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Estimating Ancestral Population Sizes and Divergence Times
Jeffrey D. Wallaa Department of Human Genetics, University of Chicago, Chicago, Illinois 60637
Corresponding author: Jeffrey D. Wall, 920 E. 58th St.--CLSC 507, Chicago, IL 60637., jwall{at}genetics.bsd.uchicago.edu (E-mail)
Communicating editor: N. TAKAHATA
| ABSTRACT |
|---|
This article presents a new method for jointly estimating species divergence times and ancestral population sizes. The method improves on previous ones by explicitly incorporating intragenic recombination, by utilizing orthologous sequence data from closely related species, and by using a maximum-likelihood framework. The latter allows for efficient use of the available information and provides a way of assessing how much confidence we should place in the estimates. I apply the method to recently collected intergenic sequence data from humans and the great apes. The results suggest that the human-chimpanzee ancestral population size was four to seven times larger than the current human effective population size and that the current human effective population size is slightly >10,000. These estimates are similar to previous ones, and they appear relatively insensitive to assumptions about the recombination rates or mutation rates across loci.
THE effective population size (Ne) of a species has a direct effect on the amount and the pattern of DNA sequence variation. Researchers have therefore used sequence polymorphism data to estimate Ne (e.g., ![]()
![]()
![]()
= 4Neµ, and the per generation mutation rate µ can be estimated either directly (![]()
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Most estimates of Ne for humans are
10,00015,000 (e.g., ![]()
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A few main methods exist for estimating Na (see ![]()
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Another method for estimating Na requires divergence data from two or three species (![]()
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510 times the current Ne (![]()
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Finally, two other methods require intraspecific polymorphism data from two species and use either a moment-based (![]()
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Large estimates of the human-chimpanzee Na are concordant with a study of Mhc that used the high levels of diversity there to estimate a long-term (i.e., over the past 1020 million years) average effective population size of
105 (![]()
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One possible explanation is that Na has been consistently overestimated. Indeed, both the trichotomy method and the two-species maximum-likelihood method have been criticized (![]()
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The maximum-likelihood methods are more rigorous and efficient, but they too have two main drawbacks. As with the trichotomy method and the method of ![]()
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In this article, I present a new method for estimating Na. The method requires orthologous sequence data from three or more species (two plus one or more outgroups) and jointly estimates Na and species divergence times using a summary maximum-likelihood approach. Unlike the previous maximum-likelihood methods, intragenic recombination is incorporated, and likelihoods are estimated from coalescent simulations. Also, the model can account for variation in mutation rates across loci. Although the method can be used on data from any taxonomic group (as long as at least one outgroup species is available), I concentrate here on analyzing human and great ape sequence data. The maximum-likelihood framework allows for the estimation of confidence intervals; this, along with a more realistic model, allows us to assess with greater rigor whether the human-chimp Na was much larger than the current human Ne, as previous studies have claimed. I apply the method to the orthologous data from 53 intergenic regions reported in ![]()
| METHODS |
|---|
I describe the model in which there are orthologous sequence data from four species. The case in which there are three species (or five or more) follows analogously.
Suppose we have four species with a known phylogeny. We assume a null model of speciation (cf. ![]()
![]()
(= 4Nhµ) and
(= 4Nhr), where µ is the mutation rate per site per generation and r is the recombination rate per site per generation. Label the species H, C, G, and O, with current diploid effective population sizes Nh, Nc, Ng, and No, respectively. Suppose H and C split at time T1, H and G at time T2, and H and O at time T3, with T1 < T2 < T3 (see Fig 2). T1, T2, and T3 are scaled in units of 4Nh generations. From time T1 until T3 both the H-C ancestral population and the H-C-G ancestral population have effective size Na, while the H-C-G-O ancestral population has effective size No. The results are similar if the latter ancestral population has effective size Na (results not shown). Finally, define ns as the number of contiguous nucleotide sites in the simulation. There are a total of 11 parameters in the model, listed in Table 1. We assume that the generation time and mutation rate do not vary across species. These assumptions are reasonable when the species considered have similar life-history traits and are closely related. There are three possible (unrooted) gene trees, with H and C, H and G, or C and G as sibling species.
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Now, suppose we have a single orthologous sequence from each species. For each site that is "segregating" (i.e., is not identical across all species), we can infer that one or more mutations happened on certain branches in the unrooted tree. We do this assuming the fewest number of mutations that can explain the data. For example, if the H, C, G, and O sequences have A, G, A, and A, respectively, then we infer that a mutation happened on the branch leading to species C. All biallelic segregating sites fall into seven categories, resulting from mutations on seven different branches of an unrooted tree. These seven branches have H, C, G, O, HC, HG, or CG as descendants and are referred to as the seven types of branches. Note that for any particular gene tree there are only five possible branches, four external ones (with a single species as a descendant) and one internal one. Any site may have one of three possible gene trees, leading to seven possible branches over all possible gene trees (the four external branches that are common to each gene tree and one internal branch from each gene tree). For sites with three segregating nucleotides, we assume that the two species with the same base share the ancestral state and that the two other bases each arose from a single mutation. The ![]()
The sequence data for the 53 intergenic regions reported in ![]()
,
, Nh, Nc, Ng, No, Na, T1, T2, T3, ns) we estimate the likelihood of observing the vector b using Monte Carlo simulations.
The population model in Fig 2 is simulated using a modification of the coalescent with recombination (![]()

To estimate the likelihood of M, we just average this probability over many replicates,

where x is large. The ![]()
The above equation describes how to estimate the likelihood of M for a single locus. Define M' as a vector containing the first 10 values of M. Estimation of the likelihood of M' over multiple loci is straightforward. Given a collection of k loci, define {Mi}ki=1 as a collection of corresponding M vectors, where the Mi are identical except for ns (which is calculated for each locus). Define bi as the vector b for the ith locus. Then, since unlinked loci are evolutionarily independent, we can estimate the likelihood of M' over multiple loci simply by taking the product of the individual lik(M|b) estimates:

We have taken the approach of summarizing the data by b before performing maximum likelihood. Summary-likelihood methods have been quite useful in other situations (e.g., ![]()
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Of the 11 parameters that make up the model M, only 9 can freely vary. ns is fixed from the actual data, while Nh is relevant only indirectly; it turns out that the simulations use only the ratios of the effective population sizes (i.e., Na/Nh, Nc/Nh, etc.), not their actual values. The actual Nh comes into play when interpreting the simulation results (e.g., translating from scaled time to actual time). Ideally, one would like to let
,
, Nc/Nh, Ng/Nh, No/Nh, Na/Nh, T1, T2, and T3 vary freely and determine which combination of parameter values maximizes the likelihood of observing the actual data. However, this is computationally prohibitive, so we fix those values for which we have prior information and let the others vary: Na/Nh, T1, T2, and T3 vary freely (at increments of 1.0, 0.25, 0.5, and 1.0, respectively), and we consider the following four schemes for the other parameters:
- Model 1:
=
= 0.001/bp; Nc = Ng = No = 3Nh. - Model 2:
ns for each locus is proportional to the total inferred number of mutations (across all four species), and the average
/bp (over all loci) is 0.001;
= 0.001/bp; Nc = Ng = No = 3Nh. - Model 3: Same as model 2, but all CpG sites were excluded, and the average
/bp (over all loci) is 0.00075. - Model 4:
= 0.001/bp;
= 0.002/bp; Nc = Ng = No = 3Nh. - Model 5:
=
= 0.001/bp; Nc = Ng = No = 6Nh.
can be easily estimated from human sequence polymorphism data (e.g., ![]()
= 0.001/bp is a good ballpark figure for the autosomes and that roughly one-fourth of all segregating mutations occur at CpG sites (e.g., ![]()
![]()
![]()
![]()
![]()
across loci by taking the same average
as model 1, but assuming that
ns for each locus is proportional to the observed number of inferred mutations. (This is equivalent to estimating
using ![]()
= 0.001/bp.) The genome-wide average rate of crossing over in humans is r = 1.3 x 10-8/bp (![]()
104, then
5.2 x 10-4/bp. We take slightly larger
values to account for the unknown contribution of gene conversion to overall rates of recombination (see, e.g., ![]()
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In addition to using the parameter combination that maximizes the likelihood as a point estimate, it would be useful to determine how much confidence we should place in the estimated values. To get a sense of how the likelihood varies as a function of T1, for example, I calculate the (approximate) profile likelihood:

Approximate 95% confidence intervals are found by using the standard
2 approximation for the likelihood-ratio statistic 2 ln(L0/L1) (where L0 is the maximum likelihood and L1 is the profile likelihood at an alternative point). The likelihood functions calculated are not true profile likelihoods, since some of the nuisance parameters are not allowed to vary freely. So, it is not clear whether the standard
2 approximation is appropriate. Approximate profile likelihoods are calculated for Na/Nh and T1, and linear interpolation is used to estimate the log-likelihood for parameter values that are not directly estimated by simulation.
To verify the accuracy of the method, I run coalescent simulations with known T1, T2, T3, and Na/Nh values; then, I use the new method on the simulated data to estimate parameters and to compare the estimated values with the actual ones. These simulations modeled 50 loci of 500 bp each, with
=
= 0.001/bp, Nc = Ng = No = 3Nh, T1 = 5.0, T2 = 8.0, T3 = 14.0, and Na/Nh = 5.0. The parameter values were chosen to roughly match both the ![]()
All programs were written in C and are available from the author on request. A total of 5 x 104 replicates were run for each model and parameter combination. To give a sense of the computational efficiency, the total simulations took 5 months to run on a pair of 1.7 GHz Pentium 4 processors.
| RESULTS |
|---|
The maximum-likelihood estimates for T1, T2, T3, and Na/Nh are presented in Table 2. The estimates across the five models are broadly similar; all of them estimate an ancestral population size five to six times larger than the current human effective population size, in keeping with previous studies (![]()
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To assess how much confidence we should place in the point estimates, I calculated approximate profile-likelihood curves and estimated
95% confidence intervals. The intervals for T1 and Na/Nh are listed in Table 2. For both T1 and Na/Nh the intervals are quite narrow, which suggests that the estimates are precise. All four models exclude Na/Nh
3.5 and Na/Nh
7.1 from the approximate confidence intervals. For T1, the lower boundaries range from 2.7 to 3.0 and the upper boundaries range from 4.2 to 4.8. If as before we take g = 25 years and N = 104, the upper boundaries range from 4.2 to 4.8 MYA; these times are still more recent than the paleontological record would suggest. As mentioned above, a small increase in Nh is sufficient to reconcile the time estimates with the paleontological record. Fig 3 shows the profile-likelihood functions of Na/Nh and T1 for model 2. The curves quickly become quite steep, suggesting that the range of plausible values is not that large. So, even if the approximate confidence intervals were nonconservative, it is likely that conservative ones would not differ much from the intervals listed in Table 2. The corresponding likelihood curves for the other models are qualitatively similar to those in Fig 3.
|
To verify the accuracy of the method, I applied it on five simulated data sets with known parameter values (see METHODS). Each one had actual values of T1 = 5.0, T2 = 8.0, T3 = 14.0, and Na/Nh = 5. The estimated parameter values, along with the confidence intervals for T1 and Na/Nh, are given in Table 3. The means of the parameter estimates are 5.0, 8.1, 14.0, and 4.8 for T1, T2, T3, and Na/Nh, respectively, which suggests that the method has no or low bias. In addition, the confidence intervals for T1 and Na/Nh contain the true value all five times. Due to the large computational burden, it was not possible to run enough replicates to accurately estimate the coverage properties of the confidence intervals.
|
Comparing the different rows in Table 2 can give us some idea of how sensitive the results are to assumptions about the nuisance parameters (i.e.,
,
, Nc/Nh, Ng/Nh, and No/Nh). Since the results from all of the models are very similar, it appears that the particular assumptions made do not appear to be very important. In particular, unlike the two-species maximum-likelihood method of ![]()
| DISCUSSION |
|---|
Estimating ancestral population sizes has been an active research area for several years. The work presented here improves on previous efforts by explicitly incorporating intragenic recombination (see also ![]()
![]()
One recent study that came to a different conclusion (namely, that Na is roughly as small as Nh) incorporated variation in mutation rates across loci but not intragenic recombination (![]()
![]()
Although this application focuses on the human-chimpanzee Na, the same method can be used to estimate Na from other taxa, as long as there are orthologous sequence data from three or more species (including at least one outgroup) at multiple unlinked loci. Below, I discuss issues that might affect the general applicability of the method.
Likelihood model:
One possible criticism of the model is that the relative locations of the segregating mutations are ignored. However, this is not likely to be very important, since the number and the pattern of segregating mutations are far more informative. Incorporating the segregating site locations may lead to narrower confidence intervals and more accurate estimation of the likelihood function, but excluding them is not expected to bias the results in either direction. Given the results, it does not seem to be worth the substantial computational burden to consider the full-likelihood model.
Mutational model:
The mutational model that was adopted makes no distinction between transitions and transversions and assumes the mutation rate at each site in a locus is the same. However, some sites have higher mutation rates than others (![]()
![]()
![]()
-arrest sites (![]()
![]()
Molecular clock:
The method described here assumes that the rate of mutation per unit time is the same on all branches. This is likely a reasonable assumption for the data considered here. Noncoding regions are less likely to be affected by natural selection than are the coding regions analyzed in other studies. Also, there is no reason to assume substantial differences in mutation rates (per generation) between humans and great apes. The data on generation times are sparse; ![]()
30 years (![]()
![]()
![]()
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For other taxa, the clock assumption may not be appropriate. It would be straightforward to generalize the model to have different rates of evolution on different branches and to estimate these as well as species divergence times and ancestral population sizes. More sequence data and more computational time would be required to accurately estimate the additional parameters, and the method (with variable rates) may not be feasible with more than three species.
Nuisance parameters:
Although the goal of this article is to estimate ancestral population sizes and species divergence times, the model presented here also includes other parameters, such as
,
, or Nc/Nh. The reason
is included is not to estimate the recombination rate from divergence data (which would be somewhat challenging). Rather, the values of parameters like
affect the likelihoods, so some assumptions must be made about them. In the interest of computational tractability, I have chosen plausible values for
,
, Nc/Nh, Ng/Nh, and No/Nh. Comparing model 1 with models 4 and 5 suggests that the choice of particular values for these other parameters may not affect the estimates of the parameters of interest. Further simulations show that this is true for a wider range of values (
= 0.00050.003/bp; Nh
Nc, Ng, No
6Nh), although it should be pointed out that assuming no recombination (as previous methods do) leads to a likelihood of 0, due to the presence of several incompatibilities within loci. So, the estimates of Na/Nh, T1, T2, and T3 are robust to the assumptions made about the other parameters.
Speciation model:
Estimates of Na/Nh and T1 provide information about the mean and the variance of the distribution of coalescent times of a single human and a single chimpanzee sequence. Under the simple speciation model considered here, greater variances in coalescent times must be the result of larger ancestral population sizes. Some researchers have suggested that there is often gene flow between "incipient species" (e.g., ![]()
| ACKNOWLEDGMENTS |
|---|
I thank M. Hare, M. Przeworski, N. Takahata, J. Wakeley, and an anonymous reviewer for comments on an earlier version of this manuscript. J.D.W. was supported in part by a National Science Foundation Postdoctoral Fellowship in Bioinformatics.
Manuscript received February 12, 2002; Accepted for publication October 14, 2002.
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