Abstract
Antimony (Sb), is thought to induce testicular toxicity, although this remains controversial. This study investigated the effects of Sb exposure during spermatogenesis in the Drosophila testis and the underlying transcriptional regulatory mechanism at single-cell resolution. Firstly, we found that flies exposed to Sb for 10 days led to dose-dependent reproductive toxicity during spermatogenesis. Protein expression and RNA levels were measured by immunofluorescence and quantitative real-time PCR (qRT-PCR). Single-cell RNA sequencing (scRNA-seq) was performed to characterize testicular cell composition and identify the transcriptional regulatory network after Sb exposure in Drosophila testes. scRNA-seq analysis revealed that Sb exposure influenced various testicular cell populations, especially in GSCs_to_Early_Spermatogonia and Spermatids clusters. Importantly, carbon metabolism was involved in GSCs/early spermatogonia maintenance and positively related with SCP-Containing Proteins, S-LAPs, and Mst84D signatures. Moreover, Seminal Fluid Proteins, Mst57D, and Serpin signatures were highly positively correlated with spermatid maturation. Pseudotime trajectory analysis revealed three novel states for the complexity of germ cell differentiation, and many novel genes (e.g., Dup98B) were found to be expressed in state-biased manners during spermatogenesis. Collectively, this study indicates that Sb exposure negatively impacts GSC maintenance and spermatid elongation, damaging spermatogenesis homeostasis via multiple signatures in Drosophila testes and therefore supporting Sb-mediated testicular toxicity.
Subject terms: Cell lineage, Cell growth
Introduction
As a silvery white metalloid of medium hardness, antimony (Sb) is generally combined with other metals to create hardened alloys, followed by industrial applications and commodity consumption, and finally leading to environmental discharge [1]. In addition to human activities, Sb in the environment can come from natural processes, such as ore weathering or volcanic activity [2]. Once it’s released into the environment, Sb is found in a variety of environmental media, including water, soil, and sediment, and even in atmospheric aerosols [3]. As a result, Sb can enter the human body through the respiratory tract, digestive tract, and skin. Oral exposure to Sb is also common due to its emetic properties [4]. Antimonials have been used to treat two parasitic diseases, schistosomiasis and leishmaniasis. Based on epidemiological studies, Sb levels in the urine or blood may be positively associated with adverse population health outcomes [5, 6], suggesting that exposure-mediated health risks should be investigated.
The primary toxic effect of Sb is cardiotoxicity when used in clinical therapeutic preparations [7]. On the other hand, occupational exposure to Sb leads to respiratory irritation or pneumoconiosis [8]. Our previous studies first tried to elucidate the neurotoxic effects and mechanisms of Sb [9, 10]. Male infertility is an important issue and has been associated with environmental pollution, including that of heavy metals [11]. Wu et al. assessed the effects of Sb exposure on reproductive organs in adult male mice and found that parameters of sperm quality, such as sperm count and the testis coefficient, were dramatically decreased [12]. However, an earlier study showed that Sb potassium tartrate exposure administered by gavage neither decreased testis or accessory sex organ weight nor impacted sperm parameters in rats or mice [13]. Taken together, Sb exposure-triggered testicular toxicity remains unclear and further research is urgently needed.
Drosophila has been used as an animal model for more than 100 years; discoveries in fruit flies have greatly contributed to our understanding of spermatogenesis and pollutant-mediated toxicity [14–16]. Spermatogenesis is a highly conserved process in Drosophila and mammalian testes and is well-understood from an anatomical and histological perspective [17, 18], but the underlying regulatory foundations between environmental pollution and genetic heredity are poorly understood. In Drosophila, the testis contains a well-structured microenvironment, the stem cell niche, which is comprised of terminally differentiated hub cells, germline stem cells (GSCs), and somatic cyst stem cells (CySCs) [19]. Hub cells maintain the self-renewal and differentiation of the two other types of stem cells [20, 21]. Interestingly, germ cells occupy the majority of testicular components, and their maintenance and differentiation are strictly controlled by functional signals that originate from somatic cells in Drosophila testes [22, 23]. CySCs differentiate into cyst cells and provide the environment necessary to trigger germ cell growth and differentiation via non-autonomous effects [24]. With the encapsulation of somatic cyst cells, GSCs produce gonialblasts (GBs) and undergo transit amplification (TA) with four rounds of mitosis and then differentiate into spermatocytes and spermatids, ultimately forming mature sperm [25].
Therefore, Drosophila is a suitable model system to assess cytotoxic effects induced by environmental pollutant exposure [26]. This study aims to explore the testicular toxicity of Sb with regard to GSC maintenance, germ cell differentiation, and spermatid deformation. In particular, we apply single-cell RNA sequencing (scRNA-seq) to comprehensively characterize the transcriptional regulatory network of different cell populations in Drosophila testes following Sb exposure. Our data provide meaningful information for Sb-mediated testicular toxicity identification.
Results
Cellular effects of Sb exposure in Drosophila testes
The Drosophila testis has been widely used as a model for male reproductive toxicity due to clear observations of different cell structures during spermatogenesis. To investigate the toxicological effects of Sb exposure in Drosophila testes, we examined the numbers of GSCs and elongated spermatid clusters in Drosophila testes following Sb exposure at 0, 0.3, 0.6, and 1.2 mg/mL.Vasa was used to label germ cells, and De-cad marked somatic hub cells and cyst cells in testes (Fig. S1). Importantly, GSCs could be identified by Vasa-positive germ cells directly adjacent to hub cells at the apex of the testis, while elongated spermatid nuclei gathered in a cluster and were highly agglutinated at the tail of the testis. Compared to control testes, Sb exposure at 0.3, 0.6, or 1.2 mg/mL dramatically reduced the number of GSCs in a dose-dependent manner (Fig. 1A, B). Whole mount staining of Vasa for 0 mg/mL Sb-treated testes (control group) and 1.2 mg/mL Sb-treated testes (Sb group) demonstrated that partial germ cell cysts were lost after Sb-treated (1.2 mg/mL) in testes (Fig. S2A). Previous study demonstrated that A-type Lamin C (LamC) was dominated expressed in spermatocytes [27]. Despite the fact that the property of missing germ cell cysts were spermatocytes, whole mount testicular LamC staining (Fig. S2B) also indicated that spermatocyte populations were not seriously damaged and the remaining spermatocytes could continue to differentiate after Sb exposure (1.2 mg/mL).
We next performed phase-contrast visualization of squashed adult testes to identify different stages of germ cells during spermatogenesis. Different stages of testicular germ cells including spermatogonia (Spg), spermatocytes (Spc), round spermatids (Round Spd), elongated spermatids (Elongated Spd) and mature sperm (Sperm) could be found in testes of both control and Sb groups. Importantly, we also identified accumulations of abnormal elongated spermatids and sperm after Sb exposure (1.2 mg/mL), while they were not found in control group (Fig. S2C).
DNA staining highly condensed at the early-stage nuclei of germ cells and the nuclei of clusters of elongated spermatozoa in the Drosophila testis [16, 23]. Based on the above observation, we next counted the number of elongated spermatid clusters and found a significant and dose-dependent decrease (Fig. 1C, D), indicating that Sb exposure participated in differentiation and injured elongated spermatozoon formation in Drosophila testes. We also stained with Dcp-1 and found that Sb exposure (1.2 mg/mL) dramatically induced apoptosis in elongated spermatid clusters (Fig. S2D). After Sb exposure (1.2 mg/mL), we also found that males reduced their fertility ability (male fertility rate: 73.33%, n = 30) when compared with control males (male fertility rate: 91.67%, n = 12) (Fig. S2E). Thus, Sb exposure in Drosophila induced reproductive toxicity during spermatogenesis.
scRNA-seq analysis identified comprehensive cell compositions in testes
To classify the cell types affected by Sb exposure in Drosophila testes, we performed scRNA-seq on the cells isolated from fresh testes with or without Sb treatment. A cell suspension was made into a library and sequenced (Fig. 2A). We obtained 10,715 testicular cells; low-quality cells were filtered out. After filtering, 9180 high quality cells were retained for downstream analyses with an average of 10,821.5 median UMIs and 2058 median genes per cell. The dimensionality of the gene/cell expression matrix was reduced to two primary axes and visualized through UMAP in Seurat, gathering similar cells into clusters. We annotated likely cell types for each cluster based on the expression pattern of published marker genes, and these clusters could be annotated into 12 cell populations that covered almost all testicular cell types in Drosophila (Fig. 2B and Table S3). Importantly, many cell types were identified by multiple marker genes and their expression patterns are shown in Fig. 2C. During spermatogenesis in Drosophila, different stages of germ cells could be clearly distinguished by various marker genes (Fig. 2D, E). For instance, nanos (nos) is a key marker of GSCs and early germ cells, and bag of marbles (bam) is specifically expressed in spermatogonia [28, 29]. Moreover, Cyclin B (CycB) is mainly expressed in spermatocytes, while fuzzy onions (fzo) are highly enriched in spermatocytes and early spermatids [30, 31]. We also used several classical markers to identify spermatids, including don juan (dj), twine (twe), oo18 RNA-binding protein (orb), calcutta cup (c-cup), and presidents-cup (p-cup) [18, 32]. Expression patterns of representative marker genes are visualized by UMAP in Fig. 2E.
Cell population and changes in transcription following Sb exposure
Distributions of cell populations in the control and Sb-treated groups were merged by UMAP (Fig. 3A). Overall, both the fraction and number of cell populations were dramatically reduced following Sb exposure (Fig. 3B, C). These cell fate changes appeared most significantly in germ cells, revealing reproductive toxicity of Sb exposure during spermatogenesis. The top 50 highly expressed genes were observed in each cell type in Drosophila testes (Fig. 3D and Table S4). Dynamic changes in the gene expression pattern and the number of DEGs in different cell populations are shown in Fig. 3E. Since phenotypes of Sb exposure for spermatogenesis were identified in GSCs and spermatids, the following analysis mainly focused on the GSCs_to_Early_Spermatogonia and Spermatids clusters. DEGs in germ cells were dramatically increased in the GSCs_to_Early_Spermatogonia and Spermatids clusters, with 925 (177 upregulated and 748 downregulated) and 605 (352 upregulated and 253 downregulated) DEGs in these cell clusters, respectively.
Transcriptional regulation of GSCs/early spermatogonia maintenance following Sb exposure
To underline Sb-mediated molecular regulation of early stage germ cells, we performed GO enrichment for DEGs in GSCs_to_Early_Spermatogonia cell types; enriched terms were related with multicellular organism reproduction and spermatogenesis (Fig. 4A). Parallel KEGG pathway analysis showed that various metabolic pathways, including carbon metabolism, were highly enriched in the interactions between Sb exposure and genetic heredity for GSCs/early spermatogonia maintenance (Fig. 4B).
Meanwhile, we also noticed that the expression trends of several family members (also named ‘signatures’ in this study) showed high consistency after Sb exposure in Drosophila testes. We identified several signatures (SCP-Containing Proteins, S-LAPs, and Mst84D signatures) that were altered dramatically following Sb exposure, and investigated correlations of these signatures with carbon metabolism pathway in corresponding testicular cell populations. Our results showed that carbon metabolism exhibited a positive correlation coefficient with SCP-Containing Proteins, S-LAPs, and Mst84D signatures (Fig. 4C). Further correlation analysis indicated positive correlations between any two of the three signatures: (1) SCP-Containing Proteins vs. Mst84D, (2) S-LAPs vs. Mst84D, and (3) SCP-Containing Proteins vs. S-LAPs (Fig. 4D).
We next examined the relative mRNA levels of key factors in correlative signatures in Drosophila testes, and found that representative DEGs of carbon metabolism related factors (CG7059, CG32026 and CG9314), SCP-Containing Proteins [SCP-containing protein A (scpr-A), SCP-containing protein B (scpr-B), and SCP-containing protein C (scpr-C)], S-LAPs [Sperm-Leucylaminopeptidase 1 (S-Lap1) and Sperm-Leucylaminopeptidase 3 (S-Lap3)], and Mst84D [Male-specific RNA 84Dc (Mst84Dc)] were dramatically decreased in testes exposed to Sb compared with control testes (Fig. 4E–G and Fig. S3). Taken together, these data provided novel transcriptional regulatory signals in GSCs_to_Early_Spermatogonia cell populations, contributing to the understanding of Sb exposure mediated GSCs/early spermatogonia maintenance.
Spermatid cell profiling revealed molecular signatures following testicular Sb exposure
To further evaluate testicular toxicity following Sb exposure during late stage spermatogenesis, we stained with several spermatid markers. F-actin marks the individualization complex (IC), a structure essential for spermatid individualization. After Sb exposure, the IC was dramatically reduced at the tail of testes and the remnant IC structure was severely damaged (Fig. 5A), leading to the differentiation defects of elongated spermatids. Orb was used as a classical marker with highly enriched expression level in elongated spermatids [23, 32]. Our results showed that the expression pattern of Orb protein was disturbed at late stage of spermatogenesis in control and Sb-exposed testes (Fig. 5B). Combined with our scRNA-seq data, we also identified Seminal Fluid Proteins, Mst57D, and Serpin signatures related to testicular Sb exposure in the Spermatids cell type. Correlation analysis in spermatid populations showed that DEGs in Seminal Fluid Proteins exhibited a positive correlation coefficient with DEGs in Mst57D (Fig. 5C) and DEGs in Mst57D exhibited a positive correlation coefficient with DEGs in Serpin (Fig. 5D); DEGs in Serpin also exhibited a positive correlation coefficient with DEGs in Seminal Fluid Proteins (Fig. 5E). We also noticed that DEGs in these signatures showed consistent expression trends in most testicular cell populations. Our qRT-PCR results showed that representative DEGs in Mst57D [Male-specific RNA 57 Da (Mst57Da), Male-specific RNA 57Db (Mst57Db), and Male-specific RNA 57Dc (Mst57Dc)], Serpin [Serpin 28 F (Spn28F) and Serpin 38 F (Spn38F)], and Seminal Fluid Proteins [Seminal fluid protein 65 A (Sfp65A) and Seminal fluid protein 70A4 (Sfp70A4)] signatures were significantly upregulated in the Sb-exposed group compared with the control group (Fig. 5F–H). The above data identified three major signatures in Drosophila testes following Sb exposure during spermatid development.
Pseudotime trajectory analysis demonstrated three novel states for Sb exposure during spermatogenesis
To further investigate the germ cell features in Drosophila testes following Sb exposure, we conducted a pseudotime trajectory analysis of germ cell maturation during spermatogenesis (Fig. 6A), and identified three novel states in Drosophila testes (Fig. 6B). By analyzing the cellular components in each state, we showed that the germ cells were consistent with differentiative stages (Fig. 6C). It is worth noting that both the number and fraction of germ cells in each state were dramatically reduced following Sb exposure (Fig. 6D, E). Importantly, germ cells in state 1 were composed of pre-meiotic GSCs/early spermatogonia and meiotic spermatocytes, while germ cells in state 2 and state 3 trended to be clustered by meiotic spermatocytes and post-meiotic spermatids (Fig. 6F). Consistent with the expression patterns of different cell populations during spermatogenesis, a large number of genes were specifically expressed in a state-biased manner. To further distinguish gene regulation in state 1, branch 2 and state 1, branch 3, spline plots were used to demonstrate the expression dynamics of the two branches. The resultant pseudotime analysis indicated that state 1, branch 3 directs to germ cell populations with high-level expression of identified novel factors and marker genes, while these genes are gradually decreased in state 1, branch 2 (Fig. 6G).
To further analyze the characteristics of the three states in Drosophila testes following Sb treatment, dot plot and heatmap views of the most highly expressed genes are shown in Fig. 7A and B, respectively. Three major expression patterns were found: genes such as those encoding the small ribonucleoprotein particle protein SmB (SmB) and FK506-binding protein 39 kDa (Fkbp39) were specifically expressed in state 1 (Fig. 7C, D), genes such as CG43371 and CG12861 were predominantly expressed in state 2 and state 3 (Fig. 7E, F), and genes such as whipple (whip) and CG12126 were highly enriched in state 3 (Fig. 7G, H). Among them, SmB formed the heterodimeric sub-complex with SmD3 production, and previous studies have indicated that both SmB and SmD3 were essential for GSCs homeostasis in Drosophila testes [22, 33]. Whip was dominant expressed in testes and mainly used as a marker for elongation stage spermatids [34].
Next, we analyzed dynamic changes in the gene expression pattern in each testis state in control and Sb-treated Drosophila, and identified 3598 (1358 upregulated and 2240 downregulated) DEGs in state 1, 379 (172 upregulated and 207 downregulated) DEGs in state 2, and 462 (208 upregulated and 254 downregulated) DEGs in state 3 (Fig. 8A). Furthermore, volcano plots showed distinct differences in the DEGs in each state of germ cell populations between the two groups (Fig. 8B). We also identified several enriched genes that were upregulated following Sb exposure in all states during germ cell differentiation (Fig. 8C). A heatmap was used to show the expression pattern of eight upregulated marker genes [CG34330, Met75Cb, CG8708, CG17242, CG43061, Ductus ejaculatorius peptide 99B (Dup99B), Accessory gland protein 54A1 (Acp54A1), and CG42782] that were identified in all differentiated states in control and Sb-exposed germ cells (Fig. 8D). Among them, Dup99B, CG42782, and Acp54A1 were found to be representative and significantly enriched genes; these genes were visualized by t-SNE maps and dramatically upregulated following Sb exposure (Fig. 8E). Since we identified a large number of DEGs in state 1, we performed a KEGG analysis of state 1 germ cells. We found that the enriched cellular processes were involved in cell growth and death, and the main genetic processing focused on the synthesis and degradation of proteins (Fig. 8F). We also noticed that many metabolic processes, including carbon metabolism, oxidative phosphorylation, glycolysis/gluconeogenesis, and the citrate cycle, participated in the differentiation of state 1 germ cells (Fig. 8F). These changes in gene expression and enrichment analysis revealed that the germ cells in the different states went through diversified signals to regulate spermatogenesis following Sb exposure.
Discussion
Drosophila has emerged as an important model for understanding conserved biological mechanisms, drawing support from the availability of convenient genetic manipulations [35–37]. scRNA-seq has provided insight into the genetic regulation of different cell populations in multiple species [38, 39]. Combined with powerful genetic tools in the fly, scRNA-seq can be used to identify novel cell states and functions at single-cell resolution [40]. Recent single-cell transcriptomic atlases have characterized novel cell populations involved in different biological events, uncovering transcriptional regulation or signaling pathways in Drosophila [41–44]. Li et al. constructed a large scale adult fruit fly atlas via single-nucleus transcriptomics, which has become a valuable resource for the Drosophila community as it has provided novel insight into rare cell types and tissue-specific sub-types [34]. In the field of environmental toxicology, Drosophila is known as an alternate animal model to explore stimuli-mediated male reproductive toxicity [45].
Accumulating evidence has revealed cellular networks at the single-cell level in both mouse and human testicles [46–48]. In Drosophila, Witt et al. generated an adult Drosophila testis atlas by scRNA-seq and identified a cluster of lineage-specific de novo genes, elucidating the distribution of lineage-specific de novo genes in spermatogenesis that might deepen our understanding of testis maintenance [49]. More importantly, further investigation indicated that the X chromosome and autosomes showed similar transcriptional activity in somatic and pre-meiotic cells, while less transcriptional activity was identified in the X chromosome than autosomes in meiotic and post-meiotic cells, implying the presence of pre-meiotic X-chromosome dosage compensation in the Drosophila testis [50].
Our data support the idea that the uptake of Sb added to fly food could cause concentration-dependent testicular toxicity, reducing the number of GSCs as well as clustering of elongated spermatids. Cell-cell communication among testicular components has not been extensively investigated. Furthermore, we identified multiple novel signatures highly correlated with GSCs/early spermatogonia maintenance and spermatid elongation. Among them, S-LAPs family members have been found with key roles for mitochondrial paracrystalline material in the elongated spermatids to control male fertility in Drosophila testes [51]. Subunits for SCP-Containing Proteins were dominant expressed in testes and involved in multicellular organism reproduction [52]. A cluster of four genes (Mst84Da, Mst84Db, Mst84Dc and Mst84Dd) for Mst84D family were also male-specifically expressed in testes and found essential roles for sperm axoneme assembly [53]. Meanwhile, seminal fluid proteins, Mst57D, and Serpin signatures secreted extracellular proteins, which were highly expressed in adult male accessory gland and transferred from males to females during mating in Drosophila [54, 55]. With the help of scRNA-seq technology, we have, for the first time, revealed the landscape of Sb-mediated reproductive toxicity and novel signatures at single cell resolution.
In Drosophila, scRNA-seq analysis of gonads allowed the reconstruction of developmental trajectories of germline cells to identify novel differentiated states [44, 49]. In our study, pseudotime trajectory analysis was used to further assess germ cell maturation and identified three novel states corresponding to two differentiative branches during spermatogenesis in Drosophila testes. Following Sb exposure, the number of germ cells in all three states was dramatically reduced. We also identified several novel factors and signals that were significantly altered by Sb exposure. Notably, KEGG analysis of DEGs in state 1 cells revealed that multiple metabolic processes, especially in terms of carbon metabolism, were involved in the maintenance of early stage germ cells. Importantly, in the testicular GSCs_to_Early_Spermatogonia cluster, we confirmed that carbon metabolism was highly correlated with SCP-Containing Proteins, S-LAPs, and Mst84D signatures, which are known to be specifically expressed in testes. Differential expression dynamics of lineage-specific genes will improve our understanding of differentiation stages of testicular Sb exposure-induced genetic heterogeneity.
Overall, this study provides evidence that Sb exposure negatively impacts GSC maintenance and spermatid elongation, affecting key steps of Drosophila spermatogenesis. This is the first study to clarify the molecular basis and regulatory signals of Sb-mediated testicular toxicity at single-cell resolution, providing new insight into the regulatory mechanism of reproductive toxicity damage caused by environmental chemicals.
Materials and methods
Fly stock maintenance
All flies were cultured on standard cornmeal food at 25 °C and grown at proper humidity levels. Two- to three-day-old male flies of the W1118 line were selected for Sb exposure and used for further functional analysis.
Chemical exposure schedule
Potassium antimonyl tartrate trihydrate (C8H4K2O12Sb2·3H2O, 99.0–103%; Sigma-Aldrich, St. Louis, MO, USA) was used in this study. Three different environmental exposures of Sb with relevant final concentrations (0.3, 0.6, and 1.2 mg/mL) were chosen. Two- to three-day-old male flies of the W1118 line were then placed in standard Drosophila food medium containing Sb for 10 days (referred as the chemical exposed group). Control male W1118 flies were placed in standard Drosophila food medium without Sb for 10 days.
RNA extraction, cDNA synthesis, and quantitative real-time PCR (qRT-PCR)
Total RNA was extracted using TRIzol reagent (15596026; Invitrogen, Waltham, MA, USA) from testes according to the manufacturer’s instructions. A PrimeScript™ II 1st Strand cDNA Synthesis Kit (6210 A; Takara, Shiga, Japan) was used to synthesize cDNA. qRT-PCR was performed using a LightCycler® 96 Real-Time PCR System (Roche, Basel, Switzerland) using TB Green Premix Ex Taq II (RR820; Takara). Data analysis was performed using the 2-∆∆Ct method. The sequences of the qRT-PCR primers are provided in Table S1.
Immunofluorescence
Immunofluorescence was carried out as described previously [16, 23, 56]. Briefly, fly testes were dissected in 1 × phosphate-buffered saline (PBS), fixed for 30 min in 4% paraformaldehyde (PFA), washed three times with 0.3% PBS-Triton X-100 (PBST), and incubated in 5% bovine serum albumin (BSA) for 30 min. Primary antibodies were diluted in 5% BSA and testes were incubated at 25 °C for 1 h, and then washed three times with 0.3% PBST. Secondary antibodies were conjugated with Cy3 or A647 (Jackson ImmunoResearch Laboratories, West Grove, PA, USA), diluted at a ratio of 1:400 with 5% BSA, and incubated at 25 °C for 1 h avoiding light. The testes were then washed three times with 0.3% PBST and stained with Hoechst 33342 (1.0 mg/mL, C0031; Solarbio, Beijing, China), which diluted with PBS according to the potency of 1: 800, for 5 min before finalizing. Detailed information on the primary antibodies is provided in Table S2. For F-actin staining, Alexa FluorTM Plus555 Phalloidin (1:50, A30106; Invitrogen) was used according to the manufacturer’s instructions.
Phase-contrast visualization
Testes from the flies were dissected in 1 × PBS, followed by several washes. Squashed testes on slides were coverslipped and observed under a phase-contrast microscope.
Sample collection and processing
Two groups [Sb, 0 mg/mL (Control) and Sb, 1.2 mg/mL (Sb)] were chosen for scRNA-seq based on the above results. For each group, the testes of 180 male flies were dissected in cold PBS. The resulting mixtures of testes were washed with cold PBS three times and immediately transferred into GEXSCOPETM Tissue Preservation Solution (Singleron Biotechnologies, Cheshire, CT, USA) on ice. The pooled segments were further processed following the procedure for tissue dissociation and single-cell preparation.
Tissue dissociation and single-cell suspension preparation
The testes were washed with Hanks Balanced Salt Solution (HBSS) three times and digested in 2 mL of GEXSCOPETM Tissue Dissociation Solution (Singleron Biotechnologies) using a Singleron PythoN™ Automated Tissue Dissociation System (Singleron Biotechnologies) at 28 °C for 15 min. The mixture was then centrifuged at 500 g for 5 min and resuspended with PBS. Finally, the samples were stained with trypan blue (Sigma-Aldrich) and cellular viability was evaluated microscopically.
scRNA sequencing library preparation
Single-cell suspensions (1 × 105 cells/mL) with PBS (HyClone, Logan, UT, USA) were loaded into microfluidic devices using a Singleron Matrix® Single Cell Processing System (Singleron Biotechnologies). Subsequently, scRNA-seq libraries were constructed according to the protocol of the GEXSCOPE® Single Cell RNA Library Kit (Singleron Biotechnologies) [57]. Briefly, a single-cell suspension was loaded onto the microchip to partition single cells into individual wells on the chip. Cell barcoding beads were loaded into the microchip and washed. Afterwards, 100 μL of single-cell lysis buffer was added to the chip to lyse the cells and capture mRNAs at room temperature for 20 min. The beads, together with the captured RNAs, were flushed out of the microchip and used for subsequent reverse transcription, cDNA amplification, and library construction. After size selection and purification, pools were sequenced on an Illumina Novaseq 6000 (San Diego, CA, USA) with 150 bp paired-end reads.
scRNA-seq quantifications and statistical analysis
Raw reads were processed to generate gene expression profiles using an internal pipeline. Briefly, for each cell barcode the unique molecular identifier (UMI) was extracted after filtering read one without poly-T tails. Adapters and poly-A tails were trimmed (fastp V1) before aligning read two to GRCh38 with Drosophila melanogaster Ensembl version 102 annotation [58]. For reads with the same cell barcode, the UMI and gene were grouped together to calculate the number of UMIs for genes in each cell. UMI count tables for each cellular barcode were employed for further analysis. Cells with an unusually high number of UMIs (>37,000) or mitochondrial gene percent (>25%) were filtered out. We also excluded cells with less than 990 or more than 4200 genes detected.
Cell type identification and clustering analysis were performed using the Seurat program [59, 60]. Cell-by-gene matrices for each sample were individually imported to Seurat version 3.1.1 for downstream analysis [60]. Uniform manifold approximation and projection (UMAP) and t-distributed Stochastic Neighbor Embedding (t-SNE) were performed to visualize cell clusters. Upregulated enriched genes were determined to be significant with a threshold standard of fold change >1.28 and a P-value <0.01. Differentially expressed genes (DEGs) were considered significant with a fold change >1.50 and P-value <0.05.
Gene Ontology (GO) and Kyoto Encyclopedia of Genes and Genomes (KEGG) analyses were carried out on the gene set using clusterProfiler software to explore biological functions or pathways significantly associated with specifically expressed genes [61].
For correlation analysis, gene sets were calculated based on average expression counts that belong to each set of features via the PercentageFeatureSet function in the Seurat package [46]. Pearson correlations were calculated among these gene sets or signatures. Gene correlation analysis was performed directly on the data matrix by the Pearson correlation method.
Monocle 2 (version 2.10.1) was used to perform single cell trajectory analysis based on the matrix of cells and gene expression [62]. Monocle 2 reduced the space down to one with two dimensions and ordered the cells [63]. Once the cells were ordered, the trajectory was visualized in the reduced dimensional space. Pseudotime trajectory analysis was used to further analyze the germ cell differentiation trajectories to identify key factors or pathways required for different novel stages during spermatogenesis.
Statistical analysis
Quantitative results were presented as the mean ± standard error of mean (SEM), and the data were evaluated for statistical differences using Student’s t-test and a one-way ANOVA with GraphPad Prism software version 6.01 (GraphPad Inc., La Jolla, CA, USA). Chi-square test was used to evaluate ratio results. Experiments conducted in this study were repeated at least three times. *P < 0.05; **P < 0.01; ***P < 0.001.
Supplementary information
Acknowledgements
The authors wish to thank all study participants, research staff, and students who assisted with this work. We would like to thank Chao Tong (Life Sciences Institute, Zhejiang University, Zhejiang, China) for sharing reagents and stocks. We are also grateful to Singleron Biotechnologies for scRNA-seq and Gene Denovo Biotechnology for assisting bioinformatics analysis in this study.
Author contributions
JY, ZG, FS, and XZ initiated the project, designed the study, coordinated the experiment, and wrote the manuscript. ZL, QH, YF, FTS, XC, LH, HY, and LJ performed the experiments and provided conceptual inputs for the paper. CS, LJ, HY, YS, JT, and PZ analyzed the data. All authors read and approved the final manuscript.
Funding
This study was funded by The National Key Research and Development Program of China (2021YFC2700200), The National Natural Science Foundation of China (82071838, 82101891, 82173554), The Key Research and Development Program of Ningxia Hui Autonomous Region (2021BEG02029), Natural Science Foundation of Jiangsu Province (BK20221376, BK20201444), Jiangsu Province Senile Health Scientific Research Project (LR2021035), Science and Technology Project of Nantong City (JC2021119), Basic Science Research Program of Nantong City (JC12022006, JC12022086), Postgraduate Research & Practice Innovation Program of Jiangsu Province (KYCX20_2794), Qing Lan Project for Excellent Young Key Teachers of Colleges and Universities of Jiangsu Province (2020).
Data availability
The raw sequence data reported in this paper have been deposited in the Genome Sequence Archive (Genomics, Proteomics & Bioinformatics 2021) in National Genomics Data Center (Nucleic Acids Res 2022), China National Center for Bioinformation / Beijing Institute of Genomics, Chinese Academy of Sciences (GSA: CRA009665) that are publicly accessible at https://ngdc.cncb.ac.cn/gsa.
Competing interests
The authors declare no competing interests.
Footnotes
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
These authors contributed equally: Jun Yu, Yangbo Fu, Zhiran Li, Qiuru Huang.
Contributor Information
Zhifeng Gu, Email: guzf@ntu.edu.cn.
Fei Sun, Email: sunfei@ntu.edu.cn.
Xinyuan Zhao, Email: zhaoxinyuan@ntu.edu.cn.
Supplementary information
The online version contains supplementary material available at 10.1038/s41420-023-01391-4.
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
The raw sequence data reported in this paper have been deposited in the Genome Sequence Archive (Genomics, Proteomics & Bioinformatics 2021) in National Genomics Data Center (Nucleic Acids Res 2022), China National Center for Bioinformation / Beijing Institute of Genomics, Chinese Academy of Sciences (GSA: CRA009665) that are publicly accessible at https://ngdc.cncb.ac.cn/gsa.