Keywords
testis, germ cells, spermatozoa, RNA, sncRNA 13
Running Head: EGME dose-dependent sperm sncRNAs 14
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Abstract
15
Ethylene glycol monomethyl ether (EGME) is a testicular germ cell toxicant that selectively 16
targets spermatocytes. In rats, male-only EGME exposure reduces mating success and can 17
lead to an increase in resorbed fetuses. In a previous study, five-day exposure to 50, 60, or 75 18
mg/kg/d EGME in male rats led to a decrease in sperm motility and increase in retained 19
spermatid heads with a LOAEL of 75 mg/kg/d. At 60 mg/kg/d, EGME exposure altered the 20
proportion of sperm small RNA reads mapped to different small RNA categories and the 21
distribution of read lengths. Because there is evidence that small non-coding RNAs (sncRNAs) 22
in sperm regulate embryonic development, we analyzed sperm sncRNA data from EGME-23
treated male rats to identify differential expression at the individual RNA level. EGME treatment 24
resulted in dose-dependent increases in the expression levels of microRNAs (miRNAs), 25
piRNAs, and tRNA-derived small RNAs (tsRNAs). We identified 12 miRNAs that were 26
differentially expressed at all EGME doses, with a monotonic, dose-dependent increase. High-27
confidence targets of these 12 miRNAs are known to be expressed in pre-implantation embryos 28
and statistically enriched for Gene Ontology (GO) biological processes related to early 29
development, such as cell fate commitment and regulation of developmental growth. These 30
Results
demonstrated that the EGME-induced changes in sperm sncRNA levels were 31
reproducible, dose-dependent, and provided a putative mechanism of paternal EGME effects on 32
embryonic development, which will be investigated in future studies. 33
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Introduction
34
Ethylene glycol monomethyl ether (EGME) is a well-characterized testicular toxicant in 35
the rat. Upon oral exposure, EGME is metabolized to the active metabolite, 2-methoxyacetic 36
acid (MAA) (Beattie and Brabec 1986). EGME selectively targets pachytene and meiotic 37
spermatocytes, resulting in apoptosis (Creasy and Foster 1984; Creasy et al. 1986). EGME-38
induced germ cell death is rapid, detectable at 12 hours after a dose of 250 mg EGME/kg body 39
weight (Creasy et al. 1986) and 24 hours after a dose of 150 mg EGME/kg body weight in rats 40
(Chapin et al. 1984). Perhaps more interestingly, EGME is an early example of a non-genotoxic 41
chemical (Hoflack et al. 1995) for which paternal exposure causes adverse effects on embryo 42
development. Short-duration exposure to EGME in rats leads to post-implantation embryo loss 43
that is delayed by five weeks (Chapin, Dutton, Ross, and Lamb 1985), a time frame that 44
corresponds with the time it takes for pachytene spermatocytes to mature into spermatozoa and 45
complete epididymal maturation. 46
The mechanisms of preconception exposure developmental toxicity are not well 47
understood. Given that there is no evidence that EGME or its major metabolite, MAA, are 48
genotoxic, it stands to reason that EGME has the potential to disrupt embryo development 49
through an epigenetic mechanism. One plausible epigenetic mechanism is disruption of sperm 50
RNA. Sperm contains mRNA, miRNA, piRNA, tsRNA, and other classes, which have putative 51
roles in embryo development (Sendler et al. 2013; Jodar et al. 2015; Conine et al. 2018). These 52
sperm RNAs are well-conserved across mammalian models; human, mouse, and rat sperm all 53
contain thousands of mRNAs, with one report identifying 6,684 transcripts expressed in all three 54
species (Bianchi et al. 2021). In particular, there is evidence for a critical role of miRNAs and 55
endo-siRNAs in the male germline. Germ-cell specific loss of Dicer or Dgcr8 from embryonic 56
day 15, driven by Dddx4-Cre in mice, leads to infertility and severe reduction of meiotic 57
progression and maturation of elongate spermatids (Zimmermann et al. 2014). Furthermore, 58
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there is increasing evidence that altered levels of regulatory RNAs in sperm contribute to 59
disease phenotypes such as metabolic disorder in offspring (Zhang et al. 2019). 60
There is evidence that EGME alters testicular gene expression and miRNA expression, 61
which suggests that sperm RNAs may be altered following EGME exposure, as well. In 62
monkeys exposed to EGME, expression of many testicular miRNAs increases, while serum 63
miRNA levels decrease (Sakurai et al. 2015). In rats, EGME exposure results in changes in 64
expression of meiosis-related genes in the testis (Tonkin et al. 2009). Further, we previously 65
reported that low-dose EGME alters the proportions and read length distributions of several 66
classes of small RNA in rat sperm (Stermer et al. 2019). Rats were treated with 50-75 mg 67
EGME/kg body weight/d for 5 days. After 5 weeks with no treatment, no testicular 68
histopathology was observed at doses lower than 75 mg/kg/d. However, at 50 mg/kg/d, the 69
proportion of miRNA reads relative to all small RNA reads increased, and the distribution of 70
piRNA and tsRNA read length was significantly altered. Here, we conducted a new analysis of 71
that dataset to determine the impact of EGME exposure on expression of specific sperm small 72
RNAs, with the goal of identifying dose-dependent regulatory RNA changes in sperm. These 73
sensitive, dose-dependent changes have the potential to serve as biomarkers of exposure to 74
EGME and possibly other toxicants, as well as candidate RNAs in the mechanisms of 75
developmental toxicity of paternal EGME exposure. 76
Materials and methods
77
Raw small RNA sequencing data were obtained from a previously published study 78
(Stermer et al. 2019). Briefly, single-end sequencing of small RNA was performed on the 39 79
libraries (one sample in the 60mg/kg exposure group lacked sufficient RNA to process) with an 80
IonProton sequencer (ThermoFisher Scientific). This yielded an average of 16 million reads per 81
library and an average read length of 30nt. 82
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Small RNA Expression Profiling 83
Initial quality control was performed using FASTQC (Andrews 2010). Two samples with 84
extremely low read counts were identified as outliers and excluded from downstream analysis. 85
Small RNA expression levels were then profiled using sRNAbench (Aparicio-Puerta et al. 2022) 86
in genome mode. Reads were mapped against the rat genome (Rnor_6_0) and compared to 87
miRBase Release 22.1 (Kozomara et al. 2019). Default sRNAbench parameters were applied: 88
the bowtie seed alignment, seed length 20, minimum read count 2, minimum read length 15, 89
allowed 1 mismatch, and 10 multiple mappings. After expression profiling, multi-map adjusted 90
read counts for small RNAs (miRNAs, tRNAs, ncRNAs, cDNA) from sRNAbench ".grouped" files 91
were parsed using a custom Python script. 92
Differential Expression Analysis 93
Differential expression of small RNAs across dosage groups was determined using 94
DESeq2 (Love et al. 2014) with default filtering. Both the Wald test and the likelihood ratio test 95
were run for each small RNA type. For miRNAs, significantly differentially expressed miRNAs (p 96
< 0.05) were identified for each of the three dosage vs. control pairs (50mg/kg vs 0 mg/kg, 97
60mg/kg vs 0 mg/kg, and 75mg/kg vs 0mg/kg). The intersection of these significant miRNA sets 98
across all comparisons was used for further analysis. 99
As RNAseq methods such as DESeq2 have high false positive rates (Li et al. 2022), we 100
assessed robustness of our results with a Monte Carlo simulation (Dere et al. 2016; Dere et al. 101
2018). We created 1000 subsamples of our dataset where each subsample consisted of smaller 102
groups of 6 individuals in each group, where the individuals were sampled without replacement 103
from the larger set of 10 individuals per group. We then ran DESeq2 again on each of the 1000 104
subsamples and counted how many times we found the same differentially expressed miRNAs. 105
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Target Gene Prediction and Functional Enrichment 106
Putative target genes for the intersection set of significant miRNAs were assembled by 107
manually querying each miRNA in miRDB (Chen and Wang 2020). Targets with scores greater 108
than 80 were retained, yielding 2073 unique genes. An over-representation analysis (ORA) was 109
performed on the full list of target genes, using the R package ClusterProfiler (Yu 2024). The 110
default background gene list (whole rat genome) was used, as gene expression was not 111
measured in this experiment. All three subontologies - biological process (BP), molecular 112
function (MF), and cellular component (CC) were investigated. All the other parameters are left 113
as default. For each subontology, we obtained a list of GO terms ranked by p-values. 114
Results
115
EGME dose-dependently increased sperm miRNA levels 116
A total of 405 miRNAs were initially identified by sRNAbench, with 277 remaining after 117
filtering in DESeq2. Sperm miRNA levels showed a high degree of clustering by treatment level, 118
based on Euclidean distance (Fig. 1A), with two main clusters forming, consisting of (1) all 10 119
vehicle controls, four 50 mg/kg/d EGME samples, and two 60 mg/kg/d EGME samples; and (2) 120
the remaining six 50 mg/kg/d samples, seven 60 mg/kg/d samples, and all ten 75 mg/kg/d 121
samples. In principal component analysis (PCA) (Fig. 1B), there was a clear gradient from 122
vehicle to 75 mg/kg/d along the first principal component. The first two principal components 123
explained 25 and 13% of the variance in the data, respectively, and the samples became more 124
variable within treatment group as the treatment level increased, suggesting that increased 125
EGME-induced germ cell stress led to greater variability. There was distinct visual separation in 126
the PCA plot between sample groups, in particular the vehicle control and 50 mg EGME/kg/d, 127
with less separation between the 60 and 75 mg EGME/kg/d groups. 128
The total number of DE miRNAs increased from 12 in the 50 mg/kg/d group to 56 in the 129
60 mg/kg/d group and 57 in the 75 mg/kg/d group, with the majority of significant DE miRNAs 130
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being upregulated in the EGME treatment groups (Fig. 1C, Table S1). There was significant 131
overlap between the treatment groups, with 12 miRNAs being shared among all three groups, 132
and a further 25 DE miRNAs shared by the 60 and 75 mg/kg/d groups (Fig. 2A). A Monte Carlo 133
analysis found that these 12 shared miRNAs were highly stable among the DE miRNAs (Fig. 134
2B). In 1000 simulations, 10 of the 12 shared DE miRNAs were in the top 12 most frequently 135
identified DE miRNAs, appearing in 748 to 992 out of 1000 iterations. The remaining two shared 136
DE miRNAs were also in the top 40 most stable DE miRNAs. The 12 shared DE miRNAs were 137
miR-200b-3p, miR-221-3p, miR-200a-3p, let-7c-5p, miR-429, miR-365-ep, miR-27a-3p, miR-138
205, miR-148-3p, miR-23a-3p, miR-24-3p, and let-7b-5p. All 12 monotonically increased across 139
the dose range (Fig. 2C). 140
EGME dose-dependent miRNA targets in embryo development 141
We used miRDB to identify the high-confidence targets of the 12 EGME dose-dependent 142
DE miRNAs, using a miRDB target score > 80 as the cutoff. At this level of confidence, we 143
identified 1,203 targets (Table S2). 787 of the 1,203 target genes were only targets of one 144
miRNA. A further 343 were targets of two miRNAs, and 50, 12, and 7 genes were identified as 145
shared targets of 3, 4, or 5 of the 12 core miRNAs, respectively (Fig. 3A). The most highly 146
shared target genes were Zeb1, Mmd, Clasp2, Hectd2, Wdr37, Sema6d, and Slc6a1, which 147
were each identified as a target of 5 of the 12 shared DE miRNAs. To assess whether these 148
target genes are likely to have roles in embryonic development, we compared the targets with 149
mRNAs enriched in the epiblast (EPI), primitive endoderm (PE), and trophectoderm (TE) of 150
human e5-7 embryos (Petropoulos et al. 2016). The targets matched 54, 31, and 36 of the EPI, 151
PE, and TE-enriched genes, respectively (Fig. 3B, Table S2), which confirms that the EGME 152
dose-dependent miRNAs target genes involved in early development and that at least a subset 153
of those genes are expressed in early embryos. That subset included well-known early embryo 154
development genes, such as Aldh1a1, Foxa2, Gata2, Gata4, Gata6, as well as fundamental 155
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genes involved in cell cycle control, cytoskeleton structure and remodeling, and cell signaling. 156
Using the 1,203 target transcripts as input, we identified 321 enriched Gene Ontology (GO) 157
terms (Table S3), including 295 biological process (BP), 9 cellular compartment (CC), and 17 158
molecular function (MF) terms (Fig. 3C-D). The top 20 GO BPs included important 159
developmental functions, such as “axonogenesis,” “regulation of developmental growth,” “cell 160
fate commitment,” “cell fate commitment,” “morphogenesis of a branching structure,” and 161
“morphogenesis of a branching epithelium” (Fig. 3D). Genes under the “cell fate commitment” 162
term, as an example, have well-characterized roles in development. These include Cyp26b1, 163
Dmrt3, Foxa2, Gata2, Gata4, Gata6, Hoxd10, Kdr, Pax6, Pou3f2, Pparg, Runx1, Runx2, 164
Smad4, Tgfb2, Tgfbr1, Wnt9a, and Wnt9b, among 40 target genes (Table S3). Analysis of 165
target gene sharing among the 12 miRNAs in the GO BP gene sets revealed a high degree of 166
overlap. Of the significant GO BPs, the majority included targets of 6 or more miRNAs, with only 167
one GO BP uniquely linked to a single miRNA (Fig. 3C). 90 out of 295 pathways were shared by 168
all 12 miRNAs, although most target genes were not shared by a large number of miRNAs (Fig. 169
3A). Beyond biological processes, the top GO CCs included compartments associated with cell 170
division, including “cleavage furrow,” and “cell division site,” as well as terms related to 171
phosphatases, Golgi, and neuronal synapses (Fig. 4A). The top GO MFs included several terms 172
related to kinase and phosphatase activity, transcription, RNA binding, and SMAD binding (Fig. 173
4B). 174
EGME effects on sperm tsRNA levels 175
Small RNA reads mapped to 365 tRNA genes in sRNAbench, which corresponded with 176
41 unique tRNAs (Fig. 5, Table S4), after removing duplicate tRNA genes (Iben and Maraia 177
2014). We performed unsupervised analyses of tRNA reads, which showed separation of 178
samples by tRNA expression, similar to the pattern observed with miRNAs. In hierarchical 179
clustering based on Euclidean distance (Fig. 5A), there were four main clusters, showing a lot of 180
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separation between the control and high dose group. One cluster contained eight of nine 75 181
mg/kg/d samples and three of nine 60 mg/kg/d samples, while another contained seven of nine 182
vehicle control samples, four 50 mg/kg/d samples, and one 60 mg/kg/d sample. PCA showed an 183
even clearer separation between dose levels than for miRNAs, with the vehicle and 50 mg/kg/d 184
groups clustered somewhat closely and the 60 and 75 mg/kg/d groups displaying a gradient 185
along principal component 1 (Fig. 5B). The first two principal components explained 69% of 186
variance in the dataset (46% and 23%, respectively). The number of significant DE tRNA genes 187
(Wald test, fold change ≥ 2, p-adj < 0.05) was 9, 117, and 204 in the 50, 60, and 75 mg/kg/d 188
treatment groups, respectively, relative to control (Fig. 5C). After removing duplicate tRNA 189
genes and comparing at the tRNA level, there were 2, 28, and 39 significant tRNAs at the 50, 190
60, and 75 mg/kg/d levels; at least one GluCTC and GlyCCC gene was significant at each of the 191
three dose levels; and of the 24 additional tRNAs with at least one significant gene at the 60 and 192
75 mg/kg/d dose levels, GluTTC, LysCTT, AlaAGC, and CysGCA had the lowest adjusted p-193
values at 50 mg/kg/d (Fig. 5D). We generated coverage maps to analyze the tsRNA fragments 194
present in the 2 consensus DE tRNAs and the next four most significant tRNAs (Fig. 5E), which 195
showed the greatest coverage for GlyCCC, and mostly 5’ coverage for all except for GluTTC, 196
which had more 3’ coverage. When analyzing coverage at the single-read level (Fig. 6), for 197
GluCTC, LysCTT, AlaAGC, and Cys GCA, the vast majority of reads were 5’ fragments or 198
halves, with a much smaller number of reads representing 3’ fragments. The reason for the 199
different coverage map for GluTTC was that reads consisted of an approximately 50:50 200
distribution of 5’ fragments and halves and 3’ fragments and halves. 201
EGME effects on sperm piRNAs 202
Small RNA reads mapped to 18,027 unique piRNAs in sRNAbench, using annotations 203
from piRBase (Wang et al. 2019). piRNAs separated by treatment group in unsupervised 204
analyses, although less separation was visible in hierarchical clustering (Fig. 6A) than for other 205
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categories of RNAs. Similarly, PCA showed a gradient of values along PC1 with a cluster of 0, 206
50, and 60 mg/kg/d EGME samples mostly separating from a cluster of 75 mg/kg/d samples 207
(Fig. 6B). The first two PCs explained 74% of the variance in the dataset (67% and 7% in the 208
first two PCs, respectively). An increasing number of piRNAs were significant in DE analysis 209
with each treatment group (Fig. 6C), with 1, 244, and 2,181 DE piRNAs in the 50, 60, and 75 210
mg/kg/d groups, respectively. This large number of DE piRNAs is consistent with the size of this 211
RNA category in spermatogenesis, which comprises more than 1 million piRNAs that are critical 212
in the germline of rats and mice (Lau et al. 2006; Beyret et al. 2012; Watanabe et al. 2015). 213
EGME effects on other sperm small RNAs 214
EGME exposure level led to changes in sperm levels of multiple classes of small RNAs 215
in addition to miRNAs, tsRNAs, and piRNAs (Fig 7, Table S6). These included rRNAs, 216
mitochondrial rRNAs, snRNAs, lincRNAs, antisense RNAs, processed transcripts, and RNAs 217
without known identities (identified as misc_RNA in Table S6). There was strong separation by 218
unsupervised clustering analyses, similar to the pattern observed with miRNAs and tsRNAs. 219
The hierarchical clustering result included two main clusters, one containing one 50 mg/kg/d 220
sample, seven 60 mg/kg/d samples, and all nine 75 mg/kg/d samples; while the other cluster 221
contained two 60 mg/kg/d samples, nine 50 mg/kg/d samples, and all nine vehicle control 222
samples (Fig. 7A). PCA showed strong separation along the first PC. However, the first two PCs 223
explained only 48% of the variance in the dataset (37% and 11%, respectively) (Fig. 7B). The 224
number of DE RNAs in each group was 16, 79, and 133, in the 50, 60, and 75 mg/kg/d EGME 225
groups, respectively. 226
Discussion
227
Ethylene glycol monomethyl ether (EGME), and its active metabolite, 2-methoxyacetic 228
acid, is a testicular germ cell toxicant that causes selective spermatocyte toxicity in the rat 229
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(Chapin and Lamb 1984; Creasy and Foster 1984; Foster et al. 1984; Gray et al. 1985; Moss et 230
al. 1985; Creasy et al. 1986), resulting in apoptosis (Ku et al. 1995). Meiotic spermatocytes are 231
most sensitive to EGME, followed by pachytene spermatocytes, leptotene/zygotene 232
spermatocytes, and step 1 round spermatids (Creasy and Foster 1984; Foster et al. 1984).The 233
NOAEL dose for germ cell death has been reported as 50 mg/kg/d following 11-day exposure to 234
EGME and 250 mg/kg EGME in a single-dose experiment (Creasy et al. 1986). EGME-induced 235
germ cell death is preceded by mitochondrial damage 16 hours after a single 500 mg/kg dose 236
(Foster et al. 1983). 237
Because EGME selectively targets spermatocytes, an exposure duration of as little as 238
five days results in decreased male fertility that becomes apparent three to four weeks after 239
cessation of exposure, with the greatest magnitude of effect occurring in weeks five to six post-240
exposure, with a LOAEL of 100 mg/kg/d (Chapin, Dutton, Ross, and Lamb 1985; Chapin, 241
Dutton, Ross, Swaisgood, et al. 1985; Holloway et al. 1990). The delayed fertility effect 242
corresponds with the 4-5 weeks required for spermatocytes to mature into sperm. A dose of 200 243
mg/kg/d has also been reported to increase the number of resorptions five to six weeks after a 244
five-day exposure (Chapin, Dutton, Ross, and Lamb 1985), suggesting that paternal EGME 245
exposure can cause developmental toxicity without exposure of the dam or embryo. Given 246
evidence that EGME is non-genotoxic (Hoflack et al. 1995), a mechanism other than germ cell 247
DNA damage must be responsible for those paternal exposure effects on embryonic 248
development. 249
Stermer et al. (2019) used low-dose EGME as a model to understand how sub-cytotoxic 250
germ cell effects of EGME could alter markers of reproductive health. Exposure of male rats to 251
50-75 mg/kg/d EGME for five days, followed by a five-week withdrawal, resulted in reduced 252
sperm count and increased retained spermatid head (RSH) count, with a NOAEL of 60 mg/kg/d 253
and a LOAEL of 75 mg/kg/d (Stermer et al. 2019). In addition to these apical effects, all doses of 254
EGME that were tested (50-75 mg/kg/d) altered the proportion of miRNA, piRNA, and tsRNA 255
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reads in sperm and the distribution of small RNA read lengths. An ROC curve analysis revealed 256
that average sperm small RNA read length was a better EGME dose classifier than sperm 257
motility or RSH. In the present paper, we performed a new analysis of these data to identify the 258
sperm small RNAs that were differentially abundant following EGME exposure, to obtain novel 259
mechanistic insights about EGME-driven changes in spermatogenesis and to identify RNAs that 260
may contribute to differences in embryonic development following paternal EGME exposure. We 261
identified EGME dose-dependent changes in abundance of sperm miRNAs (Figs. 1-2), tsRNAs 262
(Fig. 5-6), piRNAs (Fig. 7), and other classes of small RNA (Fig. 8). 263
miRNAs canonically act as negative translational regulators of their mRNA targets, but 264
they can act as positive regulators in some instances (O’Brien et al. 2018). There is evidence 265
that sperm miRNAs regulate pre-implantation embryonic transcription in the mouse, at the 4-cell 266
and blastocyst stages (Conine et al. 2018). In our analysis, the number of significant 267
differentially expressed (DE) miRNAs increased with EGME dose (Fig. 1), and there were 12 268
DE miRNAs present in all three doses, which all showed a monotonic increase in abundance 269
with dose, and which were highly reproducible based on a Monte Carlo analysis (Fig. 2). These 270
12 miRNAs have over 1,000 high confidence targets, many of which are involved in 271
developmentally important biological processes and expressed in human preimplantation 272
embryos (Fig. 3B-D, Tables S2, S3). Several of the EGME dose-dependent sperm miRNAs 273
have known functions in spermatogenesis, and/or embryo development, including miR-221-3p, 274
miR-27a-3p, miR23a-3p, and let-7b-5. miR-221-3p regulates germ cells to maintain 275
undifferentiated spermatogonia states (Yang et al. 2013). miR-27a-3p is overexpressed in 276
azoospermic men (Norioun et al. 2020), and miR-23a/b-3p are overexpressed in subfertile men 277
(Abu-Halima et al. 2019). Let-7 miRNAs regulate germ cell transcription, with let-7b being 278
especially highly expressed in pachytene spermatocytes (Sangiao-Alvarellos et al. 2015). We 279
hypothesize, therefore, that levels of miRNAs such as let-7b could be altered in sperm following 280
an injury to spermatocytes and could influence embryo development as a result. In addition to 281
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those miRNAs that have previously characterized roles in male reproductive biology, it is 282
notable that let-7c-5p, miR-200a-3p, and miR-200b-3p increased with EGME dose in our 283
dataset (Fig. 2), but decreased during epididymal maturation in the mouse in (Sharma et al. 284
2018). 285
Although miRNAs are well-characterized, recent evidence shows that the majority of the 286
RNAs in sperm are tsRNAs and rsRNAs, which are underrepresented in sequencing results 287
because of modifications that impede reverse transcription (Shi et al. 2021; Hernandez et al. 288
2023). Although the sequencing approach from which the present EGME dataset is derived did 289
not use the PANDORA-seq methodology, a significant proportion of the reads in this dataset 290
mapped to tRNA sequences: 51.4-65.5%, depending on EGME dose (Stermer et al. 2019). 291
Consistent with that finding, we identified 41 DE tRNAs, including 2 that were DE in all EGME 292
doses, GluCTC and GlyCCC (Fig. 5). Coverage maps showed that the tsRNAs that contributed 293
to these differential read counts were predominantly 5’ tRNA fragments and halves (Figs. 5-6). 294
tsRNAs may have multiple functions, including miRNA-like RNAi functions or aptamer functions 295
(Chen and Zhou 2023) or regulation of transposable elements (Sharma et al. 2016); however, 296
there is currently no broad understanding of tsRNA functions. Although there are still many 297
Limitations
to understanding the functions of tsRNAs, recent evidence shows that the sperm 298
quantity of one of our DE tsRNAs, 5’tRF-GluCTC, is negatively associated with ART outcomes 299
in humans (Hekim et al. 2025). 300
EGME caused a massive increase in the number of upregulated piRNAs from 1 301
significant DE piRNA at 50 mg/kg/d to over 1000 at 75 mg/kg/d (Fig. 7). piRNAs are important 302
for maintenance of germline genomic integrity by regulating insertion of transposable elements 303
(Wang and Lin 2021). piRNAs also control some aspects of posttranscriptional processing and 304
cleavage of RNAs (Watanabe and Lin 2014) and have a variety of other epigenetic control 305
mechanisms (Ku and Lin 2014). Hypothetically, differential expression of piRNAs could 306
indirectly destabilize the genome of germline cells, despite EGME not being a direct mutagen 307
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(Hoflack et al. 1995). This hypothesis would require further testing, but it presents a possible 308
sperm sncRNA-mediated mechanism of paternal EGME effects on embryonic development. As 309
noted above, rsRNAs are also prevalent in sperm, representing over half of sperm RNA reads 310
when PANDORA-seq is employed (Shi et al. 2021; Chen and Zhou 2023). We also analyzed 311
other sperm sncRNAs, such as rRNAs, mtRNA, snRNA, and lincRNA, and we found that the 312
number of DE RNAs increased across those classes with increasing EGME dose (Fig. 8). 313
Overall, we found that short-term exposure to low doses of EGME led to changes in 314
sperm RNA that were detectable 5 weeks after cessation of exposure, consistent with the 315
known progression of EGME-induced testicular injury and reproductive performance in rats 316
(Chapin, Dutton, Ross, and Lamb 1985). This is also consistent with prior reports that EGME 317
exposure altered testicular gene and protein expression (Wang & Chapin, 2000, Fukushima et 318
al., 2005, Yamamoto et al., 2005) and miRNA expression in rats and non-human primates 319
(Fukushima et al., 2011, Sakurai et al., 2015). EGME’s property of targeting pachytene 320
spermatocytes may be the reason why it has such potent and persistent effects on testicular 321
germ cell RNA expression, as the peak of RNA synthesis during spermatogenesis occurs in the 322
pachytene spermatocytes (Monesi, 1965). However, testicular toxicants with a variety of target 323
cells and toxicity mechanisms have been reported to alter sperm mRNA expression. These 324
include pharmaceuticals (Dere et al. 2017) and industrial or environmental testicular toxicants 325
including the germ cell toxicant, carbendazim, and the Sertoli cell toxicant, 2,5-hexanedione 326
(Pacheco et al. 2012). There is also a recent report that phthalate exposure altered miRNA, 327
tsRNA, and piRNA levels in epididymal extracellular vesicles (Oluwayiose et al. 2025), some of 328
which are transferred to sperm (Sharma et al. 2018). Similarly, a 12-week exposure to a mixture 329
of per- and polyfluoro alkyl substances (PFAS) resulted in increased numbers of sperm tsRNAs, 330
miRNAs, and piRNAs at doses that caused few phenotypic changes in adults and no changes in 331
fertilization rate (Gillespie et al. 2025). Other parental treatments alter sperm miRNAs with 332
apparent intergenerational biological effects, including maternal stress (Gapp et al. 2014), 333
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14
paternal exercise (Yin et al. 2025 Oct), and paternal metabolic disorders (Zhang et al. 2018; 334
Zhang et al. 2019). 335
In humans, there is evidence that sperm RNAs may act as markers of fertility or 336
exposures that affect fertility. For example, in one study the total amount of RNA per sperm cell 337
differed based on alcohol use (Bianchi et al. 2019). We recently reported that human sperm 338
mRNA profiles differed between study participants with different clinical fertility status (Qi et al. 339
2025 May 10). Another recent study found that miRNAs, including let-7b-5p, differed between 340
proven fertile and subfertile men (Abu-Halima et al. 2024 Sept 23). Here, our new analysis 341
identified changes in rat sperm sncRNA following EGME exposure, which is consistent with the 342
hypothesis that paternal exposure to environmental toxicants can alter sperm RNA profiles and 343
that this is a putative mechanism of reduced male fertility. Future experiments should test the 344
role of specific EGME dose-dependent candidate miRNAs on rat embryo development and 345
other sncRNA-mediated epigenetic toxicity mechanisms. In summary, EGME not only 346
sensitively alters the proportion of different classes of small RNAs present in sperm, as 347
previously reported (Stermer et al. 2019); it also leads to dose-dependent changes in specific 348
small regulatory RNAs in sperm. Investigation of the roles of those RNAs in spermatogenesis 349
and embryo development may lead to discovery of novel EGME toxicity mechanisms. 350
Data Availability Statement 351
Stored in repository: The data that support the findings of this study are openly available in the 352
NCBI Gene Ontology Omnibus (GEO) database at 353
https://www.ncbi.nlm.nih.gov/geo/query/acc.cgi?acc=GSE313131, reference number 354
GSE313131. The analysis code is publicly available at https://github.com/compbiocore/egme. 355
(which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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15
Funding Information 356
This project was funded by: Brown University; and the National Institute of General Medical 357
Sciences (NIGMS) of the National Institutes of Health (NIH) [P20 GM109035; P20 GM156712]. 358
The content is solely the responsibility of the authors and does not necessarily represent the 359
official views of the National Institutes of Health. 360
Conflicts of Interest Statement 361
The authors declare that they have no conflicts of interest. 362
(which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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16
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532
Figure Legends 533
Figure 1. Changes in sperm miRNA levels following EGME exposure. 534
A. Hierarchical clustering of EGME- and vehicle control-treated samples showing Euclidean 535
distance based on sperm miRNA read counts. B. Principal component analysis of EGME- and 536
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23
vehicle-control-treated samples based on sperm miRNA read counts. C. Differential expression 537
of sperm miRNA between vehicle control and 50, 60, or 75 mg/kg/d EGME-treated samples 538
(DESeq2 with the Wald test, p-adj 2). 539
540
Figure 2. EGME dose-dependency of sperm miRNAs. 541
A. Venn diagram showing overlap of differentially expressed miRNAs in comparisons between 542
control and 50, 60, and 75 mg/kg/d EGME. 12 miRNAs were common to all three treatment 543
levels. B. Top 40 most commonly differentially expressed sperm miRNAs in a Monte Carlo 544
analysis. Ten of the 12 common differentially expressed miRNAs (shown in red) were in the top 545
12, and the remaining two were within the top 40 most reproducibly differentially expressed 546
miRNAs. C. Normalized read counts for the 12 common differentially expressed miRNAs. In all 547
cases, the response trend was monotonic increase with increasing dose. 548
549
Figure 3. Targets of EGME dose-dependent miRNAs. 550
Using mirDB, we identified 1,203 high-confidence targets of the 12 common differentially 551
expressed miRNAs. A. Histogram showing the distribution of target genes by the number of DE 552
miRNAs that share the target. B. Venn diagram showing the overlap of the 1,203 common DE 553
miRNA target genes with genes known to be expressed in the epiblast (EPI), primitive 554
endoderm (PE), or trophectoderm (TE) of the early human embryo, from a single-cell RNA-seq 555
analysis (Petropoulos et al. 2016). The analysis identified a total of 119 early human embryo 556
genes among the 1,203 targets of common EGME differentially expressed miRNAs. Note that 557
one gene shared by the EGME-miR-target, PE, and EPI gene list and one shared by the EGME-558
miR-target, PE, and TE gene lists is not accounted for in the diagram because of graphing 559
constraints. C. Histogram showing the number of core miRNAs with target genes common to 560
each of the enriched GO BPs. D. Enrichment analysis of Gene Ontology Biological Process 561
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24
terms (GO BPs) for the 1,203 targets of the 12 common differentially expressed miRNAs. Right 562
panel shows hierarchical arrangement of enriched GO BPs. 563
564
Figure 4. Functional analysis of EGME dose-dependent miRNA targets. 565
Using the 1,203 high-confidence targets of the 12 common differentially expressed miRNAs. A. 566
Enrichment analysis of Gene Ontology Cellular Component terms (GO CCs) for the 1,203 567
targets of the 12 common differentially expressed miRNAs. B. Enrichment analysis of Gene 568
Ontology Biological Molecular Function terms (GO MFs) for the 1,203 targets of the 12 common 569
differentially expressed miRNAs. Right panels show hierarchical arrangement of enriched GO 570
MFs. 571
572
Figure 5. Changes in sperm tsRNA levels following EGME exposure. 573
A. Hierarchical clustering of EGME- and vehicle control-treated samples showing Euclidean 574
distance based on sperm tRNA read counts. B. Principal component analysis of EGME- and 575
vehicle-control-treated samples based on sperm tRNA read counts. C. Differential expression of 576
sperm tRNA between vehicle control and 50, 60, or 75 mg/kg/d EGME-treated samples 577
(DESeq2 with the Wald test, p-adj 2). D. Venn diagram showing overlap of 578
differentially expressed tRNAs in comparisons between control and 50, 60, and 75 mg/kg/d 579
EGME, after removal of duplicate tRNA genes. Two unique tRNAs were common to all three 580
treatment levels. E. Sequence coverage map showing read coverage of tRNA reads for the two 581
tRNAs that were differentially expressed at all doses, GluCTC and GlyCCC, and the next four 582
tRNAs with at least one significant gene at the 60 and 75 mg/kg/d dose levels, GluTTC, 583
LysCTT, AlaAGC, and CysGCA, based on the lowest adjusted p-value at 50 mg/kg/d, scaled by 584
read count on the y-axis. 585
586
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Figure 6. Detailed coverage maps for the most significant tsRNAs. 587
Coverage maps showing all unique tRNA reads for the tRNAs that were differentially expressed 588
at all doses, GluCTC and GlyCCC, and the next four tRNAs with at least one significant gene at 589
the 60 and 75 mg/kg/d dose levels, GluTTC, LysCTT, AlaAGC, and CysGCA, based on the 590
lowest adjusted p-value at 50 mg/kg/d. Plots show unique reads with color key based on the 591
number of copies of each unique read. The majority of reads were 5’ fragments and halves. 592
593
Figure 7. Changes in sperm piRNAs following EGME exposure. 594
A. Hierarchical clustering of EGME- and vehicle control-treated samples showing Euclidean 595
distance based on sperm piRNA read counts. B. Principal component analysis of EGME- and 596
vehicle-control-treated samples based on sperm piRNA read counts. C. Differential expression 597
of sperm piRNA between vehicle control and 50, 60, or 75 mg/kg/d EGME-treated samples 598
(DESeq2 with the Wald test, p-adj 2). 599
600
Figure 8. Changes in other sperm small RNAs following EGME exposure. 601
A. Hierarchical clustering of EGME- and vehicle control-treated samples showing Euclidean 602
distance based on remaining sperm read counts. After separating miRNA, tRNA, and piRNA 603
reads, the remaining DE RNAs were from RNA classes including rRNA, mitochondrial rRNA, 604
lincRNA, snRNA, B. Principal component analysis of EGME- and vehicle-control-treated 605
samples based on sperm sncRNA read counts. C. Differential expression of sperm sncRNAs 606
between vehicle control and 50, 60, or 75 mg/kg/d EGME-treated samples (DESeq2 with the 607
Wald test, p-adj 2). 608
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The copyright holder for this preprintthis version posted December 29, 2025. ; https://doi.org/10.64898/2025.12.29.693789doi: bioRxiv preprint
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