Community Perception of Riparian Corridors Ecosystem Services and Implications for Environmental Education in Upper Oueme Catchment in Benin, West Africa

Abstract

The assessment of the local community perception of the value of riparian corridors is relevant to understand their attitude towards the conservation of such ecosystem. We conducted a semi-structured survey on the perception and importance attributed to the ecosystem services (ESs) provided by riparian corridors in 368 households across 70 villages located in a buffer zone of 5 km of servitude around the permanent rivers of the Upper Oueme watershed in Benin. We found that local communities easily reported provisioning and cultural ESs than regulating and supporting ones, indicating their misunderstanding of the main role of riparian corridor. Moreover, the supply of cropping areas was perceived as the most important ES. Educated respondents and high-income households had more knowledge of regulating ESs and supporting ESs, respectively. Overall, the highly perceived importance of the provision of cropping areas indicates a potential risk of agricultural encroachment of riparian corridors. We suggest the consideration of the current local perception of riparian corridor’s role in designing a sound environmental education aiming at the change of local population’s perception. This perception shift will promote a sustainable management of the riparian corridors.

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Kinnoumè, S. , Adomou, S. , Gouwakinnou, G. and Houéhanou, T. (2024) Community Perception of Riparian Corridors Ecosystem Services and Implications for Environmental Education in Upper Oueme Catchment in Benin, West Africa. Open Journal of Ecology, 14, 125-147. doi: 10.4236/oje.2024.142008.

1. Introduction

Maintaining ecosystem services in the face of global environmental changes and human pressures on the world’s natural resources remains a major challenge. Despite the worldwide recognition of the services and functions that forest ecosystems provide, forest degradation continues at an alarming rate, as a result of human-induced changes in the stability of ecosystem functions at the local and global levels [1] [2] [3] [4] . This forest degradation leads to a rapid decline in the quality of ecosystem services (ESs) [5] and exacerbates biodiversity loss [6] [7] . In this regard, recent studies have demonstrated the importance of restoring ecological systems to support the continuous provisioning of ESs to human being [8] [9] [10] . Several land restoration strategies have been used to restore the ESs provided by forests [5] [11] including natural regeneration [12] , agroforestry systems [13] and watershed rehabilitation [14] . These restoration approaches depend strongly on the levels of forest degradation and the factors driving ecosystem change [12] . Although it is well acknowledged that the drivers of ecosystem changes are spatially heterogeneous and depend on the socio-economic characteristics of human communities, our knowledge of the importance that local communities attribute to the ESs is still limited [2] [15] . Given the dynamics and complexity of the interaction between people and ecosystems across spatial scales, additional insights on the range of ESs as well as the community perception of their importance in important ecosystems and areas that have received little attention are urgently needed. Knowledge of local perceptions is increasingly said to be effective and reasonable in guiding decision-makers towards ecological sustainability, economic efficiency and social justice [16] .

Several integrated approaches have been implemented to assess ESs. Such integrated methods combined ecological approaches that focus on the biophysical properties of ecosystems with social approaches that emphasize the value society places on different ESs, and economic approaches that consider the monetary value of ESs [17] - [22] . Often, the assessment of ESs is more oriented towards the ecological and/or economic approaches than the social approach [23] , while the latter is crucial to understand the complex socio-ecological systems [16] [24] . The social approach requires the consideration of stakeholders in order to ensure the optimal provisioning of ESs and the restoration of degraded ecosystems. Taking into account the perceptions of the local community in the early stages of ecosystem restoration process allows to maximize conventional restoration objectives and increase the supply of ESs to forest-dependent people [25] . The concept of ESs, which has recently extended to include the concept of nature’s contribution to humans, was invented to highlight the links between ecosystem health and human well-being [26] . The different categories of ESs [10] interact to generate benefits for humans in terms of providing livelihoods, regulating ecological systems, and supporting human life and well-being [27] [28] . Maintaining these benefits to ensure a good quality of life for human societies has been one of the main motivations of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) [29] .

Several authors have emphasized the consideration of local knowledge and perceptions as a basic tool in decision-making policy for ecosystem protection, sustainable resource management and livelihoods [30] [31] [32] . For example, an examination of the differences in perceptions of the provision and diversity of ESs showed that cultural, provisioning and regulating services are best known in various types of major ecosystems in Spain [26] and around forest reserves in northern Benin [33] . Therefore, it is obvious that perception of ESs plays a role in shaping local people’s attitude toward ecosystems use and management.

Non-direct ESs such as supporting and regulating services are generally less known to local communities, but are important for improving production systems and ensuring the sustainability of other services [33] . Riparian forests undoubtedly offer contextual conditions that are very appropriate to evaluate indirect services because they primarily serve not only as a refuge for biodiversity and habitat for many ESs (e.g., control of hydro-geomorphological dynamics, cooling of air and water, filtration of pollutants, carbon storage, provision of food or materials, etc.), but also as corridors (“riparian corridors”) of dispersion of individuals and genes through the landscapes owing to their serpentine structure along the hydrographic networks of watersheds [34] . These ecological functions of the riparian corridors are even more relevant in arid and semi-arid areas, since they can help buffer the effects of water scarcity and provide environmental conditions similar to those prevailing in wetland ecosystems [35] . Despite their importance, particularly for arid and semi-arid zones, riparian forests have been neglected in development efforts as they are often considered as alternative land use option for the development of human activities [34] . Moreover, the perception of the riparian forests’ ESs by local populations, who are the main actors in forest management and the first direct beneficiaries of these ESs, remains unexplored. Understanding how local stakeholders perceive the ESs provided by riparian forests is essential for establishing management strategies that optimize and ensure the proper functioning of these corridors as well as for predicting potential conflicts resulting from heterogeneous demand of ESs and the values attributed to them [36] [37] .

This study aims to understand 1) the local communities’ knowledge and perceived importance of ESs provided by the riparian corridors of the Upper Oueme watershed in northern Benin and 2) the factors that affect the ability of the local people to perceive ESs and their importance. This study will provide new insights on the importance of knowledge and perception of ESs for the sustainable management of the riparian corridors. In this perspective, we asked three main research questions: 1) How do the communities around the riparian forests identify and perceive the importance of the ESs provided by the riparian corridors? 2) Which factors explain variations in the perception of ESs? Finally, we discuss the implications of our findings for environmental education and the sustainable management of riparian corridors in Sudanian zones.

2. Methodology

2.1. Study Area

The study was carried out in the Upper Oueme watershed, which is located at the outlet of Bétérou in the North Benin, between 9˚9' and 10˚11' north latitude and 1˚30' and 2˚48' east longitude (Figure 1). The watershed covers an area of 10,140 km2. The climate type in the area is Sudanian, characterized by one rainy season (from mid-March to October) with a peak in August and one dry season for the rest of year [38] [39] [40] . The average rainfall in the study area is about 1160 mm over the period 1961-2010 [39] . Ferruginous soil is the dominant soil type of the watershed [39] .

The landscape of the Upper Oueme watershed is characterized by savannas, cropping lands, and gallery forests along the rivers pastures [39] . It includes three agro-ecological zones (AEZ) [41] : Zone III (South Borgou Food Zone), Zone IV (West-Atacora Zone) and Zone V (Cotton zone of central Benin). These AEZs are subjected to various agro-pedological constraints and different cropping systems. Yam (Dioscorea rotundata P), cotton (Gossypium hirsutum L), maize (Zea mays L) and groundnut (Arachis hypogaea L) are the most cultivated crops in the AEZs. Increasingly, all these areas are engaging in the intensification of cotton cultivation. The local populations in the study area consist of a diversity of ethnic groups (Lokpa, Bariba, Peulh, Nago, Fon and Natimba) with different cultural practices.

2.2. Data Collection

A survey was conducted to collect the data. Three buffer zones of 1, 3 and 5 kms of width were delineated on both sides of the permanent rivers of the Upper Oueme watershed and the residents of the villages that are located within the buffer areas were considered for the survey (Figure 1; Table 1). A sampling rate of 25% of the villages in each buffer was applied [2] [42] and the sampling villages were randomly chosen. A total of 70 villages were selected out of 280 (Table 1). The normal approximation of the binomial distribution of [43] was used to determine the number of sampling households according to the following Equation (1):

N = μ 2 1 α 2 P i ( 1 P i ) δ 2 (1)

where Pi is the proportion of households active in the riparian corridors and which are involved in the primary sector (e.g., agriculture, fishing, hunting); μ 1 α / 2 = 1.96 is the value of the normal random variable for a risk α equal to 0.05; δ = 5% is the expected margin of error. This equation was adopted because it has been widely used in studies assessing the knowledge and perception of local communities on forest ecosystems [2] [42] [44] [45] . Pi was determined through a prospective survey in the selected villages based on a random sample of 40 households and was equal to 60%. A total of 368 households were surveyed in the 70 villages, belonging to 8 districts: Copargo, Djougou, N’dali, Ouassa-Pehunco, Sinendé, Tchaourou, Bembèrèkè, Parakou (Table 1).

The respondents were heads or representatives of households, aged 20 or older. The surveys focused on socio-economic characteristics (age, gender, occupation, ethnicity, income level and education level) and the local communities’ perception of the values of the riparian corridors. The latter was assessed using a free listing technique [26] [45] . This resulted in a list of environmental benefits mentioned by respondents known as ESs. The listed services have been classified in the four ES categories (provisioning, regulating, cultural and supporting) of the Millennium Ecosystem Assessment [10] . The respondents were also asked to assess the importance of the perceived ESs based on a four-level score scale (1 for not important and 4 for extremely important). To take into account the culture of the riverside villages, respondents were asked to indicate whether they practice any religious activities (e.g., worshipping) in the corridor (Table 2).

Table 1. Sampling characteristics.

Figure 1. Location of the study area and selected villages.

Table 2. Characteristics of the 368 households surveyed in the riparian corridors of the Upper Oueme watershed of Benin.

2.3. Data Analysis

The perception of ESs was assessed by calculating the citation frequency of each service per ES category (provisioning, regulating, supporting and cultural). The citation frequency was the ratio of the number of times a given service was cited to the total number of investigated households.

To assess the relationship between ethnic groups and the recorded ESs, we develop a matrix of ESs citation frequency, with each row representing a unique ethnic group and each column representing a service recorded in our survey. The matrix was submitted to a Principal Component Analysis (PCA) using the package FactoMineR. Specific benefits of riparian corridors, defined as ESs that differ from those obtained from other ecosystems, were assessed per AEZ and gender categories by calculating the frequencies of citation of the benefits accordingly.

We identified the determinants of respondents’ perception of ESs by running a Generalized Linear Model (GLM) using the package MASS [46] . We used a negative binomial error distribution to account for overdispersion in our model. The response variable was the number of ESs citation and the explanatory variables included age, gender, ethnicity, religious practice, level of literacy, occupation, seniority in the village, income level (Table 2). We defined three age categories following [47] : young (<30 years), adult (30 - 60 years) and old (>60 years). Similarly, we defined three income levels: low, middle and high on a scale of 1 to 5, of which the average (2 to 3) corresponds to the mean annual income per capita in Benin [48] . On this basis, the respondent attributed the score corresponding to his annual income over the last two years by comparing this income to the annual mean income per capita in Benin. A score of less than 2 corresponded to a low income, a score greater than 3 corresponded to a high income, and a score between 2 and 3 corresponded to a middle income.

To evaluate the perception of ESs importance, a four-Likert scale was defined based on the score values recorded in the field. The four level of importance included: not important (1), somewhat important (2), important (3), and extremely important (4). We ran an ordinal logistic regression model [49] to test the unique effect of each factor and identify the most influential determinants of the importance of the ESs.

3. Results

3.1. Local Communities’ Perception of Ecosystem Services

In general, the local community had a good knowledge of provisioning ESs (55%), followed by cultural ESs (23.5%), regulating ESs (19.1%) and support ESs (2.4%) (Figure 2). The provisioning of cropping areas (95.9%), medicinal plants (92.1%) and fodder (91.8%) were the most perceived provisioning services compared to the other services. Cultural and regulating services such as cultural practices (59.8%) and storm control (55.4%) were equally well recognized. Soil formation was the only recognized supporting service and was perceived by only 8.4% of respondents.

The PCA results showed that 74% of the relationship between ESs and ethnicities was explained by the first two axes (Figure 3). This percentage reflects a strong association between the ESs and ethnic groups. The first axis opposed the Yom, who better recognized cultural ESs (e.g., preservation of spiritual values

Figure 2. Citation frequency (%) of different ES categories by the local communities along the riparian corridors of the Upper Oueme watershed of Benin.

Figure 3. Biplot of the principal component analysis (PCA) showing the correlation between the socio-cultural groups and ecosystem services (ESs).

and cultural practices) to the Bariba, whom perception was more oriented towards the provisioning ESs (e.g., fish collection), supporting ESs (e.g., soil formation) and regulating ESs (e.g., control of diseases and parasites). The second axis opposed the Peulh to the other ethnic groups, which included the Nago, Fon, Dendi, Wama, Adja, Zerma and Natimba. The other groups represented the minority (7.33%) of the population. The Peulh had a better perception of the provisioning ESs (e.g., livestock feed and fresh water) compared to the other ethnic groups, who recognized better the regulating ESs (e.g., storm control, noise mitigation) and cultural ESs (e.g., ecotourism).

3.2. Perceived Benefits Specific to Riparian Corridors

Beyond the ESs that other forest ecosystems provide, the local communities in the study corridors identified some specific benefits that led them to exploit the resources in the corridors. These benefits included: high crop yield with low chemical fertilizer inputs, soil moisture availability, high soil fertility, possibility for off-season cropping, supply of freshwater for irrigation and provision of cropping areas. These specific benefits were unanimously mentioned by both men and women (Figure 4).

3.3. Importance Value of Ecosystem Services Perceived by the Local Community

Soil formation was the only supporting ES cited in this study by the local community and was the second most important recognized ES category after the provisioning ES category. The cultural ES category was the least important (Table 3). Among the provisioning ESs, food resource, medicinal plants, cropping areas, wood energy and fresh water were considered most important (importance value above average), while ornamental resources and fodder were perceived as least important (importance value below average; Table 3). Among the regulating ESs, disease and pest control, erosion regulation, protection against storms and pollination were perceived as more important than waste treatment and noise reduction. In the cultural ES category, the cultural practice, education and spiritual value were perceived as more important than ecotourism.

Figure 4. Perception of corridor-specific benefits by the local communities according to gender. Moisture: soil moisture availability; Fertility: high soil fertility; Yield: high crop yield; Water: supply of fresh water; Herds watering: availability of water for herds watering; Crops: provision of cropping areas; Off season: possibility for off-season cropping; Bamboo: bamboo availability; Fishing: possibility for fishing.

Table 3. Importance value of provisioning, regulating, supporting and cultural ecosystem services (ESs) specific to riparian corridors of the Upper Oueme watershed of Benin, as perceived by local communities. Shown are mean and standard deviation (SD) of the scores assigned to each ES based on the four-Likert scale (1 - 4).

ES = Ecosystem Services, SD = Standard Deviation.

3.4. Factors Influencing the Perception of Ecosystem Services Category

With regards to the socio-economic factors, the results revealed that the older respondents reported the regulating ESs more than the adult and young respondents (β = 0.24, p < 0.01, Figure 5(a), Table 4). Moreover, the young respondents identified less the cultural ESs than the adult respondents (β = −0.36, p < 0.05, Figure 5(b), Table 4). The livestock herders recognized the cultural ESs more than the crop farmers and other occupational groups (β = 0.86, p < 0.01, Figure 5(c), Table 4). In contrast, the crop farmers were those who identified the regulating ESs the most (Figure 5(d)). The importance of the seniority was also highlighted in the identification of ESs, since the households with more than 20 years of seniority in the village recognized the regulating ESs the most (β = 0.39, p < 0.05, Figure 5(e), Table 4). Finally, the level of the income significantly influenced the identification of the cultural and supporting ESs. The low-income households recognized the cultural ESs the most (β = 0.39, p < 0.01, Figure 5(f), Table 4). Similarly, the low-income households recognized the supporting ESs the most (β = 0.14, p < 0.01, Figure 5(g), Table 4).

Figure 5. Boxplots showing the distribution of the identification of ecosystem services (ESs) and socio-economic (age, occupation, seniority and income) factors in the riparian corridors of the Upper Oueme watershed of Benin. RS = Regulating Services, CS = Cultural Services, SS = Supporting Services.

Table 4. Results of the Generalized Linear Model (GLM) with negative binomial error distribution, showing the effect of socio-economic variables on the identification of ESs by the local communities inhabiting the riparian corridors of the Upper Oueme watershed of Benin. PS: Provisioning Service; RS: Regulating Service; CS: Cultural Service SS: Supporting Service.

* p < 0.05. ** p < 0.01. *** p < 0.001, PS = Provisioning Service, RS = Regulating Service, CS = Cultural Service, SS = Supporting Service, SE = Standard Error, β = Regression coefficients.

3.5. Factors Shaping the Relative Importance Given to Ecosystem Services Category

Several factors have determined how local communities perceived the importance of ESs. The influence of these factors on the perceived importance of ESs varied between the ES categories (Table 5). The local communities worshiping in the riparian corridors recognized less the importance of regulating ESs than non-believers (β = −0.63, p < 0.05). Also, the level of literacy has significantly influenced the perceived importance of regulating and supporting ESs. On the one hand, illiterate respondents perceived the importance of regulating ESs less than those who had basic education (literate; β = −0.85, p < 0.05), while those who had formal education recognized more the importance of regulating ESs than literate people (β = 1.81, p < 0.001). On the other hand, the illiterate respondents perceived the importance of supporting ESs the most (β = 1.05, p < 0.05). Finally, the level of income influenced the perceived importance of the supporting ESs, with the low-income households being the least aware of the importance of these ESs (β = −1.05, p < 0.05).

4. Discussion

4.1. Perception of Ecosystem Services and Their Importance to Local Communities

Our findings support the opinion that exploring perception within the local community is an effective way to understand traditional ecological knowledge, with implication to ecosystem management [31] [32] [50] . Our results demonstrated that local communities living in the riparian corridors of the Upper Oueme watershed were very attached to the resources provided by the riparian forests, as also reported in previous studies [51] [52] [53] . The local communities identified more easily the most direct ESs (provisioning and cultural) than the indirect (regulating and supporting), likely because of their heavy dependence on these services to maintain their livelihood and cultural values [15] [33] [47] . Indeed, the riparian corridors harbor a great diversity of multi-use plant resources, which are highly valued by local communities. An example is Pentadesma butyracea (Sabine), which is highly valued for its social, cultural and economic importance [54] . The riparian corridors also provide freshwater for irrigation [55] . As reported by the local communities, the corridors provide favorable

Table 5. Results of the ordered logistic regression, showing the effect of socio-economic and environmental factors on the perceived importance of ESs provided by the riparian corridors of the Upper Oueme watershed of Benin.

* p < 0.05. ** p < 0.01. *** p < 0.001, AEZs = Agro-Ecological Zones, PS = Provisioning Service, RS = Regulating Service, CS = Cultural Service, SS = Supporting Service, SE = Standard Error, β = Regression coefficients.

conditions for off-season cropping due to the year-round availability of water and prevailing soil moisture. The recognition of the prevalence of high soil fertility in the corridors suggests that the local communities had a good knowledge of the supporting ESs in addition to that of the provisioning and cultural ESs. This knowledge allows them to adopt management strategies that are still not sustainable, as they are confronted with the cumulative effects of climate change [56] and anthropogenic activities [57] .

This study shows a strong association between the perception of ESs and ethnicity. The Yom people, who perform more worshipping activities in the riparian corridors than the other ethnic groups, had a very good knowledge of cultural ESs as opposed to the Bariba (farmers in majority), for whom the perception was more diversified but oriented towards the provisioning, supporting and regulating ESs. The Peulh (herders) identified the provisioning ESs (livestock feed and fresh water) mostly. Because of their socio-cultural affiliation, the Peulh are not only nomadic cattle herders looking for new rangelands to graze their animals, but they also live in camps within forest areas and corridors. This divergence in the perception of ESs between socio-cultural groups suggests the need to account for socio-cultural differences in the design of programs aimed at sustaining the supply of ESs by the riparian corridors.

As reported by several studies [33] [58] [59] , the local communities in the study area recognized the importance of provisioning ESs, confirming the idea that the local communities tend to give the highest priority to the most tangible, easy-to-collect services to meet their basic needs [59] . However, although soil formation is the only supporting ES cited in this study by the local communities, this category of ES was recognized as the second most important ES, followed by the regulating ESs (Table 2). Similar results were reported in Ethiopia [34] , where local communities living around Lake Ziway also ranked the provisioning and supporting ESs at the top of the priority. Among all the enumerated ESs, the provisioning ESs and particularly the supply of cropping areas were the most recognized and important ESs by the local communities in the study area. With regard to the primary roles of the riparian corridors which consist in supplying supporting and regulating ESs and ensuring the dispersal of individuals of animal species and genes across the landscape [34] , the greater value assigned to the provisioning ESs points to a potential risk of fragmentation of the riparian corridors if agricultural encroachment is not prevented. Considering that the installation of cropping areas into the riparian corridors is forbidden by the forest legislations of Benin (Law No. 93-009 of 2 July 1993 on forest regime in the Republic of Benin; Law No. 2013-01 of 14 August 2013 on the Land and State Code in the Republic of Benin), our result also highlights a weak enforcement of the existing laws and regulations related to the protection of riparian corridors. Overall, our findings on the perception and importance of ESs suggest a potential risk of an unsustainable use of riparian corridors.

4.2. Effects of Socio-Economic and Environmental Factors on the Perception of Ecosystem Services and Their Importance to Local Communities

Socio-economic and environmental factors influenced the perception of ESs and their importance in the riparian corridors of the Upper Oueme watershed in Benin. We found that the socio-economic and environmental factors did not influence the identification of provisioning ESs (Table 4). The provisioning ESs are tangible services and were more recognized by the local communities than the other categories of ESs (Figure 2), as previously reported [33] [60] [61] . Moreover, the provisioning ESs are directly involved in the physical, economic and social well-being of the community [15] . Therefore, the lack of significant effect of socio-economic factors on the identification of the provisioning ESs could be attributed to the homogeneity of knowledge on these services across various socio-economic groups. This result suggests that the perceived importance of ESs of an ecosystem by local communities is also determined by the utilitarian value that these services bring them.

The age of the respondents significantly influenced the identification of the regulating ESs but not the perception of their relative importance. The higher citation of the regulating ESs by older people than the adults and youth, underlines the central role that experiential local knowledge plays in the identification of ESs. Studies assessing changes in ecosystems reported that older people have a history and experience with their environment [2] . The accumulation of traditional ecological knowledge is a lifelong process, indicating that older people had more time to acquire it [62] . Cultural ESs such as cultural practices, education and spiritual value gained more interest from the local communities around the riparian corridors although this category of ES was perceived to be less important. The cultural importance of forests reflects the positive attitudes of the local communities towards its conservation [41] . Thus, the interest in cultural practices and spiritual values observed in this study, which was also recognized for forests and trees in Africa [63] , may be an asset in the protection of riparian corridors. Furthermore, the better identification by older people and adults compared to youth reflects a low transmission of the cultural and spiritual values related to riparian forests between generations.

The identification of ESs was also influenced by the type of profession, since the farmers had a better knowledge of the regulating ESs than the herders and other socio-professional workers (traders, artisans, carpenters, etc.). Similar findings were reported by previous studies [61] [64] . This indicates that farmers are aware of the impact of poor agricultural practices (slash-and-burn farming, pesticide use) on the provision of regulating ES. It also emerged from our results that seniority was a significant predictor of local knowledge on the regulating ESs, which is in line with the findings of previous studies [65] . For instance, [41] found that plant knowledge and evaluation were the lowest among migrants. Studies on the drivers of sustainable harvesting of Syagrus coronata (Mart) Becc. (Ouricuri palm) leaves in northeastern Brazil came to the same conclusion that local harvesters tend to harvest leaves more sustainably than non-indigenous people [66] . Increasingly, more people are settling down in the riparian corridors in the quest of wet and fertile lands and livestock feed [52] . However, the migrants (defined in our study as people with <20 years of seniority) are less aware of the usefulness of adopting sustainable ecosystem management strategies [66] [67] that guarantee the maintenance of the ecological functions of riparian ecosystems.

We also observed that low-income households were less likely to recognize the importance of the supporting ESs than the high-income households, but they had a better knowledge of the supporting and cultural ESs than the high-income households. This result is in agreement with previous studies reporting that the wealthiest groups perceived the importance of soil protection and fertility [41] . The United Nations Development Program (UNDP, 2022) found that the poorest local populations were not aware of the close links between agriculture and the ESs provided by forests. Although low-income households had a better knowledge of supporting ESs than high-income households, these ESs were not as much important for them probably because they have limited resources to engage in intensive farming activities. It could also be that low-income households valued more other income-generating activities (e.g., fishing, crafting). The finding that the supporting ESs were more important for the high-come households likely reflects the ability of wealthy households to crop large areas to maximize yields and increase their incomes due to the favorable edaphic conditions (high soil fertility and humidity) prevailing within the riparian corridors, as mentioned by the respondents. This suggests that the wealth conditions of rural households characterize the demand for resource exploitation and the perceived importance of ESs.

The level of education also influenced the perception of the importance of the regulating ESs. The fact that the uneducated respondents mentioned the regulating ESs less than those who were literate or received a school education reflects the link between education level and environmental sensitivity [68] . The same results were reported by [41] and [41] . In Benin, in addition to the environmental concepts inserted in the curricula of school training, the annual celebrations of the various statutory days related to the environment (e.g., International Day of Forests, International Day of Biodiversity, National Tree Day, World Environment Day, World Day to Combat Desertification and Drought) through the development of several topics on the importance of forests or biodiversity for communities, are usually held in schools or educational centers. This likely resulted in the high level of awareness of educated respondents. Finally, we also found that the regulating ESs were less important to the respondents who practiced cultural and religious activities within the corridors. This finding may be explained by the lower level of education of the cultural and religious practioners (56% of the practioners were illiterate whereas the proportion of ilitrate non-practioners amounted to 38%), since our results similarly revealed that ilitrate respondents had a lower perception of the importance of regulating ESs than the litrate ones (Table 5).

4.3. Implications of the Findings for the Management of the Ecosystem Services Provided by the Riparian Corridors

The social-economic factors influencing the local perception of the ESs provided by the riparian corridors deserve to be taken into account for the sustainable preservation of the ecological functions of this ecosystem. The finding that traditional ecological knowledge accumulated with age and increased with seniority highlights the need to account for the migration factor in the design of ecosystem management strategies to support the transmission of local knowledge [69] . The close link observed between educational attainment and environmental sensitivity suggests that successful policies for the management of the ESs supplied by the riparian corridors should support the education system through multiple awareness creation and environmental education sessions for the benefit of all social strata. The perception of the supply of cropping areas as the most important ES in this study highlights that the main uses of the riparian corridors by local communities can differ from the primary roles of riparian corridors (regulation and support of ecological processes and landscape connectivity), thereby underscoring the need to account for the local uses of the riparian corridors for their successful management. Moreover, the promotion of sustainable land management strategies such as integrated soil fertility management, wetland reclamation and irrigation on the plateau could help reduce the potential risk of agricultural encroachment on the riparian corridors. In addition, it is also important for decision-makers to identify and prioritize riparian corridors where management efforts are needed to maintain landscape connectivity [70] [71] . This can be achieved using spatial modelling [70] [71] .

5. Conclusion

This study assessed the perceptions of ESs, the socio-economic factors that determine them and the values attributed to the riparian corridors of the Upper Oueme watershed in Benin. The local communities perceived the direct ESs (provisioning and cultural) more easily than the non-tangible ones (regulating and supporting). Moreover, the respondents had limited knowledge of the main functions (regulation and support of ecological processes and landscape connectivity) of the riparian corridors, which they perceived more as providers of ESs. In line with this, the supply of cropping areas was perceived as the most important ES, pointing to a potential risk of agricultural encroachment of the corridors. Age, occupation, seniority, and level of education were key to the perception of the other categories of ESs. In addition, level of education and income were the factors that influenced the perception of the importance of the ESs. Taking these different factors into account would be necessary to design management strategies aimed at sustaining the functions and ESs provided by the riparian corridors.

Acknowledgements

We extend our sincere appreciation to Jacques AYENA and Zakiou Deen SALIFOU-MALICK for their help in field data collection. Special thanks to Florent NOULEKOUN for his assistance and insights in data analysis.

Conflicts of Interest

The authors declare no conflicts of interest regarding the publication of this paper.

References

[1] Armenteras, D., Rodríguez, N., Retana, J. and Morales, M. (2011) Understanding Deforestation in Montane and Lowland Forests of the Colombian Andes. Regional Environmental Change, 11, 693-705.
https://doi.org/10.1007/s10113-010-0200-y
[2] Biaou, S., Gouwakinnou, G.N., Biaou, H.S.S., Tovihessi, M.S., Awessou, B.K., Ahononga, F.C., et al. (2022) Identifying the Land Use and Land Cover Change Drivers: Methods and Case Studies of Two Forest Reserves in Northern Benin. Environment, Development and Sustainability, 24, 9885-9905.
https://doi.org/10.1007/s10668-021-01849-4
[3] Carr, D.L. (2004) Proximate Population Factors and Deforestation in Tropical Agricultural Frontiers. Population and Environment, 25, 585-612.
https://doi.org/10.1023/B:POEN.0000039066.05666.8d
[4] Fasona, M., Adeonipekun, P.A., Agboola, O., Akintuyi, A., Bello, A, Ogundipe, O., et al. (2018) Drivers of Deforestation and Land-Use Change in Southwest Nigeria. In: Leal Filho, W., Ed., Handbook of Climate Change Resilience, Springer International Publishing, Cham, 1-24.
https://doi.org/10.1007/978-3-319-71025-9_139-1
[5] Maginnis, S., Rietbergen-McCracken, J. and Sarre, A. (2012) The Forest Landscape Restoration Handbook. Routledge, London.
https://books.google.bj/books?id=jq8eBAAAQBAJ&lpg=PP1&ots=qDT41y6H43&dq=Maginnis%2C%20S.%2C%20Rietbergen-McCracken%2C%20J.%20and%20Sarre%2C%20A.%20(2012)%20The%20Forest%20Landscape%20Restoration%20Handbook.%20Routledge.&lr&hl=fr&pg=PP1#v=onepage&q=Maginnis,%20S.,%20Rietbergen-McCracken,%20J.%20and%20Sarre,%20A.%20(2012)%20The%20Forest%20Landscape%20Restoration%20Handbook.%20Routledge.&f=false
https://doi.org/10.4324/9781849773010
[6] Saha, S., Hasan, S.S., Haque, M.E. and Ahamed, T. (2021) Perception Based Assessment of Ecosystem Services of Madhupur Sal Forest in Bangladesh. European Journal of Agriculture and Food Sciences, 3, 39-44.
https://doi.org/10.24018/ejfood.2021.3.1.194
[7] Seidl, R., Spies, T.A., Peterson, D.L., Stephens, S.L. and Hicke J.A. (2016) Searching for Resilience: Addressing the Impacts of Changing Disturbance Regimes on Forest Ecosystem Services. Journal of Applied Ecology, 53, 120-129.
https://doi.org/10.1111/1365-2664.12511
[8] Fischer, M., Rounsevell, M., Rando, A.T.-M., Mader, A., Church, A., Elbakidze, M., et al. (2018) The Regional Assessment Report on Biodiversity and Ecosystem Services for Europe and Central Asia: Summary for Policymakers. Regional Assessment Report on Biodiversity and Ecosystem Services for Europe and Central Asia, Bonn, 48.
[9] Guo, Z., Zhang, L. and Li, Y. (2010) Increased Dependence of Humans on Ecosystem Services and Biodiversity. PLOS ONE, 5, e13113.
https://doi.org/10.1371/journal.pone.0013113
[10] Millennium Ecosystem Assessment (2005) Ecosystems and Human Well-Being: Health Synthesis. A Report of the Millennium Ecosystem Assessment, MEA.
https://www.unioviedo.es/ranadon/Ricardo_Anadon/docencia/DoctoradoEconomia/Millenium%20Eco%20Assesment%2005%20Health.pdf
[11] Noulekoun, F., Mensah, S., Birhane, E., Son, Y. and Khamzina, A. (2021) Forest Landscape Restoration under Global Environmental Change: Challenges and a Future Roadmap. Forests, 12, Article 276.
https://doi.org/10.3390/f12030276
[12] Chazdon, R.L. (2008) Beyond Deforestation: Restoring Forests and Ecosystem Services on Degraded Lands. Science, 320, 1458-1460.
https://doi.org/10.1126/science.1155365
[13] Christin, Z., Bagstad, K. and Verdone, M. (2016) A Decision Framework for Identifying Models to Estimate Forest Ecosystem Services Gains from Restoration. Forest Ecosystems, 3, Article No. 3.
https://doi.org/10.1186/s40663-016-0062-y
[14] Elliot, W.J., Miller, I.S. and Audin, L. (2010) Cumulative Watershed Effects of Fuel Management in the Western United States. General Technical Report RMRS-GTR-231, United States Department of Agriculture.
https://doi.org/10.2737/RMRS-GTR-231
[15] Ouko, C., Mulwa R., Kibugi, R., Owuor, M.A., Zaehringer, J.G. and Oguge, N.O. (2018) Community Perceptions of Ecosystem Services and the Management of Mt. Marsabit Forest in Northern Kenya. Environments, 5, Article 121.
https://doi.org/10.3390/environments5110121
[16] Lhoest, S., Dufrene, M., Vermeulen, C., Oszwald, J., Doucet, J.-L. and Fayolle, A. (2019) Perceptions of Ecosystem Services Provided by Tropical Forests to Local Populations in Cameroon. Ecosystem Services, 38, Article 100956.
https://doi.org/10.1016/j.ecoser.2019.100956
[17] Benra, F., Nahuelhual, L., Felipe-Lucia, M., Jaramillo, A., Jullian, C. and Bonn, A. (2022) Balancing Ecological and Social Goals in PES Design-Single Objective Strategies Are Not Sufficient. Ecosystem Services, 53, Article 101385.
https://doi.org/10.1016/j.ecoser.2021.101385
[18] Burkhard, B., Petrosillo, I. and Costanza, R. (2010) Ecosystem Services-Bridging Ecology, Economy and Social Sciences. Ecological Complexity, 7, 257-259.
https://doi.org/10.1016/j.ecocom.2010.07.001
[19] Felipe-Lucia, M, Comín, F. and Escalera-Reyes, J. (2015) A Framework for the Social Valuation of Ecosystem Services. Ambio, 44, 308-318.
https://doi.org/10.1007/s13280-014-0555-2
[20] Jacobs, S, Dendoncker, N, Martín-López, B, Barton, D.N., Gomez-Baggethun, E., Boeraeve, F., et al. (2016) A New Valuation School: Integrating Diverse Values of Nature in Resource and Land Use Decisions. Ecosystem Services, 22, 213-220.
https://doi.org/10.1016/j.ecoser.2016.11.007
[21] Ruiz-Frau, A, Krause, T. and Marbà, N. (2018) The Use of Sociocultural Valuation in Sustainable Environmental Management. Ecosystem Services, 29, 158-167.
https://doi.org/10.1016/j.ecoser.2017.12.013
[22] Valatin, G., Ovando, P., Abildtrup J., Accastello, C., Andreucci, M.B., Chikalanov, A., et al. (2022) Approaches to Cost-Effectiveness of Payments for Tree Planting and Forest Management for Water Quality Services. Ecosystem Services, 53, Article 101373.
https://doi.org/10.1016/j.ecoser.2021.101373
[23] Satz, D., Gould, R., Chan, K., Guerry, A., Norton, B., et al. (2013) The Challenges of Incorporating Cultural Ecosystem Services into Environmental Assessment. Ambio, 42, 675-684.
https://doi.org/10.1007/s13280-013-0386-6
[24] Orenstein, D.E. and Groner, E. (2014) In the Eye of the Stakeholder: Changes in Perceptions of Ecosystem Services across an International Border. Ecosystem Services, 8, 185-196.
https://doi.org/10.1016/j.ecoser.2014.04.004
[25] Sena, P.H.A., Gonçalves-Souza, T., Gonçalves, P.H.S., Ferreira, P.S.M., Gusmão, R.A.F. and Melo, F.P.L. (2021) Biocultural Restoration Improves Delivery of Ecosystem Services in Social-Ecological Landscapes. Restoration Ecology, 30, e13599.
https://doi.org/10.1111/rec.13599
[26] García-Llorente, M., Castro, A.J., Quintas-Soriano, C., Oteros-Rozas, E., Iniesta-Arandia, I., González, J.A., et al. (2020) Local Perceptions of Ecosystem Services across Multiple Ecosystem Types in Spain. Land, 9, Article 330.
https://doi.org/10.3390/land9090330
[27] Bennett, E., Cramer, W., Begossi, A. and Cundill, G. (2015) Linking Biodiversity, Ecosystem Services, and Human Well-Being: Three Challenges for Designing Research for Sustainability. Current Opinion in Environmental Sustainability, 14, 76-85.
https://doi.org/10.1016/j.cosust.2015.03.007
[28] Fischer, A. and Eastwood, A. (2016) Coproduction of Ecosystem Services as Human-Nature Interactions—An Analytical Framework. Land Use Policy, 52, 41-50.
https://doi.org/10.1016/j.landusepol.2015.12.004
[29] Díaz, S., Pascual, U., Stenseke, M., Martín-López, B., Watson, R.T., Molnár, Z., et al. (2018) Assessing Nature’s Contributions to People. Science, 52, 41-50.
https://doi.org/10.1126/science.aap8826
[30] Berkes, F., Colding, J. and Folke, C. (2000) Rediscovery of Traditional Ecological Knowledge as Adaptive Management. Ecological Applications, 10, 1251-1262.
https://doi.org/10.1890/1051-0761(2000)010[1251:ROTEKA]2.0.CO;2
[31] Cummings, A.R. and Read, J.M. (2016) Drawing on Traditional Knowledge to Identify and Describe Ecosystem Services Associated with Northern Amazon’s Multiple-Use Plants. International Journal of Biodiversity Science, Ecosystem Services & Management, 12, 39-56.
https://doi.org/10.1080/21513732.2015.1136841
[32] Parrotta, J., Yeo-Chang, Y. and Camacho, L.D. (2016) Traditional Knowledge for Sustainable Forest Management and Provision of Ecosystem Services. International Journal of Biodiversity Science, Ecosystem Services & Management, 12, 1-4.
https://doi.org/10.1080/21513732.2016.1169580
[33] Gouwakinnou, N.G., Biaou S., Vodouhe, F.G., Tovihessi, M.S., Awessou, B.K. and Biaou, H.S.S. (2019) Local Perceptions and Factors Determining Ecosystem Services Identification around Two Forest Reserves in Northern Benin. Journal of Ethnobiology and Ethnomedicine, 15, Article No. 61.
https://ethnobiomed.biomedcentral.com/articles/10.1186/s13002-019-0343-y
https://doi.org/10.1186/s13002-019-0343-y
[34] Martin, F.-M., Evette, A. and Bergès, L. (2020) Pour une meilleure prise en compte de la connectivité écologique dans l’aménagement et la gestion des berges de cours d’eau. Sciences Eaux & Territoires, No. hors-série, 1-4.
https://doi.org/10.3917/set.hs1.0001h
[35] Natta, A.K. (2003) Ecological Assessment of Riparian Forests in Benin: Phytodiversity, Phytosociology and Spatial Distribution of Tree Species. Wageningen University, Wageningen.
https://www.proquest.com/openview/70fd1ec5994c106dff0cc9fda35acc8b/1?pq-origsite=gscholar&cbl=2026366&diss=y
[36] Ebner, M., Fontana, V., Schirpke, U. and Tappeiner, U. (2022) Stakeholder Perspectives on Ecosystem Services of Mountain Lakes in the European Alps. Ecosystem Services, 53, Article 101386.
https://doi.org/10.1016/j.ecoser.2021.101386
[37] Zoderer, B.M., Tasser, E., Carver, S. and Tappeiner, U. (2019) Stakeholder Perspectives on Ecosystem Service Supply and Ecosystem Service Demand Bundles. Ecosystem Services, 37, Article 100938.
https://doi.org/10.1016/j.ecoser.2019.100938
[38] Akognongbe, A., Abdoulaye, D., Vissin, E.W. and Boko, M. (2014) Dynamique de l’occupation du sol dans le bassin versant de l’Oueme à l’exutoire de Bétérou (Bénin). Afrique Science: Revue Internationale des Sciences et Technologie, 10, 228-242.
[39] Biao, E.I. (2017) Assessing the Impacts of Climate Change on River Discharge Dynamics in Oueme River Basin (Benin, West Africa). Hydrology, 4, Article 47.
https://doi.org/10.3390/hydrology4040047
[40] Kodja, D.J., Akognongbé, A.J.S., Amoussou, E., Mahé, G., Vissin, E.W., Paturel, J.-E., et al. (2020) Calibration of the Hydrological Model GR4J from Potential Evapotranspiration Estimates by the Penman-Monteith and Oudin Methods in the Ouémé Watershed (West Africa). Proceedings of the International Association of Hydrological Sciences, 383, 163-169.
https://doi.org/10.5194/piahs-383-163-2020
[41] PNUD (2022) Benin—Enquête sur les Conditions de Vie des Ménages en Milieu Rural 1994.
https://catalog.ihsn.org/catalog/290/related-materials
[42] Ahononga, F.C., Gouwakinnou, G.N., Biaou, H.S.S. and Biaou, S. (2020) Facteurs socio-économiques expliquant la déforestation et la dégradation des écosystèmes dans les domaines soudanien et soudano-guinéen du Bénin. Annales de l’Université de Parakou-Série Sciences Naturelles et Agronomie, 10, 43-60.
https://doi.org/10.56109/aup-sna.v10i2.36
[43] Dagnelie, P. (1998) Inférence statistique à une et à deux dimensions. De Boeck Supérieur, 2.
https://www.amazon.fr/Statistique-th%C3%A9orique-appliqu%C3%A9e-statistique-dimensions/dp/2804163369
[44] Lokonon, B.E., Tchandao Mangamana, E., Gnonlonfoun, I., Akpona, T.J.D., Assogbadjo, A.E., Glèlè Kakaï, R., et al. (2019) Knowledge, Valuation and Prioritization of 46 Woody Species for Conservation in Agroforestry Systems Along Ouémé Catchment in Benin (West Africa). Environment, Development and Sustainability, 21, 2377-2399.
https://doi.org/10.1007/s10668-018-0142-y
[45] Djagoun, C.A.M.S., Zanvo, S., Padonou, E.A., Sogbohossou, E. and Sinsin, B. (2022) Perceptions of Ecosystem Services: A Comparison between Sacred and Non-Sacred Forests in Central Benin (West Africa). Forest Ecology and Management, 503, Article 119791.
https://doi.org/10.1016/j.foreco.2021.119791
[46] Venables, W.N. and Ripley, B.D. (2002) Modern Applied Statistics with S. 4th Edition, Springer, New York, 435-446.
https://www.researchgate.net/publication/224817420_Modern_Applied_Statistics_With_S#fullTextFileContent
https://doi.org/10.1007/978-0-387-21706-2
[47] Nyangoko, B.P., Berg, H., Mangora, M.M., Shalli, M.S. and Gullström, M. (2022) Local Perceptions of Changes in Mangrove Ecosystem Services and Their Implications for Livelihoods and Management in the Rufiji Delta, Tanzania. Ocean & Coastal Management, 219, Article 106065.
https://doi.org/10.1016/j.ocecoaman.2022.106065
[48] World Bank (2022) RNB Par Habitant (Monnaie Locale Actuelle)—Benin. Data 2020.
https://donnees.banquemondiale.org/indicator/NY.GNP.PCAP.KN?locations=BJ
[49] McCullagh, P. (1980) Regression Models for Ordinal Data. Journal of the Royal Statistical Society, Series B (Methodology), 42, 109-127.
https://doi.org/10.1111/j.2517-6161.1980.tb01109.x
[50] Chakraborty, S. and Gasparatos, A. (2019) Community Values and Traditional Knowledge for Coastal Ecosystem Services Management in the “Satoumi” Seascape of Himeshima Island, Japan. Ecosystem Services, 37, Article 100940.
https://doi.org/10.1016/j.ecoser.2019.100940
[51] Ryan, R.L. (1998) Local Perceptions and Values for a Midwestern River Corridor. Landscape and Urban Planning, 42, 225-237.
https://doi.org/10.1016/S0169-2046(98)00089-9
[52] Natta, A.K., Sinsin, B. and Maesen, L.J.G. (2002) Riparian Forests, a Unique but Endangered Ecosystem in Benin. Botanische Jahrbücher fur Systematik, Pflanzengeschichte und Pflanzengeographie, 124, 55-69.
https://doi.org/10.1127/0006-8152/2002/0124-0055
[53] Mohan, M., Saritha, V.N.K., Rameshan, M., Chacko, A. and Gopikrishna, V.G. (2021) Restoring Degraded Riparian Forest Ecosystems of the Western Ghats for Ecological Sustainability. Restoration Ecology, 29, e13254.
https://doi.org/10.1111/rec.13254
[54] Natta, A., SogbéGnon, R. and Tchobo, F. (2010) Connaissances endogènes et importance du Pentadesma butyracea (Clusiaceae) pour les populations autochtones au Nord-Ouest Bénin. Fruit, Vegetable and Cereal Science and Biotechnology, 4, 18-25.
http://www.globalsciencebooks.info/Online/GSBOnline/images/2010/FVCSB_4(SI1)/FVCSB_4(SI1)18-25o.pdf
[55] Witing, F., Forio, M.A.E., Burdon, F.J., Mckie, B., Goethals, P., Strauch, M., et al. (2022) Riparian Reforestation on the Landscape Scale: Navigating Trade-Offs among Agricultural Production, Ecosystem Functioning and Biodiversity. Journal of Applied Ecology, 59, 1456-1471.
https://doi.org/10.1111/1365-2664.14176
[56] Ackerly, D.D., Ryals, R., Cornwell, W.K. and Loarie, S.R. (2012) Potential Impacts of Climate Change on Biodiversity and Ecosystem Services in the San Francisco Bay Area. California Institute for Energy and Environment, UC Berkeley.
https://escholarship.org/uc/item/1qm749nx
[57] Kiourtziadis, P., Iakovoglou, V. and Zaimes, G.N. (2016) Hydrologic and Anthropogenic Impacts on Riparian Areas in Agricultural Dominated Landscapes of Greece. 3rd International Conference—Water Resources and Wetlands, 8-10 September 2014, Tulcea, 8-10.
https://www.limnology.ro/wrw2016/proceedings/13_George_Zaimes.pdf
[58] Hartel, T., Fischer, J., Campeanu, C., Milcu, A.I., Hanspach, J. and Fazey, I. (2014) The Importance of Ecosystem Services for Rural Inhabitants in a Changing Cultural Landscape in Romania. Ecology and Society, 19, 42.
https://www.jstor.org/stable/26269549
https://doi.org/10.5751/ES-06333-190242
[59] McNally, C.G., Gold, A.J., Pollnac, R.B. and Kiwango, H.R. (2016) Stakeholder Perceptions of Ecosystem Services of the Wami River and Estuary. Ecology and Society, 21, 34.
https://www.jstor.org/stable/26269972
https://doi.org/10.5751/ES-08611-210334
[60] Zhang, L., Fu, B., Lü, Y. and Zeng, Y. (2015) Balancing Multiple Ecosystem Services in Conservation Priority Setting. Landscape Ecology, 30, 535-546.
https://doi.org/10.1007/s10980-014-0106-z
[61] Moutouama, F.T., Biaou, H.S.S., Kyereh, B., Asante, W.A. and Natta, A.K. (2019) Factors Shaping Local People’s Perception of Ecosystem Services in the Atacora Chain of Mountains, a Biodiversity Hotspot in Northern Benin. Journal of Ethnobiology and Ethnomedicine, 15, Article No. 38.
https://doi.org/10.1186/s13002-019-0317-0
[62] Gaoue, O.G., Coe, M.A., Bond, M., Hart, G., Seyler, B.C. and McMillen, H. (2017) Theories and Major Hypotheses in Ethnobotany. Economic Botany, 71, 269-287.
https://doi.org/10.1007/s12231-017-9389-8
[63] Ryan, C.M., Pritchard, R., McNicol, I., Owen, M., Fisher, J.A. and Lehmann C. (2021) Ecosystem Services from Southern African Woodlands and Their Future under Global Change. Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences, 371, Article 20150312.
https://doi.org/10.1098/rstb.2015.0312
[64] Leary, J., Aslan, C., Mark M., Frey, S. and Bath-Rosenfeld, R. (2021) Landowners’ Socio-Cultural Valuation of Ecosystem Services Provided by Trees in Costa Rican Agricultural Landscapes. Environmental Management, 67, 974-987.
https://doi.org/10.1007/s00267-021-01442-5
[65] Gandolfo, E.S. and Hanazaki, N. (2014) Distribution of Local Plant Knowledge in a Recently Urbanized Area (Campeche District, Florianópolis, Brazil). Urban Ecosystem, 17, 775-785.
https://doi.org/10.1007/s11252-014-0345-4
[66] Campos, J.L.A., De Lima Araújo, E., Gaoue, O.G. and Albuquerque, U.P. (2018) How Can Local Representations of Changes of the Availability in Natural Resources Assist in Targeting Conservation? Science of the Total Environment, 628-629, 642-649.
https://doi.org/10.1016/j.scitotenv.2018.02.064
[67] Buot Jr., I.E. and Buhay, A.F.V. (2022) Types of Socioecological Production Landscapes of the Philippines Based on Dominant Biodiversity: Status, Problems and Future Directions. Biodiversitas, 23, 3755-3770.
https://doi.org/10.13057/biodiv/d230752
[68] Abdul-Wahab, S.A. and Abdo, J. (2010) The Effects of Demographic Factors on the Environmental Awareness of Omani Citizens. Human and Ecological Risk Assessment, 16, 380-401.
https://doi.org/10.1080/10807031003670410
[69] McMillen, H. (2012) Ethnobotanical Knowledge Transmission and Evolution: The Case of Medicinal Markets in Tanga, Tanzania1. Economic Botany, 66, 121-131.
https://doi.org/10.1007/s12231-012-9201-8
[70] Atkinson, S.F. and Lake, M.C. (2020) Prioritizing Riparian Corridors for Ecosystem Restoration in Urbanizing Watersheds. PeerJ, 8, e8174.
https://doi.org/10.7717/peerj.8174
[71] Salviano, I.R., Gardon, F.R. and Dos Santos, R.F. (2021) Ecological Corridors and Landscape Planning: A Model to Select Priority Areas for Connectivity Maintenance. Landscape Ecology, 36, 3311-3328.
https://doi.org/10.1007/s10980-021-01305-8

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