early communal rearing of all families pooled as soon as hatching,
the common environmental effects (c2) was minimized. The logarithmic likelihood ratio test
showed that the c2 effect was not significant for all body traits (Chi-square test with one
degree of freedom, P > 0.05). Ninh et al. (2011) also report a close to zero c2 in communal
early rearing of a common carp population in Vietnam. Similar findings were reported in
other species (Fishback et al., 2002; Vandeputte et al., 2004; Kocour et al., 2007).
4.4Correlations
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The high positive genetic correlations among body traits and fillet weight in this current
study suggests that all of the above body traits were closely genetically correlated and are
likely to be controlled by similar sets of genes. Hence, any one of these traits tested could
be used, on its own or simultaneously, to improve overall growth performance of the
animals without a requirement for making different measurements. However, harvest
weight is reported to be the best predictor of fillet weight, with R2 = 0.94 and a correlation
between observed and predicted value of 0.97 in tilapia (Nguyen et al., 2008). The genetic
correlation of fillet weight with body weight was higher than for fillet weight with other
body traits (Nguyen et al., 2010b). In practical selection programs live weight is
recommended due to its greater heritability and the ease and accuracy of measurements
relative to other body traits (length or width). Therefore both performance and fillet weight
can be improved simultaneously.
In the present population of yellowtail kingfish, the estimated genetic correlation of fillet
yield with body weight was moderate and positive (0.57 0.28). By contrast in a study of
striped catfish, Sang (2010) found low genetic correlations between fillet yield and body
weight or between fillet yield and fillet weight. Realised correlated response to selection for
body weight was also reported to be negligible for fillet yield in this species or in tilapia
where the fish were slaughtered at an average weight of 500 g (Nguyen et al., 2010b).
Hence, direct improvement of fillet yield in farmed aquaculture species is predicted to be
difficult because ratios have been long known to lead statistical hurdles. This is due to the
likely disproportionate nature by which selection pressure is exerted on component traits
(Gunsett et al., 1987; Simm et al., 1987). However, we may be able to overcome some of
these issues relating to ratios by selection on fillet weight adjusted for body weight. In this
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case indirect improvement in fillet yield to selection for increased body weight may be
expected as calculated using selection index theory by Nguyen et al. (2010b).
The positive genetic correlations of body and fillet weight with fat content (0.92 and 0.98
respectively) indicated that selection for increased growth can result in increased fat
content. The reported genetic correlation between fat and body weight was at the high end
ranges, from 0.11 to 0.80, reported in salmonids (Neira et al., 2004; Quinton et al., 2005;
Powell et al., 2008; Vieira et al., 2007) and from 0.16 0.40 reported in tilapia (Hamzah, A.
pers. comm). The great range of values may reflect slightly different practices in the
methods. In any case, such a large range makes it difficult to determine if our values are
typical or not. In this study, we examine total fat content from the same region of the fillet,
whereas different measurements of fat are reported in the literature. For instance in a
rainbow trout (Oncorhynchus mykiss) breeding program, Kause et al. (2007) measured
muscle (dissected above the lateral line of the fish) and body lipid (samples of un-gutted
fish) as two different traits. Across studies, the percentages of fat deposits in fish fillet and
visceral weight were different. Therefore, fillet fat contents should be measured as a
genetically different trait from the fat deposits at other body locations. Gjerde and Schaeffer
(1989), Kause et al. (2002) and Tobin et al. (2006) also proposed that fat deposits at
different body locations should be measured as genetically different traits. In the present
study, only fillet fat content was examined due to the high costs of chemical analysis and
labours involved (fats of other body compartments were not analysed). The present
estimates of the genetic correlation of body weight with fat content, are generally in line
with other fish species in which either fillet or whole body fat contents were measured
(0.36, Iwamoto et al., 1990; 0.73, Neira et al., 2004; 0.31, Quinton et al., 2005; 0.80, Powell
et al., 2008; 0.11, Vieira et al., 2007).
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In our study, the genetic correlations between body traits and deformity were weak (0.09 to
0.34) and not significant due to their large standard errors (results not shown). In Atlantic
cod, Kolstard et al. (2006) also reported a low genetic correlation between growth and
various measures of deformities. The genetic relationship between growth and deformity
reported in the literature vary with species (positive in European sea bass, Karahan et al.
2012, but negative in Atlantic salmon, Gjerde et al., 2005), history of populations, and
rearing phases (Vehvilainen et al., 2012) to which the fish subject. In practical selective
breeding programs for farmed aquaculture species, this trait (deformity) should be closely
monitored.
Although our study showed that deformity had a low heritability and no significant
correlation with other traits, this character probably should be included in any recording
scheme, the breeding objective and the selection index to ensure the sustainability of long
term genetic improvement programs for yellowtail kingfish. In farmed animals, high
performing individuals resulted from long term selection programs tend to prone to
diseases such as mastitis in dairy cattle, leg weakness in pigs or egg defects in layers chicken.
Both allocation resource and selection theories (Beilhharz et al., 1993) suggests that fitness
related traits may show a tendency to decline due to selection for other traits and due to
inbreeding depression (Goddard, 2009). They thus merit further considerations in practical
selective breeding programs to meet future demands of the aquaculture industry.
In summary, there is large potential for genetic improvement to increase productivity for
production traits in yellowtail kingfish in Australia. Among these traits, body and fillet
weights are of particular interest because the fish are priced on the basis of their wet body
weight or fillet weight. Fillet weight can be indirectly improved through selection for
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increased growth due to the strong positive genetic correlation between the traits.
Alternatively a linear index combining measurements of available body dimensions can be
applied (Nguyen et al., 2010b). For some species such as tuna, fat can be a factor in the
value of a fish. Should there be consumer and or market demand to increase the fat content
of kingfish, it may be possible to achieve this with genetic selection. To enable routine data
recording on a large scale for genetic evaluation and selection in kingfish, cheap and non-
invasive measurements of fats on live animals should be considered such as using fat-
meters, near infrared spectroscopy or computerised tomography (Cozzorino and Murray,
2012).
5. ConclusionsGenetic properties of muscle fat content, condition score and deformity and their genetic
associations with body and carcass traits are reported for the first time in yellowtail kingfish.
Selection for improving body weight, fillet weight and fat content could be effective as
evidenced by their moderate heritability. Genetic correlations among these traits (body
weight, fillet and fat) are positive and high, i.e. desirable. Our present results provide a basic
genetic inheritance for traits of economic importance, and thus should be useful for the
design and conduct of practical selective breeding programs in yellowtail kingfish. Due to
the limited number of parents and families involved in the present study, frequent update
of the genetic parameters would be necessary to guide future breeding programs in this
population of yellowtail kingfish.
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Acknowledgements
This work was supported financially by the Australian Seafood Cooperative Research Centre
with the Fisheries Research Development Cooperation (project 2010/768 Broodstock
management for Southern Bluefin Tuna and Yellowtail Kingfish). Facilities, fish and
experimental support was provided by Clean Sea Tuna, Inc. We would like to acknowledge
technical input and other advice from Jane Quinn (at USC), Morten Deichmann and Craig
Foster (CST).
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Vieira, V.L., Norris, A., Johnston, I.A., 2007. Heritability of fibre number and size parameters and
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Table 1a: Means, standard deviations (SD), coefficient of variation (CV, %) for traits studied
Traits Unit N Mean SD CV
WT Kg 385 3.1 0.35 11.4
LG Cm 385 59.7 2.20 3.7
FW Kg 385 1.8 0.28 15.4
FY % 341 60.7 5.06 8.3
FC % 379 4.9 2.14 43.3
CS Score 385 3.8 0.57 15.1
DF % 385 20.0 40.1 200.2
aWT = weight, LG = Length, FW = Fillet weight, FY = Fillet yield, FC = Fillet Fat content, CS =
Visual condition score and DF = Deformity. Some data were not taken in the case of FY when
there was seal bight or when factory operations prevented timely data acquisition.
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Table 2a, b, c: Least squares means of fixed effects
Traits Gender Seal bite Deformity
Female Male Yes No Yes No
WT 3.000.036 2.970.038 2.980.057 3.060.023 3.060.023 3.130.057
LG 59.10.224 59.00.233 59.20.354 59.40.144 58.50.296 60.00.185
FW 1.600.024 1.580.025 1.300.038 1.850.015 1.500.032 1.650.020
FY 53.10.313 53.10.326 43.80.493 60.30.201 51.80.413 52.40.258
FC 4.230.226 4.090.232 3.260.354 4.800.143 3.610.298 4.150.184
CS 3.570.056 3.620.058 -d 3.620.040 3.380.072 3.870.036
DF 17.50.278 16.10.290 11.60.476 23.70.145 - -
aBetween gender difference was not significant for all traits (P > 0.05)
bSeal bite has significant effect (P
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Table 3a,b,c,d: Heritability (h2), and maternal and common environmental effects (c2) for
economically important traits in yellowtail kingfish
Traits Model 1 Model 2 -2(LogLModel2
LogLModel1)h2 SE h2 SE c2 SE
WT 0.26 0.13 0.17 0.16 0.05 0.09 0.21
LG 0.15 0.09 0.15 0.09 0.00 0
FW 0.31 0.15 0.24 0.19 0.04 0.09 0.15
FY 0.19 0.11 0.19 0.11 0.00 0
FC 0.94 0.21 0.41 0.26 0.29 0.20 2.3
CS 0.15 0.11 0.15 0.11 0.00 0
DF1 0.001 0.03 0.001 0.027 0.00 0
DF2 0.023 0.11
DF3 0.021 0.11
aModel 1 (standard animal model): Spawning batch (tank) was not included. bModel 2:
Spawning batch (tank) nested with dam as a random factor in addition to the additive
genetic effect. Chi-square test (i.e. -2LogL difference between models 2 and 1) with one
degree was not significant for all traits (P > 0.05).
cDF1 estimated from linear animal model. The heritability from linear model transformed to
liability scale was 0.0006.
dDF2 estimated from logit threshold sire model
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dDF3 estimated from probit threshold sire model
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Table 4: Phenotypic (above) and genetic (below the diagonal) correlations among body andfillet traits, using model 1Traits WT LG FW FY CS
WT 0.80 0.02 0.92 0.008 0.14 0.06 0.69 0.04
LG 0.57 0.27 0.83 0.03 0.07 0.05 0.45 0.05
FW 0.96 0.05 0.91 0.05 0.47 0.05 0.63 0.04
FY 0.57 0.28 -0.19 0.46 0.72 0.22 0.06 0.07
CS 0.94 0.35 0.23 0.44 0.95 0.19 0.24 0.46
Model 1: Standard animal model with only the additive genetic effect.
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Table 5: Phenotypic (rP) and genetic correlations (rG) of body and carcass traits with fillet fat
content
Traits rP rG
WT 0.52 0.07 0.92 0.13
LG 0.24 0.07 0.37 0.43
FW 0.54 0.07 0.78 0.14
FY 0.24 0.06 0.98 0.20
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Highlights
We found body fat is highly heritable in kingfish.
We report genetic parameter estimates from industrial crops of kingfish.
We report the application of new microsatellites to establish kingfish pedigrees.