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Corals and their associated ecosystems are of great ecological and economic importance to Caribbean island nations and must be protected. Despite the Aichi target 111 that stipulated that by 2020 each country should have 10% of its maritime area devoted to protected areas, Marine protected areas (MPAs), both within the Caribbean and elsewhere, are all affected by the lack of funding to carry out conservation activities and enhancement of the existing ecological heritage. MPA funding takes on essentially four forms: (1) funding of state public funds or from local authorities, (2) self-financing, based on revenues generated by the sale of fees for entrance, activities and various services, (3) public-private partnership, achieved particularly with environmental foundations of large industrial groups and (4) research and development projects, which provide support to MPAs in a timely manner, and even more frequently when incurred by activities of research or ecological monitoring. The future Regional Nature Reserve (RNR) of "le Prêcheur", located in the North-West of Martinique (see map below) must, as of today, include the financing of daily operations and investments on the agenda of priority actions. In addition to the financial support granted from the region, additional income modes should be considered.
1 See: https://www.cbd.int/sp/targets/rationale/target-11/.
The main objective of this article is to highlight the various possible additional funding sources for the sustainable functioning of the MPA of le Prêcheur. Several feasibility assessments of the implementation of funding of MPA mechanisms exist but each of them focus on a specific type of financing and its related feasibility, usually based on the willingness to pay (Reid-Grant and Bhat, 2009; Chen et al., 2014; Thur, 2010), while the contribution of this article is to present all possible options for complementary funding of MPAs and evaluate their feasibility in the context of Martinique. The options of taxes, royalties and entry fees that can be used to partially finance the future RNR of le Prêcheur are developed according to criteria of general framework for tax implementation and regimes. Of these options, only those that appear achievable are retained and their feasibility is analysed in more detail. This further analysis of the feasibility allows us to rank the options and thus evaluate which one to keep. The article also introduces the concept of "payment for ecosystem services" (PES) which, in the context of the RNR of le Prêcheur, could be used to compensate fishermen for their efforts towards the improvement of environmental services of the MPA of le Prêcheur (Failler, 2016). PES are not used directly to finance the operation of the reserve, but to compensate fishermen for their efforts towards the improvement of ecosystem services of MPAs, which compensates for the reduction of fishing activity while involving fishermen in the process of habitat conservation and sustainable use of fisheries resources.
The paper is structured in 3 parts. It starts by presenting an inventory of the volume and sources of public funding for natural areas in the French metropolitan area and in the French overseas territories. It then provides an analysis of main potential sources of income through the assessment of current options. It follows with a presentation of other funding options for which investigative work is required. Finally, the concept of payment for environmental services, and it applicability in the functioning of the RNR of le Prêcheur, is analysed. A conclusion gives the summary of key findings and some research and policy orientations.
The current system of public budget allocated to the protection of French natural areas in the mainland and French overseas aims to improve the quality of sites, landscapes, natural environments, as well safeguarding natural habitats. It also aims, when health status and vulnerability of natural areas allows it, to be used for spatial planning towards the opening to the people.
According to the French Environmental Code, which applies in Martinique, protection and financing of protected natural areas is a shared jurisdiction between state and local authorities. The French protected natural areas are therefore currently funded almost exclusively by the public sector. Private funding through foundations and corporate sponsorship, is more uncommon, while self-financing from private operating revenue remains marginal.
State public financing assigned to protect the French marine and coastal environments are estimated at €74 million (see Table 1). These, however, are largely underestimated: State grants are supplemented by the budgets earmarked to policies in favour of environment conservation by local authorities (at nearly four times the state budget).
Level | Budget (million €) | Notes |
State | 28.1 | Allocated budget, program 113 action 7* |
French Marine Protected Areas Agency |
1 | - |
French Coastal Protection Agency | 40 | €2.4 million of which come from repayments of the state and €37.6 million come from an individual taxation regime |
Other operators | 5 | - |
Total State + operators | 74.1 | In comparison, the total state budget allocated to the conservation of natural areas and water management amounts to €2447 million |
Source: Translated from Badré M and Duranthon JP, 2010. *Current financial resources allocated by the state to the budget for biodiversity policies are partly addressed by action 7 "management of environments and biodiversity" program 113 of the Ministry of Ecology, Energy, Sustainable Development and the Sea. |
The state gets almost all of its income from compulsory levies (taxes, royalties, etc.). Those of regional authorities come from the state repayments or are induced by the individual tax system (e.g., the development tax, for which part of it is allocated to natural areas). The Environmental Code acknowledging the "polluter-payer" principle, taxation of the environment uses taxes and royalties to prevent or punish damaging behaviour to natural areas. Tax revenues are intended to pay for public services provided by the state or "collectivities" (local authorities). The revenues of royalties are used to pay for the services provided by private supplier or by common pool resources (here marine ecosystems) for a service provided to users. However, as some royalties work as eco-taxes, the distinction between both payments does not always fit to this definition (see Box 1).
The French law identifies three principles of taxation of natural areas, which meet three distinct objectives:
a. To compensate exploitation of natural resources
b. To compensate disturbances and damages to ecosystems
c. To compensate use of the marine area
To get a better outlook of their relative relevance, the overview of taxes and royalties related to the use and exploitation of natural resources is structured below based on the amount of income they generate.
The tax is levied from the provision of a service. It may be required not only from actual users but also from potential users and the amount is not strictly equivalent to the service provided (e.g. tax for household waste collection). The tax is provided by the law. Royalties (or remuneration) for services rendered are received in return for a service, such as the use of a piece of work or a benefit provided by a public service to a user while bearing the cost, and therefore must match the value of the benefit or service. A royalty can be established through regulation. The amount of the royalty must be equivalent to the value of the benefit or proportional to the cost of the service rendered. Such is the case of the "institution of a royalty comprising of a fixed part and a variable part, provided that the calculation of the fee allows to ensure the proportionality with the cost of the service rendered" (EC No. 220803 of July 9 2009). 'Respect for the rule of equivalence between the fare of a royalty and the value of the benefit or service can be ensured by withholding the cost of the latter, but also according to the characteristics of the service, by taking into account the economic value of the benefit to the recipient; that in all cases, the fare must be established according to objective and rational criteria, in full conformity with the principle of equality between the users of public services and the competition rules (EC No 309 499 of 7 October 2009). Environmental royalties can be defined as payment for environmental services: in return for their payment, the taxpayer receives an environmental service. As pollution could be interpreted as a particular use of a natural resource (right to pollute), a levy associated with a degradation of the environment can then be likened to a royalty. The distinction between taxes and royalties is also based on the allocation of revenues. Into the general budget for the first case, revenues are earmarked for specific purposes in the case of royalties. Yet, in the field of environmental taxation, these two aspects of distinction between taxes and royalties are not systematically combined. This explains why these two terms are sometimes interchangeably used. |
The majority of tax revenues related to natural areas are dependent on water management policies: more than nine tenths of the budget and total tax resources for natural areas originate from royalties and charges levied by the National Office for Water and Aquatic Environments (ONEMA) and water agencies and offices, representing €1.9 billion according to Badré and Duranthon (2010). In comparison, the marine environment, and to a lesser extent, terrestrial biodiversity, appear as the poor relation.
The Water Office of Martinique, as well as other water agencies, collects a number of royalties for the use or consumption of water resources, which are devoted to actions to promote a better use of water in the territory2.
2 See Article L213-10 of the Environment Code.
The state also draws royalties from the occupation or use of public ground. In the maritime area, this includes for example fishing and hunting rights, the product of exploitation of marine cultures, products of extractions, rights of way for operators of telecommunication networks. The income amounted to almost €300 million in 2010.
At the scale of local authorities, tax measures to raise funds in favour of protected natural areas mainly belong to the departments, through the development tax. Formerly Departmental Tax on Sensitive Natural Areas (TDENS), it is primarily intended to generate resources to finance actions in favour of biodiversity. Governed by the Urban Planning Code, it subdues the construction, reconstruction, expansion of buildings and other facilities projects subject to licence or declaration. Optional, it has nevertheless enabled significant financial reserve estimated at €269 million in 2010 (République Française, 2011). This net balance is due to under-utilization and a recurring postponement of a year on year revenue from this tax. Its rate varies according to the department, but it cannot exceed 2% of the value of the housing complexes. In 2009, of the 95 metropolitan departments and 4 overseas departments, nine departments had not implemented the TDENS, 20 had introduced a rate of 2%, 16 a rate between 1 and 2%, 34 a 1% rate, and 21 a rate lower than 1%. Among the charted expenditures, the TDNES is used mainly for the development and maintenance of sensitive natural areas—the rest is devoted to the acquisition of these areas or is donated to another collectivity.
Some taxes are not directly associated to natural areas but their employment is linked through tourism depending on them. For municipalities and groups of collectivities with their individual tax, the visitor's tax3 is usually applied to expenses dedicated to promoting tourist visitation of the territory. However, some municipalities have instituted this tax for actions of protection and management of their natural areas, the revenue from the tax can be allocated4, to expenses to promote the protection and management of their natural areas for tourism purposes. The law provides that when these municipalities are situated in whole or in part on the territory of a national park or a regional park administered by a public administrative establishment, the product of the visitor's tax can be donated by the municipality or public establishment of inter-municipal cooperation to the park management organization as part of a convention. The visitor's tax has yielded €158 million for municipalities and €45 million for groups of collectivities of individual tax in 2010.
3 See Article L2333 - 26-46 of the General Code of territorial collectivities.
4 Subject to the provisions of Article L. 2231-14.
Other taxes on exploitation or use of natural areas exist, although they are less substantial. They are assigned to other legal entities then the state. In the area of environmental protection, those who have yielded the highest average tax revenue in 2010 (French Republic, 2011) are:
a. The general tax on polluting activities TAGP5 for €489 million, part of which benefits the ADEME;
5 Article 266 of the Customs Code.
b. The levy on the product of premiums or additional contributions relating to the guarantee against natural disasters risk (€158 million) intended for the Prevention of major natural disasters fund (FPRNM);
c. The hunting royalties that benefit primarily the National Agency for Hunting and Wildlife (€70 million);
d. The right to francization and navigation that benefits the Coastal and Lake Shore Conservation Authority in particular (€39 million);
Finally, some taxes reflect the compensation for inconvenience generated by the transport of passengers but generate far less income. For example, the tax on passengers departing to natural protected areas6 generated less than €1 million in revenue in 2010, revenue that shared the Conservatoire du Littoral, the marine park of Port-Cros, the National Forestry Office, affected collectivities, etc. For overseas territorial collectivities specifically, the tax due by air and maritime public transport companies on passengers (Article 285 ter of the Customs Code) is dedicated to classified or listed natural areas, national parks, natural reserves, CELRL sites or ports exclusively or mainly one of the protected areas mentioned above without being included. In 2010, Martinique, Guadeloupe, Guyana and Reunion have drawn together €8 million.
6 Article 285 quater of the Customs Code.
RNRs are under the competence of the Region. From the ranking to the implementation of the management plan and organization of events, the Region therefore supports technically and financially the owner or organization managing the protected natural area (or in process of being ranked). According to the provisions prescribed by the regulations for intervention, it can subsidise a part of the operating and investment expenditures (actions of restoration, preservation and enhancement)—never all of the expenditures.
The region exclusively uses its budget, supplemented by the state, to finance the management of RNRs (unlike for example Departments that have the ability to use the revenues from the development tax). The use of taxation to complement the funding of the RNR of le Prêcheur includes the study of obstacles and opportunities for the establishment of such a design, as well as the definition of the base, geography or rate.
Options for the implementation of one (or more) tax(es) to partially finance the RNR of le Prêcheur fit into three distinct approaches:
a. The introduction of a new tax/royalty;
b. The assignment of an existing tax in whole or in part to the financing of the reserve;
c. Broadening the rate of an existing tax to include the financing of the reserve. These three approaches set the general framework of the tax implementation. For each approach, it is possible to consider various regimes of taxes and royalties, in terms of:
d. The subjected population: involved populations may include residential tourists, users of marine ecosystems, companies that pollute or have a negative impact on marine ecosystems;
e. The geographical scale: the intervention scale of the tax may be local and limited to the municipality of le Prêcheur (and potentially the neighbouring municipalities of Saint-Pierre and Trois-Rivières; see map 1 above) or regional and extended to the whole of Martinique. In the first case, taxes only apply to users of the marine environment and/or of the watershed of the municipality of le Prêcheur. It enables an effective reduction of marine and land pressures on the marine ecosystems of le Prêcheur. The second case extends the taxation regime to the users of the whole regional area. It calls for empowerment and awareness of environmental issues by all users on the island.
Using these criteria, 24 taxes, royalties and entry fees have been devised (Table 2). A part of these taxes seems a priori seldom enforceable in the case of the RNR of le Prêcheur (boxes highlighted in blue in Table 2). The decision to exclude these taxes a priori derives from the combination assessment of: social acceptability of the tax, legislative difficulties in the implementation of this tax, injustice or equity problems created by the tax, etc. For example, a new tax on polluting activities in Martinique that have impacts on marine ecosystems only to finance the reserve of le Prêcheur would result in a significant opposition from businesses located far from the northwest of Martinique and having no apparent negative impact on the area.
Introduction of a new tax or royalty | Assignment of an existing tax | Broadening of the rate of an existing tax | ||
Regional scale | Residential tourists | Tax to finance regional reserves of Martinique (on the template of the tourist tax) | Share of the tourist tax of the municipalities of Martinique | Broadening of the airport tax; broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance regional reserves of Martinique (on the template of the housing tax) | Share of dock dues | Broadening of the airport tax; broadening of the transportation tax | |
Marine ecosystem users | Tax on uses of the ecosystems of Martinique (in addition to fishing licences for e.g.), tax on offshore recreational practices (surf, kitesurf, etc.) | Share of revenue of fishing licences | Broadening of fishing licences | |
Corporations that pollute | Taxes on polluting activities in Martinique that have impacts on marine ecosystems (urbanisation coastal fringe, granulate extraction, non-biological agricultural activities, etc.) | Share of the tax on marine polluting activities | Broadening of the tax on polluting activities | |
Local scale (area of the reserve and surrounding area) | Residential tourists | Tax to finance the RNR of le Prêcheur enforceable to tourist operators of the municipality (on the template of the tourist tax) | Share of the tourist tax of the municipality of le Prêcheur | Broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance the RNR of le Prêcheur enforceable to the inhabitants of the municipality (on the template of the housing tax) | Share of the housing tax of the municipality of le Prêcheur | Broadening of the transportation tax | |
Marine ecosystems users | Local tax on extracting and/or damaging of the RNR activities (fishing, spearfishing); royalty on diving activities; royalty on taxi-boats, recreational boats and private sailing boats | n.a. | n.a. | |
Corporations that pollute | Tax on polluting activities of the watershed | n.a. | n.a. | |
Note: n.a. = not applicable; Source: authors own creation. |
Ten other taxes seem more feasible and are worthy of a further analysis on their feasibility (boxes highlighted in green in Table 2 above). The strengths and weaknesses of the implementation of these taxes are presented in table 3 below.
Strengths | Weaknesses | |
Introduction of a new tax/royalty | ||
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | Tourism figures increasing, potential source of growing incomes Potential modulation of the rate based on the environmental impact of the operator |
Penalises supply of tourism services of the municipality of le Prêcheur only, already seldom developed Potentially penalises visitors that are non-users of marine ecosystems (e.g. Hikers) |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality | Empowers inhabitants on the impact of their everyday practices on the ecosystem Potential modulation of the rate based on the environmental impact of the building | Penalises the inhabitants of the municipality of le Prêcheur only, potentially making the area less attractive Potentially penalises the inhabitants that are non-users of marine ecosystems (e.g. Hikers) |
Local tax on extractive and/or damaging of the RNR activities (fishing, spearfishing) | Reduces through a fiscal leverage the extractive activities and other damaging practices while producing revenues for the reserve Enables guidance by incentives for reorientation of fishermen or discontinuing of damaging practices (frequent use of beach-seine for example) |
Low acceptability upon populations of fishermen and underwater hunters already affected by management actions Difficult to weigh the burden of a tax only on fishermen and underwater hunters Revenues of this tax are destined to decrease, thus jeopardizing the financing Penalises operators who take measures voluntarily (eco-responsible construction, choice of a fishing net with larger mesh, etc.) |
Tax on polluting activities of the watershed | Polluter-payer principle: polluting activities must be subjected to financial compensation; to go further, it is possible to implement a payment for ecosystem services: polluting activities fund the reserve for improvement of the treatment of waste produce by these activities; enables to give a tax preference to non-polluting local activities (idea of a partial exemption from tax for the reduction of pollutants) |
Seldom educational, as it can be interpreted as a "right to pollute"
Concerning the development of the tourism sector, operators are already subject to obligation to avoid, reduce and compensate damages to the environment |
Royalty on diving activities | Positive image from alerted and sensitized persons, usually willing to pay extra if their participation in the reserve is transparent Widely favourable view of diving operators in the area, willing to raise the average price per dive |
Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Royalty on taxi-boats, recreational and private sailing boats | Taxation affects primary beneficiaries of the reserve (through tourism increase), the acceptability of such a tax should be good Can be done through various taxes and lead to development (tax for the access to mooring buoys in the reserve) | Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Assignment of an existing tax | ||
Share of the tourist tax of the municipality of le Prêcheur | Tourism in the area is closely related to visitation of natural resources, particularly marine resources Figures of tourism increasing, potential source of growing incomes Highlight the willingness of local authorities to participate in the implementing of the reserve Opportunity for neighbouring municipalities (Saint-Pierre, Grand Rivière, Cabaret, etc.) to devote part of their tourist tax to the reserve |
Little profitable as long as visitation and supply of accommodation are limited in capacity Difficult to arbitrate for the reallocation of a share of the tax to the reserve Participation of neighbouring municipalities to the reserve presumably difficult |
Share of dock dues | Taxation of all products sold in French overseas – modulation of the rate based on environmental impact of products | Difficult to justify the financing when dock dues ought to help in economic development Advocacy work needed for an arbitration in favour of the reserve and at the expense of the financing item which loses the income of the tax |
Share of the tax on marine polluting activities | Polluter-payer principle extended to the region: polluting activities must be subject to financial compensation Gives a fiscal preference to non-polluting regional activities (idea of a partial tax exemption for reduction of pollutants) | Lack of acceptability of activities not directly linked with le Prêcheur (e.g. Intensive agriculture of southern Martinique) |
Broadening of the rate of an existing tax | ||
Broadening of the airport tax | Can generate very high revenues at a low cost per person Attachment to marine ecosystems of airport passengers, tourists or inhabitants | Airport taxes usually intended to upgrade safety and comfort of passengers; can pose problems of arbitration of tax revenues thus needs an expansion and not a modification of assignment |
Broadening of the transportation tax | The possibility of a justification of an environmental approach of transport helps social acceptance of the broadening of the tax | Political and legislative difficulties of broadening the rate of an existing tax |
Source: authors own creation. |
To compare them, the ten selected options are quantitatively analysed through these six criteria:
a. Ease of implementation: this criterion depends on the conditions of establishment of the tax, from the easiest (broadening the tax base or the rate of an existing tax for the management of future MPA of le Prêcheur) to the most constraining (introducing a new tax, the proceeds of which will be donated to the managing organization for the management of future MPA of le Prêcheur);
b. Acceptability: this criterion reflects the reaction of users and non-users to the implementation of the tax. It is strongly related to the legibility of the tax objective. It also calls for a higher level in communication and information which should accompany the implementation of the tax (the lower the acceptability, the more communication activities must be well crafted, targeted);
c. Income generation: this criterion expresses the potential of the tax to generate revenues for the RNR; depending on the choice of tax base and subject population; the wider the base and population, the higher the contribution of the tax to partial financing of the RNR;
d. Sustainability: this criterion evaluates the life expectancy of the considered tax; taxes may be transient or permanent, depending especially on their purpose, for instance a tax on destructive fishing practices aims at eliminating these practices on the medium-term and not to sustain them in order to continue taxing these activities;
e. Resilience to the economic context: this criterion foresees the consequences of the risks related to economic uncertainties on the collection of tax revenues and provides better transparency on the stability of the RNR's financing;
f. Selectivity of the subjects: this criterion reflects the number and diversity of people subject to tax; the considered tax should not, as far as possible, be restricted to a single occupational category, or there will be poor social acceptability and economic risk.
The taxes considered for having a good potential to complete the financing of the future RNR of le Prêcheur are qualitatively analysed according to these six criteria. The results are displayed in Table 4 below: one star means "little" or "low"; two stars mean "a lot" or "strong". Red means "negative" and the blue "positive".
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From the elements of the previous analysis, it is possible to rank the ten selected options. By assigning a score by ranking the criteria of the comparative analysis of Table 4 (+1 for a blue star and −1 for a red star), the feasibility of each option is relatively estimated (see Table 5).
General valuation | |
Introduction of a new tax/royalty | |
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | 0 |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality |
−1 |
Tax on extractive and/or damaging of the reserve activities (fishing, spearfishing) | −3 |
Tax on polluting activities of the watershed | 1 |
Royalty on diving activities | 7 |
Royalty on taxi boats, recreational and private sailing boats | 8 |
Assignment of an existing tax | |
Share of dock dues | 2 |
Share of the tourist tax | 6 |
Share of the tax on polluting activities | 2 |
Broadening of the rate of an existing tax | |
Broadening of the airport tax | 7 |
Broadening of the transportation tax | 2 |
Source: authors own creation. |
The overall feasibility valuation shows a definite relevance to weigh the burden of taxation on local leisure activities, through the establishment of a new royalty. The two options that cumulate the most points are the royalty on recreational and sailing activities (8 points) and the royalty on diving activities (7 points). Besides the financial contribution to the management of RNR of le Prêcheur, these options also have the virtue of offering a tool to regulate the use of marine ecosystems. In this respect, they function as an entrance fee (Voltaire et al., 2011). With the difference that they are better accepted in France, the principle of the entrance fee faces legal (see right of the public domain) and social (tradition of free access to nature) constraints (Vourc'h and Natali, 2000). However, possible difficulties of introducing a new royalty in the currently depressed economic environment must be noted.
The expansion of the airport tax seems to also be an interesting option (7 points). Its implementation can be difficult because it is a broadening of the tax that does not directly benefit to the management of the airport. But the revenue generated can be very large in view of visitation of the airport Aimé Césaire.
The allocation of part of the tourist tax levied on all hosts of Martinique also proves relevant, with a score of 6 points. This option provides a better distribution of the tax burden than a strictly local royalty, which could penalize the attractiveness of the municipality of le Prêcheur.
Less interesting are the options that suggest the introduction of a tax on polluting activities of the watershed and at regional scale, to allocate part of the dock dues or to expand the transportation tax (1 or 2 points). The introduction of a tax on extractive activities in the area, or taxes to explicitly finance the RNR with tourists or inhabitants of the municipality, prove to be among the least favourable of the selected options. Yet these low scores, with regard to the complementary revenue generation target for the RNR, should not mask the advantage in terms of management of marine ecosystems and associated activities of the latter options. Thus, a tax on polluting or damaging activities reduces pressures on ecosystems of the reserve and encourage virtuous practices for the environment (Binet et al., 2013; Failler et al., 2015).
With approximately 18,000 dives per year for around fifteen dive centres in the area of le Prêcheur (Failler et al., 2010), the implementation of a royalty could generate between 36,000 and 90,000 euros per year. For reference, an investigation undertaken with the visitors of Martinique had shown the possibility to increase prices of 2 to 5 euros per dive as long as spectacular fish or marine areas can be observed, for a dive of an average price of 40 euros (Borot Battisti et al., 2011). This range is equivalent to the introduction of a tax with a rate between 5 and 12.5%.
The implementation of an enlargement of the airport tax of 1 euro to finance regional marine reserves would allow, with a passenger flow of 1.6 million on average for the last three years, generation of an income of 1.6 million euros.
With a yearly average of 1500 excursionists visiting the area of le Prêcheur by taxi-boat or sailing boat, the introduction of a royalty on tours could yield about 3,000 euros a year (for a willingness to pay estimated at €2 per tour). This relatively low estimate does not take into account, for a lack of assessment of their number, visitors on boats in the area. This is a potentially significant income, as they are estimated at about 40,000 a year on all of Martinique.
With 19,000 residential tourists each year in the territory of the municipality of le Prêcheur, the allocation of part of the tourist tax levied on all hosts of the municipality would generate an income of 3,800 euros per year for €0.20 and €7600 per year for €0.40. The neighbouring municipalities (Saint-Pierre, Grand Rivière, le Carbet, etc.) may also earmark a share of their tourist tax to fund the reserve. This solidarity contribution of neighbouring municipalities could generate tens of thousands of euros.
The implementation of an MPA results in a decrease in fishing activities, little or not compensated (Binet et al., 2013). To maintain their activity, fishermen tend to increase fishing efforts in the unprotected territory, which goes against the MPA's conservation efforts. It is therefore essential to find a way to compensate for this loss of territory without increasing fishing efforts. In addition, the ousting of the fishermen for the MPA results in a loss of knowledge for society in general, as fishermen have empirical knowledge of the marine ecosystem transmitted in an ancestral way. This knowledge is crucial to anticipate the consequences of global change on marine and coastal ecosystems of the Caribbean islands. The traditional knowledge of the fishermen can also be harnessed for the maintenance or improvement of coastal environments. This can be done simultaneously to fishing activities. The point is not to convert fishermen to conservationists; no, it is much more about involving them in the process of habitat conservation and sustainable use of fisheries resources. Thus the two functions, fishing and protection, become inseparable.
The goal is therefore to develop a simple mechanism where fishermen can be rewarded for their efforts towards the improvement of ecosystem services of marine protected areas. This realization warrants a reflection on "payments for environmental services" or PES. The PES concept emerged in the 1990s (Meral, 2010), notably with the establishment of the PES program in Costa Rica that protects to this day 25,000 hectares of forest. But it was not until 2002 that the PES experienced a real increase of interest thanks to two books published by Landell-Mills and Porras, and Pagiola, Bishop and Landell-Mills. Although the definition of PES is still controversial, the one established by Wunder (2005) is widely accepted. It defines a PSE as a voluntary transaction where a particular ecosystem service is 'purchased' by (at least) one individual consumer from (at least) one individual supplier, if and only if the supplier guarantees the production of this service. Designed in a market-driven, voluntary exchanges between providers and consumers of services can thus be subject to negotiations, nonetheless forcing suppliers to engage in activities of specific use and to consider the demand to set the price. Moreover, the compensation is carried out in a 'logic of additionality', as the presence of service must provide a benefit to biodiversity, and in a 'logic of conditionality' ensuring the effectiveness of the service, its supply becoming mandatory to obtain the payment (Froger et al., 2012).
Several PES programs similar to that of Costa Rica have been implemented, including in Mexico (protection of about 2 million hectares of forest). However, the vast majority of PES initiatives are implemented on a smaller scale. Thus, many PES program projects are being implemented or prepared at national scale or the scale of a watershed (Pagiola, 2008). As of today, no PES program has been established for marine and coastal ecosystems. The establishment of PES in le Prêcheur would be a pioneering action that may, if successful, be replicated in other MPAs.
Behind the name of PES stands a simple mechanism that is to reward the actions of those that enhance (or do not cause a decrease in) the quality of ecosystem services; the contributors being the users. In other words, the fishermen can be paid for efficient actions in favour of biodiversity and for the knowledge they provide to the governance of MPAs. In the first case, it is the direct users (divers, boaters, hikers, swimmers, etc.) that will contribute to the remuneration of the actions of fishermen, in the second, it is the society in general that is indebted (through the MPA) as protected areas act as places with higher resistance to global change than non-protected areas, and with greater resilience. The PES mechanism is all the more relevant as it generates funding for activities towards biodiversity that would not exist otherwise. It is also sustainable because it is based on self-interest of fishermen and users and not on the good will of the government or non-governmental organizations. It is all the more sustainable as it has a net positive toll for both individuals and society as a whole.
A survey was conducted among the fishermen of le Prêcheur in 2015 and 2016 (Thirot et al., 2017). The study sample, composed of 16 fishermen, represents about 50% of the fishermen declared in activity. It is characterized by an ethnic diversity, ensuring a wide spectrum of responses and access to the various existing categories in the professional group7. The fishermen's knowledge on the marine environment originates from a daily presence at sea and the data transmission by peers during the apprenticeship. They are presented very synthetically in Table 6 below. They can be promoted in the context of ecotourism, where it is direct users who contribute to the payment of fishermen's actions, or in scientific monitoring and more generally the MPA management.
7 However, some fishermen fiercely opposed to the creation of the MPA refused to be interviewed.
Knowledge of fishermen | Ecotourism | Scientific monitoring and MPA management |
Physical characteristics, behaviour and habits (feeding, habitat, spawning grounds) of fish (ethology) | X | X |
Spawning grounds | X | |
Fish life cycles (breeding and migration seasons) | X | |
Impact of abiotic factors (hydraulic, oceanographic, climatic) on fish life cycle | X | |
Adaptive and resiliency capabilities of the marine environment to climate change | X | |
Endangered species | X | X |
Health status of the marine environment (coral bleaching or algal invasion for example) | X | |
Evolution of the fishery resource with notably species rotation, disappearance or appearance (lion fish), etc. | X | |
Rhythm, temporality et cycle of fishing seasons and species presence | X | |
Interconnections between species (between fish species but also between fish and plants) | X | |
Impact of human activities on the marine environment | X | |
Source: authors own creation. |
The knowledge of fishermen encompasses both elements of local (nursery places for example) and global (including climate change) knowledge, observed on a long timescale since some have been working for over 30 years. With this sharp empirical knowledge, they are able to interpret ecological processes at work in the marine environment by making hypotheses they can later test in situ. This exercise is essential for those who wish to appreciate the evolution of the marine environment, its adaptability and resilience to climate change. This integrated vision of the marine ecosystem can thus be useful to the scientific monitoring and generally the management of the MPA of le Prêcheur and for any type of action beneficial to the restoration, maintenance and improvement of biodiversity in general (through awareness-raising of the educational world).
Although the MPA of le Prêcheur was formally created by deliberation of the Regional Council of Martinique on October 14, 2014, no management structure exists at this time to make it run. The PES therefore cannot be implemented. However, when an effective management is established, their implementation should allow fishermen to contribute to the preservation of a common asset. Thus, PES can act as catalysts and promote the MPA as means to add value to the fishing profession.
The feasibility analysis of taxation as an additional income for the RNR of le Prêcheur demonstrates the relevance of the enlargement of the airport tax to finance the RNR. This analysis also demonstrates the benefits of the introduction of a new royalty on tourism activities related to the enjoyment of the marine ecosystems of the area: the recreation and sailing on the one hand and on the other hand diving. The allocation of part of the tourist tax, collected for the benefit of the management of RNRs of Martinique, also appears an attractive option.
The estimation of the financial benefits of the four selected taxes is approximately €1.6 to 1.7 million. This income will probably be destined to increase for taxes levied locally with the establishment of the RNR, the label of which will function as a guarantee of quality and therefore of attractivity to visitors. For regional taxes on the other hand (primarily the airport tax), this participation will be reduced with the possible creation of other regional marine reserves in Martinique.
However, the final selection of the preferred option requires a thorough operational analysis, including in particular the implementation schedule, costs and results associated with the collection of taxes and forecasted financials. In particular, the reality of the institutional context, fiscally constrained, forces to reckon with limited resources and no guarantee of sustainability. It requires in all cases to fully optimize the effectiveness and efficiency of resource use. For this, a detailed analysis of the starting funds needed for the future reserve and then for the medium-term management seems essential, in parallel of the study of potential sources. Finally, we must remember that, regardless of the option selected, no action can succeed without first involving all stakeholders for concertation.
Finally, the implementation of a sustainable management of marine resources requires the development of specific systems of gratification, such as payments for environmental services, ensuring the recognition and enhancement of knowledge and actors who hold them, here the fishermen. These compensation mechanisms need to take into account two types of environmental services provided by fishermen. The first is based on the commitment to protect the marine environment and requires a change in practices. The direct beneficiary is biodiversity. The second service is to exploit the knowledge held by engaging in sustainable resource management operations, in the short and medium term. The beneficiary is the society (more generally humanity) and specifically the services recipients that are institutional players, other sea users and the local population. In all cases, these bonuses must meet requirements of justice and fair redistribution.
This paper has been produced with the financial support of the European Commission, under the BEST Scheme and within the Project CARIPES (Payments for Ecosystem Services in the Caribbean). Opinions expressed in this article do not necessarily reflect the ones of the European Commission and don't anticipate the Policy of the Commission in this area.
The authors declare no conflict of interest.
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71. | Prachi Simran Vig, Jia Yin Lim, Randal Wei Liang Lee, Huixin Huang, Xiu Hui Tan, Wei Qiang Lim, Marie Bernadette Xin Yi Lim, Alexia Sze Inn Lee, Min Chiam, Crystal Lim, Vijayendra Ranjan Baral, Lalit Kumar Radha Krishna, Parental bereavement – impact of death of neonates and children under 12 years on personhood of parents: a systematic scoping review, 2021, 20, 1472-684X, 10.1186/s12904-021-00831-1 | |
72. | Elaine Li Ying Quah, Keith Zi Yuan Chua, Jun Kiat Lua, Darius Wei Jun Wan, Chi Sum Chong, Yun Xue Lim, Lalit Krishna, A Systematic Review of Stakeholder Perspectives of Dignity and Assisted Dying, 2023, 65, 08853924, e123, 10.1016/j.jpainsymman.2022.10.004 | |
73. | Onouma Thummapol, Sadaf Murad, Oluwakemi Amodu, Megan Kennedy, Exploring the Therapeutic Effects of Music Intervention Embedded With Binaural Beats on Health and Well-Being of Older People: A Scoping Review, 2024, 0733-4648, 10.1177/07334648241275965 | |
74. | Yao Hao Teo, Tan Ying Peh, Ahmad Bin Hanifah Marican Abdurrahman, Alexia Sze Inn Lee, Min Chiam, Warren Fong, Limin Wijaya, Lalit Kumar Radha Krishna, A modified Delphi approach to nurturing professionalism in postgraduate medical education in Singapore, 2024, 65, 0037-5675, 313, 10.11622/smedj.2021224 | |
75. | Natalie E. Pope, Emily A. Greenfield, Laura Keyes, Elizabeth Russell, A Review of Public Sector Engagement in Age-Friendly Community Initiatives, 2024, 0895-9420, 1, 10.1080/08959420.2024.2376934 | |
76. | Sunny C Okoroafor, Christmal Dela Christmals, Optimizing the roles of health workers to improve access to health services in Africa: an implementation framework for task shifting and sharing for policy and practice, 2023, 23, 1472-6963, 10.1186/s12913-023-09848-z | |
77. | Gábor Rónaföldi-Széll, Succession and gender dynamics in family firms – A systematic literature review and future research agenda, 2024, 55, 01330179, 59, 10.14267/VEZTUD.2024.07-08.06 | |
78. | Nami Kawakyu, Megan Coe, Bradley H. Wagenaar, Kenneth Sherr, Sarah Gimbel, Edward Nicol, Refining the Performance of Routine Information System Management (PRISM) framework for data use at the local level: An integrative review, 2023, 18, 1932-6203, e0287635, 10.1371/journal.pone.0287635 | |
79. | Michal Kaššaj, Tomáš Peráček, Synergies and Potential of Industry 4.0 and Automated Vehicles in Smart City Infrastructure, 2024, 14, 2076-3417, 3575, 10.3390/app14093575 | |
80. | Johan Högberg, Ramana Piussi, Johan Lövgren, Mathias Wernbom, Rebecca Simonsson, Kristian Samuelsson, Eric Hamrin Senorski, Restoring Knee Flexor Strength Symmetry Requires 2 Years After ACL Reconstruction, But Does It Matter for Second ACL Injuries? A Systematic Review and Meta-analysis, 2024, 10, 2198-9761, 10.1186/s40798-023-00666-5 | |
81. | Cara Evans, Julia Abelson, Nick Kates, Alice Cavanagh, John N. Lavis, Tommaso Martino, A Multilevel Framework for Complex Care: A Critical Interpretive Synthesis, 2023, 2023, 1365-2524, 1, 10.1155/2023/4487200 | |
82. | Jasmine Svantesson, Ramana Piussi, Elin Weissglas, Eleonor Svantesson, Alexandra Horvath, Erik Börjesson, Andy Williams, Robert Prill, Kristian Samuelsson, Eric Hamrin Senorski, Shedding light on the non-operative treatment of the forgotten side of the knee: rehabilitation of medial collateral ligament injuries—a systematic review, 2024, 10, 2055-7647, e001750, 10.1136/bmjsem-2023-001750 | |
83. | Zoe Guerrero, Dagmar Civišová, Petr Winkler, Mental health and access to care among the Roma population in Europe: A scoping review, 2024, 61, 1363-4615, 118, 10.1177/13634615231200853 | |
84. | Palaniappan Ganesh Nagappan, Samuel Brown, Alex McManus, Sarah Sayers, Shazia Absar, Sapphire Rou Xi Tan, Isla Kuhn, Edward Lau, Charlotte Tulinius, Changes in medical student attendance and its impact on student educational outcomes: a systematic review protocol, 2024, 14, 2044-6055, e078252, 10.1136/bmjopen-2023-078252 | |
85. | Begetayinoral Kussia Lahole, Tesfahun Simon, Wondimu Ewunetu, Wondafrash Kussia, Protocol for a systematic review and meta-analysis on intention to screen for cervical cancer and predictors among women of reproductive age in Ethiopia, 2024, 2, 2753-4294, e000585, 10.1136/bmjph-2023-000585 | |
86. | Katja Rogers, Teresa Hirzle, Sukran Karaosmanoglu, Paula Toledo Palomino, Ekaterina Durmanova, Seiji Isotani, Lennart E. Nacke, An Umbrella Review of Reporting Quality in CHI Systematic Reviews: Guiding Questions and Best Practices for HCI, 2024, 31, 1073-0516, 1, 10.1145/3685266 | |
87. | Gillian Li Gek Phua, Jasmine Lerk Juan Owyong, Ian Tze Yong Leong, Suzanne Goh, Nagavalli Somasundaram, Eileen Yi Ling Poon, Anupama Roy Chowdhury, Simon Yew Kuang Ong, Crystal Lim, Vengadasalam Murugam, Eng Koon Ong, Stephen Mason, Ruaridh Hill, Lalit Kumar Radha Krishna, A systematic scoping review of group reflection in medical education, 2024, 24, 1472-6920, 10.1186/s12909-024-05203-w | |
88. | Yvonne Fitzmaurice, Suzanne Beeke, Jytte Isaksen, Una Cunningham, Caroline Jagoe, Éidín Ní Shé, Ruth McMenamin, Communication partner training for student health and social care professionals engaging with people with stroke acquired communication difficulties: A protocol for a realist review., 2024, 6, 2515-4826, 60, 10.12688/hrbopenres.13783.2 | |
89. | Anne Hammarström, Hugo Westerlund, Urban Janlert, Pekka Virtanen, Shirin Ziaei, Per-Olof Östergren, How do labour market conditions explain the development of mental health over the life-course? A conceptual integration of the ecological model with life-course epidemiology in an integrative review of results from the Northern Swedish Cohort, 2024, 24, 1471-2458, 10.1186/s12889-024-18461-6 | |
90. | Jodie Gill, Alexis Jones, Klara Price, Egan Goodison, Philip Tyson, A mixed‐method systematic review of the perspectives of young people, carers and professionals on psychiatric diagnosis in childhood and adolescence, 2024, 37, 1073-6077, 10.1111/jcap.12459 | |
91. | Amalia Kouskoura, Eleni Kalliontzi, Dimitrios Skalkos, Ioannis Bakouros, Assessing the Key Factors Measuring Regional Competitiveness, 2024, 16, 2071-1050, 2574, 10.3390/su16062574 | |
92. | Anu-Riina Svenlin, Tiina Lehto-Lundén, Respite care from the child’s perspective – The Support Family Intervention in Finland, 2023, 47, 0308-5759, 138, 10.1177/03085759231176566 | |
93. | Ramana Piussi, Rebecca Simonson, Bálint Zsidai, Alberto Grassi, Jon Karlsson, Francesco Della Villa, Kristian Samuelsson, Eric Hamrin Senorski, Better Safe Than Sorry? A Systematic Review with Meta-analysis on Time to Return to Sport After ACL Reconstruction as a Risk Factor for Second ACL Injury, 2024, 54, 0190-6011, 161, 10.2519/jospt.2023.11977 | |
94. | Yun Xue Lim, Elaine Li Ying Quah, Keith Zi Yuan Chua, Casper Keegan Lin Ronggui, Ranitha Govindasamy, Simone Meiqi Ong, Eng Koon Ong, Gillian Li Gek Phua, Lalit Kumar Radha Krishna, A Systematic Scoping Review on Dignity Assessment Tools, 2024, 67, 08853924, e263, 10.1016/j.jpainsymman.2023.12.008 | |
95. | Elaine Li Ying Quah, Keith Zi Yuan Chua, Casper Keegan Ronggui Lin, Andrew Vimal Vijayan, Nur Amira Binte Abdul Hamid, Jasmine Lerk Juan Owyong, Neeta Satku, Natalie Woong, Crystal Lim, Gillian Li Gek Phua, Eng Koon Ong, Warren Fong, Lalit Kumar Radha Krishna, The role of patients’ stories in medicine: a systematic scoping review, 2023, 22, 1472-684X, 10.1186/s12904-023-01319-w | |
96. | Tim Stroh, Anne-Laure Mention, Cameron Duff, The impact of evolved psychological mechanisms on innovation and adoption: A systematic literature review, 2023, 125, 01664972, 102759, 10.1016/j.technovation.2023.102759 | |
97. | Neha Burla, Rui Song Ryan Ong, Ryan Choon Hoe Chee, Ruth Si Man Wong, Shao Yun Neo, Nur Amira Binte Abdul Hamid, Crystal Lim, Eng Koon Ong, Nagavalli Somasundaram, Lalit Kumar Radha Krishna, A systematic scoping review on group non-written reflections in medical education, 2024, 24, 1472-6920, 10.1186/s12909-024-06117-3 | |
98. | Rita Elaine Silver, Vinay Kumar, Deborah Chua Fengyi, Michael Tan Lip Thye, Johannis Auri Bin Abdul Aziz, For What and for Whom? Expanding the Role of Research Syntheses for Diverse Stakeholders, 2024, 53, 0013-189X, 464, 10.3102/0013189X241285414 | |
99. | Yvonne Fitzmaurice, Suzanne Beeke, Jytte Isaksen, Una Cunningham, Caroline Jagoe, Éidín Ní Shé, Ruth McMenamin, Communication partner training for student health and social care professionals engaging with people with stroke acquired communication difficulties: A realist review., 2023, 6, 2515-4826, 60, 10.12688/hrbopenres.13783.1 | |
100. | Danielle Allard, Tami Oliphant, With a Little Help from Our Friends: Applying a Critical Friends Orientation to Critical Literature Reviews, 2024, 61, 2373-9231, 13, 10.1002/pra2.1004 | |
101. | Sunday Adeola Ajagbe, Joseph Bamidele Awotunde, Ademola Temidayo Opadotun, Matthew O. Adigun, 2023, Chapter 4, 978-981-99-5084-3, 39, 10.1007/978-981-99-5085-0_4 | |
102. | Darius Wei Jun Wan, Laura Shih Hui Goh, Mac Yu Kai Teo, Celestine Jia Ling Loh, Gerald Hng Kai Yak, Joanna Jing Hui Lee, Nila Ravindran, Nur Diana Abdul Rahman, Min Chiam, Eng Koon Ong, Nagavalli Somasundaram, Ying Yin Lim, Gillian Li Gek Phua, Lalit Kumar Radha Krishna, Enhancing self-care education amongst medical students: a systematic scoping review, 2024, 24, 1472-6920, 10.1186/s12909-023-04965-z | |
103. | Tea Rosic, Elizabeth Lovell, Harriet MacMillan, Zainab Samaan, Rebecca L Morgan, Components of Outpatient Child and Youth Concurrent Disorders Programs: A Critical Interpretive Synthesis: Composantes des programmes de troubles concomitants des enfants et des jeunes ambulatoires : une synthèse interprétative critique, 2024, 69, 0706-7437, 381, 10.1177/07067437231212037 | |
104. | Katherine P. Kelly, Kathleen A. Knafl, Susan Keller, Pamela S. Hinds, Thematic expansion: A new strategy for theory development, 2021, 43, 0193-9459, 962, 10.1177/0193945920984795 | |
105. | Rahma K. Dewi, Sri Sumarni, Parenting style and family empowerment for children's growth and development: a systematic review, 2023, 14, 2038-9930, 8, 10.4081/jphia.2023.2582 | |
106. | Milou S. H. van Dieën, Wolter Paans, Massimo A. Mariani, Willem Dieperink, Fredrike Blokzijl, Roles and competencies of nurses and physicians in shared decision‐making in cardiac surgery: A scoping review, 2024, 80, 0309-2402, 60, 10.1111/jan.15811 | |
107. | Katarzyna Turoń, Factors Affecting Car-Sharing Services, 2023, 6, 2624-6511, 1185, 10.3390/smartcities6020057 | |
108. | Tiago Bigolin, Edson Talamini, Impacts of Climate Change Scenarios on the Corn and Soybean Double-Cropping System in Brazil, 2024, 12, 2225-1154, 42, 10.3390/cli12030042 | |
109. | Vitaliano Fiorillo, Biagio Maria Amico, Milk Quality and Economic Sustainability in Dairy Farming: A Systematic Review of Performance Indicators, 2024, 5, 2624-862X, 384, 10.3390/dairy5030031 | |
110. | Astrid Bertrand, Tiphaine Viard, Rafik Belloum, James R. Eagan, Winston Maxwell, 2023, On Selective, Mutable and Dialogic XAI: a Review of What Users Say about Different Types of Interactive Explanations, 9781450394215, 1, 10.1145/3544548.3581314 | |
111. | Jelena Komanchuk, Judy L. Cameron, Stefan Kurbatfinski, Linda Duffett-Leger, Nicole Letourneau, A realist review of digitally delivered child development assessment and screening tools: Psychometrics and considerations for future use, 2023, 183, 03783782, 105818, 10.1016/j.earlhumdev.2023.105818 | |
112. | Jonathan Zhen Liang, Donovan Kai Wei Ng, Vijayprasanth Raveendran, Mac Yu Kai Teo, Elaine Li Ying Quah, Keith Zi Yuan Chua, Jun Kiat Lua, Jasmine Lerk Juan Owyong, Andrew Vimal Vijayan, Nur Amira Binte Abdul Hamid, Ting Ting Yeoh, Eng Koon Ong, Gillian Li Gek Phua, Stephen Mason, Warren Fong, Crystal Lim, Natalie Woong, Simon Yew Kuang Ong, Lalit Kumar Radha Krishna, Marsa Gholamzadeh, The impact of online education during the Covid-19 pandemic on the professional identity formation of medical students: A systematic scoping review, 2024, 19, 1932-6203, e0296367, 10.1371/journal.pone.0296367 | |
113. | Rosa Angélica Priego Morales, Management leadership in the New Mexican School and teacher revaluation from the recognition of human talent: a scoping review, 2024, 29546168, 10.58763/rc2024197 | |
114. | Nofie Iman, Service modularity in the digital era: integrating environmental sustainability and post-pandemic insights, 2024, 1756-669X, 10.1108/IJQSS-05-2023-0061 | |
115. | Camila F. Pfeiffer, Wendy L. Magee, Rebecca Fülöp, Travis C. Nace, Candela Castro, Agustina Iturri, Jimena Franceschi, Gabriela Echauri, Liliana Gassull, María Julieta Russo, Exploring Music-Based Interventions for Executive Functioning and Emotional Well-Being in Stroke Rehabilitation: A Scoping Review, 2024, 5, 2673-4087, 565, 10.3390/neurosci5040041 | |
116. | Verónica Estruch-García, María Dolores Gil-Llario, Estefanía Ruiz-Palomino, Olga Fernández-García, Vicente Morell-Mengual, Zélia Ferreira Caçador Anastácio, Systematic Integrative Review: Sex Education for People with Autism Spectrum Disorder, 2025, 43, 0146-1044, 10.1007/s11195-024-09877-4 | |
117. | Kari Dee Vallury, Amanda Asher, Olivia Sarri, Nicola Sheeran, Jami Leichliter, Characteristics and determinants of quality non-directive pregnancy options counselling: a scoping review, 2025, 22, 1448-5028, 10.1071/SH24170 | |
118. | Kirsten M. Greer, Kyla M. Cary, Morgan E. PettyJohn, Gianna Casaburo, Carin Graves, Kristen N. Jozkowski, A Qualitative Meta-Synthesis of Women’s Experiences of Internalized Sociocultural Sexual Pressure, 2025, 0022-4499, 1, 10.1080/00224499.2025.2451144 | |
119. | Wei Chen Chang, Wan Zi Lin, Wen-Zhi Chen, Wen-Ko Chiou, Oliver Shinbou Lin, Design-driven innovation in the public sector: insights from case studies of initiatives in Taiwan, 2025, 1751-6234, 1, 10.1080/17516234.2025.2457166 | |
120. | Hiroyuki Suzuki, Yusuke Tsuboko, Manabu Tamura, Ken Masamune, Kiotaka Iwasaki, Synthesis of the clinical utilities and issues of intraoperative imaging devices in clinical reports: a systematic review and thematic synthesis, 2025, 25, 1472-6947, 10.1186/s12911-025-02915-x | |
121. | Charles Birungi, Michael A. Obst, Using economics to advance health equity: What we know, don't know and need to know (but may never know) from Markus Haacker, 2025, 2, 2994-4694, 10.1080/29944694.2025.2456791 | |
122. | Abdullah Almunifi, Impact of Artificial Intelligence on Metabolic Bariatric Surgery (MBS) and Minimally Invasive Surgery (MIS): A Literature Review, 2025, Volume 17, 1178-7082, 161, 10.2147/OAS.S482690 | |
123. | Yoeurng Sak, Paradise Ros, Reviewing Needs and Techniques of Mentors for Mentoring New Teachers , 2025, 14, 2327-2619, 52, 10.11648/j.edu.20251402.13 | |
124. | Luke Tan, Sonia Sheri, Yun Yao Goh, Raeanne Fong, Ranitha Govindasamy, Yun Ting Ong, Nur Amira Binte Abdul Hamid, Tessa Li Xiang Low, Lalit Kumar Radha Krishna, Experiences of healthcare professionals providing palliative care in home settings - a scoping review, 2025, 24, 1472-684X, 10.1186/s12904-025-01728-z | |
125. | Kathleen Parry, Christopher Picard, Rashmi Devkota, Kaitlyn Tate, Emergency Department Navigator Interventions and Outcome Measures: A Scoping Review, 2025, 20, 1748-3735, 10.1111/opn.70026 | |
126. | Ольга Подпалова, Євдокія Решетнік, Олександр Ковальчук, Ірина Прибитько, Руслан Мневець, ПІДВИЩЕННЯ ІННОВАЦІЙНОСТІ МЕДИЧНОЇ ОСВІТИ ЧЕРЕЗ СТУДЕНТСЬКІ НАУКОВІ ОБ’ЄДНАННЯ, 2025, 2710-3056, 479, 10.36074/grail-of-science.10.01.2025.071 | |
127. | Douglas S. Lownsbery, A Synthesis Review of Four Literature Reviews of Disaster Risk Reduction Education for Children, 2025, 22124209, 105555, 10.1016/j.ijdrr.2025.105555 | |
128. | Chiara Bernuzzi, Giulia Paganin, Sara Petrilli, Simona Margheritti, Old trends in new clothing? Exploring the quiet quitting phenomenon through a scoping review, 2025, 1046-1310, 10.1007/s12144-025-07920-x | |
129. | Giti Bahrami, Nooshin Ghavidel, Zohreh Mahmoodi, Ronan McDermott, Hamed Seddighi, The health effects of climate change: identifying strategies, policies, and knowledge gaps: an umbrella review, 2025, 0960-3123, 1, 10.1080/09603123.2025.2498624 | |
130. | Ukachukwu O Abaraogu, Philippa Dall, Chris Seenan, Sarah Rhodes, Trish Gorely, Joanna McParland, Julie Brittenden, Ebuka M Anieto, Lorna Booth, Cathy Gormal, Jeremy Dearling, Candida Fenton, Sarah Audsley, Kimberley Fairer, Lindsay Bearne, Dawn A Skelton, Behaviour change interventions to promote physical activity in people with intermittent claudication: the OPTIMA systematic review, 2025, 2046-4924, 1, 10.3310/ZBNG5240 | |
131. | David Steingard, Kathleen Rodenburg, Assessing the Societal Impact of Academic Research With Artificial Intelligence (AI): A Scoping Review of Business School Scholarship as a ‘Force for Good’, 2025, 38, 0953-1513, 10.1002/leap.2010 | |
132. | Quan Nha Hong, Ginny Brunton, Helping Trainees Understand the Strategies to Minimize Errors and Biases in Systematic Review Approaches, 2025, 41, 0167-8329, 161, 10.1177/01678329251323445 | |
133. | Charan Bijlani, Denise Ndlovu, Dianna Smith, Claire Thompson, Leandro Garcia, Cornelia Junghans, Eszter P. Vamos, Paraskevi Seferidi, Understanding food insecurity in England: a systems-based approach, 2025, 2574-1292, 1, 10.1080/25741292.2025.2523114 | |
134. | Julie B. Grant, Jacqueline Jones, Carey Candrian, Kathleen S. Oman, Sean M. Reed, The Role of Nursing Communication: A Critical Interpretive Synthesis, 2025, 2666142X, 100373, 10.1016/j.ijnsa.2025.100373 |
Level | Budget (million €) | Notes |
State | 28.1 | Allocated budget, program 113 action 7* |
French Marine Protected Areas Agency |
1 | - |
French Coastal Protection Agency | 40 | €2.4 million of which come from repayments of the state and €37.6 million come from an individual taxation regime |
Other operators | 5 | - |
Total State + operators | 74.1 | In comparison, the total state budget allocated to the conservation of natural areas and water management amounts to €2447 million |
Source: Translated from Badré M and Duranthon JP, 2010. *Current financial resources allocated by the state to the budget for biodiversity policies are partly addressed by action 7 "management of environments and biodiversity" program 113 of the Ministry of Ecology, Energy, Sustainable Development and the Sea. |
The tax is levied from the provision of a service. It may be required not only from actual users but also from potential users and the amount is not strictly equivalent to the service provided (e.g. tax for household waste collection). The tax is provided by the law. Royalties (or remuneration) for services rendered are received in return for a service, such as the use of a piece of work or a benefit provided by a public service to a user while bearing the cost, and therefore must match the value of the benefit or service. A royalty can be established through regulation. The amount of the royalty must be equivalent to the value of the benefit or proportional to the cost of the service rendered. Such is the case of the "institution of a royalty comprising of a fixed part and a variable part, provided that the calculation of the fee allows to ensure the proportionality with the cost of the service rendered" (EC No. 220803 of July 9 2009). 'Respect for the rule of equivalence between the fare of a royalty and the value of the benefit or service can be ensured by withholding the cost of the latter, but also according to the characteristics of the service, by taking into account the economic value of the benefit to the recipient; that in all cases, the fare must be established according to objective and rational criteria, in full conformity with the principle of equality between the users of public services and the competition rules (EC No 309 499 of 7 October 2009). Environmental royalties can be defined as payment for environmental services: in return for their payment, the taxpayer receives an environmental service. As pollution could be interpreted as a particular use of a natural resource (right to pollute), a levy associated with a degradation of the environment can then be likened to a royalty. The distinction between taxes and royalties is also based on the allocation of revenues. Into the general budget for the first case, revenues are earmarked for specific purposes in the case of royalties. Yet, in the field of environmental taxation, these two aspects of distinction between taxes and royalties are not systematically combined. This explains why these two terms are sometimes interchangeably used. |
Introduction of a new tax or royalty | Assignment of an existing tax | Broadening of the rate of an existing tax | ||
Regional scale | Residential tourists | Tax to finance regional reserves of Martinique (on the template of the tourist tax) | Share of the tourist tax of the municipalities of Martinique | Broadening of the airport tax; broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance regional reserves of Martinique (on the template of the housing tax) | Share of dock dues | Broadening of the airport tax; broadening of the transportation tax | |
Marine ecosystem users | Tax on uses of the ecosystems of Martinique (in addition to fishing licences for e.g.), tax on offshore recreational practices (surf, kitesurf, etc.) | Share of revenue of fishing licences | Broadening of fishing licences | |
Corporations that pollute | Taxes on polluting activities in Martinique that have impacts on marine ecosystems (urbanisation coastal fringe, granulate extraction, non-biological agricultural activities, etc.) | Share of the tax on marine polluting activities | Broadening of the tax on polluting activities | |
Local scale (area of the reserve and surrounding area) | Residential tourists | Tax to finance the RNR of le Prêcheur enforceable to tourist operators of the municipality (on the template of the tourist tax) | Share of the tourist tax of the municipality of le Prêcheur | Broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance the RNR of le Prêcheur enforceable to the inhabitants of the municipality (on the template of the housing tax) | Share of the housing tax of the municipality of le Prêcheur | Broadening of the transportation tax | |
Marine ecosystems users | Local tax on extracting and/or damaging of the RNR activities (fishing, spearfishing); royalty on diving activities; royalty on taxi-boats, recreational boats and private sailing boats | n.a. | n.a. | |
Corporations that pollute | Tax on polluting activities of the watershed | n.a. | n.a. | |
Note: n.a. = not applicable; Source: authors own creation. |
Strengths | Weaknesses | |
Introduction of a new tax/royalty | ||
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | Tourism figures increasing, potential source of growing incomes Potential modulation of the rate based on the environmental impact of the operator |
Penalises supply of tourism services of the municipality of le Prêcheur only, already seldom developed Potentially penalises visitors that are non-users of marine ecosystems (e.g. Hikers) |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality | Empowers inhabitants on the impact of their everyday practices on the ecosystem Potential modulation of the rate based on the environmental impact of the building | Penalises the inhabitants of the municipality of le Prêcheur only, potentially making the area less attractive Potentially penalises the inhabitants that are non-users of marine ecosystems (e.g. Hikers) |
Local tax on extractive and/or damaging of the RNR activities (fishing, spearfishing) | Reduces through a fiscal leverage the extractive activities and other damaging practices while producing revenues for the reserve Enables guidance by incentives for reorientation of fishermen or discontinuing of damaging practices (frequent use of beach-seine for example) |
Low acceptability upon populations of fishermen and underwater hunters already affected by management actions Difficult to weigh the burden of a tax only on fishermen and underwater hunters Revenues of this tax are destined to decrease, thus jeopardizing the financing Penalises operators who take measures voluntarily (eco-responsible construction, choice of a fishing net with larger mesh, etc.) |
Tax on polluting activities of the watershed | Polluter-payer principle: polluting activities must be subjected to financial compensation; to go further, it is possible to implement a payment for ecosystem services: polluting activities fund the reserve for improvement of the treatment of waste produce by these activities; enables to give a tax preference to non-polluting local activities (idea of a partial exemption from tax for the reduction of pollutants) |
Seldom educational, as it can be interpreted as a "right to pollute"
Concerning the development of the tourism sector, operators are already subject to obligation to avoid, reduce and compensate damages to the environment |
Royalty on diving activities | Positive image from alerted and sensitized persons, usually willing to pay extra if their participation in the reserve is transparent Widely favourable view of diving operators in the area, willing to raise the average price per dive |
Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Royalty on taxi-boats, recreational and private sailing boats | Taxation affects primary beneficiaries of the reserve (through tourism increase), the acceptability of such a tax should be good Can be done through various taxes and lead to development (tax for the access to mooring buoys in the reserve) | Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Assignment of an existing tax | ||
Share of the tourist tax of the municipality of le Prêcheur | Tourism in the area is closely related to visitation of natural resources, particularly marine resources Figures of tourism increasing, potential source of growing incomes Highlight the willingness of local authorities to participate in the implementing of the reserve Opportunity for neighbouring municipalities (Saint-Pierre, Grand Rivière, Cabaret, etc.) to devote part of their tourist tax to the reserve |
Little profitable as long as visitation and supply of accommodation are limited in capacity Difficult to arbitrate for the reallocation of a share of the tax to the reserve Participation of neighbouring municipalities to the reserve presumably difficult |
Share of dock dues | Taxation of all products sold in French overseas – modulation of the rate based on environmental impact of products | Difficult to justify the financing when dock dues ought to help in economic development Advocacy work needed for an arbitration in favour of the reserve and at the expense of the financing item which loses the income of the tax |
Share of the tax on marine polluting activities | Polluter-payer principle extended to the region: polluting activities must be subject to financial compensation Gives a fiscal preference to non-polluting regional activities (idea of a partial tax exemption for reduction of pollutants) | Lack of acceptability of activities not directly linked with le Prêcheur (e.g. Intensive agriculture of southern Martinique) |
Broadening of the rate of an existing tax | ||
Broadening of the airport tax | Can generate very high revenues at a low cost per person Attachment to marine ecosystems of airport passengers, tourists or inhabitants | Airport taxes usually intended to upgrade safety and comfort of passengers; can pose problems of arbitration of tax revenues thus needs an expansion and not a modification of assignment |
Broadening of the transportation tax | The possibility of a justification of an environmental approach of transport helps social acceptance of the broadening of the tax | Political and legislative difficulties of broadening the rate of an existing tax |
Source: authors own creation. |
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General valuation | |
Introduction of a new tax/royalty | |
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | 0 |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality |
−1 |
Tax on extractive and/or damaging of the reserve activities (fishing, spearfishing) | −3 |
Tax on polluting activities of the watershed | 1 |
Royalty on diving activities | 7 |
Royalty on taxi boats, recreational and private sailing boats | 8 |
Assignment of an existing tax | |
Share of dock dues | 2 |
Share of the tourist tax | 6 |
Share of the tax on polluting activities | 2 |
Broadening of the rate of an existing tax | |
Broadening of the airport tax | 7 |
Broadening of the transportation tax | 2 |
Source: authors own creation. |
Knowledge of fishermen | Ecotourism | Scientific monitoring and MPA management |
Physical characteristics, behaviour and habits (feeding, habitat, spawning grounds) of fish (ethology) | X | X |
Spawning grounds | X | |
Fish life cycles (breeding and migration seasons) | X | |
Impact of abiotic factors (hydraulic, oceanographic, climatic) on fish life cycle | X | |
Adaptive and resiliency capabilities of the marine environment to climate change | X | |
Endangered species | X | X |
Health status of the marine environment (coral bleaching or algal invasion for example) | X | |
Evolution of the fishery resource with notably species rotation, disappearance or appearance (lion fish), etc. | X | |
Rhythm, temporality et cycle of fishing seasons and species presence | X | |
Interconnections between species (between fish species but also between fish and plants) | X | |
Impact of human activities on the marine environment | X | |
Source: authors own creation. |
Level | Budget (million €) | Notes |
State | 28.1 | Allocated budget, program 113 action 7* |
French Marine Protected Areas Agency |
1 | - |
French Coastal Protection Agency | 40 | €2.4 million of which come from repayments of the state and €37.6 million come from an individual taxation regime |
Other operators | 5 | - |
Total State + operators | 74.1 | In comparison, the total state budget allocated to the conservation of natural areas and water management amounts to €2447 million |
Source: Translated from Badré M and Duranthon JP, 2010. *Current financial resources allocated by the state to the budget for biodiversity policies are partly addressed by action 7 "management of environments and biodiversity" program 113 of the Ministry of Ecology, Energy, Sustainable Development and the Sea. |
The tax is levied from the provision of a service. It may be required not only from actual users but also from potential users and the amount is not strictly equivalent to the service provided (e.g. tax for household waste collection). The tax is provided by the law. Royalties (or remuneration) for services rendered are received in return for a service, such as the use of a piece of work or a benefit provided by a public service to a user while bearing the cost, and therefore must match the value of the benefit or service. A royalty can be established through regulation. The amount of the royalty must be equivalent to the value of the benefit or proportional to the cost of the service rendered. Such is the case of the "institution of a royalty comprising of a fixed part and a variable part, provided that the calculation of the fee allows to ensure the proportionality with the cost of the service rendered" (EC No. 220803 of July 9 2009). 'Respect for the rule of equivalence between the fare of a royalty and the value of the benefit or service can be ensured by withholding the cost of the latter, but also according to the characteristics of the service, by taking into account the economic value of the benefit to the recipient; that in all cases, the fare must be established according to objective and rational criteria, in full conformity with the principle of equality between the users of public services and the competition rules (EC No 309 499 of 7 October 2009). Environmental royalties can be defined as payment for environmental services: in return for their payment, the taxpayer receives an environmental service. As pollution could be interpreted as a particular use of a natural resource (right to pollute), a levy associated with a degradation of the environment can then be likened to a royalty. The distinction between taxes and royalties is also based on the allocation of revenues. Into the general budget for the first case, revenues are earmarked for specific purposes in the case of royalties. Yet, in the field of environmental taxation, these two aspects of distinction between taxes and royalties are not systematically combined. This explains why these two terms are sometimes interchangeably used. |
Introduction of a new tax or royalty | Assignment of an existing tax | Broadening of the rate of an existing tax | ||
Regional scale | Residential tourists | Tax to finance regional reserves of Martinique (on the template of the tourist tax) | Share of the tourist tax of the municipalities of Martinique | Broadening of the airport tax; broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance regional reserves of Martinique (on the template of the housing tax) | Share of dock dues | Broadening of the airport tax; broadening of the transportation tax | |
Marine ecosystem users | Tax on uses of the ecosystems of Martinique (in addition to fishing licences for e.g.), tax on offshore recreational practices (surf, kitesurf, etc.) | Share of revenue of fishing licences | Broadening of fishing licences | |
Corporations that pollute | Taxes on polluting activities in Martinique that have impacts on marine ecosystems (urbanisation coastal fringe, granulate extraction, non-biological agricultural activities, etc.) | Share of the tax on marine polluting activities | Broadening of the tax on polluting activities | |
Local scale (area of the reserve and surrounding area) | Residential tourists | Tax to finance the RNR of le Prêcheur enforceable to tourist operators of the municipality (on the template of the tourist tax) | Share of the tourist tax of the municipality of le Prêcheur | Broadening of the transportation tax |
Inhabitants of Martinique | Tax to finance the RNR of le Prêcheur enforceable to the inhabitants of the municipality (on the template of the housing tax) | Share of the housing tax of the municipality of le Prêcheur | Broadening of the transportation tax | |
Marine ecosystems users | Local tax on extracting and/or damaging of the RNR activities (fishing, spearfishing); royalty on diving activities; royalty on taxi-boats, recreational boats and private sailing boats | n.a. | n.a. | |
Corporations that pollute | Tax on polluting activities of the watershed | n.a. | n.a. | |
Note: n.a. = not applicable; Source: authors own creation. |
Strengths | Weaknesses | |
Introduction of a new tax/royalty | ||
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | Tourism figures increasing, potential source of growing incomes Potential modulation of the rate based on the environmental impact of the operator |
Penalises supply of tourism services of the municipality of le Prêcheur only, already seldom developed Potentially penalises visitors that are non-users of marine ecosystems (e.g. Hikers) |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality | Empowers inhabitants on the impact of their everyday practices on the ecosystem Potential modulation of the rate based on the environmental impact of the building | Penalises the inhabitants of the municipality of le Prêcheur only, potentially making the area less attractive Potentially penalises the inhabitants that are non-users of marine ecosystems (e.g. Hikers) |
Local tax on extractive and/or damaging of the RNR activities (fishing, spearfishing) | Reduces through a fiscal leverage the extractive activities and other damaging practices while producing revenues for the reserve Enables guidance by incentives for reorientation of fishermen or discontinuing of damaging practices (frequent use of beach-seine for example) |
Low acceptability upon populations of fishermen and underwater hunters already affected by management actions Difficult to weigh the burden of a tax only on fishermen and underwater hunters Revenues of this tax are destined to decrease, thus jeopardizing the financing Penalises operators who take measures voluntarily (eco-responsible construction, choice of a fishing net with larger mesh, etc.) |
Tax on polluting activities of the watershed | Polluter-payer principle: polluting activities must be subjected to financial compensation; to go further, it is possible to implement a payment for ecosystem services: polluting activities fund the reserve for improvement of the treatment of waste produce by these activities; enables to give a tax preference to non-polluting local activities (idea of a partial exemption from tax for the reduction of pollutants) |
Seldom educational, as it can be interpreted as a "right to pollute"
Concerning the development of the tourism sector, operators are already subject to obligation to avoid, reduce and compensate damages to the environment |
Royalty on diving activities | Positive image from alerted and sensitized persons, usually willing to pay extra if their participation in the reserve is transparent Widely favourable view of diving operators in the area, willing to raise the average price per dive |
Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Royalty on taxi-boats, recreational and private sailing boats | Taxation affects primary beneficiaries of the reserve (through tourism increase), the acceptability of such a tax should be good Can be done through various taxes and lead to development (tax for the access to mooring buoys in the reserve) | Cannot be the only measure because: i) little profitable and ii) it shows a taxation disparity of one activity without taxing the others (fishing, swimming on beaches, access, etc.) |
Assignment of an existing tax | ||
Share of the tourist tax of the municipality of le Prêcheur | Tourism in the area is closely related to visitation of natural resources, particularly marine resources Figures of tourism increasing, potential source of growing incomes Highlight the willingness of local authorities to participate in the implementing of the reserve Opportunity for neighbouring municipalities (Saint-Pierre, Grand Rivière, Cabaret, etc.) to devote part of their tourist tax to the reserve |
Little profitable as long as visitation and supply of accommodation are limited in capacity Difficult to arbitrate for the reallocation of a share of the tax to the reserve Participation of neighbouring municipalities to the reserve presumably difficult |
Share of dock dues | Taxation of all products sold in French overseas – modulation of the rate based on environmental impact of products | Difficult to justify the financing when dock dues ought to help in economic development Advocacy work needed for an arbitration in favour of the reserve and at the expense of the financing item which loses the income of the tax |
Share of the tax on marine polluting activities | Polluter-payer principle extended to the region: polluting activities must be subject to financial compensation Gives a fiscal preference to non-polluting regional activities (idea of a partial tax exemption for reduction of pollutants) | Lack of acceptability of activities not directly linked with le Prêcheur (e.g. Intensive agriculture of southern Martinique) |
Broadening of the rate of an existing tax | ||
Broadening of the airport tax | Can generate very high revenues at a low cost per person Attachment to marine ecosystems of airport passengers, tourists or inhabitants | Airport taxes usually intended to upgrade safety and comfort of passengers; can pose problems of arbitration of tax revenues thus needs an expansion and not a modification of assignment |
Broadening of the transportation tax | The possibility of a justification of an environmental approach of transport helps social acceptance of the broadening of the tax | Political and legislative difficulties of broadening the rate of an existing tax |
Source: authors own creation. |
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General valuation | |
Introduction of a new tax/royalty | |
Tax for the financing of the RNR of le Prêcheur enforceable to tourist operators of the municipality | 0 |
Tax for the financing of the RNR of le Prêcheur enforceable to inhabitants of the municipality |
−1 |
Tax on extractive and/or damaging of the reserve activities (fishing, spearfishing) | −3 |
Tax on polluting activities of the watershed | 1 |
Royalty on diving activities | 7 |
Royalty on taxi boats, recreational and private sailing boats | 8 |
Assignment of an existing tax | |
Share of dock dues | 2 |
Share of the tourist tax | 6 |
Share of the tax on polluting activities | 2 |
Broadening of the rate of an existing tax | |
Broadening of the airport tax | 7 |
Broadening of the transportation tax | 2 |
Source: authors own creation. |
Knowledge of fishermen | Ecotourism | Scientific monitoring and MPA management |
Physical characteristics, behaviour and habits (feeding, habitat, spawning grounds) of fish (ethology) | X | X |
Spawning grounds | X | |
Fish life cycles (breeding and migration seasons) | X | |
Impact of abiotic factors (hydraulic, oceanographic, climatic) on fish life cycle | X | |
Adaptive and resiliency capabilities of the marine environment to climate change | X | |
Endangered species | X | X |
Health status of the marine environment (coral bleaching or algal invasion for example) | X | |
Evolution of the fishery resource with notably species rotation, disappearance or appearance (lion fish), etc. | X | |
Rhythm, temporality et cycle of fishing seasons and species presence | X | |
Interconnections between species (between fish species but also between fish and plants) | X | |
Impact of human activities on the marine environment | X | |
Source: authors own creation. |