Abstract
The Arabian Gulf (hereafter ‘the Gulf’) is renowned for its unique ecological characteristics and distinct marine life. It offers a diverse range of ecosystems that have adapted to the impacts posed by natural stress and human activities. Regular biomonitoring and diversity assessments are necessary to document the health of the Gulf ecosystem and to implement appropriate measures for effective conservation and management. Recently, environmental DNA (eDNA), a total pool of DNA isolated from environmental samples, has emerged as a highly effective tool for ecological studies. This review explores the opportunities, prospects, and challenges associated with employing eDNA metabarcoding in the ecological assessment and biomonitoring of the Gulf. It provides an overview of the status of the Gulf ecosystem and discusses the potential applications of eDNA metabarcoding in assessing biodiversity, monitoring invasive species, and evaluating ecosystem health. Additionally, the investigation addresses the challenges inherent in implementing this technique, considering environmental complexities, methodological intricacies, and data interpretation. Overall, this review emphasizes the immense potential of eDNA metabarcoding in advancing ecological assessment in the Gulf and calls for further research and collaboration to harness its benefits in this unique marine ecosystem.
1 Introduction
The Arabian Gulf (hereafter ‘the Gulf’) is a shallow sedimentary basin located between 24° and 30° N in latitude and 48° and 57° E in longitude and is bordered by eight rapidly developing nations. The Gulf constitutes a part of the Arabian Sea ecoregion and represents a realm of the tropical Indo-Pacific Ocean (Spalding et al., 2007). The Gulf spans a length of 1000 km and varies in width from 200 to 300 km with a total area of approximately 240,000 km2. It reaches a maximum depth of 100 m at the Strait of Hormuz, with an average depth of 35 m (Taher et al., 2012). Owing to extreme environmental conditions, the Gulf hosts a unique ecosystem characterized by mangroves, coral reefs, seagrass, and algal beds with low species biodiversity (Naser, 2014; Samimi-Namin and Hoeksema, 2023). The Gulf ecosystem is under pressure from both anthropogenic and natural disturbances that disrupt normal functioning, underscoring the importance of marine researchers to quantify and monitor the biodiversity trends to ensure the health of this ecosystem (Sharifinia et al., 2019; Lin et al., 2021a). Traditionally, marine biodiversity has been monitored by various methods, including observation-based data collection, capturing marine organisms via nets, hooks, and traps, sediment collection using grab samplers, and the analysis of acoustic, chemical, and electrical properties using diverse instruments (). Nonetheless, these methods have limitations, including invasiveness, destructiveness, time consumption, labor intensiveness, and dependence on a dwindling number of taxonomic experts to identify specimens (Thomsen and Willerslev, 2015). These constraints emphasize the importance of developing novel techniques for effectively monitoring global biodiversity.
In recent years, the use of environmental DNA for biodiversity assessment has become increasingly popular. Environmental DNA or eDNA refers to the DNA from skin, hair, urine, feces, gametes, mucus, or carcasses of organisms that are released to the environment, such as water or sediment (Taberlet et al., 2012; Thomsen and Willerslev, 2015). The use of eDNA can potentially revolutionize the field of conservation science and practices. It has been proven to be an efficient approach for assessing the biodiversity of marine ecosystems on vast temporal and spatial scales (). The advantages of eDNA include its sensitivity, non-invasiveness, capability to monitor rare or elusive species, and early detection of invasive species (Smart et al., 2015; ; ). The advent of high-throughput sequencing has opened new opportunities for employing the eDNA approach to study species communities. In this context, eDNA metabarcoding has gained prominence, allowing the identification of multiple taxa using DNA extracted from environmental samples through amplicon sequencing (Pawlowski et al., 2022). The eDNA metabarcoding enables the simultaneous detection of micro/macro-organisms, ranging from small metazoans to large vertebrates employing multiple markers for monitoring marine biodiversity (; Topstad et al., 2021). Therefore, this technique surmounts the obstacles of conventional, labor-intensive methods and offers the prospect of characterizing the Gulf biodiversity effectively in terms of time and space. The eDNA metabarcoding projects are being carried out across the globe to assess marine biodiversity (), analyze anthropogenic impacts (), and monitor marine protected areas (). Figure 1 illustrates the worldwide distribution of eDNA studies conducted in marine environments and published between 2015 and 2023, sourced from the Scopus database. Based on the literature review, it was observed that the focus of eDNA studies was predominantly on the North Atlantic Ocean and the western Pacific Ocean, with less representation in the Indian, South Pacific, and South Atlantic Ocean regions. The meta-data available from these investigations could be recovered and reused for systematic comparison with traditional biomonitoring methods and statistical analyses to address new questions or identify an overall trend regarding biodiversity and conservation of marine ecosystems (Shea et al., 2023).
Figure 1
The methodology for eDNA metabarcoding should be customized according to the specific goals of the investigation and the unique characteristics of the samples being studied. Numerous review articles have been published that delve into the various steps in eDNA metabarcoding, covering aspects such as sampling, DNA extraction, primer selection, sequencing platforms, and bioinformatics analysis (; van der Loos and Nijland, 2021; Pawlowski et al., 2022; Takahashi et al., 2023; Zhang et al., 2023). Moreover, the methods and pipelines for bioinformatics analysis are constantly being refined and updated to enhance biodiversity assessments. Developing various metabarcoding data analysis pipelines underscore the requirement for user-friendly software and customized workflows tailored for specific sequencing datasets (Hakimzadeh et al., 2023). While the growing use of eDNA metabarcoding facilitates cross-study comparisons, it is crucial to ensure consistency and uniformity in the methods employed to establish it as a standard for monitoring biodiversity (van der Loos and Nijland, 2021).
2 Status of the Arabian Gulf ecosystem and the need for biomonitoring
The Gulf ecosystem can be categorized into coastal and subtidal ecosystems (). Coastal ecosystems comprise diverse habitats such as wetlands, sandy beaches, and rocky shores. Wetlands consist of salt flats, salt marshes, and mangroves. Salt flats, also known as sabkhas in Arabic (area of low-lying salty ground), have extensive microbial mats, making them an ecologically important and productive habitat in the Gulf (). Mangroves in the Gulf are dominated by a single species of Avicennia marina adapted to highly variable seasonal temperature and salt concentrations. These ecosystems play a crucial ecological role by providing food and shelter to diverse terrestrial and marine organisms. Dunes with halophyte vegetation characterize sandy beaches. Subtidal ecosystems comprise seagrass and coral reef habitats. Seagrass beds (containing species Halodule uninervis, Halophila stipulacea and H. ovalis) are distributed along most of the coastlines, serving as food sources and habitats for turtles, dugongs, pearl oysters, and shrimps in the Gulf. Coral reefs serve as reservoirs of biodiversity in the Gulf, and approximately 40 species of hard corals and 31 species of soft corals have been identified. Coral growth is best observed on offshore shoals, and fringing reefs are present along the mainland shoreline (Naser, 2014). These are extensively studied for thermal adaptations due to their tolerance to harsh environmental conditions (Riegl et al., 2011; ). The Gulf (Figure 2) represents a highly vulnerable ecosystem challenged by a myriad of local and global factors that threaten to destroy biodiversity, potentially leading to ecological destruction. Due to the severity and complexity of these challenges, the Gulf has attracted considerable attention from marine researchers and ecologists worldwide. It has become a “hotspot” for research, indicating that scientists from various parts of the world are actively studying the Gulf to understand its threats, develop strategies for biomonitoring and conservation, and contribute to global knowledge about preserving marine biodiversity. The focus on the Gulf reflects its importance in understanding and addressing broader issues related to marine conservation and the impact of environmental changes on ecosystems.
Figure 2
2.1 Natural environmental variables and seasonality
The Gulf receives water from the Indian Ocean through the Strait of Hormuz, which then flows northwest along the Iranian coast to Kuwait and further south along the coast of Saudi Arabia (Vaughan et al., 2019). As the water circulates anticlockwise around the Gulf, it experiences increased salinity due to evaporation. The Gulf is characterized by extreme environmental conditions, including high salinity, extreme temperature, limited water exchange, and high evaporation rates (Sheppard et al., 2010; Manokaran et al., 2021). The climate in the Gulf region is characterized as transitional between tropical and subtropical. Despite being geographically located in the subtropics, the arid surroundings contribute to a tropical climate during the summer. Winter spans from December to March, while summer extends from June to September, with two transitional periods in between (
2.2 Anthropogenic stressors in the Gulf
Rapid industrialization in the Gulf has introduced numerous anthropogenic stressors significantly impacting the natural environment (Figure 3). A massive boom in coastal development has led to the exploitation of shallow marine intertidal habitats (
Figure 3

A conceptual diagram illustrating the cross-section of the Arabian Gulf’s ecosystems and its human pressures showcasing the importance of eDNA-based biodiversity assessments.
The desalination industry has become an increasingly alarming issue in the Gulf. As stated by Ibrahim and Eltahir (2019), countries in the region, such as Saudi Arabia, the Emirates, Kuwait, Qatar, and Bahrain, are responsible for processing approximately half of the world’s desalinated seawater. Consequently, the discharge of effluents from seawater desalination into the coastal and subtidal areas of the Gulf poses a significant menace to marine habitats (
3 Application and prospects of eDNA metabarcoding in the Arabian Gulf
The Gulf, characterized by its unique biodiversity, is a subject of significant scientific interest, primarily due to its potential vulnerability to natural and anthropogenic stressors in the future (Riegl and Purkis, 2012;
Table 1
| Sl. No. | Taxon/taxa studied | Use | Target gene | References |
|---|---|---|---|---|
| 1 | Benthic bacteria | Oil pollution | 16S rRNA | Lee et al., 2019 |
| 2 | Vertebrates | Habitat biomonitoring | 12S rRNA | Sigsgaard et al., 2020 |
| 3 | Benthic bacteria and eukaryotes | Oil pollution | 16S/18S rRNA | Oladi et al., 2022 |
| 4 | Benthic foraminifera | Environment quality assessment | 18S rRNA |
eDNA metabarcoding studies reported from the Arabian Gulf.
3.1 Application in ecology
The Gulf provides a distinct habitat for various organisms adapted to extreme environmental conditions. Each habitat supports unique assemblages of organisms, from benthic organisms in intertidal sediments and mangrove ecosystems to phyto- and zooplankton in the pelagic region (Qurban et al., 2012; Naser, 2014; O’Donnell et al., 2017).
3.2 Application in biomonitoring and industry
Monitoring marine life relies on time-consuming traditional surveys that pose significant risks to marine organisms (Wheeler et al., 2004). The challenges were further intensified by restrictions on bottom trawling in specific countries, such as Qatar, and numerous marine protected areas in the Gulf. The eDNA metabarcoding offers a feasible alternative for biomonitoring in the Gulf, especially in marine protected areas where routine biodiversity monitoring and assessment of species and habitats is a critical factor. Also, the eDNA approach can be effectively employed in monitoring certain marine species, especially those that are difficult to track due to their small size or residents in deep-sea habitats (Stefanni et al., 2022). The data collected through monitoring activities employing eDNA can play a crucial role in guiding management practices aimed at preserving the Gulf ecosystems. This approach ensures the maintenance of healthy ecosystems, along with their associated functions and services. However, challenges such as a lack of standardized methodology, incomplete reference databases, and the lack of appropriate contamination controls or sensitivity measures may pose obstacles to interpreting eDNA results within environmental impact assessments (Hinz et al., 2022). In recent times, there has been growing validation of the effectiveness of eDNA for biomonitoring and evaluating the response of biotic communities to environmental stress associated with anthropogenic activities. Previous studies in the Gulf have employed the eDNA approach to evaluate the environmental impacts of industrial activities on benthic communities (Lee et al., 2019;
The Gulf is home to critically endangered groups such as dugongs, sea turtles, and several endangered fishes (
Researchers have been using the ecological index, AZTI’s Marine Biotic Index (AMBI), for assessing the ecological status of macrobenthic communities in the Gulf (Shokat et al., 2010; Joydas et al., 2017, Joydas et al., 2023). The genetic versions of this index, genomic AMBI (gAMBI) and presence/absence genomic AMBI ((pa)gAMBI) are calculated using metabarcoding-derived read counts and presence/absence, respectively, for each identified taxon in eDNA metabarcoding investigations. Kappa analysis was used to evaluate the correlation between the different indices, indicating the validity of eDNA metabarcoding for assessing marine benthic ecosystems (
3.3 Application in invasion biology
For centuries, anthropogenic activities have been responsible for introducing non-native species into new ecosystems, posing significant threats such as disruptions to ecosystems, loss of biodiversity, and considerable ecological and economic impacts. The introduction of non-native organisms to a new marine ecosystem, commonly referred to as marine bio-invasion, can occur through a variety of means, including maritime shipping, trade of live organisms for aquaculture, fisheries, stock enhancement, ornamental markets, and maritime canals (Ojaveer et al., 2018). Marine bio-invasions have been identified as a serious threat to biodiversity and the regular functioning of marine ecosystems (Lubchenco, 1991;
Previous investigation using taxonomic data has identified 14 suspected alien species, ranging from microalgae to fish in the Gulf (
4 Challenges
The process of eDNA metabarcoding presents numerous technical hurdles that need to be addressed in the Gulf, spanning from sample collection to eDNA extraction, primer selection, and subsequent bioinformatics analysis.
4.1 Challenges in the field
The shallow nature of coastal waters and inner bays in the Gulf demands the use of small boats for sampling. Consequently, smaller boats make sampling dependent on favorable weather conditions, leading to variability in schedules and possible delays. This situation can result in extended storage periods for eDNA samples. Filtration of seawater samples on smaller boats presents significant challenges, particularly amid adverse weather conditions in the Gulf. Furthermore, it is crucial to note that various physicochemical, biological, and ecological factors influence the release, retention, transportation, and degradation of eDNA. In the context of the Gulf, a comprehensive awareness of the interplay of these factors becomes imperative for identifying potential influences on eDNA dynamics. However, the existing literature suggests that elevated water temperature is likely to have a negative impact on the persistence of eDNA (Sigsgaard et al., 2020). The variability of eDNA in the Gulf at both spatial and temporal dimensions highlights the importance of a meticulous approach when designing a sampling plan. Hence, pilot studies are highly recommended.
4.2 Challenges in laboratory analysis
The establishment of standardized procedures for sample collection and laboratory analysis is a fundamental step toward ensuring the reliability and reproducibility of eDNA analysis in the Gulf. Obtaining high-quality DNA with a good yield is crucial to ensure the maximum representation of the biotic community in environmental samples. Elevated levels of PCR inhibitors such as humic acid and tannic acid in sediment samples collected from wetlands, coral reefs, and fish landing sites in the Gulf can affect PCR analyses. Therefore, it is necessary to either dilute the eDNA or implement additional purification steps to eliminate these inhibitors (Patin and Goodwin, 2023). As eDNA samples are highly heterogeneous, it is challenging to achieve a complete primer-target match during amplification, which could lead to biased PCR results (Stadhouders et al., 2010). Moreover, the risk of false positives and negatives in eDNA analysis exists due to potential field or laboratory contaminations, which can result in the misinterpretation of data (
4.3 Challenges in data analysis
The accuracy of taxonomic identification in eDNA analysis is significantly dependent on the quality of the reference database utilized. A key challenge in this procedure involves assigning gene sequences to particular taxa, a task typically accomplished through comparisons with established databases such as GenBank or Barcode of Life Data System (BOLD). Past studies have emphasized that gaps in reference databases significantly impede the taxonomic assignment of recovered sequences (Wangensteen et al., 2018; Ruppert et al., 2019; Weigand et al., 2019; Hestetun et al., 2020). Despite the existing DNA barcoding efforts for various fish species in the Gulf region (
5 Conclusion and future directions
The remarkable progress in DNA sequencing technologies has significantly broadened the range of applications for eDNA in ecological monitoring, impact assessment, and global mitigation measures. The eDNA metabarcoding, a versatile and powerful tool, offers extensive applicability for addressing fundamental biological inquiries related to species diversity, distribution, and ecology. It enables the simultaneous detection of multiple taxonomic groups across large geographical scales, especially in regions undergoing significant habitat changes, environmental variations, or human-induced pressures. The Gulf, characterized by its extreme environment and substantial anthropogenic activities, faces challenges of marine pollution that impact its biodiversity. The eDNA metabarcoding can potentially revolutionize biodiversity assessment, biomonitoring, and environmental impact studies in the Gulf, offering a more comprehensive and efficient approach to understanding and conserving this extreme environment. As the Gulf region undergoes rapid economic development, having baseline data on biodiversity and ecological health is crucial. The present requirement entails establishing collaborative platforms and initiating foundational studies utilizing eDNA metabarcoding to generate essential baseline data on marine biodiversity in the Gulf. This data will serve as a guiding framework for future regional biomonitoring initiatives. Integrating eDNA metabarcoding into regular monitoring programs and environmental management practices is essential for the sustained health and conservation of the Gulf. Though eDNA metabarcoding offers numerous advantages, it also presents certain challenges that necessitate careful consideration and resolution. These encompass the requirement for standardized protocols, quality control measures, advancements in bioinformatics for accurate data analysis and interpretation and a lack of comprehensive reference databases. The key requirement in eDNA research in the Gulf is establishing a regional reference database for accurately identifying the species which help researchers differentiate between native and invasive species, assess biodiversity, and monitor ecosystem health. However, the lack of well-equipped laboratories specializing in Molecular Biology in the Gulf region severely restricts the capacity to conduct efficient and comprehensive barcoding studies. This deficiency hinders scientists and researchers from exploring and cataloging the rich biological diversity within the Gulf, limiting their ability to identify and characterize various species accurately. The establishment of modern Molecular Biology facilities tailored for DNA barcoding research is essential to overcome this challenge. Additionally, there is a knowledge gap regarding the impact of environmental conditions and oceanographic patterns on eDNA degradation and transport rates in the Gulf. Advancing knowledge in these areas is crucial for accurately interpreting eDNA data and optimizing its effectiveness in monitoring initiatives. Overall, the progress achieved in eDNA research presents significant opportunities but necessitates ongoing efforts to address challenges, expand reference databases, improve understanding of environmental influences, and foster the integration of eDNA with traditional monitoring approaches.
Statements
Author contributions
TJ: Conceptualization, Writing – original draft, Writing – review & editing. SM: Conceptualization, Writing – original draft. JG: Conceptualization, Investigation, Writing – original draft, Writing – review & editing. JR: Investigation, Writing – review & editing. LY-J: Conceptualization, Writing – original draft, Writing – review & editing. MH: Writing – review & editing. MN: Writing – review & editing. KM: Writing – review & editing. MQ: Writing – original draft. SM: Formal Analysis, Writing – review & editing. SH: Visualization, Writing – review & editing. RM: Writing – review & editing, Project administration, Supervision. AQ: Writing – original draft. DL-C: Writing – review & editing. NA: Project administration, Supervision, Writing – review & editing.
Funding
The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.
Acknowledgments
The authors would like to thank the Applied Research Center for Environment and Marine Studies, KFUPM, Saudi Arabia and Environmental Protection Department, Saudi Aramco, Saudi Arabia, for providing all the necessary support to prepare this manuscript. Authors are grateful to the two anonymous reviewers for their detailed and constructive comments to improve the quality of the paper. This review was conducted as part of the project entitled, ‘Saudi Aramco / KFUPM-RI Sustaining Research Project Marine Environmental Studies – Phase VII’ (KFUPM Project No. CEM2700) funded by Saudi Aramco.
Conflict of interest
Authors MQ, AQ and DL-C are employees at Saudi Aramco.
The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
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Summary
Keywords
environmental DNA, high-throughput sequencing, biomonitoring, anthropogenic activities, marine ecosystem
Citation
Joydas TV, Manokaran S, Gopi J, Rajakumar JP, Yu-Jia L, Heinle M, Nazal MK, Manikandan KP, Qashqari M, Mohandas SP, Hussain SA, Maneja RH, Qasem AM, Lozano-Cortés D and Abuzaid NS (2024) Advancing ecological assessment of the Arabian Gulf through eDNA metabarcoding: opportunities, prospects, and challenges. Front. Mar. Sci. 11:1276956. doi: 10.3389/fmars.2024.1276956
Received
13 August 2023
Accepted
23 February 2024
Published
18 March 2024
Volume
11 - 2024
Edited by
Stelios Katsanevakis, University of the Aegean, Greece
Reviewed by
Cory Douglas Bishop, St. Francis Xavier University, Canada
Charlotte Havermans, Alfred Wegener Institute Helmholtz Centre for Polar and Marine Research (AWI), Germany
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© 2024 Joydas, Manokaran, Gopi, Rajakumar, Yu-Jia, Heinle, Nazal, Manikandan, Qashqari, Mohandas, Hussain, Maneja, Qasem, Lozano-Cortés and Abuzaid.
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*Correspondence: Seerangan Manokaran, manokaran.pappathy@kfupm.edu.sa; Jayanath Gopi, jayanath.gopi@kfupm.edu.sa
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