Abstract
26
Early Stuart sockeye salmon Oncorhynchus nerka undergo one of the most intensive and far-reaching 27
migrations in the Fraser River ( British Columbia, Canada) that has likely exerted selective pressure s 28
shaping their genetics and physiology. To support upper Fraser River sockeye management objectives, 29
there is a need to further understand the unique genetics of these populations. Based on neutral genetic 30
markers, Early Stuart sockeye are considered a metapopulation with little to no genetic differentiation 31
among their approximately 50 spawning streams. In this study we make use of existing resources to 32
evaluate genome-wide genetic differentiation in this metapopulation and put it into the context of other 33
nearby populations. We confirm that genetic differentiation is low or negligible in the metapopulation 34
at a whole-genome level, although we identify a slight increase in differentiation at greater distances 35
within the watershed compared to more proximal streams (e.g., FST = 0.001-0.002 compared with 36
undifferentiated). Even the greatest differentiation detected is very low, being nine times lower than 37
that between run timing groups (Early Stuart vs. Stuart-Summer; e.g., FST = 0.0091). Notably, a region 38
of major differentiation was detected between the run timing groups on Chr18 between 56.3-58.0 Mbp 39
(average FST = 0.661). This genomic region appears to contain a unique haplotype specific to the Stuart-40
Summer, Nadina River, and Stellako River populations (i.e., upstream to the Nechako River). By 41
contrast, Early Stuart and other upper Fraser River sockeye outside of the Nechako Watershed do not 42
possess this haplotype. The genomic region is within ancestral chromosome 15.2, the homeolog to a 43
chromosome arm of Chr12 (i.e., 15.1); this arm of Chr12 is known to contain a major differentiated 44
region associated with run timing and life history variation in Alaska and the Okanagan. This finding 45
provides additional evidence for the importance of this genomic region in both homeologous 46
chromosomes within different populations of the same species, and points to the uniqueness of upper 47
Fraser River sockeye in this potential major effect locus. 48
49
Keywords
Early Stuart; Fraser River; genomics; major effect locus; run timing; sockeye salmon 50
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Introduction
51
Genetic differentiation is a key metric to provide insight into population distinctiveness (Weir and 52
Cockerham 1984) and is the substrate for applications such as genetic stock identification (GSI). 53
Population differentiation can be evaluated using 10s of neutral microsatellite markers (e.g., Beacham 54
et al. 2004) or 100s of single nucleotide polymorphism (SNP) markers for example by amplicon panels 55
(Meek and Larson 2019) , 10,000s of SNPs through reduced representation sequencing (Baird et al. 56
2008; Peterson et al. 2012) or 100,000s to millions of SNPs through whole-genome resequencing 57
(Christensen et al. 2024; Bemmels et al. 2025). These approaches can recover similar trends, although 58
power can be influenced by population coverage and genomic coverage. Population coverage can 59
include collecting sufficient sample sizes to effectively represent the population, where more subtle 60
population structure can be identifiable at higher sample sizes (Araujo et al. 2014). Genomic coverage 61
is particularly critical when differentiation is specific to small regions of the genome, while the rest of 62
the genome remains in an undifferentiated state (e.g., Barry et al. 2024). These relatively small regions 63
with significantly increased differentiation relative to the rest of the genome may involve adaptive 64
variation (Tigano and Russello 2022) and/or structural variation such as inversions (Akopyan et al. 65
2025), which can prevent local recombination, retaining haplotypes of adaptive alleles (Wellenreuther 66
and Bernatchez 2018). 67
The Fraser River watershed is the largest sockeye salmon Oncorhynchus nerka complex in 68
British Columbia (BC), Canada, and has the greatest sockeye abundance in the world for any single 69
river system (COSEWIC 2017) . Over the past century, there have been significant declines in all 70
species of salmon in the Fraser River; based on genetic evidence, sockeye salmon have had particularly 71
drastic declines (Christensen et al. 2024). Multiple salmon species show similar trends in hierarchical 72
population genetic structure in the Fraser River , with the greatest differences observed among broad 73
regional groupings of lower, middle, and upper Fraser River (greatest between the lower and middle, 74
likely due to the significant migration barrier of the Fraser Canyon; Christensen et al. 2024) . Th e 75
overall population structure of sockeye salmon in the Fraser has been documented using multiple 76
different marker types, includin g microsatellites and SNPs (Beacham et al. 2004; Rondeau 2022) . 77
Subgroupings and structure among spawning locations is generally based on geographic proximity as 78
well as ecotype and run timing (Beacham et al. 2004; Beacham and Withler 2017) . The genetic 79
diversity of Fraser River salmon collectively represents the standing genetic variation for the species 80
in the region, and holds adaptive traits and genetic diversity that is irreplaceable on timescales that are 81
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relevant to humans (Waples et al. 2001; COSEWIC 2017), critical for fisheries, culture, and resilience 82
to climate change. 83
Early Stuart sockeye spawn in the upper Stuart River watershed, a major sub-basin of the Fraser 84
River watershed in central BC that is comprised of two large lakes, Takla Lake and Trembleur Lake, 85
that are connected by the wide and shallow Middle River (Bradford and Braun 2021) . Early Stuart 86
sockeye are the sole representative of the Early Stuart run timing group, one of the four run timing 87
designations in the Fraser River (COSEWIC 2017). Early Stuart sockeye have the earliest upstream 88
migration of all Fraser River sockeye (Idler and Clemens 1959; Bradford and Braun 2021). Returning 89
adults enter the Fraser River in early July and quickly migrate to spawning streams in the Stuart system, 90
where peak spawning occurs in natal streams in mid -August (Bradford and Braun 2021) . 91
Approximately half of the Early Stuart run timing group passes Hell’s Gate by July 14 th, whereas the 92
early summer, summer, and late run timing groups correspond to Aug. 6 th, Aug. 17th, and Sept. 21 st, 93
respectively (COSEWIC 2017) . The Early Stuart sockeye and other neighbouring populations, 94
including the Stuart-Summer sockeye, must travel great distances and overcome significant river force 95
(Wright et al. 2025) to reach the spawning grounds . This migration is thought to have shaped Early 96
Stuart sockeye genetics and physiology through long-exerted evolutionary forces based on energetic 97
requirements and local environments of the route (Hinch and Rand 1998; Rand et al. 2006; Crossin et 98
al. 2004; Eliason et al. 2011). Early Stuart sockeye have smaller and more fusiform body shapes than 99
other deeper bodied morphologies that occur in sockeye populations with easier routes, higher somatic 100
energy density, fewer carried eggs and exhibit more efficient travel (Gilhousen 1980; reviewed by 101
Crossin et al. 2004) , are capable of higher aerobic scope and cardiac capacity (Crossin et al. 2004; 102
Eliason et al. 2011). 103
Early Stuart sockeye are considered to exist in a metapopulation, or a collection of streams that 104
all comprise one large population with some extent of gene flow expected between streams (Bradford 105
and Braun 2021). The sockeye populations that spawn most temporally and geographically proximal 106
to the Early Stuart sockeye are from the genetically distinct Stuart-summer run timing group (Beacham 107
et al. 2004; Rondeau 2022) . Of the over 50 Early Stuart spawning sites within the Stuart River 108
watershed (COSEWIC 2017), 36 streams have been characterized in detail by Bradford and Braun 109
(2021), who report that 12 streams contain good and stable habitat, are occupied in more than 90% of 110
evaluated years, and contain at least 85% of the spawners of the metapopulation. The other 24 streams 111
exhibit poorer habitat, are not persistently abundant with spawners, and are periodically recolonized 112
by dispersers from the 12 strong streams, which are therefore considered to be the key to the resiliency 113
of the system (Bradford and Braun 2021). Genetic characterization with high numbers of samples and 114
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microsatellite or SNP markers have not identified significant population structure in the 115
metapopulation (Beacham et al. 2004; Rondeau 2022) , and so the current expectation for the 116
metapopulation is panmixia. However, this type of analysis has yet to be conducted at a genome-wide 117
level. Evaluating differentiation in the metapopulation at this scale will provide valuable information 118
to support management and conservation objectives. 119
The primary purpose of this work is to determine whether any neutral or putatively functional 120
genetic variation , including that within punctuated and relatively small genomic regions, are 121
differentiated between sockeye spawning in individual tributaries used by Early Stuart sockeye salmon. 122
A secondary objective is to determine whether unique characteristics exist in the genome of the Early 123
Stuart sockeye relative to Stuart-Summer or other nearby populations that can aid in our understanding 124
of differences between these populations. By using the recently published genome-wide SNP data for 125
Fraser River sockeye salmon (Christensen et al. 2024), we directly address these two objectives in the 126
aim to guide conservation and management of these important populations. 127
128
Methods
129
Samples and genotypes 130
Multilocus genotypes were obtained as a VCF file from a recent study on salmonids of the Fraser River 131
(see Data Availability; Christensen et al. 2024). The VCF file was subset with bcftools (Danecek et al. 132
2021) to retain sockeye collections from the mid- or upper-Fraser River (Table 1). Annotations were 133
added to the VCF file and SNPs were filtered to only retain those with minor allele frequency (MAF) 134
> 0.01. An additional dataset was generated for use in population genetic analyses by filtering for MAF 135
> 0.05 and removing SNPs in high linkage (maximum r2 = 0.5 in 50 kb windows) using bcftools. 136
137
Population genetics 138
The population genetic dataset (MAF > 0.05 and LD -filtered) was used as an input to a principal 139
components analysis (PCA) including all samples. Region-specific analyses were also conducted, with 140
datasets filtered for (1) all waters that flow into the Nechako River (i.e., Early Stuart, Stuart-Summer, 141
Nadina River, and Stellako River); (2) all waters that flow in to the Quesnel River (i.e., Quesnel and 142
Horsefly); and (3) all waters that flow into the Chilcotin River (i.e., Chilko Lake, Chilko River, Taseko 143
River). The region-specific analyses used PCA to identify general trends, and discriminant analysis of 144
principal components (DAPC) to identify loci contributing to the separation of the most differentiated 145
groups in each dataset. Loading values for these loci were plotted on sockeye salmon chromosomes 146
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(GCF_034236695.1; Christensen et al. 2020) using fastman (Paria et al. 2022) . To investigate 147
substructure within the Early Stuart sockeye, a dataset was generated containing only the Early Stuart 148
collections, and a DAPC was conducted and loading values plotted across the chromosomes. Genetic 149
differentiation was evaluated using FST (Weir and Cockerham 1984) calculated as the average of all 150
per-locus FST values between specific contrasts calculated by VCFtools (Danecek et al. 2011). 151
152
Outlier region characterization 153
To explore a detected region of increased differentiation, the full dataset with all SNPs (MAF > 0.01) 154
was limited to only Chr18 and only Early Stuart and Stuart-Summer samples (i.e., the two genetically 155
most proximal populations that exhibited the elevated differentiation on Chr18. Monomorphic and low 156
MAF loci (MAF ≤ 0.01) in the subset dataset were removed and per-locus FST was calculated for all 157
loci on Chr18 using pegas (Paradis 2010) in R (R Core Team 2025) . To understand the geographic 158
context of the differentiated region, the section of the chromosome with FST > 0.5 was identified and 159
SNPs from this region for all individuals in the study were selected using bcftools and read into R 160
using vcfR (Knaus and Grünwald 2017). Genotypes were converted to allele dosage and plotted in a 161
heatmap in R, allowing dendrogram clustering of samples , but not SNPs, using heatmap function 162
defaults. 163
To inspect the genomic context of the differentiated region, the identified region and its 164
flanking sections were inspected for annotated genes in NCBI and for indications of inversions based 165
on manual inspections of short read alignments, respectively. The SNP positions from the genome used 166
by Christensen et al. (2024) were converted to the latest genome available in NCBI (i.e., 167
GCF_034236695.1; Christensen et al. 2020) using SNPlift (Normandeau et al. 2023) . The region of 168
interest was confirmed to be in a similar position based on the positions of the SNPs delimiting the 169
region, as well as re -running an FST analysis for the Stuart River system samples only with the 170
converted dataset. Inspections for structural variation was explored using two representative samples 171
from each haplotype group (i.e., unique haplotype to upstream to Nechako represented by Kuzkwa 172
River, and the haplotype more typical of the rest of the Fraser River from the Driftwood River). These 173
samples were obtained as fastq data from NCBI using SRA -toolkit. The samples were trimmed for 174
quality using cutadapt (Martin 2011), and aligned against Chr18 of the reference genome using bwa 175
mem (Li 2013). All alignments or discordant alignments were inspected using the Integrated Genomics 176
Viewer (IGV; Robinson et al. 2011) with a focus on the delimiters of the elevated differentiation region 177
for indications of inversions. 178
179
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Results
180
Population genetic structure in upper Fraser River sockeye salmon 181
Upper Fraser River sockeye salmon samples sourced from Christensen et al. (2024) that are included 182
in the present analysis are presented in Table 1 and include the following regions: Stuart (Early Stuart, 183
Stuart-Summer), Nadina/Francois, Francois/Fraser, Bowron, Quesnel and Horsefly, and Chil ko. For 184
each collection included, year of sampling was obtained from Christensen et al. (2024), and run timing 185
designations were sourced from Rondeau (2022). 186
Population genetic trends were explored using linkage filtered SNPs (n = 627,769 ; MAF > 187
0.05). A PCA clustering all samples by SNPs shows four main clusters in PC1 and PC2 (Figure 1A; 188
PVE = 3.6% and 1.8%, respectively) . These clusters include the populations using tributaries to the 189
Nechako River as natal habitat (i.e., both run timing groups from the Stuart River watershed, Nadina, 190
and Stellako), the Bowron River, Quesnel/Horsefly, and the Chilcotin Watershed (Figure 1A). 191
Populations from Quesnel, Horsefly, and Chilcotin regions have a similar position on PC1 but are 192
separated across PC2. A genetic dendrogram shows similar groupings, with the largest difference in 193
the data being between the populations upstream to the Nechako from the other collections (Figure 194
S1). The second grouping contains Bowron as the most external population to the grouping, followed 195
by Chilcotin region populations, and a grouping containing Quesnel and Horsefly populations, which 196
are grouped together but in separate branches (Figure S1). Some indication of unexpected clustering 197
due to low sample size is suggested by the dendrogram, with Felix (n = 5) and Takla (n = 4) collections 198
grouping closely and separately from other collections , as well as poor clustering of Middle River (n 199
= 7) and Pinchi (n = 4). Notably, Driftwood (n = 7) also clusters on the outside of the other Early Stuart 200
collections. 201
Within-region variation was inspected for populations upstream to the Nechako River (n = 96 202
samples, 12 collection sites, and 620,725 SNPs). A PCA groups all Early Stuart collections separately 203
from Stuart-Summer, Nadina, and Stellako on PC1 (PVE = 2.7% ; Figure 1B) . Nadina and Stellako 204
collections grouped generally with the Stuart -Summer for some samples along PC1, but other 205
individual samples within these collections cluster distantly on both PC1 and PC2. Applying a DAPC 206
separates three groups: (1) Early Stuart; (2) Stuart-Summer and Stellako; and (3) Nadina (Figure 2A). 207
Loci contributing the most to this separation were clustered in a region on Chr18, showing a peak that 208
is significantly elevated relative to the rest of the genome (Figure 2B; see Major differentiating region 209
on Chr18 below). 210
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Populations upstream to the Chilcotin River (n = 45 samples, 611,274 SNPs) evaluated by PCA 211
found that all Chilko Lake and Chilko River samples (run timing: Summer) grouped together and 212
separately from the Taseko River collection (run timing: Early Summer ; Figure S2A ; PC1 PVE = 213
5.3%). These two groups were strongly separated by DAPC (Figure S2B) and the loci separating the 214
groups came from throughout the genome without any clear outlier regions (Figure S2C). 215
Populations upstream to the Quesnel River (n = 59 samples, 612,528 SNPs) evaluated by PCA 216
found overlap in groupings within some Quesnel collections, and separate clustering of the Horsefly 217
collections (i.e., Horsefly and McKinley; Figure S3A; PC1 PVE = 5.4%). A DAPC recovered similar 218
trends (Figure S3B) , and loci contributing to the separation o f Quesnel and Horsefly came from 219
throughout the genome, with no clear indication of outlier genomic regions (Figure S3C). 220
221
Major differentiating region on Chr18 222
The major differentiating region on Chr18 observed between the Early Stuart and Stuart -Summer, 223
Nadina and Stellako populations (Figure 2B) was explored further. The approximate genomic 224
coordinate boundaries of the outlier region , based on these populations, were identified as being 1.7 225
Mbp in size and spanning from 56,293,719 - 57,982,347 bp, a region with average (± s.d.) FST of 0.661 226
± 0.133 (Figure 3A). 227
To understand the geographic context of the differentiated region, a heatmap was constructed 228
including the 10,563 SNPs within the genomic region (MAF > 0.01) from all samples in the study (n 229
= 210; Figure 3B). The heatmap shows a distinct haplotype with low heterozygosity specific to the 230
grouping of Stuart-Summer, Nadina, and Stellako, whereas the rest of the upper Fraser River 231
collections (including Early Stuart) do not have this haplotype. The top differentiated SNPs had FST 232
values of 0.975 and were at positions 57,673,269 bp, 57,712,980 bp, and 57,982,347 bp. These three 233
SNPs show near fixation between the more derived grouping ( i.e., Stuart-Summer, Nadina, Stellako) 234
and the rest of the samples (Additional File S1). For example, SNP Chr18:57,712,980 is a homozygous 235
alternate genotype (A/A) in 49 of 50 samples and a heterozygote in one sample (from Tachie) in the 236
Stuart-Summer/Stellako/Nadina grouping, and is homozygous reference (G/G) in 158 of 160 samples 237
and heterozygous in two samples (both from Horsefly River) in the rest of the upper Fraser River 238
populations analyzed. The other two SNPs show the same pattern, or exhibit three heterozygotes in the 239
Horsefly River (for SNP Chr18:57,712,980). Visualizing read alignments from representatives of each 240
grouping of the major differentiation region with a focus on discordant alignments in flanking genomic 241
regions did not provide any clear evidence of an inversion (data not shown). 242
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The annotated gene content in the outlier region was inspected, finding 48 annotated putative 243
genes (RefSeq annotation; Additional File S2). Putative genes within this region included leucine-rich 244
repeat-containing protein 9-like (lrrc9-like; 56.33-56.36 Mbp), fibroblast growth factor receptor-like 245
1 (56.48-56.56 Mbp), and homeobox protein OTX2 (57.88-57.89), among others. 246
247
Metapopulation differentiation in Early Stuart sockeye 248
To determine whether the whole-genome data indicates genetic distinctiveness or separation between 249
tributaries within the Early Stuart metapopulation, a limited dataset with the four populations with the 250
greatest sample sizes was analyzed (i.e., between 7-10 samples per site; total n = 37 samples, 611,155 251
SNPs). The four collections were sourced from throughout the two-lake system, including Driftwood 252
River from the northern end of Takla Lake (n = 7), Dust Creek from the western arm of Takla Lake (n 253
= 10), Bivouac Creek from the southern end of Takla Lake (n = 10), and Paula Creek from the western 254
end of Trembleur Lake (n = 10). All of these samples were collected in 2005 (Table 1). 255
Many of the contrasts within this system showed 95% confidence intervals (CI) for FST that 256
overlapped zero, suggesting no discernable differentiation at a genome -wide scale between the 257
tributaries (Table 2). Two of the contrasts had very low, non-zero FST values: Driftwood River-Bivouac 258
Creek and Driftwood River-Paula Creek 95% CI FST of 0.0017-0.0021 (mean = 0.0019) and 0.0008-259
0.0012 (mean = 0.0010) , respectively. A PCA shows a general overlap of all ellipses around each 260
collection (Figure S4A), suggesting low to negligible FST. A DAPC recovers similar trends to the FST 261
contrasts, where Driftwood is projected furthest from Bivouac Creek and Paula Creek, although some 262
overlap exists between Bivouac Creek and Driftwood River (Figure 4). Therefore, the most distant 263
locations geographically ( i.e., Paula Creek or Bivouac Creek with Driftwood River) were the most 264
distant genetically, albeit with very low genetic difference. Notably, there were no genomic regions 265
showing elevated contributions to the separation of the Early Stuart collections by DAPC (Figure S4B), 266
suggesting equal differentiation or lack thereof throughout the genome. 267
To put the slight non-zero genetic distance observed between the Driftwood River and Paula 268
Creek into context, contrasts between an Early Stuart collection (Paula Creek) and populations from 269
outside the Early Stuart group were conducted. Paula Creek compared with Kuzkwa River (Stuart -270
Summer) shows an average genome-wide FST of 0.0091 (95% CI: 0.0089-0.0093) based on this dataset, 271
which is 9.1x higher than Driftwood River vs. Paula Creek. Paula Creek compared with Bowron River 272
shows an average genome -wide FST of 0.0355 (95% CI: 0.0353 -0.0358), or 35.5x higher than 273
Driftwood vs. Paula. 274
275
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Discussion
276
The present study took an in -depth and region -specific investigation into genome-wide genetic 277
variation within the upper Fraser River sockeye salmon through the re -use of existing genomic 278
resources generated as part of a three-species analysis of the Fraser River salmonids (Christensen et al. 279
2024). General population genetic trends were similar to those observed using other resources 280
including microsatellites (Beacham et al. 2004) or SNPs (Rondeau 2022) , with some notable 281
exceptions, as described below. 282
283
Major region of differentiation on Chr18 in sockeye from the Nechako Watershed 284
A main finding of this work was the identification of a major differentiating region between the Early 285
Stuart sockeye and the Stuart-Summer/Nadina/Stellako sockeye. This genomic region may be involved 286
in phenotypic variation in run-timing between these groupings. The Nadina and Stellako populations 287
are considered to be Early Summer and Summer run timing groups , respectively (COSEWIC 2017). 288
The unique haplotype identified here appears to be in a derived form with low heterozygosity in the 289
Stuart-Summer/Nadina/Stellako samples, as the Early Stuart samples share alleles with samples from 290
other populations within the upper Fraser River. Interestingly, some variants within this haplotype are 291
nearly fixed between the Stuart-Summer/Nadina/Stellako grouping and the rest of the upper Fraser 292
River. At the most differentiated loci, there are very few heterozygous genotypes in either grouping . 293
This suggests that these populations have very low gene flow between the haplotype groups. There 294
was no clear evidence of an inversion in the area, but this remains inconclusive as the current available 295
data was comprised of short reads, whereas a long -read analysis could provide a more definitive 296
Conclusion
regarding structural variation. 297
The putatively derived state of the haplotype in the Stuart-Summer/Nadina/Stellako groupings 298
poses interesting questions around the emergence of this haplotype, as the putatively ancestral form is 299
present in the group with the unique run timing designation, i.e., the Early Stuart sockeye. If the unique 300
haplotype is related to phenotypic run timing variation, it therefore follows that the derived phenotype 301
would be that of the Stuart-Summer/Nadina/Stellako grouping. If this genomic region underlies run 302
timing variation, this may indicate that the early run for Early Stuart sockeye is the ancestral run timing 303
form, and the later runs to the region (e.g., Stuart -Summer) would be an adaptation allowing for 304
expanded timing of spawning resource access (as discussed by Barry et al. 2024). However, it is also 305
possible that the unique region of differentiation is not related to run timing but is rather only coincident 306
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to the run timing difference between the analyzed groups. However, other details around the major 307
differentiated region on Chr18 suggest involvement in run timing or other life history variation. 308
The region of major differentiation on Chr18 at 56.3 – 58.0 Mbp falls within the sockeye 309
salmon chromosome arm that corresponds to the ancestral chromosome 15. 2 (see Sutherland et al. 310
2016). The ancestral designation is related to the post -whole-genome duplication chromosome 311
correspondence where each of 25 ancestral chromosomes has two copies in the present-day salmonid 312
genome, and where the 25 chromosomes roughly correspond to the present -day northern pike Esox 313
lucius genome (Rondeau et al. 2014). Importantly, a major differentiated section on the chromosome 314
arm of Chr12 of sockeye salmon and Chr10 of pink salmon has been identified as being involved in 315
run timing in Alaska (Barry et al. 2024). These two chromosomes both contain 15.1, the homeolog (or 316
ohnolog) to 15.2 (Sutherland et al. 2016; Christensen et al. 2020; Barry et al. 2024) . Furthermore, a 317
major differentiating region of Chr12 is associated with life history variation in Okanagan O. nerka 318
(Tigano and Russello 2022). Recently, this region has been proposed as a master regulatory region in 319
multiple salmonid species including pink salmon O. gorbuscha, chum salmon O. keta, and sockeye 320
salmon in Alaska (Barry et al. 2024; Barry et al. 2025). Secondary regions of high differentiation have 321
been identified on the homeolog 15.2 in chum salmon and coho salmon O. kisutch related to run timing 322
(ancestral 15.2 or chum Chr29; Barry et al. 2025), but not yet in sockeye salmon until the present work. 323
A gene of interest in the genomic region of differentiation previously identified and highlighted 324
is leucine-rich repeat -containing protein 9 (lrrc9) (Barry et al. 2024) . The region of major 325
differentiation in the Stuart sockeye identified here contains a gene annotated as lrrc9-like, the 326
homeologous gene to lrrc9 highlighted previously. However, in the sockeye salmon genome, this gene 327
is annotated as a putative pseudogene by the NCBI RefSeq annotation. Interestingly, Barry et al. (2025) 328
propose that the region of differentiation is likely driving phenotypic effects through transcription 329
regulation activity rather than changes in protein coding sequences due to the lack of non-synonymous 330
mutations identified and the prevalence of transcription factors in the region. If lrrc9-like is a 331
pseudogene, this would support the lack of direct involvement of this gene in any downstream 332
phenotype. There are other genes in the major differentiated region identified here in sockeye salmon 333
that may be of interest regarding a migratory timing phenotype, most notably homeobox protein OTX2 334
(orthodenticle homeobox 2), a transcription factor involved in brain and sensory organ development 335
(Beby and Lamonerie 2013) . OTX2 is involved in the formation of the pituitary gland in zebrafish 336
(Bando et al. 2020) , and the pituitary -gonadal axis activity in salmonids is connected to season and 337
directly related to homing adults, return migration and spawning preparation (Onuma et al. 2009; Ueda 338
2011). Furthermore, the role of OTX2 in the development of olfactory system, including imprinting 339
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and homing has been demonstrated in the anemonefish Amphiprion percula (Veilleux et al. 2013), of 340
interest given the important role of the olfactory system in homing migration in sockeye salmon (Bett 341
et al. 2018). 342
The present study therefore identifies new evidence that points to potential involvement of the 343
proposed master control region on ancestral chromosome 15 in a completely different population to 344
that originally identified, and that has taken an alternate homeologous chromosome path to that which 345
was previously identified in sockeye salmon (Tigano and Russello 2022; Barry et al. 2024) . This 346
supports the conclusions of Barry et al. (2025), and points to unique genetics and evolutionarily 347
significant adaptation route of the upper Fraser River sockeye salmon. As functional analysis of the 348
major differentiated region here has not been conducted, the role of this region in run timing remains 349
putative. Although other run timing differences are reported in the populations analyzed in this study, 350
most notably the two run timings of the Chilcotin Watershed sockeye (i.e., Chilko as Summer and 351
Taseko as Early Summer), there were no similar regions of major differentiation observed in these 352
other populations using the available samples. 353
Considering the important role of ancestral chromosome 15.1 and 15.2, it is worth briefly 354
noting other features of these chromosomes in the evolution of salmonids. First, these chromosomes 355
are part of ancestral and conserved fusion events; ancestral 15.1 is proposed to have been fused to 4.1 356
prior to the divergence of genera Salmo and Oncorhynchus, although lineage -specific fissions and 357
fusions occurred in the lineage leading to the pink, chum, sockeye branch (Sutherland et al. 2016) . 358
Ancestral 15.2 was part of a conserved fusion to 25.2 that occurred prior to the diversification of 359
Oncorhynchus; this fusion remains in all Oncorhynchus species. Second, the ancestral chromosome 360
15.1 is within the chromosome that holds the master sex determining gene in Arctic charr Salvelinus 361
alpinus and brook charr S. fontinalis (Sutherland et al. 2017) . Although these features may not be 362
related to the specific life history and run timing variation described here, given the proposed role of 363
this genomic region as a master control region for multiple salmonid species, continued understanding 364
of these chromosomes may yield valuable insights in the evolution of phenotypic variation in the 365
salmonids. 366
367
Metapopulation genetics in Early Stuart sockeye 368
Using genome-wide data we found some evidence of increased genetic differentiation with distance 369
within the Early Stuart spawning tributaries, specifically that only the spawning sockeye from the most 370
distant tributaries showed non-zero FST. However, this level of differentiation was still very low, being 371
9-times lower than that which occurs between run timing groups. Further, in this genome -wide 372
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analysis, we did not identify any regions with elevated differentiation relative to the rest of the genome, 373
suggesting that the results from panels of neutral markers should be similar to that obtained with 374
genome-wide data. In the absence of large genetic differences among spawning tributaries of Early 375
Stuart sockeye, i t is possible that any phenotypic variation observed between streams could be 376
associated with plasticity, environmental effects, or epigenetic differences between populations 377
(Lamka et al. 2022). The greatest differentiation identified was still much lower than the FST 0.01 cutoff 378
proposed as the lower limit of what is possible for genetic stock identification (GSI) (Araujo et al. 379
2014). Therefore, these results support previous work indicating an inability to discriminate between 380
populations using GSI (Beacham et al. 2004; Rondeau 2022) , and support the connectivity and 381
characteristics of a metapopulation (Bradford and Braun 2021), but do provide some evidence for slight 382
spatial differentiation that is worthwhile considering as not completely panmictic. Although low 383
sample size appears to have resulted in misplaced populations in the genetic dendrogram (most 384
noticeable with sample size under n = 5), and therefore raises the potential concern that this could drive 385
the non-zero FST observed between Driftwood and other more distant streams, the observation that 386
Driftwood (n = 7 ) compared to Dust Creek (n = 10) , the more proximal sampling location, had an 387
estimated zero differentiation indicates that the conclusion of no differentiation could be determined at 388
this sample size. It should also be noted that the samples used to represent the Early Stuart sockeye in 389
this study were from 2005 , and if large scale genetic changes occurred for salmon spawning in these 390
tributaries since 2005, these results may not reflect current day genetic signatures. 391
Further investigation of the extent of gene flow in this metapopulation could be conducted by 392
parentage-based tagging (i.e., PBT) or other tagging methods that track returning adults to determine 393
the extent of flow between tributaries. Furthermore, epigenetic analyses could be conducted to 394
determine the level of differentiation epigenetically between streams with different environmental 395
parameters (Venney et al. 2021; Lamka et al. 2022). 396
397
Conclusions
398
In the present study we made use of existing genomic resources to characterize upper Fraser River 399
sockeye salmon populations from waterbodies that flow into the Nechako (including Nadina, Stellako, 400
and Stuart River systems), the Bowron River, Quesnel and Horsefly, and the Chilcotin Watershed. This 401
analysis would not have been possible without the generation and publication of large -scale, open-402
source genomic resources and metadata. The finding of a major differentiating region on Chr18 403
(ancestral 15.2) between two conservation units (Early Stuart and Stuart-Summer) with differing run 404
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timings points to the potential for this region to contain adaptive variation underlying the run timing 405
phenotype, although interestingly the more unique run timing (i.e., Early Stuart) was in the grouping 406
with the putatively more ancestral form of the haplotype on Chr18. Convergence upon the Chr18 (15.2) 407
chromosome near the lrrc9-like gene fits with other work that has proposed that this region, in both 408
duplicate chromosomes, is a major control region of run timing, evolving independently in multiple 409
species. This region and the genes within it, including otx2, merit further investigation. The genome-410
wide data on the Early Stuart metapopulation supports previous work indicating differentiation being 411
too low for GSI, but does identify a very minor increase in differentiation with increased geographic 412
distance within the Early Stuart spawning tributaries . These results collectively provide new insights 413
on upper Fraser River sockeye salmon that will be useful for conservation and management. 414
415
Acknowledgements
416
Thanks to Drs. Ben Koop , Eric Rondeau , and Kris Christensen for discussion on the major 417
differentiation region, and to Linda Stevens of UFFCA for technical support on the project. Thanks to 418
the UFFCA for supporting this work in the interests of Upper Fraser First Nations. 419
420
Funding 421
Funding for this work was made available via the Pacific Salmon Strategy Initiative in support of the 422
Tuzist'ol T'ah process. Tuzist'ol T'ah is a collaboration between the Upper Fraser Fisheries 423
Conservation Alliance, Binche Whut’en, Nak’azdli Whut’en, Takla Nation, Tl’azt’en Nation, 424
Yekooche Nation, Province of British Columbia, and Fisheries and Oceans Canada tasked with 425
developing a recovery strategy for Early Stuart Sockeye. 426
427
Competing Interests 428
BJGS is affiliated with Sutherland Bioinformatics. The authors have no competing financial interests to 429
declare. 430
431
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Data Availability 432
SNP data were downloaded from FigShare: https://doi.org/10.25387/g3.25705428.v1 433
The following analytic repositories supported this analysis: 434
Code and README for project: https://github.com/bensutherland/ms_oner_estu 435
Population genetic functions: https://github.com/bensutherland/simple_pop_stats 436
437
Additional Materials 438
A Supplemental Results section is provided with supplemental figures and tables. 439
Additional File S1. Genotypes of top differentiated loci in major differentiation region. 440
Additional File S2. Annotated gene content in major differentiation region. 441
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Figures 563
564
565
Figure 1. (A) All upper Fraser River samples clustered by principal components analysis (PCA) using 566
MAF and LD -filtered SNPs (n = 627,769) shows main groupings of study, including the Nechako 567
Watershed (negative PC1), the Bowron River (positive PC1), the Chilcotin Watershed (negative PC2), 568
and Horsefly and Quesnel regions (positive PC1 and PC2). (B) PCA with only the populations from 569
the Nechako Watershed shows Early Stuart grouping separately from Stuart-Summer, which were more 570
genetically proximal to populations from the Nadina River and Stellako River. 571
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572
573
Figure 2. (A) Discriminant analysis of principal components (DAPC) analysis of populations from the 574
Nechako Watershed including Early Stuart, Stuart -Summer, Nadina River, and Stellako River shows 575
separation across discriminant function 1 ( DF1) from the Early Stuart and Stuart -Summer (and 576
Stellako), and Nadina River grouping separately. (B) The loadings of SNP loci contributing to the 577
separation on DF1 indicate a major contributing genomic region on Chr18. 578
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579
Figure 3. (A) Genetic differentiation by FST within the Nechako Watershed for Chr18 between the 580
Early Stuart and Stuart summer populations. (B) Heatmap of the differentiated genomic region based 581
on allelic dosage of alternate alleles (0, 1, 2) coloured as grey, yellow, and blue, respectively. All 582
samples from the study (n = 210) were included and allowed to cluster based on genotypes. Samples 583
are coloured on the vertical axis based on the source collection site as indicated in the legend. 584
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585
Figure 4. Disciminant analysis of principal components (DAPC) of collections from Early Stuart 586
spawning tributaries that contained at least seven samples each. 587
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Tables 588
Table 1. Samples available for the analysis from Christensen et al. (2024) genotyped by whole-genome 589
resequencing. Collection names and dates were provided in sample metadata from the original study, 590
full names were determined from BC Geographical Names (Government of BC ), and run -timing 591
designations were obtained from Rondeau (2022). 592
593
Region Run-Timing Collection Full Name Sample
size
Year(s)
sampled
Stuart Early-Stuart Bivouac Bivouac Cr. 10 2005
Driftwood Driftwood R. 7 2005
Dust Dust Cr. 10 2005
Felix Sidney (Felix) Cr. 5 2005
Paula Paula Cr. 10 2005
Takla Takla Lk. 4 unkn.
Summer Kuzkwa Kuzkwa R. 9 2001
Middle Middle R. 7 2001
Pinchi Pinchi Cr. 4 2005
Tachie Tachie R. 11 2012, unkn.
Nadina/Francois Early summer Nadina Nadina R. 9 2000
Francois/Fraser Summer Stellako Stellako R. 10 2011
Bowron Early summer Bowron Bowron R. 10 2001
Quesnel Summer BlueLead Blue Lead Cr. 5 2001
McKinley McKinley Cr. 9 2001
Mitchell Mitchell Bay 8 2001
Wasko Wasko Cr. 5 2001
Horsefly* Horsefly R. and
Lk.
24 2001, unkn
Quesnel Quesnel R. and
Lk.
8 2013
Chilcotin Summer Chilko* Chilko R. and Lk. 35 2001, 2008,
unkn
Early Summer Taseko Taseko R. 10 2011
TOTAL 210
*includes various sub-naming 594
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Table 2. (A) Average FST between Early Stuart collections showing non -weighted estimate in the 595
bottom and weighted estimate in the top section; or (B) 95% confidence interval of FST showing the 596
upper limit in the top and lower limit in the bottom. 597
598
(A) 599
Bivouac Driftwood Dust Paula
Bivouac NA 0.0056 0.0010 0.0008
Driftwood 0.0019 NA 0.0022 0.0046
Dust -0.0011 -0.0009 NA 0.0016
Paula -0.0011 0.0010 -0.0006 NA
600
(B) 601
Bivouac Driftwood Dust Paula
Bivouac NA 0.0021 -0.0009 -0.0010
Driftwood 0.0017 NA -0.0007 0.0012
Dust -0.0013 -0.0011 NA -0.0004
Paula -0.0013 0.0008 -0.0007 NA
602
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