1. Introduction
Global climate change has a great impact on water resources. Strengthening the protection of water resources and the restoration of water ecological environment are the only ways to realize the harmonious development of man and nature. The ocean is the largest reservoir on Earth. The destruction of the marine ecosystems will seriously affect the quality of life and health of people. The whole ocean is a large ecosystem, including many different levels of marine ecosystems. Further, oyster reefs are among the most depleted marine ecosystems globally. According to Beck et al. [
1], an estimated 85% of all oyster reefs globally have been lost. For example, the population size of the eastern oyster (
Crassostrea virginica; a.k.a., American oyster) has declined in many estuaries throughout the mid-Atlantic and southeastern United States, including eastern North Carolina and the Chesapeake Bay, where populations have been reduced to 1–2% of their historic peaks approximately a century ago [
2]. Historically, it took the Chesapeake Bay’s large oyster population approximately 3.3 days to filter the entire bay’s water, compared with nearly a year for existing populations after the 1980s [
2].
Oyster reefs are reefs formed of layers of oysters attaching to one another and can represent massive aggregations. They are widely distributed in estuaries, bays, and lagoons in subtropical and temperate regions. Globally, oyster reefs are found in the European Union (e.g., the Wadden Sea), the USA (e.g., Chesapeake Bay), China (e.g., Bohai Bay), Australia (e.g., Port Phillip Bay), New Zealand (e.g., North Canterbury), Argentina (e.g., Golfo San Matías), Canada (e.g., Nootka Sound) and other places [
3]. Oyster reefs are an essential type of marine habitat that provides a wide variety of ecosystem services, such as providing food, improving water clarity [
4], facilitating denitrification [
5], protecting shorelines [
6], increasing landscape diversity [
7,
8], and providing habitats for marine life [
9,
10,
11]. Therefore, because of their large impacts and ability to transform ecosystems, oysters are known as “ecosystem engineers” [
12].
The severe degradation and loss of natural oyster reefs, caused by activities such as overharvesting, disease, habitat degradation [
13], water pollution and coastal zone development, has been recognized as a global problem since scientists became aware of their important ecological function [
1,
14]. Due to the diversity and high values of ecosystem goods and services provided by oyster reefs, there has been increasing interest in oyster reef restoration in many regions of the world [
15,
16,
17]. Early attention to oyster reef recovery was mainly in the USA, especially in the Gulf of Mexico and the East Coast. The species preferred for restoration in the USA has been
C. virginica [
18]. In addition to the USA, New Zealand, Australia, some European countries, and China have also researched and applied oyster reef restoration practices [
3]. To provide ideas and basic information for the whole process of reef restoration project, Fitzsimons et al. [
12] published shellfish reef restoration guidelines based on the latest global scientific research achievements and practical experience.
In recent years, people have begun to study the essential ecosystem services provided by oyster reefs [
19,
20]. Through assessing oyster reef ecosystem services can assist coastal managers in realigning management plans to maximize the benefits of oyster reef restoration efforts. In addition to the research on oyster reef restoration and ecosystem services, extensive work has been conducted on the effectiveness of oyster reefs in serving as coastal defense [
21], the impact of global climate change on oyster reefs [
22,
23,
24], the role of oyster reefs in coping with climate change [
25,
26] and other aspects. Oyster reef studies have also evolved from single-factor exploration to ecological function restoration, from restoring degraded habitats to focusing on habitat changes under the combined influence of climate change and human activities.
At present, there are a number of summaries and literature reviews of oyster reef research [
27,
28,
29,
30,
31]. As examples of reviews in the field, each of these review articles has its specific emphasis, and each plays an important role in the in-depth exploration of specific research directions. However, a broad-scale understanding of the current research status, hotspots, and future development direction of oyster reefs is lacking. Therefore, it is necessary to carry out a systematic analysis that considers oyster reef research in general based on existing publications. In the face of the large quantity of studies related to oyster reefs, a sufficiently comprehensive and accurate analysis of this field can only be achieved through bibliometrics and a visual review combining quantitative and qualitative methods.
Bibliometrics is an objective and quantitative method of researching and analyzing data obtained from databases [
32,
33,
34,
35,
36]. CiteSpace is an information visualization software that can be used to scientifically analyze literature and extract pertinent information [
37]. According to the characteristics of literature data, this software can conduct analyses of citation networks, co-occurrence networks, and conduct literature coupling [
38]. These analyses can show the evolution of hot topics, identify the impacts of landmark studies, and analyze the relationships among articles and references [
39]. To date, CiteSpace has been used in many research fields, including microplastics [
40,
41], biochar [
42,
43], pesticides [
44], sustainable urbanization [
45], waste management [
46], and others [
47,
48,
49]. Based on the bibliometrics method, this paper applies the CiteSpace software to comprehensively sort the relevant literature on oyster reefs available in the core collection database of the Web of Science. This effort will clearly and intuitively present an overview of oyster reefs research and identify research hotspots and describe the evolution of related topics, as well as identify future trends in this field. This information will provide a useful reference and invaluable insight for future oyster reefs research and conservation practices.
4. Discussion
4.1. Trends in the Number of Published Papers
Overall, the number of publications each year on oyster reefs exhibited an increasing trend, with especially large increases in recent years (
Figure 1). This trend may be attributed to the relatively recent global consensus that oyster reef conservation and research will benefit ecosystems and economies worldwide. For example, the world’s largest oyster reef restoration project in Chesapeake Bay started in the 1990s, contributing to the increase in relevant research in the coinciding period. Entering the 21st century,
Shellfish Reefs at Risk, the first global review of the condition of oyster reefs was published [
1,
53], which was followed by shellfish reefs being added to the list of protected Wetlands at the Ramsar Convention on Wetlands in 2012 [
12] and the publication of the Oyster Habitat Restoration Monitoring and Assessment Handbook [
54] and Setting Objectives for Oyster Habitat Restoration Using Ecosystem Services: A Manager’s Guide [
55] by The Nature Conservancy (TNC) in 2014 and 2016, respectively. Oyster restoration in Europe, in contrast, is a new but fast-growing field. In order to best advance the practice of oyster restoration in Europe, the Native Oyster Restoration Alliance (NORA) was established in 2017. The NORA is a growing network of professionals seeking to exchange knowledge on the restoration of native oysters and native oyster habitats in European waters [
61]. To date, there has been a much heavier emphasis in the scientific literature around oyster reef conservation and restoration worldwide.
4.2. Scientific Contributions
The most cited article by Laura Airoldi and Michael W. Beck [
59], pointed out that oyster reefs may be among the most endangered marine habitats in Europe, with some of the largest impacts on oyster reefs coming from destructive fishing and overexploitation, with additional impacts from disease. Native oyster reefs were ecologically extinct by the 1950s along most European coastlines and well before that in many bays. Their article noted that the sustainable management of the few remaining fragments of native and semi-native coastal habitats in Europe should be prioritized. But perhaps the most cited fact about this article has to do with its broad scope. The article provides an overview of the distributions, historical losses, threats, and conservation measures of coastal habitats in the European gulf as well as estuarine and near-shore continental shelf environments. Furthermore, it covers a variety of coastal habitats in Europe, including coastal wetlands and salt marshes, oyster reefs, seagrass meadows, macroalgal beds, maerl beds, and sedimentary habitats (mudflats, sandflats, and subtidal soft bottoms).
The paper published by Beck et al. (2011) [
1] was contributed to by experts from more than ten organizations in the USA, Italy, Uruguay, Australia, and China. They examined the condition of oyster reefs across 144 bays and 44 ecoregions. Overall, the study estimated that 85% of global oyster reefs had been lost. The authors also identified the most promising cost-effective solutions for oyster reef restoration. This article was the first global assessment of oyster reef survival, bringing global attention to this important coastal habitat. After publication, in 2012, shellfish reefs were added to the list of protected wetlands by the Ramsar Convention on Wetlands [
12].
To explain the losses of oyster reefs, Lenihan et al. [
60] did a series of surveys in the Neuse River estuary, North Carolina, USA. Their findings indicated that interaction between the degradation of reef habitats (height reductions) due to fishery disturbances and extended bottom-water hypoxic/anoxic conditions caused the observed mortality on natural oyster reefs. Interactions among environmental disturbances illustrate the need to use integrative approaches in ecosystem management to restore and sustain estuarine habitats.
The other highly cited articles mainly focus on the cost and feasibility of coastal restoration, the economic valuation of ecosystem services, the role of ecosystems in coastal protection, etc. These widely cited studies have played an important role in promoting the development of oyster reef research and conservation practices.
4.3. Research Hotspots in Oyster Reef
The research hotspots in the oyster reef field focus on oyster reef habitat conservation and restoration, oyster growth, causes of habitat degradation, and oyster reef ecosystem services.
Crassostrea virginica, the most common keyword, is a reef-building oyster species that has formed extensive intertidal oyster reefs in most estuaries and bays on the east coast of North America, from the mid-Atlantic states of the USA to the Gulf of Mexico and the Caribbean [
61,
62,
63]. The next most common keyword was “Chesapeake Bay”, which is a bay located in the middle of the east coast of the USA and is the largest bay in the USA. Historically, this bay has large populations of various oyster species, with
C. virginica being most iconic.
The first regions in the world to initiate oyster reef restoration projects and related academic research were in the USA. These included locations across the U.S. Atlantic and Gulf coasts, especially in Chesapeake Bay [
64,
65,
66] and the Gulf Coast [
67,
68,
69]. From 1964 to 2018, 1,768 projects have been implemented, and since 2000, an average of 190 hectares of oyster reefs have been established each year in the USA [
18]. Of the species used in restoration projects,
C. virginica has predominated. In these projects, a variety of substrates have been used, including oyster shells, mixed oyster substrates, concrete and mixed concrete substrates, and others (e.g., limestone, granite, and surf clam shell) [
70,
71]. Through the implementation of many projects (generally large-scale with an average project size of 2.85 ha between 1999 and 2016) [
18], practitioners have steadily increased the constructed reef area in Chesapeake Bay. As the number of oyster reef restoration projects has gradually increased, scholars have also begun to quantify important ecosystem services provided by oyster reefs in marine ecosystems, such as enhancing reef-generated shoreline stabilization, habitat provisioning, water-quality improvement services, etc. [
68,
71,
72,
73].
Currently, oyster reef ecological restoration has been carried out in coastal areas of the USA, Australia, some European countries, New Zealand, and China. For example, in 2020, China issued the Technical guideline for investigation and assessment of coastal ecosystem—Part 7: Oyster reef and the Technical guideline on coastal ecological rehabilitation for hazard mitigation—Part 6: Oyster reef, to provide technical support and a basis for the conservation and restoration of oyster reefs. Oyster reef restoration has become a hotspot in international marine ecological restoration research.
4.4. Hotspots Evolution and Research Frontiers in Oyster Reef
The first identified keyword was “nitrogen”, which appeared in 1990 (
Figure 9). Because in coastal ecosystems, nitrogen has been found to be the predominant limiting factor for primary producers. Nitrogen plays an important role in determining ecosystem function. Piehler et al. [
74] found significantly higher rates of denitrification in structured habitats such as oyster reefs. Nitrogen removal by these habitats was found to be an important contributor to estuarine ecosystem function. Around 2000, the global consensus began to shift toward oyster reef conservation and research. Subsequently, “habitat degradation” became a hot topic from 2001 to 2007. In addition, “degradation” exhibited continued use with strong citation bursts from 2011 to 2015. During 2013–2022, a large number of research hotspots in the field of oyster reefs emerged and related studies increased in abundance. Since 2013, oyster reef “restoration” has attracted much attention and become a prominent research topic. This remains true to this day, with “restoration” being the keyword with the largest citation bursts and most abundant research achievements. Furthermore, in addition to Chesapeake Bay and the Gulf of Mexico, Mosquito Lagoon has emerged as a hot research area since 2018. A total of 27 articles were retrieved using “oyster reef*” and “Mosquito Lagoon” as search terms. For example, Locher et al. [
75] studied the immediate (first-year) effects of restoration on sediment nutrients through a
Crassostrea virginica restoration program conducted in Mosquito Lagoon, and Troast et al. [
76] explored how fish communities responded in the first 12–24 mo following oyster reef restoration in Mosquito Lagoon. The focus species have been the eastern oyster (
Crassostrea virginica) and Pacific oyster (
Crassostrea gigas). In addition to the USA, in recent years, other countries have gradually conducted more research on oyster reefs, including Australia (mainly involving the Sydney rock oyster,
Saccostrea glomerata), China (mainly in Bohai Bay), and some European countries (e.g., England, Germany, Netherlands, France, and Scotland; mainly involving the Wadden Sea). Along with restoration efforts, the attention paid to the ecosystem services provided by oyster reefs has increased since 2014, indeed “ecosystem service” became the keyword with second strongest burst intensity. Since 2016, under the influence of human activities and global climate change, oyster reef research has tended to diversify. In addition to research on oyster reef restoration and ecosystem services, the impact of global climate change on oyster reefs has become an important research hot topic [
22,
23,
24], as has the role of oyster reefs in responding to global climate change [
25,
26]. Finally, “substrate” became a hot topic from 2018 to 2022. These keyword bursts illustrate how oyster reef conservation research has shifted through the years.
Looking at evolution of trends over time, it can be seen that oyster reef research has developed from single factor explorations to ecological function restoration, and from the restoration of habitats degraded by human activities to focusing on habitat restoration and development under the joint influences of climate change and human activities. As research has continually provided new insight into the ecological and economic importance of oyster reefs, recent research has increasingly focused on oyster reef conservation, restoration, and ecosystem services.
However, the research evaluating the effectiveness of oyster reef ecological restoration as a Nature-based Solution (NbS), including assessing oyster reef ecosystem services, the impacts of climate change on oyster reefs, the role of oyster reefs in responding to climate change, the effectiveness of oyster reefs as a coastal defense, and effective restoration plans, has not sufficiently matured. Additional and longer-term studies are needed on these topics in the future. For example, oyster reef ecosystem restoration, as a form of NbS, is seen as an increasingly important intervention strategy to counteract the degradation of coastal ecosystems and assist in climate change adaptation. Hynes et al. [
77] pointed out that even if oyster reef restoration plans only consider the recreational use value and coastal protection services, without considering the value of many other additional ecosystem services, the benefit-cost ratios of oyster reef protection options always exceed one. But such approaches often face a variety of obstacles that can impede their development, such as the lack of knowledge at the local planner level [
78]. However, Narayan et al. [
21] also noted the lack of available evidence of wave attenuation by oyster reefs in their literature review focusing on the effectiveness of nature-based coastal defenses. Therefore, additional studies measuring the effectiveness of oyster reefs as a coastal defense are needed to provide a foundation on which to base project goals and set reasonable expectations.
While oyster reef restoration has had considerable success, many challenges remain. For example, restoration costs per unit area are high, the incidence of restoration failure is high, and the pressure imposed by climate change is increasing. Therefore, effective measures must be found to improve restoration efficiency and the resilience of reef ecosystems. Reeves et al. [
28] suggested that identifying positive species interactions and systematically incorporating them into restoration practices could improve restoration success and enhance ecosystem services of restored oyster reefs. To do this, further research would be needed to understand the potential impacts of positive interactions and their applicability. Furthermore, Seavey et al. [
79] pointed out that understanding the resilience of oyster reef communities to disturbances is key to developing effective conservation and restoration plans. Jiang et al. [
17] showed that August was the most favorable window for capturing oyster spat via substratum additions to waters around natural reefs. Hernández et al. [
18] pointed out that site characteristics, including access to adequate larval supply and elevation, greatly influence restoration success. Consequently, establishing longer-term, larger-scale, and standardized water-quality and oyster recruitment monitoring datasets to identify sites where restoration activities are likely to stimulate the recovery of self-sustaining, productive oyster reefs is an essential first step when designing projects that will yield positive return-on-investments. Moreover, in order to effectively enhance oyster reef protection and restoration, we must strengthen the academic knowledge in this field and transform practical experience into systematic and scientific guidelines. Furthermore, as pointed out by Draper et al. [
80], global temperatures will continue to rise and warming will likely have a stronger impact on community dynamics in oyster reefs. Therefore, oyster reef restoration efforts should focus on accounting for climate change factors to maximize sustainability and success [
81].
5. Conclusions
To sum up, the bibliometric analysis based on CiteSpace revealed the development trend, current hotspots and research frontiers of oyster reef research. Over the past 40 years, there has been a noticeable increase in publications on oyster reefs, indicating a growing interest in this subject. As an important coastal ecosystem, the oyster reef has many ecological functions such as providing habitats, purifying water, facilitating de-nitrification, and protecting coastlines. But they are also among the most degraded marine ecosystems and worth protection. Through the analysis of the cooperation network among countries, institutions and authors involved in oyster reef research, it can guide the direction of scientific research cooperation and help us select institutions, experts or journals accordingly. The study on the keywords co-occurrence analysis, the keywords timeline analysis and the identification of burst keywords can provide new insights for the hotspots and trends in this field.
At present, the research of oyster reef shows a trend of diversification. Habitat conservation and restoration, oyster reef ecosystem services, impacts of climate change, biodiversity and selection of substrate are the latest frontiers of research in this field. However, at present, studies on issues such as carbon sequestration in oyster reef ecosystems, ecosystem services assessment and valuation, effectiveness assessments of oyster reef ecological restoration as an NbS, measurement of the effectiveness of oyster reefs as coastal defenses, impacts of global climate change on oyster reef habitat and the roles of oyster reefs in coping with climate change have not been in depth, which is worth further attention. In the future, systematic investigation and research on natural oyster reefs can be carried out. Taking oyster reef ecosystem restoration as an NbS will help realize win–win situations, where ecological protection and economic development both benefit from these natural habitats.