This study develops a nearly unbiased estimator of the ratio of the contemporary effec-
tive mother size to the census size in a population, as a proxy of the ratio of contemporary
effective size to census size (Ne/N). The proposed estimator is based on both known mother–
offspring (MO) and maternal-sibling (MS) relationships observed within the same cohort, in
which sampled individuals in the cohort probably share MO relationships with sampled moth-
ers. The rationale is that the frequency of MO and MS pairs contains information regarding the
contemporary effective mother size and the (mature) census size, respectively. Therefore, the
estimator can be obtained only from genetic data. Moreover, We also evaluate the performance
of the estimator by running an individual-based model. The results of this study provide the
following: i) parameter range for satisfying the unbiasedness, and ii) guidance for sample sizes
to ensure the required accuracy and precision, especially when the order of the ratio is avail-
able. Furthermore, the results demonstrate the usefulness of a sibship assignment method for
genetic monitoring, providing insights for interpreting environmental and/or anthropological
factors fluctuating Ne/N, especially in the context of conservation biology and wildlife man-
agement.
Running head: Estimator of Ne/N
∗Corresponding author: National Research Institute of Fisheries Science, Japan Fisheries Research and Education
Agency, 2-12-4 Fukuura, Kanazawa, Yokohama, Kanagawa, 236-8648, Japan. E-mail:
[email protected]
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1 INTRODUCTION
The Estimation of the ratio of the contemporary effective population size to the census size
(Ne/N) has attracted much research attention for providing information about a current population,
especially in the context of conservation biology and wildlife management (Frankham, Bradshaw,
& Brook, 2014; Palstra & Fraser, 2012). Small Ne/N demonstrates large variance in reproductive
success (Akita, 2019; Wang, Santiago, & Caballero, 2016; Waples, 2016), resulting from the vari-
ance of reproductive potential (e.g., the big old fat fecund female fish hypothesis; Hixon, Johnson,
& Sogard, 2014) or from the situation in which only some families successfully reproduce (re-
ferred to as the “Sweepstakes reproductive success” hypothesis, Hedgecock & Pudovkin, 2011).
Moreover, if Ne/N is invariant across years, thenNe may behave like an index ofN, and vice versa
(Luikart, Ryman, Tallmon, Schwartz, & Allendorf, 2010). However, if Ne/N fluctuates across
years, the trends can clarify the interpretation of environmental and/or anthropological factors,
causing the variance of reproductive potential, family-correlated survivorship, or fluctuating pop-
ulation dynamics.
The estimation of Ne/N has been performed by utilizing the estimated values of contemporary
effective population size (Ne) and census size (N), unless complete pedigree data and/or full census
data are available. Additionally, there are numerous methods for estimatingNe from genetic mark-
ers (Wang et al., 2016, and the references contained therein). There are also numerous methods
for estimating N, such as a mark-recapture method or population dynamics modeling with survey
data (e.g., K´ery & Schaub, 2011; Methot & Wetzel, 2013; Quinn & Deriso, 1999; Seber, 1982). It
is known that there are large variations in both estimators; thus, their combination (i.e., the esti-
mator of Ne/N) also shows large variation (Marandel et al., 2018; Palstra & Fraser, 2012). There
is currently a little theoretical foundation for the estimator of Ne/N, indicating no guidance for a
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sample size to ensure the required accuracy and precision.
Close-kin mark-recapture (CKMR) is a recently developed method for estimating N that uti-
lizes the information about kinship in a sample. This was possible owing to the recent advances
in genetic methods for kinship determination (Bravington, Grewe, & Davies, 2016; Bravington,
Skaug, & Anderson, 2016; Hillary et al., 2018; Skaug, 2017) although similar methods have been
proposed in the beginning of the 21st century (Nielsen, Mattila, Clapham, & Palsbøll, 2001; Pearse,
Eckerman, Janzen, & Avise, 2001; Skaug, 2001). Besides, the rationale is that the presence of a
kinship pair in the sample is analogous to the recapture of a marked individual in mark-recapture.
Therefore, kinship pairs in the sample are less likely to be observed in larger populations; thus,
the number of kinship pairs may reflect N. Since the original CKMR is designed to estimate adult
abundance (i.e., N), the monitoring data for CKMR also produce the estimator of Ne by detect-
ing half-sibling (HS) pairs within the same cohort (Akita, 2019). Since kinship determination is
more accurate, this kinship-oriented estimation of Ne was presented in the context of the sibship
assignment method (Wang, 2009) and is expected to provide a much more accurate estimator.
In this study, we propose a new method for estimating the ratio of contemporary effective
mother size to the census size (Ne,m/Nm) in a population, as a proxy of Ne/N. Assuming that kin-
ships are genetically detected without any error, this method is based on the numbers of maternal-
sibling (MS) and mother–offspring (MO) pairs in a sample. Thus, sampling is completed at a
single breeding time; sampling offspring within the same cohort and mothers probably shares MO
relationship with sampled offspring. Our model provides a nearly unbiased estimator of Ne,m/Nm
that explicitly incorporates two types of overdispersed reproduction (i.e., parental and nonparental
variations; Akita, 2019), making it possible to target a species that shows iteroparity (i.e., multiple
reproductive cycles during the lifetime) and/or sweepstakes reproductive success. First, we explain
the modeling assumption and sampling scheme. Then, we analytically determine (nearly) the un-
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biased estimators of Ne,m, 1/Nm, and Ne,m/Nm, which are based on the numbers of MS and/or MO
pairs. Finally, by running an individual-based model, we investigate the performance of the estima-
tor and provide a guide for a sample size. Moreover, it is noteworthy that our modeling framework
can be applied to diverse animal species. However, the description of the model focuses on fish
species, which are presently the best candidate target of our proposed method.
2 THEORY
The main symbols used in this paper are summarized in Table 1.
2.1 Hypothetical population
We suppose that there is a hypothetical population comprising Nm mothers and there is also
no population subdivision or spatial structure. In this study, a mature female is called a mother
even if she does not produce offspring. For mathematical tractability, we assume that only one
spawning ground exists in which the mothers remain for the entire spawning season. Following
Akita (2019), our modeling framework employs two types of overdispersed reproduction: parental
and nonparental variations. Thus, the former indicates a variation caused by the mother’s covari-
ates, such as age, weight, and residence time on the spawning ground, while the latter indicates a
variation caused by non-random stochastic events during a series of reproductive episodes, which
are independent of the mother’s covariates, such as family-correlated survivorship or the mating
behavior effects (e.g., competition for males/females and correlation between mating opportuni-
ties of the mother and the number of her offspring). Figure 1 illustrates a schematic diagram of
the effects of parental and nonparental variations exemplified by age-dependent reproduction and
family-correlated survival on kinship relationships in a population. Detailed definitions of parental
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and nonparental variations are stated in Akita (2019).
Let ki denote the number of surviving offspring of motheri (i = 1,2, . . . ,Nm) during sampling.
It is noteworthy that ki is assumed to be observed at the sampling, as explained in the next sub-
section. Following Akita (2019) and giving the expected number of the surviving offspring per
mother during the sample timing, λi (> 0), ki is assumed to follow a negative binomial distribution
through a conventional parametrization:
Pr[ki|λi] = Γ[ki + φ ]
ki!Γ[φ ]
( λi
φ + λi
)ki( φ
φ + λi
)φ
, (1)
where φ (> 0) denotes the overdispersion parameter that describes the degree of the nonparental
variation. Presently, φ is assumed to be constant across mothers, whereas the expected number of
the surviving offspring (λi) varies across mothers. The mean and variance of this distribution are
denoted by λi and λi + λ 2
i /φ, respectively. In the limit of infinite φ, this distribution becomes a
Poisson distribution, which is given by Pr[ki|λi] = λ ki
i e−λi/(ki!). We assumed thatλi is independent
and identically distributed with the density function f (λ ), which produces a parental variation.
The shape of the density function is often complex, but it may be described by information, for
example, the mother’s weight composition in the population. The specific form off (λ ) is given in
Supporting Information and is used for running an individual-based model.
2.2 Sampling
To obtain the estimator of Ne,m/Nm, we utilize the number of MS and MO pairs observed in a
sample. For the mathematical tractability, only one reproductive season is targeted for sampling.
Thus, whether the sampling method does not affect our modeling framework whether it is invasive
or noninvasive. In the population, nM mothers are randomly sampled immediately after the end of
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the reproductive season. Additionally, in the population, nO offspring are also randomly sampled
but allowed to die before sampling. The numbers of MS and MO pairs are determined by pairwise
comparison of all the sample individuals (nOC2 and nMnO comparisons, respectively). As depicted
in Fig 1, six offspring and three mothers are sampled and two MS and three MO pairs are observed.
In our modeling framework, if an MS pair also shares a paternal-sibling (PS) relationship, we count
it as an MS pair and ignore the existing full-sibling (FS) relationship.
2.3 Effective mother size (N e,m) and the ratio to census size (N e,m/Nm)
Akita (2019) derived the approximate probability showing that two offspring share an MS
relationship with an arbitrary mother (denoted by πMS) as follows:
πMS≈ c
Nm + c− 1 , (2)
where
c = (1 + φ−1)E[λ 2]
E[λ ]2 .
Without both parental and nonparental variations (i.e., λ is constant among mothers and φ→ ∞),
πMS converges to 1/N , corresponding to the Poisson variance for all mothers in a population.
Moreover, the effect of the two factors causing a deviation from the Poisson variance can be com-
bined as parameter c (≥ 1). In the sequel, we refer to “overdispersion” as the distribution of the
offspring number that results from this combined effect. By applying the combined effect, the
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variance of the offspring number can be given by
V[k] = E[V[k|λ ]] +V[E[k|λ ]]
= E[λ + λ 2/φ ] +V[λ ]
= E[λ ] +E[λ ]2(c− 1), (3)
suggesting that the variance substantially increases with c.
Akita (2019) defined the contemporary effective mother size as follows:
Ne,m = 1
πMS
. (4)
Besides, this definition is related to the inbreeding effective population size (Nordborg & Krone,
2002; Wang, 2009). When sampling from a single cohort in a population with overlapping gener-
ations, the effective mother size in our definition corresponds to the effective breeding mother size
that produces a single cohort. We obtain the ratio of the effective mother size to census size using
Eqs. 2 and 4 (Akita, 2019), and it is given by
Ne,m
Nm
= 1
πMS
1
Nm
≈ 1
c , (5)
where Nm≫ 1 is assumed for approximation.
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2.4 Estimator of Ne,m/Nm
This subsection proposes the estimator of Ne,m/Nm as follows:
ˆ(Ne,m
Nm
)
= ˆNe,m
ˆ( 1
Nm
)
. (6)
A “hat” denotes the estimator of a variable in this study. The requisite condition that satisfies Eq. 6
is independent of ˆNe,m and ˆ1/Nm. This property will be shown later in this subsection. Akita
(2019) derived the nearly unbiased estimator of Ne,m, which is given by
ˆNe,m =
ˆ( 1
πMS
)
=
(nO
2
)
+ 1
Hobs
MS + 1 , (7)
where Hobs
MS denotes the observed number of MS pairs in a sample. This estimator works well
unless nO is very small. Akita (2018) obtained a probability in which a randomly sampled mother
and her offspring shares an MO relationship, which is given by
πMO = 1
Nm
. (8)
This indicates that πMO is independent of the distribution of the offspring number. By definition of
πMO, we can set its estimator by Hobs
MO/(nMnO), where Hobs
MO denotes the observed number of MO
pairs in a sample. Thus, the estimator of 1/Nm can be determined as follows:
ˆ( 1
Nm
)
= Hobs
MO
nMnO
. (9)
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Finally, substitutingˆNe,m (Eq. 7) and ˆ1/Nm (Eq. 9) into Eq. 6, we obtain the estimator of Ne,m/Nm
as follows:
ˆ(Ne,m
Nm
)
=
(nO
2
)
+ 1
Hobs
MS + 1
Hobs
MO
nMnO
. (10)
Let both nM and nO be given. We numerically confirmed that there is no correlation between
Hobs
MO and Hobs
MS (results are not shown). To intuitively explain this independency, we consider three
mothers (i = 1,2,3) and their offspring, and assume that (k1,k2,k3) = ( 3,1,1) and (nM,nO) =
(1,3). Moreover, when the three offspring born to the first mother are sampled (i.e.,Hobs
MS = 3), the
expected number of MO relationship is one (= 1/3× 3 + 1/3× 0 + 1/3× 0). Meanwhile, when
an offspring is sampled from each mother’s offspring (i.e.,Hobs
MS = 0), the expected number of MO
relationship is also one (= 1/3× 1 + 1/3× 1 + 1/3× 1). Therefore, we conclude that both ˆNe,m
and ˆ1/Nm are independent, and ˆNe,m/Nm is expected to work well (see details in the RESULTS
section).
The bias of ˆNe,m/Nm is defined by b, which is approximately given by (see APPENDIX for
the derivation)
b = E
[ ˆ(Ne,m
Nm
)]
−
(Ne,m
Nm
)
≈ −
(Ne,m
Nm
)(
1− 1
Ne,m
)(nO
2 )+1
. (11)
It is noteworthy that ˆNe,m/Nm is downwardly biased, especially when nO is very small. However,
this bias may be ignored for a wide range of parameters (see details in theRESULTSsection). The-
oretically, b asymptotically converges to zero as nO increases, making ˆNe,m/Nm a nearly unbiased
estimator. Moreover, as demonstrated in the RESULTS section, it is observed that an extremely
skewed reproduction breaks down the unbiasedness (e.g., in the case that c = 20 and 100 in the
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results).
2.5 Individual-based model
We developed an individual-based model that tracks kinship relationships to evaluate the es-
timator’s performance (e.g., ˆNe,m/Nm). The population structure was assumed to be identical to
that in the development of the estimators. In addition, the population comprised mothers and their
offspring, and it was assumed to follow a Poisson or negative binomial reproduction. The expected
number of the surviving offspring of a mother followed the density distribution f (λ ) (see Sup-
porting Information for details). We calculated overdispersion parameter (c) fromφ and f (λ ), as
well as confirmed numerically that the value ofc gives the same statistics of the estimators even if
the combination of φ and f (λ ) differs (results are not shown). Therefore, each offspring retained
the mother’s ID, making it possible to trace an MS and MO relationship.
Let a parameter set (n O, nM, Nm, φ, and parameters that determine f (λ )) be given. We sim-
ulated a population history in which Nm mothers generated offspring; this process was repeated
100 times. The sampling process for each history was repeated 10,000 times, acquiring 1,000,000
data points that were utilized to construct the distribution of the estimators for each parameter set.
Furthermore, true value of Ne,m was calculated from Nm and c (Eqs. 2 and 4).
3 RESULT
We numerically evaluated the performance of ˆNe,m/Nm for the case in which the number of
mothers, Nm, and the combined effect of deviation from the Poisson, c, were unknown. Moreover,
we changed the parameter values for Nm (103 and 104) and c (1, 10, 20, and 100). In addition,
based on a given parameter set (N m and c), we mainly addressed the number of samples (n M and
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nO) required to obtain adequate accuracy and precision. In this study, we evaluated the performance
of ˆNe,m/Nm for specific ranges of the sample sizes (50-200 when Nm = 103, and 200-1000 when
Nm = 104). Meanwhile, other estimators (i.e., ˆNe,m and ˆ1/Nm) are also evaluated and provided in
Supporting Information.
First, we evaluated the accuracy of estimators based on their relative bias calculated by ap-
plying the individual-based model, which is defined as follows: “(averaged estimator − true
value)/true value.” For a given combination of Nm and c, the value of the relative error of ˆNe,m/Nm
is represented on a heatmap as a function of nM and nO, as dpicted in Fig. 2. For most of the
investigated parameter sets, we observed that their relative error is less than 10%. As expected,
the relative error is not affected by nM since ˆ1/Nm is exactly an unbiased estimator of 1/N m (see
Eq. A2 in APPENDIX and also Fig. S2 in Supporting Information). Meanwhile, ˆNe,m is down-
wardly biased when nO is relatively small to true Ne,m (e.g., see c = 1 in Fig. 2 and also Fig. S1
in Supporting Information), as presented in Akita (2019); thus, ˆNe,m/Nm is downwardly biased.
Contrary to the theoretical prediction for the direction of the bias (Eq. 11), relatively strong overdis-
persion results in an upwardly bias for ˆNe,m/Nm when c is relatively large (e.g., c = 20 and 100 in
Fig. 2a). This inconsistency may be caused by the breakdown of the approximation for deriving
ˆNe,m (Eq. S14 in Akita, 2019). Thus, as described in Eq. 3, extremely large c results in a large
variance of offspring number, generating a situation in which the behavior of random variableHMS
far deviates from the binomial distribution.
Next, we evaluated the precision of estimators based on their coefficient of variation. As
demonstrated in Fig. 3, the value of the coefficient of variation of ˆNe,m/Nm is also represented
on a heatmap as a function of nM and nO. For the investigated parameter sets, the degree of
the coefficient of variation strongly depends on the sample sizes. As shown in Figs. S3 and S4
in Supporting Information, the dependency results from the combined effects of variation of
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both ˆ1/Nm and ˆNe,m. As c increases, it is noteworthy that the parameter space of sample sizes
demonstrating large variation of ˆ1/Nm (e.g., CV > 30%) expands; however, when c is small (e.g.,
c = 1), relatively small nO results in large variation ofˆNe,m because of a relatively large Ne,m.
4 DISCUSSION
We theoretically developed a nearly unbiased estimator of the ratio of contemporary effec-
tive mother size to the census size (N e,m/Nm) in a population (Eq. 10). The proposed estimator
is based on known MO relationship and MS relationships observed within the same cohort, in
which sampled individuals in the cohort probably share MO relationships with sampled mothers
(Fig 1). Moreover, the performance of the estimator (accuracy and precision) was quantitatively
evaluated by running an individual-based model (Figs. 2 and 3). Meanwhile, the bias is analyt-
ically provided (Eq. 11). Our modeling framework utilizes two types of reproductive variations
(Akita, 2019): variance of the average offspring number per mother (parental variation, denoted
by f (λ )), and variance of the offspring number across mothers with the same reproductive po-
tential (nonparental variation, denoted by φ). Additionally, these two effects result in a skewed
distribution of offspring number and are summarized into one parameter (c) in the framework.
Thus, our estimator can be calculated from sample sizes of mother and offspring (n M and nO, re-
spectively) and the observed numbers of MS and MO pairs (H obs
MS and Hobs
MO, respectively), and it
does not require other parameters. The rationale for this is the following: i) the frequency of MS
and MO pairs contains information about Ne,m and Nm, respectively; ii) the estimators of Ne,m and
1/Nm are independently determined based on a pedigree structure in the population and sample
sizes, generating the estimator of Ne,m/Nm by multiplying both estimators ( ˆNe,m and ˆ1/Nm). In
this study, although ˆNe,m/Nm is considered as a proxy of ˆNe/N, our theoretical results can easily
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be extended to the estimator of the ratio of contemporary effective father size to the census size if
fathers are also sampled. The comparison of both ratios could clarify the underlying processes that
differentiate between the sexes in the context of reproductive ecology.
The novelty of this study is that ˆNe,m/Nm can be obtained only from the genetic data, and there
are numerous advantages in using the proposed estimator instead of separately estimating Ne (via
genetical method) and N (via non-genetical method). First, sampling and analyzing designs have
become substantially simplified. Moreover, requirements for the proposed estimator are sampling
of mothers and (potentially) their offspring in an appropriate time, and the extraction of their
DNA that satisfies an adequate number of markers for kinship detection. In addition, both MO
and MS pairs can be detected by a applying unified framework of genetic analyzes (there are
many algorithms to detect kinship pairs from single nucleotide polymorphisms (SNPs) or short
tandem repeats (STRs)), although an MS pair involves many more DNA markers (e.g., several
thousands of SNPs are required for detection) than an MO pair (e.g., several hundreds of SNPs are
required for detection). Second, our theoretical results guide sample sizes (n M and nO) to ensure
the required accuracy and precision, especially if the order of the number of effective mothers is
approximately known. This is due to the simple formulation of the estimator determined only by
the observed values (Eq. 10). Third, the proposed estimator directly reflects the amounts of Ne,m
and Nm at the same timing (i.e., immediately after the end of the reproductive season), leading to a
clear interpretation of the results, especially for genetic monitoring. For example, when the strong
cohort is added to the spawning population in the beginning of the year, the estimator ofNe without
reflecting this addition may results in an inappropriate estimation of Ne/N (details of the temporal
scale relevant to estimated Ne for each method were discussed in Wang et al., 2016).
Our modeling framework is presented by combining the context of the sibship assignment