1. A Global Perspective on Cage Aquaculture and Biodiversity
Over the past 40 years, aquaculture made significant contributions to global seafood production [
1]. In 2020, global fisheries and aquaculture production amounted to 178 million tonnes, with aquaculture representing 49% (88 million tonnes) of the entire volumes [
2]. There are different aquaculture holding units, namely cages, concrete or mobile tanks, ponds, flow through, and recirculatory aquaculture systems [
3,
4,
5]. Ponds are the oldest and most dominant among the holding systems [
6]. In the past 20 years however, cages have dominated and attracting worldwide attention for intensified production in natural and artificial water bodies [
7,
8,
9].
The exponential growth of cage aquaculture poses severe threats to vital aquatic ecosystem services and can strongly interfere with freshwater and marine biodiversity [
10,
11,
12,
13,
14]. Escaped fish from cages are almost inevitable due to accidents, flooding, and equipment failures. Escapees can cause genetic alterations in receiving wild stocks, which is one of the most significant impacts of cage aquaculture on biodiversity [
13,
15,
16,
17]. Precisely because farmed fish are selectively bred for faster growth, including modification of broodstock to produce infertile fry, escapees can have deleterious effects on wild fish stocks [
18,
19,
20]. Apart from lionfish, which are less commonly farmed [
21], tilapines are frequently cited as examples of the negative impacts of aquaculture-mediated invasive species, having successfully displaced numerous native species [
13,
22,
23,
24]. The movements of escapees and their increased chances of interacting with wild fish, increase the risks of transmitting diseases and parasites to wild fish populations [
25,
26]. The issues associated with escapees have contributed to the rapid development of antimicrobial resistance due to excessive antimicrobial use [
27,
28]. Biological interventions such as the use of cleaner fish to reduce parasites infestation are also implicated in the transmission of diseases to wild fish populations [
29,
30,
31].
One important but often overlooked issue affecting marine and freshwater biodiversity in West Africa is the depletion of capture fishery resources used for aquafeed production. Fishmeal and fish oil, which are limited resources are derived from small pelagic such as anchovies, sardines, Atlantic herring, and menhaden [
32,
33,
34]. Although marine fish farming is a big business, global production of fishmeal and fish oil have remained relatively stable at about 5 million tonnes and 1 million tonnes, respectively [
35]. In 2020, 86% of fishmeal and 73% of fish oil from global marine production were used in aquaculture [
36]. Unlike freshwater aquaculture, the demand for fishmeal and fish oil is highest in mariculture [
37,
38,
39], which is predominantly practiced in advanced countries. This high demand contributes to the overexploitation of capture fisheries in relatively poorer countries [
40]. Irrespective of the aquaculture type, these statistics highlight the exploitative pressure on the source ingredients harvested, including their derailed purpose as seafood intended for human consumption. The overexploitation of fisheries resources force affected countries to resort to aquaculture to meet fish nutritional needs. Capture fisheries and aquaculture remain volatile as their overexploitation continue to pose potential biodiversity threats.
The dispersion of faecal matter, dissolved nutrients and feed waste from floating cages are major sources of pollution in receiving waters and a clear example of the harmful impacts of aquaculture on biodiversity [
41,
42,
43]. Unlike emerging closed cages, poorly sited and mismanaged open cages are associated with dire consequences, such as changes in microbial diversity, abundance, and community structure [
44,
45,
46]. Benthic environmental footprint is a common concern in invertebrate communities due to the biofouling caused by different aquaculture wastes on the sediment, which reduces species richness [
47,
48,
49]. Additional evidence supports the negative effects of aquaculture, namely, reduced diversity and lower species richness in zooplankton communities at cage sites [
50].
Despite the negative effects of aquaculture on biodiversity, fish farming can also have positive impacts. These include reduced fishing pressure on already overexploited stocks, support for conservation efforts through the stocking of farmed fish, and increases in species diversity, abundance, and richness [
13,
51,
52,
53,
54,
55,
56].
2. Negative Impacts of Lake Volta Cage Aquaculture in Ghana
Cage aquaculture commenced in Ghana in the mid-2000s with the establishment of the first commercial cage on Lake Volta [
57,
58]. Earlier on, fish farming began in 1953, with the conversion of irrigation reservoirs in the Northern region of the country [
59]. Currently, most fish farmers prefer Lake Volta (
Figure 1) for various reasons, including good water quality and flow rate, as well as optimal water depths [
60,
61]. Lake Volta contributes approximately 90% of the annual farmed production of Nile tilapia (
Oreochromis niloticus) and African catfish (
Clarias gariepinus). In 2021, Ghana earned approximately 140 million U.S. dollars from a total aquaculture production of 89,400 metric tonnes (
Figure 2) [
62]. Of this production, tilapia accounted for 68,740 metric tonnes, while catfish constituted 20,660 metric tonnes [
63,
64].
The socio-economic benefits derived from Lake Volta have made it the aquaculture hub in Ghana. Currently, Lake Volta is one of the few water resources that is not visibly polluted. However, future projections suggest that Lake Volta may lose its relevance and importance due to increasing pollution of other water bodies in Ghana through illegal mining [
65]. Similar forecasts suggest that expanding cage culture beyond Lake Volta’s carrying capacity could lead to chemical and nutrient pollution, the introduction of non-native species and pathogens, as well as sediment and organic matter loading [
66,
67,
68,
69,
70]. Some of these forecasts have already been substantiated [
67,
68]. Therefore, the objective of this paper is to provide alternative perspectives on rethinking cage aquaculture in Lake Volta to better protect its ecosystem services and biodiversity. This is particularly important and could inform trans-regional management decisions, as Lake Volta connects to the Volta Basin, which borders Benin, Burkina Faso, Côte d’Ivoire, Mali, and Togo.
Numerous studies have assessed the potential impacts of cage aquaculture on the physico-chemical parameters of Lake Volta. Majority of these studies concluded that there were no significant variations in water quality parameters, such as ammonia, pH, nutrient level, dissolved oxygen and the total suspended solids between cage sites and reference sites within the Lake. Additionally, comparisons of data collected over the past three decades with recent facts support these findings [
57,
71]. Nevertheless, concerns have been raised about fish culture-related impacts, such as effluents affecting Lake water quality when evaluating the social acceptance of cage aquaculture in Lake Volta [
72].
Ongoing disease outbreaks and unusual mortalities in the Lake since 2018 have created increasingly stressful conditions for the farmed fish population. A recent study conducted by Zornu et al. [
66] to understand tilapia mortalities in Lake Volta identified a combination of pathogens and non-infectious factors as contributors to these unusual mortalities. Farmed fish mortalities have been linked to water pollution from human-mediated pollutants, aquaculture wastes, and other non-infectious factors. Despite these challenges, the Fisheries Commission (FC) has projected an 8% annual growth in aquaculture production over the next three years [
63]. Meeting this projected increase in annual fish production could trigger intensified production and the establishment of new cage farms on the Lake. Hosting additional cages on the Lake could lead to an increased influx of feed, assuming each farm on the Lake operates with an average Feed Conversion Ratio of 1.5 and at an annual growth rate of 8% [
63]. Other consequences include the introduction of large amounts of aquaculture waste into the water and further deterioration of Lake water quality.
Aiming for higher fish production increases the risk of aquatic diseases with medium to large-scale effects. Consequently, Lake Volta will become the primary ecosystem affected by these diseases and a sink for chemical remnants introduced to combat diseases (
Figure 3). Addressing fish diseases in Lake Volta has led to increased antimicrobial use and subsequent resistance [
73,
74]. Land-based aquaculture operations have its peculiar environmental issues, including but not limited to chemical pollution. Nonetheless, cage culture systems can aggravate negative environmental impacts on native species and lead to overall deterioration of the Lake. Native species in the Lake may contract diseases that could have originated from importation of unapproved fish species (
Figure 3). Lake Volta also serves as a source of drinking water, which is treated by Ghana Water Company Limited (GWCL). The GWCL will therefore incur higher costs for treating the Lake water to make it potable. Water treatment costs in Ghana are generally rising due to mining, industrial, agricultural, housing, and commercial activities [
65]. This implies that increases in water contaminants in Lake Volta will have significant economic implications for water treatment costs.
Finally, with most farms located downstream of the Lake (below the Akosombo dam), any planned or unplanned spillage from the dam could have devastating effects on floating cages and riparian communities. The 2023 water spillage from the Akosombo dam brought various destructions to fish farms and affected over 100 fishing communities. To safeguard the socio-economic wellbeing of fish farmers and riparian communities, it is prudent to seek alternative production systems. Cage fish farmers incurred losses of 46 million Ghana Cedis due to the dam spillage. This incident also raised ecological concerns, as unapproved foreign fish species from the cages escaped into the Lake. Non-indigenous fish species can outcompete local species, disrupt the Lake’s ecosystem balance, and alter ecological relationships [
75]. The loss of genetic integrity in indigenous fish species is a potential consequence of the invasion of foreign species through aquaculture (
Figure 3). Anane-Taabeah et al. [
68] reported such a loss in Lake Volta, highlighting significant threats to native fish species that could ultimately impact fish food security. These arguments corroborate findings suggesting that non-native species have demonstrated superior competitive abilities, outcompeted indigenous species, and potentially led to the extinction of local strains [
76,
77]. Escapees can also affect local ecosystems in several adverse ways, posing threats such as hybridization, disease transmission, disruption of ecosystem health, predation on native stocks, competition, and alterations to habitat structure [
78,
79].
The consequences of escaped fish on the environment are multifaceted and have long-term implications for ecosystem stability. Therefore, mitigating the risks associated with introducing non-native species into the wild is crucial for safeguarding the integrity of natural ecosystems. Given these challenges, it is essential to consider environmentally sustainable alternatives rather than focusing solely on cage aquaculture. Countries within and outside Africa are feverishly pursuing diverse aquaculture systems to boost production and maximize socio-economic benefits. Advances in aquaculture engineering and research have made it possible to farm fish using alternative culture methods aside farming on natural water bodies. Some of these systems include raceways, aquaponics, ponds, and tanks constructed from various materials such as concrete, tarpaulin, and fiberglass. Shifting to these alternative systems can reduce the environmental footprint of aquaculture compared to the predominant open-water fish farming. The United States, Norway and Canada are among the few countries that have strict measures to regulate open cage fish farming [
80,
81]. Canada in particular is committed to considering only marine or land-based closed-containment systems for aquaculture licenses in coastal British Colombia [
80]. It is vital to adopt such best practices to encourage the exploration of alternative culture systems suited to the Ghanaian terrain. Otherwise, any disaster related to cage aquaculture could be disastrous for Ghana’s fish food security.
4. Government’s Role in Transitioning from Open-Water to Land-Based Aquaculture
Good aquaculture governance creates an enabling environment for effective productivity and long-term industry growth [
99]. Limited technical know-how among Ghanaian fish farmers is often reported as inadequate knowledge of fish husbandry practices [
61,
100,
101]. It is insufficient for farmers to have requisite aquaculture knowledge without awareness of environmental sustainability. The government must identity and provide the necessary human competence and infrastructure for the industry [
99]. This can be a collaboration with the Aquaculture Sectorial Chamber [
85] or National Aquaculture Committee in identifying the needed human competence and infrastructure for a sustainable industry. The government can support infrastructure such as laboratories while resourcing education and research institutions to enhance industry competence and diagnostic services. In addition, the government should use media as an educational tool to amplify knowledge among aquaculture stakeholders. This knowledge should encompass technical feasibility in fish reproductive biology, culture systems, husbandry and management, legislation and enforcement. Gaining understanding of aquaculture environmental and social interactions is imperative for spatial planning and creating inland aquaculture zones [
102]. Nonetheless, it is incumbent on government to allocate human resources such as aquaculture and veterinary officers, and develop essential infrastructure like electricity and road networks to enhance transport and access to inputs and outputs within and beyond zoned areas.
Fish farm registration in Ghana is burdened by complex bureaucratic protocols across multiple institutions, resulting in weak enforcement. The current FfD Ghana project in collaboration with the Fisheries Commission is addressing this concern through a proposed one-stop-shop regime. The government must then monitor and regulate registered farms to ensure compliance with the Aquaculture Code of Conduct and to ensure operations within environmental and ethical boundaries. The Canadian government is committed to considering only marine or land-based closed-containment systems for aquaculture licenses in Coastal British Colombia [
80]. Adopting such closed-containment systems in Ghana can be challenging. Therefore, government through the competent Ministries can introduce PTS and PPP policies in both land and water-based aquaculture. However, due to higher environmental footprints of water-based aquaculture and large-scale operations [
103,
104], penalties for environmental pollution will be significant. This can include penalties for non-compliance measured in penalty units as adopted in Ghana’s marine captures fisheries [
94]. Adhering to regulatory standards fulfils BMPs or Aquaculture Code of Conduct, as farmers are responsible for implementing specific measures to minimize negative environmental impacts. By fully enforcing all industry regulations, the government can prevent fish farmers from prioritizing short-term gains over environmental and societal well-being.
In addition to the interagency collaborations evolving through the one-stop-shop permitting system, government’s involvement in partnership between farmers, academic, and research institutions cannot be overemphasized [
84]. Government should intentionally fund academic and research institutions in this cross-sectoral partnership to generate critical knowledge for contingency planning and sustainable aquaculture development. The sector Ministry can solicit innovative proposals through competitive bidding, focussing on scientific and technological advancements that drive aquaculture growth. Research should be based on industry needs and provide innovative production systems and resilient seeds. It should also identify suitability of inland areas based on environmental data, water availability and quality to develop inland-specific criteria for aquaculture zoning and planning. Government must prioritize resourcing aquaculture development and ensure fiscal constraints do not hinder human competence and infrastructural growth in the industry.
Author Contributions
P.K.B and K.F.A.: Investigation, Formal analyses, Writing—original draft, review and editing. J.Z.: Investigation, Formal analyses, Visualization, Writing—original draft, review and editing. M.A., D.N.B., K.I., and A.A.: Investigation, Formal analyses, Writing—review and editing. S.E.A.: Supervision, Investigation, Visualization, Validation, Writing—review and editing. S.A.: Supervision, Investigation, Validation, Writing—review and editing. K.S.C.: Conceptualization, Funding acquisition, Project administration, Validation, Writing—review and editing. All authors have read and agreed to the published version of the manuscript.