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Agricultura, sociedad y desarrollo

versão impressa ISSN 1870-5472

agric. soc. desarro vol.13 no.1 Texcoco Jan./Mar. 2016

 

Articles

Perception of pollution of the Tlapaneco River by the riverside population

Angel Bustamante-González1  * 

Gerardo Galindo-De Jesús1 

José L. Jaramillo-Villanueva1 

Samuel Vargas-López1 

1 Colegio de Postgraduados, Campus Puebla. Boulevard Forjadores de Puebla No. 205, Santiago Momoxpam, Municipio San Pedro Cholula, estado de Puebla. México. 72760. (angelb@colpos.mx) (ggj1970@yahoo.com.mx) (jjaramil301@yahoo.es) (svargas@colpos.mx)


Abstract:

This article presents the perception of inhabitants of the communities of the Tlapaneco River basin, in the state of Guerrero, México, regarding the river water’s pollution, its effects, its origin, the expected benefits of cleaning the river, and their opinion on the role of institutions and authorities in solving the problem. It was found that the quality of the river water was generally perceived to be regular to very bad. The majority of those interviewed consider that river water is not clean and that it has bad quality for vegetable production, is not good for bathing, and has caused a decrease in aquatic fauna (fish and birds). The primary sources of contamination of the river are recognized to be the riverside communities due to wastewater discharge into the river. Those interviewed hold the viewpoint that the future cleanup of the river has benefits, particularly for their children and grandchildren, who could then enjoy a river with clean water for agricultural, domestic, and recreational use. However, they are skeptical about the role of government institutions in solving the problem.

Key words: actors interested; willingness; participation; restoration

Resumen:

En este artículo se expone la percepción de los habitantes de las comunidades de la cuenca del Río Tlapaneco, en el estado de Guerrero, México, sobre la contaminación del agua del río, sus efectos, su origen, los beneficios esperados del saneamiento del río y su opinión sobre el papel de las instituciones y autoridades en la solución del problema. Se encontró una percepción generalizada de que la calidad del agua del río es de regular a muy mala. La mayoría de los entrevistados considera que el agua del río no es limpia, es de mala calidad para la producción de hortalizas, no es buena para bañarse y ha causado la disminución de la fauna acuática (peces y aves). Se identifica como la fuente principal de contaminación del río son las comunidades ribereñas, por las descargas de aguas residuales al río. Los entrevistados tienen la visión de que el saneamiento futuro del río tiene beneficios, sobre todo para sus hijos y nietos, quienes podrán disfrutar de un río con agua limpia para uso agrícola, doméstico y de recreación. Sin embargo, son escépticos sobre el papel de las instituciones gubernamentales en la solución del problema.

Palabras clave: interesados; disposición; participación; restauración

Introduction

River water is the basis for aquiculture, irrigation, recreation, electrical and industrial generation, and an important part of public supply (Mora et al., 2002). The global demand for river water for these activities is greater every day, which escalates its extraction and reduces the volume of water available in rivers. On the other hand, these same rivers have been receiving the waste generated by human activities. These two factors determine the alteration in river water, both in quantity (volume) and quality. A lower availability of water leads to between communities and between users, as well as to disturbances of aquatic ecosystems, vegetation, and riparian wildlife. Pollution of rivers has effects on human health, availability of water with adequate quality for different economic and recreational activities, and on aquatic biodiversity.

The solution to the problem of river pollution in México, as in many other parts of the world, within the traditional vision of policy and program design, is predominantly perceived as a matter of technology (Balkema et al., 2002) and availability of financial resources. It has been oriented towards the construction of wastewater treatment plants as a sanitation practice, with smaller emphasis on supervision and sanctions against dumping of residual waters with high levels of contaminants. Government institutions only worry about social problems when there are grave cases of human illness or conflicts over water use. In river sanitation or restoration programs, the role of the local population is not considered, who are fellow participants in generating the problem, suffer the consequences, and should play an important part in the solution.

The lack of participation of the local population as a factor for failure in river basin management programs has been recognized for over a decade (Hanna, 1999). Effective participation of local residents or actors interested, for its part, leads to better quality decisions, improved interaction between those involved in decision making, greater capacity for managing environmental problems, and effective observance in improving environmental quality (Beierle and Konisky, 2001). The local population should intervene both in planning and in executing the programs, projects, and actions in water management. It has been suggested that this participation take place from the local input of knowledge and involvement in follow-up activities (Nare et al., 2006), as well as granting real spaces within political processes for decision making, in the formal and informal institutional processes where the allotment of scarce resources is decided for water management projects (Warner, 2006), and in the development of real deliberative processes (Pedregal et al., 2011). A deliberative process requires mutual exchange between actors, avoiding decision making according to the status or power of participants, subliminal persuasion strategies, or socio-political pressure (Renn, 2006). A fundamental element for this process is the decision of the local population to participate and the degree of involvement or participation, since it is common for their past experiences with programs or projects to predispose the population to view any new water management or restoration initiative with suspicion.

The level of participation may vary, ranging from being receptors or information generators, expressing opinions upon consultation, participating partially or completely, to the development of the capacity for self-determination (Videira et al., 2006). It is also possible for participation to occur in all phases of the process (problem definition; plan, program, and project designs; analysis of alternatives; decision making; follow-up and evaluation), or only in one of them. Both the level of participation and its duration are a personal decision, unless there are coercive measures associated with local or external institutions and organizations.

Various factors influence the decision of local residents to participate in environmental projects like the restoration of water resources. Among those factors are personal values, such as their willingness to learn from new experiences, their self-esteem, social contact, and capacity for friendly relationships (Petts, 2001). In particular, the perceptions, attitudes, and learning preferences about a resource like water influence the population’s participation (Bayard and Jolly, 2007; Adams et al., 2013). Another factor is the role that a member of the local population plays in a problem such as sanitation of the water resource. Local residents are part of the interested actors, defined as those who have an interest in a particular decision, individually or as a group, and includes both those who have an impact on the decision and those who are affected by it (Blackstock and Richards, 2007). In this concept an individual can have a different role due to the way he/she relates to the resource. For example, the type of water use of an individual results in the expression of different perceptions, opinions, and attitudes in relation to the problem of the resource’s depletion (Adcock and Hall, 2003).

Environmental perception is defined as knowledge of the immediate physical environment through the senses (Holahan, 2002). This is specific to each individual according to his/her experience, previous knowledge, and values. Humans perceive environmental variables in a given moment and construct their own perception of the world, in accordance with their sociocultural context and their own experience (Ittelson, 1978; Feijoó and Momo, 1991). Experiences and perceptions generate the storage, organization, and construction of images of the physical world (environmental knowledge), in addition to a favorable stance (or not) towards the characteristics of the physical world (attitude), which is the sum of evaluative beliefs (Eiser et al., 1998) and a behavior or action (conduct). In this process, the values and previous experiences, positive or negative, are defining (Spash et al., 2006; Dolisca et al., 2007). That is why environmental perception, knowledge, attitude and conduct involve a high degree of subjectivity and singularity. The decision makers and resource managers should understand that apart from technical and economic aspects, the social capital and social learning processes of water resource users should be considered (Jiggins et al., 2007). Comprehensive models for environmental management that consider learning processes are required. The elements of social learning for the management of a river strive to reach a shared perception of the problem in a group or in actors, build trust for self-reflection, and recognize mutual dependencies and interactions to initiate a collective process of learning and decisions (Wostl, 2007).

In México, the effective participation of the local population in planning and executing strategies and programs for pollution prevention and river cleanup is still in the process of moving from official discourse to real practice. Government programs, directed primarily at the river basins with greatest social or economic interest based on the amount of concentrated population and the concentration of industrial activities, have a top to bottom orientation. There are few studies directed at recognizing the opinions, perceptions, and attitudes of the local basin population concerning the water resource problems. This study has the objective of understanding how the riverside population of the Tlapaneco river basin perceives the problem of river water pollution, how much they have been directly or indirectly affected, and whether the population identifies the causes and primary sources of contamination, with the aim of contributing elements for better planning and decision making. The study is based on the hypothesis that the riverside population perceives and knows about the state of deterioration of the river, derived in large part from their everyday coexistence with it, principally through their use of the resource. The Tlapaneco River is important in the region of Montaña de Guerrero as a source of water for agriculture. However, in recent years some crops, mostly vegetables, have been limited due to pollution of the river water, according to previous studies (Bustamante et al., 2010).

Materials and Methods

The study was carried out in 18 communities located on the banks of the Tlapaneco River, in the hydrological region of the Balsas River in the state of Guerrero (Figure 1). A questionnaire was applied with questions involving seven aspects: socio-economic characteristics of those interviewed, use of the water resource, perception of the problem of water pollution, origin of water pollution, effects of water pollution, perceived solutions to water pollution, and expected benefits from the river restoration. To analyze the perception of the water pollution problem, seven statements were established in order to evaluate the general opinion regarding the river water quality; the quality of the water for cultivation of vegetables and other crops; the perception of change in the amount of fish and aquatic birds due to changes in the river water quality; and the perception of change in water transparency, as an indicator of the change registered in the historical memory of the interviewees. To evaluate the statements, an ordinal Likert scale was created, with values, depending on the statement, of: 1, very bad; 2, bad; 3, neither good or bad; 4, good; and 5, very good; and also of: 1, I strongly disagree; 2, I disagree; 3, I do not know; 4, I agree; and 5, I strongly agree.

Figure 1 Tlapaneco River basin and study locations. 

Due to the lack of socio-demographic information about the river basin available for establishing a sampling framework, a mixed sample was used (Casal and Mateu, 2003; Sing and Clark, 2012). Through sampling by quota (Namakforoosh, 2010), a sample of five interviewees was obtained in rural communities and 10 for the municipal townships, with a total of 95 people interviewed; 38 were key informants (authorities and agrarian leaders), and 57 informants were heads of households selected randomly in quadrants traced for each locality (Figure 2) and numbered upon aerial photographs scaled at 1:20000. This type of sampling has been proposed as a robust and trustworthy method for rural regions where there are no listings or detailed maps of households (Pearson et al., 2015).

Figure 2 Randomly selected quadrants (in yellow) of the Oztocingo, Guerrero locality. 

A descriptive analysis of the general information was completed. The variables of age, education, and irrigation surface (class intervals) were subjected to the non-parametric Kruskal-Wallis statistical test, according to Burger (2002), using the IBM SPSS Statistics software version 15, to see if there were significant differences in the perception of pollution of the Tlapaneco River in different groups. The variable types of economic activity, informant type, and sex were evaluated with the non-parametric Mann-Whitney test. The resulting statistics examine if the populations are identical (Anderson et al., 2009) in their opinion about pollution.

Results and Discussion

Socio-demographic characteristics of the interviewees

The average age of the interviewees was 52.82 years, with a minimum age of 18 years and a maximum of 86; of those, 85.3 % were male and 14.7 % were female, with an average schooling of 4.96 years. In addition, 80.0 % practice agriculture and livestock breeding as their primary activity and 20 % practice tertiary sector activities. These characteristics are common for rural producers in México. Ávila et al. (2011), for example, report that the age of rural producers of northern México is 53.4 years old and they have an average schooling of 6.5 years. For the present study, the advanced age and low formal education of the interviewees are relevant because they signify a long-term coexistence with the river; also, their perception of the problem of river pollution derives in large part from this experience, not from information transmitted by formal education.

Relationship between local residents and the Tlapaneco River

Of those interviewed, 72.6 % currently use water from the Tlapaneco River; of these, 96.2 % are users from before 2001. The water use has changed since 1990, due to pollution of the river; 95.8 % would use the water for washing, bathing, and recreation activities. Currently, 69.5 % use it for agricultural activity, 5.26 % for washing, bathing, or amusement, and 1.05 % for livestock activities. The generalized use of water from rivers in México for activities relating to cleaning and hygiene, as well as for watering livestock, is a practice that has been inherited from the conquistadors of México, a practice still present today in the rural communities of México like the ones by the Tlapaneco River and certain regions of Spain, and whose historical vestiges have been documented in Spain in the Municipal Ordinances (Rodríguez, 1998). Of those that are not users today, 83.5 % stopped using the water before 1990 due to river contamination. The reasons why they stopped using the river water are: they do not cultivate (2.22 %), they use another water source (10.53 %), or because it is polluted (11.58 %).

Perception of the quality of water of the Talpaneco River

The riverside population perceives that the Tlapaneco River water quality has deteriorated. Of those interviewed, 84.2 % agreed that the water was clearer in the past; 10.5 % strongly agree; 35.8 % consider that currently the water exhibits changes in appearance (foamy, greasy, ashy, dirty, cloudy, ugly, or brown); 26.3 % consider that its color has changed (black, brown, greenish, greyish, yellowish, not clear, or dark); and 23.2 % consider that it suffers from contamination processes (discharges of drainage, hospital and chemical waste). The evaluation of the river’s condition reflects the predominance of visual indicators for landscape (Hu and Keeley, 2014), particularly the clarity of the water. In general, the perception predominates that the water quality ranges from regular to bad (Table 1). Interestingly, the people who recently began to utilize the river water coincide in that its quality is regular or very bad. In general, the water is used even when there is awareness that it is not good.

Table 1 Use of the Tlapaneco River water and perception of its quality. 

1=Used the water previously and still uses it; 2=Used the water previously and stopped using it; 3=Did not use water previously and uses it presently; 4=Never has used the water.

The Kruskal-Wallis test indicated that the amount of irrigation surface was a variable that had an effect on the general perception of the water quality (Table 2). The Mann-Whitney test used for comparing the groups indicated that whoever has more than one hectare differ in opinion from those who have less than one hectare of irrigation land and that their perception is more pessimistic. Of the group with more than one hectare, 92 %considers that the water is bad or very bad, while for the group with 0.0 to 0.25 ha and 0.26 to 1.0 ha, the percentage is 86.7 % and 89.5 %, respectively. This variable also influenced the opinion about the water quality for vegetable cultivation; 100 % of those who have more than one hectare of irrigation lands held the opinion that the river water is not adequate for vegetable cultivation, an opinion shared by 93.1 % who own 0.0 to 0.25 ha and 97.4 % who own 0.26 to 1.0 ha. In these last groups there were interviewees that thought that the river water is good or very good for farming vegetables.

Table 2 Kruskal-Wallis test for evaluation of differences in perception of pollution of the Tlapaneco River between age, education, and irrigation surface area groups (value of p). 

Age groups (years): 18 - 40, 41 - 60, more than 60; Education (years): 0 - 3, 4 - 6, more than 6; Irrigation surface area (ha): 0.0 - 0.25, 0.26 - 1.0, more than 1.0.

Opinions on the change in river water quality that has taken place over time were influenced by the level of schooling (Table 2); 100 % of those who had less years of formal education (0 to 3 years) thought that the river water was clearer in the past than now, while in the stratum of those who have four to six years of schooling, there were opinions where they did not know if that was true (3.8 %) or that they disagreed with the statement (3.8 %). Among those who received more than six years of formal education, there was a similar tendency, where 4.3 % said they didn’t know and 8.7 % were in disagreement (Table 2).

The variable economic activity (differentiated between activities of the primary sector and those of the secondary and tertiary sectors) influenced opinions about the quality of river water for the cultivation of vegetables (Table 3). While 100 % of those interviewed whose activity was not agriculture and livestock production considered that the quality varied from not very good to very bad, 3.9 % of those who have agriculture or livestock as their primary economic activity considered that the water good for vegetable farming. We consider that this difference can be explained by the fact that some agriculture and livestock producers continue to cultivate vegetables on Tlapaneco riverside lands and their opinion somehow attempts to avoid the spread of a negative opinion on the quality of their products.

Table 3 Mann-Whitney test for evaluation of differences in perception of pollution of the Tlapaneco River between economic activity, informant type, and gender groups (value of p). 

Economic activity: primary sector, secondary or tertiary sector; Type of informant: key informant, non-key informant; Gender: masculine, femenine.

The type of informant influenced the opinions over changes in water quality (Table 3). Of key informants (older people or who have some position of responsibility in the community), 100 % had the opinion that the river water was clearer in the past. By contrast, 3.4 % of those who were not considered key informants said they did not know if this was true, and 5.2 % of them had the opinion that they did not agree with the statement that the river water was clearer in the past. We consider that this difference could be correlated with the less frequent contact that they have had with the river’s ecosystem and because they have less knowledge than the key informants. For the development of restoration policies, strategies and programs, the selection of local participants will be influenced by these differences in knowledge and perception about the river, which generates different visions and conceptualizations. Their selection will depend more on the objectives to be reached, and this will require building different participation models (Antunes et al., 2009).

Perception of the origin of pollution in the Tlapaneco River

Of the interviewees, 82.1 % had the opinion that the population in general is responsible for polluting the Tlapaneco River water; 56.8 % consider that the city of Tlapa, the center with highest demographic concentration of the river basin, is the primary cause; 35.8 % believe that the pollution originates in the high part of the basin, encompassing Copanatoyac to Tlaquiltzinapa. Only 7.37 % mentioned that it originates in the low zone of the basin, from Atlamajac to Huamuxtitlán.

The primary source of contamination identified was the discharge of residual waters (65.3 % of interviewees); 25.3 % considered that the contamination is caused by solid waste (garbage); 4.2 % by waste from clinics, mechanical workshops, and car washes; and 5.2 % by the increase in population, lack of treatment of sewage water, and lack of awareness in the population. The fact that the discharge of wastewater is perceived as the primary cause of pollution by the majority of those interviewed agrees with what was reported by Crona et al. (2009), who mention that the communities located near wastewater dumping sites are the ones who perceive the problem of pollution more. In contrast, the population in densely populated urban centers, in addition to wastewater dumping, assigns great importance to factors like the generation and disposal of solid residues (Arellano et al., 2009).

Perception of the effects of pollution of the Tlapaneco River

The population of the basin perceives that the pollution affects them directly. After interviewing them, 98.9 % answered affirmatively that it affects them and their family; 55.8 % considered that it deteriorates their health; 15.8 % obtained a reduced harvest; 9.5 % said that the water can only be used for watering certain crops; 8.4 % mention that it contaminates food and they cannot fish; and 5.3 % say that it causes a bad odor and harms the environment. All of them (100 %) manifested that the water pollution affects other people in their community, mainly their health (56.8 %), the irrigation of certain crops and their production (30.5 %), and because it contaminates sources of drinking water and agricultural products (10.5 %). 27.4 % mentioned that they stopped cultivating watermelon, melon, green chile, or tomatoes; 27.4 % stopped using the water for drinking, washing, or bathing; 17.9 % stopped planting crops that are not vegetables; 12.6 % stopped fishing; and 10.5 % stopped frequenting the river or using it in general. 93.7 % consider that they have had some economic loss because of the polluted water from the Tlapaneco River; 47.4 % had a lower income, 42.1 % acquired substitute products (pipe or bottled water and fishes), and only 4.2 % suffered a total loss at some occasion.

Those interviewed are aware of the consequences of the river pollution on their agricultural and recreational activities. All the interviewees consider that the river water is not clean and that it is of bad quality for cultivating vegetables because it sickens plants and contaminates the harvest, which cannot be sold. In addition, 74.7 % consider that it is not good for bathing. This perception is because they think that bathing in the river will provoke allergies (irritation, welts, itchiness) or pimples on the skin. The consensus regarding the river water’s low quality for agricultural production is notable, and can be explained because riverside agriculture depends on irrigation with river water. The fact that the residents pay more attention to the effects on crops coincides with studies that have shown that users perceive more clearly the effects on production than on the environment (Barnes et al., 2009). The interviewees seemed worried because the produce could not be sold, and not because of the effects on the health of the population that consumes the agricultural products, which coincides with the attitude of rural producers from other regions (Carr et al., 2011). The perceived effects on the health of those who use the river water is related to the individual’s prior experience, as reported by Fleisher and Kay (2006), who found that bathers that frequently use the water reported as polluted have a greater perception bias concerning the risk of contracting skin diseases from bathing in these waters, compared to non-bathers.

Even though the riverside population pays greater attention to the effects of river pollution on agricultural production, they also perceive the ecological effects of contamination; 81.1 % manifested being in agreement that there were more fish in the river in the past, and 18.9 % strongly agreed. They consider that people would fish in the river before and now they do not, and that fish have decreased due to the presence of contaminants in the river water (grease, chlorine, oils, and pesticides). They also consider that there were more birds in the in the river and along its banks (86.3 % agreed and 7.4 % strongly agreed). They associate this with there being more food in the past because the water was less contaminated. The understanding that the residents have of the problem of river pollution, its causes, and its consequences, is important so they can assume responsibility in the restoration and conservation of the river, as well as in the induction of conservationist behavior (Larson et al., 2009).

Perceived solutions to water pollution

Of those interviewed, 61 % consider that the pollution of the Tlapaneco River has a solution, while for 39 % it is an irreversible process. Although the majority of the interviewees are older than 50 years of age, they have a positive opinion about the rehabilitation of the river, in contrast to residents of riverside towns from other areas and of similar age who express pessimistic opinions on the subject (Braun and Shoeb, 2011). Concerning who is responsible for restoring the river water’s quality, 34.7 % of interviewees answered that it is the population, the three levels of government (municipal, state, and federal), and institutions; 28.4 % believe that it is the responsibility of the municipal president and offices, with the support of legislators, while 20 % think that it should be the municipality of Tlapa and other municipalities that cause most pollution, with support from dependencies.

Regarding perceptions of the solution to the pollution of water, and coinciding with what was stated by Balkman et al. (2002), 16.8 % of interviewees consider that the solution is in the construction of municipal wastewater treatment plants, and 10.5 % consider other treatment options, such as filtration ditches. Raising awareness in people is also considered important, in the sense of not throwing garbage into the river and retrieving the garbage already there, an opinion expressed by 23.2 % of those interviewed. 12.6 % believe that the solution lies in organizing the population (including orientation groups for assemblies and gatherings). The interviewees are aware that the decontamination of the Tlapaneco River is expensive or very expensive, primarily because it is a long river, an opinion shared by 72.6 %. 9.5 % consider cleanup of the river economically feasible only if there is organized participation from local residents.

The population is skeptical about the role that authorities have in solving the problem. 55.8 % of interviewees believe that the authorities only make promises; 12.6 % attribute this failure to deliver to the authorities’ lack of financial resources; 10.5 % believe they would deliver if the town applied more pressure; and 7.4 % believe that authorities do not assume responsibility for sanitation of the river, even though it is their duty because it is harmful to the town. Trust in institutions and authorities is important for any river sanitation initiative and, although in this case it is low, it is possible to involve the population since the majority is aware of the problem; as Jorgensen et al. (2006) report, the lack of trust in institutions is not always associated with negative environmental attitudes and with a low willingness to pay for improving the quality of the polluted waters. It is necessary for government institutions to rebuild their social capital with the communities, and one medium is through dialogue with them, as in ecological restoration projects where the population expects to be an active part of the process or, at least, to be consulted (Tunstaff et al., 2000).

Perceived future benefits of river sanitation

The interviewees perceive future positive and beneficial effects from cleaning up the Tlapaneco River; 63.2 % consider it important or very important that their children and grandchildren enjoy a river with clean water for agricultural, domestic, and recreational use, while 30.8 % consider that diseases and conflicts between water users would be avoided. The fact that the riverside population worries about the resource’s quality for future generations is important, and this worry is associated with an expected benefit as a result of its use. This is important to consider in the design of any environmental awareness and river cleanup program, as there is evidence that people are more willing to participate when they perceive benefits for the individual or the community than when they perceive risks or real damages (Hartley, 2006). This also complements the idea that environmental decisions are part of a long term process in which people evaluate the future benefits and costs, not just the present ones (Hendricks and Nicolaij, 2004).

Conclusions

The population of communities that use the Tlapaneco River recognizes that it is polluted and that this affects their health, agricultural production, and recreational activities. They also identify the sources of contaminants and consider that sanitation of the river is desirable. In contrast, there is a difference of opinions concerning who should be responsible for the river cleanup, and a high level of skepticism about the willingness and responsibility of federal, state, and local authorities in solving the problem. The rebuilding of social capital by government institutions related with the management and sanitation of the water resource of the Tlapaneco River requires incorporating the opinion and participation of riverside residents in the processes of planning and execution of strategies and programs, not only as subjects in charge of carrying out activities established by decision makers in government spheres.

Acknowledgments

To the Mixed Fund CONACYT- Government of the State of Guerrero, for their support in the performance of this study through the project: “Evaluation of natural resources and participative planning for the development of a local strategy for the sustainable management of natural resources in the Tlapaneco River basin.”

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Received: September 2014; Accepted: November 2015

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