Biological invasions have emerged as a prominent feature of global change in the Anthropocene, simultaneously acting as both a consequence of human-induced transformations and a major driver that actively accelerates further global disruptions [1–3]. Mounting evidence reveals that invasions interact with other global change drivers in complex and nonlinear ways, often leading to unexpected ecological and evolutionary consequences [4, 5]. Beyond their well-documented ecological disruptions, their economic impacts are more alarming, exceeding at least US$423 billion globally and CNY 400 billion annually in China alone [1, 6]. The cost is comparable to those of major natural disasters such as earthquakes, floods, and wildfires, but continue to escalate at an even faster rate [1, 2]. The growing frequency and magnitude of invasions highlight the urgent need for an integrated theoretical framework and science-based strategies for their monitoring, prediction, and management, particularly in identifying crucial determinants of invasion success.
Invasive species must overcome a sequence of environmental challenges to achieve establishment and invasion success in a new region [7, 8]. A critical factor underpinning this success is the ability to respond to both abiotic and biotic stresses throughout the invasion process [9, 10]. During early stages such as transport, introduction, and establishment, invasive species often encounter rapidly changing, harsh, and repeated abiotic challenges, including temperature extremes, drought, or salinity, as well as biotic stresses such as competition, predation, and novel mutualistic interactions [10–12]. The capacity to acclimate within a single generation through phenotypic plasticity, or to adjust trait distributions rapidly via epigenetic modifications or swift evolutionary changes, mitigates demographic bottlenecks and increases the likelihood of successful establishment [9, 11, 13]. Of various mechanisms contributing to success during the early stages of invasions, phenotypic plasticity allows individuals to maintain performance across variable environments, effectively “buying time” for further adaptive evolution [14–16]. By enabling populations to persist under a broader range of conditions, sustain growth in disturbed habitats, and expand their geographic range more efficiently, these rapid stress-response mechanisms form a crucial bridge between initial exposure to novel environments and long-term invasion success [14, 16, 18].
Among multiple molecular mechanisms contributing to phenotypic plasticity, microRNAs (miRNAs) are crucial epigenetic regulators that influence the response of invasive species by post-transcriptionally modulating gene expression [19–21]. These small, non-coding RNAs can function independently or in concert with other regulatory elements to fine-tune gene activities, thereby enabling rapid and reversible phenotypic changes essential for response to environmental challenges [22, 23]. For example, our former study has confirmed that invasive tunicates can utilize miRNAs to mediate a “stress memory” that enhances the ability to cope with recurrent salinity changes, primarily by regulating genes involved in osmotic homeostasis such as free amino acid metabolism and ion transport [21]. Similarly, in invasive agricultural weeds, a failure to induce certain miRNAs after herbicide exposure can lead to the successful constitutive expression of detoxification enzymes (e.g., Cytochrome P450s), effectively conferring herbicide resistance and ensuring the weed's survival and subsequent invasion success [24]. Although the importance of miRNAs in stress responses has been well recognized, comprehensive studies are largely needed to advance from descriptive identification of differentially expressed miRNAs to mechanistic understanding of their regulatory dynamics and evolutionary significance.
Traditionally, mature miRNAs were regarded as single, invariant sequences. However, accumulating evidence reveals that a single miRNA locus can generate multiple sequence variants, collectively known as microRNA isoforms (isomiRs) [25, 26]. These variants arise through several molecular mechanisms. Imprecise cleavage by the RNase III enzymes Drosha and Dicer can process pri-miRNA and pre-miRNA at alternative positions, producing templated isomiRs with variable 5’ or 3’ ends [27]. Exonucleolytic trimming by exonucleases further contributes to length heterogeneity by removing nucleotides from miRNA termini [28, 29]. In addition, non-templated nucleotide additions catalyzed by terminal nucleotidyl transferases (TUTases), such as TUT4 and TUT7, introduce uridine (uridylation) or adenine (adenylation) residues at the 3’ end, thereby influencing miRNA stability and Argonaute (AGO) loading efficiency [30, 31]. Less frequently, RNA editing, such as adenosine-to-inosine conversions mediated by Adenosine Deaminases Acting on RNA (ADAR) enzymes, introduces internal nucleotide substitutions that give rise to non-templated isomiRs with potential regulatory divergence [32]. Collectively, these mechanisms generate diverse classes of isomiRs, including 5’ variants (alterations at the 5’ end), 3’ variants (alterations at the 3’ end), polymorphic variants (nucleotide substitutions without length changes), and mixed-type variants (combining sequence and length variations).
Interestingly, multiple lines of evidence have established that isomiRs are functionally active, being selectively incorporated into AGO complexes and capable of regulating both distinct and overlapping target genes relative to their canonical miRNAs [33, 34]. Among the various classes, 5’ isomiRs exert particularly strong functional effects, as 5’ diversification alters the seed region (nucleotides 2–8) and thereby reshapes target specificity. For instance, a 5’ isomiR of miR-9-1 gains the ability to inhibit DNMT3B and NCAM2 while losing regulation of CDH1 compared with the canonical sequence [35]. Some isomiRs, especially those with minor 3’ or internal variations, share many targets with their canonical counterparts, providing functional redundancy and potentially enhancing overall gene repression [33, 36]. Nevertheless, experimental evidence demonstrates that distinct isomiRs can possess unique targetomes and biological roles, as observed for miR-411 [37], miR-34/449 [38], and miR-183 [39]. Beyond target recognition, 5’ variations may also influence miRNA stability and half-life due to structural alterations affecting RNA-induced silencing complex (RISC) interactions [40]. Although the relative rate of 5’ variants was lower than 3’ variants, 5’ isomiRs could directly affect the seed sequence and weigh more in influencing the targetome, 3’ isomiRs were proved to influence the regulation process on targets, but the mechanisms are still unclear [41]. As for the polymorphic variants, it was observed that the frequency of single-nucleotide polymorphisms (SNPs) was lower than other genomic regions, for instance, the density of miRNA genes’ SNPs among the total SNPs in human genome was less than 1% [42].
Given the diverse forms and flexible functions of isomiRs, it is plausible that they play crucial roles in mediating rapid environmental responses during biological invasions. By generating a spectrum of regulatory variants from a single miRNA locus, isomiRs can enhance transcriptomic versatility and fine-tune gene expression dynamics, thereby promoting stress tolerance in invasive populations. Accordingly, we hypothesize that the diversification of isomiR variants facilitates rapid gene regulatory adjustments, further supporting stress responses and environmental resilience during biological invasions. To effectively test this hypothesis, it is essential to select a model invasive species that combines high ecological impact with well-characterized biology.
Ciona robusta is a highly invasive ascidian presumably native to the Northwest Pacific and has invaded coastal ecosystems globally, including extreme environments such as the Red Sea [43, 44]. This species has caused substantial economic losses through biofouling in aquaculture and has strongly affected invaded ecosystems by reducing species richness and overall biodiversity [45, 46]. During its invasion process, C. robusta often encounters rapid and severe environmental fluctuations, such as salinity changes of ~ 15‰ [46]. As a sessile species, it cannot actively escape these challenges and instead rely on a highly resilient physiological system to maintain homeostasis under rapidly changing, harsh conditions [46]. Its combination of high invasiveness, exceptional stress tolerance, and a compact, well-characterized genome makes C. robusta an ideal model for exploring the mechanisms driving invasion success [46].
Using C. robusta as a model system here, we aim to (1) characterize the expression patterns of 5’ isomiRs and their corresponding canonical miRNAs under osmotic stress, (2) identify overlapping and specific targets of 5’ isomiRs and canonical miRNAs, and (3) examine functional differences between the targets of canonical miRNAs and their isomiRs. Our results are expected to shed light on how osmotic fluctuations influence isomiR expression and function, thus providing deeper insights into the dynamic roles of miRNAs under varied environmental conditions during biological invasions.