Environmental and Anthropogenic Influences on Coliform Concentrations in the Octopus insularis Production Chain in the Veracruz Reef System, Gulf of Mexico
by
, , , , , , and
Sarai Acuña-Ramírez
1,
María de Lourdes Jiménez-Badillo
1,*
,
Gabriela Galindo-Cortes
1,
Angel Marval-Rodríguez
1,
María del Refugio Castañeda-Chávez
2,
Christian Reyes-Velázquez
2,
Hectorina Rodulfo-Carvajal
3 and
Marcos De Donato-Capote
3 1
Instituto de Ciencias Marinas y Pesquerías, Universidad Veracruzana, Hidalgo 617, Boca del Río 94290, Mexico
2
Instituto Tecnológico de Boca del Río, Tecnológico de México, Carretera Veracruz-Córdova, km 12, Boca del Río 94290, Mexico
3
Escuela de Ingeniería y Ciencias, Tecnológico de Monterrey, Epigmenio González 500, Querétaro 76130, Mexico
*
Author to whom correspondence should be addressed.
Animals 2023, 13(19), 3049; https://doi.org/10.3390/ani13193049
Submission received: 7 August 2023
/
Revised: 14 September 2023
/
Accepted: 25 September 2023
/
Published: 28 September 2023
(This article belongs to the Special Issue Assessment and Management of Cephalopod Fisheries and Ecosystems)
Abstract
:Simple Summary
The contamination of coastal waters, unhealthy conditions and inadequate handling practices tend to reduce the sanitary quality of fishery products, thus impacting its marketing. With this in mind, we investigate the microbiological quality of the Octopus insularis in each stage of the production chain, comprehending capture, post-capture, processing and commercialization, in terms of the presence of total and fecal coliforms at the Veracruz Reef System, Gulf of Mexico. The environmental and anthropogenic influence on the space–temporal concentration of coliforms were analyzed in sea water, fresh octopus, fresh water, ice and octopus, both packed in ice and boiled. Most relevant results indicated that coliforms are present in the octopus production chain, being highest in the marketing stage. The coliform concentration increased during the rainy season and was highest in the reefs closer to the coast, which has a major anthropogenic influence. These results point out the urgent need to implement an efficient cold chain with adequate handling practices to try to reverse these microbiological conditions and improve the octopus quality and food safety.
Abstract
Coliforms are relatively common in aquatic environments, but their concentrations can be increased by environmental changes and anthropogenic activities, thus impacting fisheries resources. To determine the microbiological quality in the octopus production chain (capture, post-capture, processing and commercialization), total (TC) and fecal (FC) coliforms were quantified in sea water, fresh octopus, fresh water, ice and octopus in two presentations: packed in ice and boiled. Samples came from fishing zones Enmedio, Chopa and La Gallega at the Veracruz Reef System (VRS) during dry, rainy and windy seasons. The coliforms were determined using the most probable number technique (MPN). The most relevant results indicated that octopus packed in ice coming from the commercialization stage had FC levels >540 MPN/100 g, which exceeded the permissible limits (230 MPN/100 g). Therefore, these products present a risk for human consumption. Differences in FC were observed in octopuses between the three fishing zones (H = 8.697; p = 0.0129) and among the three climatic seasons, increasing during the rainy season, highlighting La Gallega with 203.33 ± 63 MPN (H = 7.200; p = 0.0273). The results provide evidence of the environmental and anthropogenic influences on coliform concentrations and the urgent need to implement an efficient cold chain throughout octopus production stages with adequate handling practices to reverse this situation.
1. Introduction
Foods of marine origin are important sources of protein of high biological value but are highly perishable if proper safety measures are not taken. The quality and safety of fishery products is essential for their commercialization [1,2]. The contamination of coastal waters caused by the continuous discharges of untreated industrial and domestic waste [3,4] and the sanitary and handling conditions of fishery resources are the principal causes of problems with food safety in these products. Monitoring at each stage of the production chain is recommended to prevent contamination and inhibit the multiplication of microorganisms that can cause gastrointestinal diseases in humans [5,6].
The octopus fishery in Mexico is important from an economic and social point of view, being the second most important fishery in the Gulf of Mexico and the Caribbean. [7,8]. The octopus fishery in the Veracruz Reef System (VRS) is an economic activity on which fishing communities depend [9], and it is also characterized by being related to reef systems, within a natural protected area [10]. The production chain of the octopus Octopus insularis in the VRS consists of four stages before consumption: capture, post-capture, processing and commercialization [11]. Artisanal fishing for octopus occurs in the VRS in the form of freediving with octopus hooks at depths of 0.5–5 m from March to July and September to December [10,12,13]. Post-capture handling consists of keeping the octopuses in fresh water until they are processed or commercialized. Boiling at high temperatures is the only process to which part of catches are subjected. Commercialization of the octopuses takes place on the beach shore, in local fish markets, restaurants and regional seafood markets in two presentations: boiled or packed in ice [14].
The commercialization of artisanal catches increases the risk of transferring alimentary infections due to limitations on the sanitary and handling conditions of fishery products, such as intermittent access to potable water, frequent breakdowns of freezing systems, and surface areas inadequate for processing raw materials [5,6,15]. There are protocols for the handling of fishery and aquaculture products from their capture in small boats through to commercialization [16], such as those used in Yucatán for the handling of Octopus maya [17]. Nevertheless, the handling practices and microbiological status in O. insularis production chain have not been evaluated, it being essential to know them to improve their quality and marketability.
Microbiological quality in fishery resources is determined by the presence and concentration of total and fecal coliforms. The habitat of both coliforms is the intestine [18], but these bacteria have the capacity to survive and multiply in other substrates, so high concentrations are indicative of poor sanitary practices [1]. In addition, it is possible that the concentration of FC may increase during the rainy season caused by the increment of discharges containing industrial and domestic wastes. The VRS is exposed to a high anthropogenic impact due to its proximity to a large urban area and one of the main ports of Mexico; therefore, an increase in fecal coliforms would be expected in the octopus production chain, thus affecting its safety.
Here, we present data on the microbiological quality of the O. insularis in each stage of the production chain and provide evidence of the environmental and anthropogenic influences on the space–temporal concentration of coliforms, sustaining the urgent need to implement an efficient cold chain with adequate handling practices to revert this situation.
2. Materials and Methods
2.1. Sampling Strategy
Two representative octopus fishing zones in the VRS (19°05′–19°14′ N and 95°93′–96°15′ W) were chosen for sampling: in the northern zone, considering the proximity to the coast and the port in La Gallega reef, and in the southern zone in Enmedio and Chopa reefs, considering the influence by anthropogenic activities and discharge from rivers (Figure 1). The influence by climatic seasons, namely dry (April to June), rainy (July to September) and the northern winds “windy” (October to March), were considered too.
Samples of seawater, freshwater, octopuses, and ice from each stage of the production chain in the three-sample site and the three climatic seasons were taken. Capture stage included seawater samples from the water column at 150 cm depth, in duplicate, and stored in sterile containers of 250 mL capacity. They were kept refrigerated until processing. Also, three whole octopus freshly caught were preserved in sterile whirl-pak bags, on ice until processing. In post-capture stage, 100 mL freshwater, where the octopuses are stored before being sold, was sampled, and then preserved in sterile whirl-pak bags until its analyses. For the processing stage, three samples of the boiled octopus were taken, preserved in sterile conditions, and analyzed, while for the commercialization stage, three octopuses packed in ice and 250 g of the ice in which the octopuses are placed for exhibition and sale were sampled. All samples were collected, processed, and contrasted following the norms stipulated in APHA 2012 [19] and NOM-242-SSA1-2009 [20].
Figure 1.
Study area. Veracruz Reef System (VRS). Octopus fishing zones: La Gallega reef (northern), Chopa and Enmedio Reefs (southern). Jamapa river in blue lines. Map prepared using Ocean Data View software (Version 4.7.8) [21].
Figure 1.
Study area. Veracruz Reef System (VRS). Octopus fishing zones: La Gallega reef (northern), Chopa and Enmedio Reefs (southern). Jamapa river in blue lines. Map prepared using Ocean Data View software (Version 4.7.8) [21].
2.2. Determination of Fecal and Total Coliforms in Sea Water, Fresh Water, Ice and Octopuses
For the water samples (sea, fresh and ice) three serial dilutions were made by transferring 1 mL of the sample in 9 mL of saline peptonized water to obtain 3 concentrations (10−1, 10−2 and 10−3). In the case of octopus, 10 g of muscle was taken and homogenized in 90 mL of saline peptonized water, from which serial dilutions were performed for presumptive and confirmatory tests, in the same way as was described for water samples.
The microbiological analysis of seawater, freshwater, ice and octopuses were carried out in accordance with the protocols described by the U.S. Food and Drug Administration [22], which specify three serial dilutions per sample. These dilutions were used to perform presumptive and confirmative tests for total (TC) and fecal (FC) coliforms, respectively. The enumeration of TC and FC was realized via the Most Probable Number (MPN) technique, according to APHA [23], using the following media: Lauryl Sodium Sulfate Broth (presumptive test for the total coliforms), Lactose Bile 2% Brilliant Green Broth in 37 °C (confirmative test for the TC and the presumptive for FC) and Escherichia coli Broth in 44 °C (confirmation for the FC).
From the number of positive tubes in the presumptive and confirmatory tests, the MPN of TC and FC in 100 mL of sample was calculated, referring to the MPN statistical tables. In the case that the presumptive test did not show turbidity and gas production, the minimum value expressed in the table was reported.
The MPN for TC and FC in each sample was obtained in accordance with norm NOM-112-SSA1-1994 [24] and then contrasted to the values established in norm NOM-201-SSA1-2015 [25], which refers to the quality of water and ice for human consumption, and norm NOM-242-SSA1-2009 [20], which specifies the quality standards for fresh, refrigerated, frozen, and processed marine products.
2.3. Statistical Analysis
Normality and homoscedasticity tests were applied on TC and FC data to discern about the use of parametric or non-parametric tests. Results led us to choose the Kruskal–Wallis test to determine the influence of the climatic seasons and fishing zones on the MPN for TC and FC on each stages of the production chain. In the cases where significant differences were found, multiple contrast tests were applied following the Dunn test. All tests were carried out considering a significance level of α = 0.05. Analyses were performed with the STATA package version 13.1.
2.4. Environmental Parameters
To analyze climatic variation, we utilized the database MOHICOVER (Monitoring of Hydrography and Currents in Veracruz), which contains monthly data of temperature and salinity of the study area (VRS) during 2019. Also, we collected precipitation data and water discharge flow from the Jamapa River based on official CONAGUA statistics (Comisión Nacional del Agua, National Water Commission) from January 2019 to December 2020.
3. Results
3.1. Total Coliforms by Stage of Octopus Production Chain
The spatial and temporal analysis of the TC and FC show that the seawater did not detect statistically significant differences in TC concentrations between the three climatic seasons in the reefs evaluated (Table 1). The highest MPN value for TC in the fresh octopus was obtained in La Gallega reef in the capture stage during the rainy season (Figure 2).
The MPN for TC in the fresh octopuses captured in the different climatic seasons presented statistically significant differences within the reefs sampled: Enmedio (H = 7.20; p < 0.05), Chopa (H = 8.526; p < 0.05) and La Gallega (H = 7.200; p < 0.05). In contrast, there were no significant differences in the MPN for TC among the reefs (H = 1.734; p > 0.05) (Table 1).
With respect to the post-capture stage, statistically significant differences (H = 7.200 p < 0.05) were observed in the MPN for TC isolated in fresh water in the different climatic seasons, with higher values in the dry season, while for the processing stage, no statistically significant differences (H = 1.046; p > 0.05) were observed between the MPN for TC of the boiled vs. fresh octopuses (Figure 2).
Regarding the commercialization stage, the MPN for TC obtained from the octopuses packed in ice was higher than in the boiled octopuses, with statistically significant differences between the two sets of samples (H = 8.750; p <0.05). For the samples of ice, the same high MPN value for TC was found during the three climatic seasons (Figure 2).
3.2. Fecal Coliforms by Stage of Octopus Production Chain
The spatial and temporal FC concentrations in sea water from the capture stage did not reveal statistically significant differences (H = 0.762; p > 0.05) in the reefs evaluated (Table 2). The MPN of CF in fresh octopus captured in the different climatic seasons presented statistically significant differences both between (H = 8.697; p < 0.05) and within reefs sampled: Enmedio (H = 3.857; p < 0.05), Chopa (H = 5.44; p ≤ 0.05) and La Gallega (H = 7.200; p < 0.05) (Figure 3).
The post-capture stage analyses identified statistically significant differences in the MPN for FC isolated in fresh water in the different climatic seasons (H = 7.200; p < 0.05), with a marked increase in this value for the fresh water in the rainy season, while for the processing stage, no statistically significant differences between the MPN for FC in the boiled vs. fresh octopuses (H = 0.198; p > 0.05) (Figure 3).
Regarding the commercialization stage, the MPN for FC obtained from the octopuses packed in ice was higher than in the boiled octopuses, with statistically significant differences between these samples (H = 8.2611; p < 0.05). Moreover, the ice used to preserve the octopuses presented FC values (>800 MPN/100 g) above allowable levels (230 MPN/100 g) in all three climatic seasons (Table 2).
3.3. Environmental Parameters
The analysis of temperature anomalies in the sea indicated below-average values from February to May and from November to December 2019, but higher values from June to October. The maximum (29.9 °C) and minimum (21.8 °C) values for this variable were obtained in August and March, respectively. In relation to salinity, variations from average values were observed throughout the year. The lowest value was registered in April 2019 (30.8 UPS), the highest in October 2019 (35.5 UPS). Precipitation in 2020 was higher than in 2019, with above-average increases in October 2019 and September 2020, and periods of low precipitation between December and April in both years. A similar tendency was found for the rate of discharge from the Jamapa River, where we found an increase from June/July to October in both 2019 and 2020 (Figure 4).
4. Discussion
The analysis of coliform concentrations in the different stages of the octopus production chain in the VRS revealed an increased tendency in the MPN for both total (TC) and fecal (FC) coliforms in the octopuses from capture to the commercialization stage. In most of the cases, both values exceeded the allowable levels stipulated in the norm NOM-242-SSA1-2009 [20]. These results provide evidence of the failure in the good handling practices on these fishery resource. In addition, the direct discharge of untreated wastewater into seawater can be a source of fecal contamination to which octopuses are exposed.
The highest MPN of FC values in all samples of fresh octopus captured from La Gallega, during the rainy season, could be due to the greater anthropogenic impact, such as direct discharges of untreated wastewater [26], intense maritime traffic [27], pollution from oil spills, industrial discharges, domestic effluents, etc. [28,29,30], that these reefs receive owing to their proximity to a metropolitan area and port zone. This increase in coliforms during the rainy season has been evidenced in several studies, where it is associated with an increase in runoff and wastewater towards the coasts [31]. In addition, this increase in discharges decreases the salinity and increases the temperature of the system, thus favoring bacterial growth [32,33].
A previous study had warned that La Gallega reef is one of the most susceptible to suffering a high degree of degradation of its waters, which can cause diseases in fish and coral [34]. The results reported herein provide evidence of the impact of these conditions on the octopuses extracted in this zone.
In the post-capture stage, the MPN values for TC and FC in the fresh water that fishers use to preserve their catches prior to commercialization were also found to exceed the allowable limits for potable water (0 MPN for TC) [35]; also, these levels were highest in the rainy season, when according to Cho et al. [36], ambient temperatures tend to rise. The inadequate post-capture handling practices, the limited availability of potable water in the zone and the use of unsuitable recipients provoked high TC and FC concentrations.
The handling practices of the octopus resource in both zones of the VRS do not comply with the norms NOM-242-SSA1-2009 [35], OIRSA [16] and SAGARPA-SENASICA [37]. We detected a breaking off in the cold chain from capture to commercialization stages. In addition, the CF values obtained in the ice suggest that it does not come from potable water. The exhibition of catches for commercialization in trays with no incline and with water-ice that does not comply with norm NOM 251-SSA1-2009 [20] can be another source of contamination of the octopuses. Even in boiled octopus, our analyses found values for TC and FC that exceeded allowable levels, therefore representing a risk for human health when consumed, which, according to Steffen et al. [38], can cause gastrointestinal infections. While the study did not apply a confirmatory test for the presence of Escherichia coli and, thus, the MPN could pertain to this species or some other in the group of thermotolerant bacteria, the presence of fecal coliforms is an indicator of anthropogenic contamination that must be addressed.
Despite having a good cooking process, there is “cross contamination” due to the lack of instruments and materials used exclusively for handling cooked products, sharing scales, trays, knives, boards and ice with other uncooked seafood products. In the same way, the high CF values in the ice during all the months sampled indicate that they do not come from potable water; in addition, the ice was used only in the commercialization stage, in non-inclined trays, which means that as the ice melts, water ice forms and is not at the temperature determined for the maintenance of the resources and the inhibition of bacterial growth. It is necessary to use and continually replace ice throughout the octopus production chain to reduce the growth of fecal coliforms.
In addition to anthropogenic factors, which influence the number of total and fecal coliforms, the VRS presents a stratification of the water column that differs between seasons (rainy, dry, windy) [39]. Temperature is a determining factor in bacterial growth, having a directly proportional relationship. In warm climates, bacterial growth is faster, observing that during the months of July to September, the highest temperatures are reported, relating this value to the highest concentration peaks of fecal coliforms found in this study. Higher temperatures are also recorded during the rainy season with increased water flow discharges, which increases the concentration of nutrients and wastewater discharges that bring with them fecal coliforms.
The results of this study provide clear evidence that in order to correct this situation, the following issues must be addressed: treating all residual waters before discharging them into the sea; maintaining the cold chain throughout all stages of the octopus production chain; improving fishery infrastructure and the access to potable water; implementation of good handling and monitoring practices; and providing technical orientation and support to all the personnel involved in the octopus production chain. These measures should be complemented by the practices in Shawyer and Medina [40], DOF [26] and norm NOM-242-SSA1-2009 [35]. Practical measures include daily cleaning of boats, use of coolers with lids for the octopus caught, ice from potable water, personnel hygiene and the use of equipment exclusively for cooked products. Finally, increasing the awareness of all the personnel involved of the risks of contamination by biological, physical or chemical factors [2] will contribute to improving the quality and food safety of this product.
5. Conclusions
Total and fecal coliforms are present in the octopus production chain from the VRS, being highest in the marketing stage, with FC values above the permissible values even in cooked octopus. The most affected octopuses were those captured in coastal waters near reefs with the greatest anthropogenic pressure. During the rainy season, the concentration of FC increases. It is necessary to strengthen the cool chain and implement good handling practices throughout the octopus production chain to improve the quality and food safety of this product.
Author Contributions
Conceptualization, S.A.-R. and M.d.L.J.-B.; methodology, C.R.-V. and H.R.-C.; investigation, S.A.-R. and M.d.L.J.-B.; resources, M.d.R.C.-C. and M.D.D.-C.; writing—original draft preparation, S.A.-R.; writing—review and editing, M.d.L.J.-B. and G.G.-C.; image design, A.M.-R. All authors have read and agreed to the published version of the manuscript.
Funding
This research was funded by CONSEJO NACIONAL DE CIENCIA Y TECNOLOGÍA (CONACYT) trough PhD scholarship grant number 895413.
Institutional Review Board Statement
All octopus samples were obtained from dead individuals caught by the commercial multi-species artisanal fleet and following the recommendations of the Ethics Committee of the Academic Group: Management and Conservation of Aquatic Resources of the Instituto de Ciencias Marinas y Pesquerías of the Universidad Veracruzana, Boca del Rio, Veracruz, Mexico.
Informed Consent Statement
Informed consent was obtained from all fishermen involved in the study.
Data Availability Statement
Data supporting the conclusions of this study are available from the corresponding author, [J.-B.M.d.L]. The data are not publicly available because they contain data that have not yet been published. Furthermore, it could compromise the privacy of the fishermen who collaborated in the research.
Acknowledgments
We extend our gratitude to the support provided by the following institutions in the development of this research: Instituto de Ciencias Marinas y Pesquerías (Universidad Veracruzana), for their support in the conception of the project, the field work, the approach with the fishing cooperatives and the publication process and economic support; Laboratorio de Investigación de Recursos Acuáticos (Instituto Tecnológico de Boca del Río), for the provision of facilities to carry out laboratory tests; Laboratorio de Biología Molecular del Departamento de Bioingenierías (Instituto Tecnológico y de Estudios Superiores de Monterrey), for the provision of laboratory material; Monitoreo Hidrográfico y de Corrientes de Veracruz Project (Instituto de Ciencias Marinas y Pesquerías), for facilitating the database of environmental variables; and the Sociedad Cooperativa Arrecifes de Antón Lizardo and VRS fishermen, for their help during the sampling.
Conflicts of Interest
The authors declare no conflict of interest.
References
- Organismo Internacional Regional de Sanidad Agropecuaria (OIRSA). Manual de Buenas Prácticas de Manufactura para Productos Acuícolas y Pesqueros; Dirección Regional de Inocuidad de los Alimentos: San Salvador, El Salvador, 2017; pp. 18–24. [Google Scholar]
- FAO; World Health Organization. Code of Practice for Fish and Fishery Products; FAO: Rome, Italy, 2020; p. 372. [Google Scholar]
- Gutiérrez-Ruiz, C.; Román-Vives, M.; Vergara, C.; Badano, E. Impact of anthropogenic disturbances on the diversity of shallow stony corals in the Veracruz Reef System National Park. Rev. Mex. Biodivers. 2011, 82, 249–260. [Google Scholar] [CrossRef]
- Stark, J.S.; Bridgen, P.; Dunshea, G.; Galton-Fenzi, B.; Hunter, J.; Johnstone, G.; King, C.; Leeming, R.; Palmer, A.; Smith, J.; et al. Dispersal and dilution of wastewater from an ocean outfall at Davis Station, Antarctica, and resulting environmental contamination. Chemosphere 2016, 152, 142–157. [Google Scholar] [CrossRef] [PubMed]
- Pena-Puch, A.; Pérez-Jiménez, J.C.; Espinoza-Tenorio, A. Advances in the study of Mexican fisheries with the social-ecological system (SES) perspective and its inclusion in fishery management policy. Ocean. Coast. Manag. 2019, 185, 105065. [Google Scholar] [CrossRef]
- Estrella-Gómez, N.; Escalante-Réndiz, D.; González-Borgos, A.; Sosa-Cordero, D.; Rojas-Herrera, R. Análisis microbiológico del pulpo rojo en puertos pesqueros de Campeche, Mexico. Salud Pública Mex. 2016, 58, 453–460. [Google Scholar] [CrossRef] [PubMed]
- CONAPESCA. Anuario Estadístico de Acuacultura y Pesca 2017; Comisión Nacional de Acuacultura y Pesca: Ciudad de Mexico, Mexico, 2017. [Google Scholar]
- Galindo-Cortés, G.; Hernández-Flores, A.; Santos-Valencia, J. Pulpo del Golfo de Mexico Octopus maya y Octopus vulgaris. In Sustentabilidad y Pesca Responsable en Mexico, Evaluación y Manejo; Beléndez-Moreno, L.F., Espino-Barr, E., Galindo-Cortes, G., Gaspar-Dillanes, M.T., Huidobro-Campos, L., Morales-Bojórquez, E., Eds.; Instituto Nacional de Pesca: Ciudad de Mexico, Mexico, 2014; pp. 179–210. [Google Scholar]
- Jiménez-Badillo, M.L.; Castro-Gaspar, L. Pesca artesanal en el Parque Nacional Sistema Arrecifal Veracruzano, Mexico. In Investigaciones Científicas en el Sistema Arrecifal Veracruzano; Granados Barba, A., Abarca Arenas, L.G., Vargas-Hernández, J.M., Eds.; Universidad Autónoma de Campeche: Ciudad de Mexico, Mexico, 2007; pp. 221–240. [Google Scholar]
- Jiménez-Badillo, M.L. Manejo de la pesquería de pulpo en el estado de Veracruz con énfasis en el Sistema Arrecifal Veracruzano. In Manejo de los Recursos Pesqueros de la Cuenca del Golfo de Mexico y del Mar Caribe; Aldana, A.D., Enriquez, D.M., Elías, V., Eds.; Colección La Ciencia en Veracruz; Editorial de la Universidad Veracruzana: Veracruz, Mexico, 2013; Volume 1, pp. 229–236. [Google Scholar]
- Pardo, F. Diseño de una Estrategia de Evaluación de Cadenas Productivas para el Desarrollo Sustentable de Comunidades Pesqueras Ribereñas. Estudio de Caso: Antón Lizardo, Municipio Alvarado, Veracruz, Mexico. Master’s Thesis, Instituto de Investigaciones y Estudios Superiores de las Ciencias Administrativas, Universidad Veracruzana: Veracruz, Mexico, 2007; p. 128. [Google Scholar]
- SAGARPA. Acuerdo Por el Que se da a Conocer la Actualización de la Carta Nacional Pesquera; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 2018; 11/06/2018. [Google Scholar]
- Jiménez-Badillo, M.L. Geographic information system: A tool to manage the octopus fishery in the Veracruz Reef System National Park, Mexico. In GIS/Spatial Analyses in Fishery and Aquatic Sciences; Nishida, T., Caton, A.E., Eds.; Fishery GIS Society: Saitama, Japan, 2010; Volume 4, pp. 319–328. [Google Scholar]
- SAGARPA. Acuerdo por el que se da a Conocer el Plan de Manejo Pesquero de Pulpo (O. maya y O. vulgaris) del Golfo de Mexico y Mar Caribe; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 2014; 28/03/2014. [Google Scholar]
- CONAPESCA. Anuario Estadístico de Acuacultura y Pesca 2020; Comisión Nacional de Acuacultura y Pesca: Ciudad de Mexico, Mexico, 2020. [Google Scholar]
- Organismo Internacional Regional de Sanidad Agropecuaria (OIRSA). Manual de Introducción a la Inocuidad de los Alimentos; Dirección Regional de Inocuidad de los Alimentos: San Salvador, El Salvador, 2018. [Google Scholar]
- Contreras, D.; Vázquez, A.; Romero, Y.; Pardo, J.; Guevara, M.; Rivera, J. Plan Estratégico: Plataforma Tecnológica Pulpo Maya Para el Desarrollo de Productos de Alto Valor Agregado; Centro de Investigación y Asistencia en Tecnología y Diseño del Estado de Jalisco A.C (CIATEJ): Jalisco, Mexico, 2019. [Google Scholar]
- Robert, M. Microorganismos indicadores de la calidad del agua potable en Cuba. Rev. CENIC Cienc. Biol. 2014, 45, 32–43. [Google Scholar]
- American Public Health Association (APHA). Standard Methods for the Examination of Water and Waste Water, 22nd ed.; American Public Health Association: Washington, DC, USA, 2012. [Google Scholar]
- Secretaría de Salud. NOM-251-SSA1-2009, Prácticas de Higiene para el Proceso de Alimentos, Bebidas o Suplementos Alimenticios; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 2008; 10/10/2008. [Google Scholar]
- Schlitzer, R. Ocean Data View. 2023. Available online: http://odv.awi.de (accessed on 5 September 2023).
- Food and Drug Administration. Bacteriological Analytical Manual, 9th ed; AOAC International: Arlington, TX, USA, 2004; Chapter 4. [Google Scholar]
- American Public Health Association (APHA). Standard Methods for the Examination of Water and Wastewater, 20th ed.; American Public Health Association: Washington, DC, USA, 1998. [Google Scholar]
- Secretaría de Salud. NOM-112-SSA1-1994, Bienes y Servicios. Determinación de Bacterias Coliformes. Técnica del Número Más Probable; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 1995; 10/19/1995. [Google Scholar]
- Secretaría de Salud. NOM-201-SSA1-2015, Productos y Servicios. Agua y Hielo para Consumo Humano, Envasados y a Granel. Especificaciones Sanitarias y Métodos de Prueba; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 2015; 12/22/2015. [Google Scholar]
- Ortíz-Lozano, L.; Pérez-España, H.; Granados-Barba, A.; González-Gándara, C.; Gutiérrez-Velázquez, A.; Martos, J. The Reef Corridor of the Southwest Gulf of Mexico: Challenges for its management and conservation. Ocean. Coast. Manag. 2013, 86, 22–32. [Google Scholar] [CrossRef]
- APIVER. Datos Estadísticos del Movimiento de Carga Enero-Junio. 2019. Available online: http://www.puertodeveracruz.com.mx/wp-content/uploads/2019/07/Estadistica_Apiver_junio_2019 (accessed on 13 February 2022).
- Ortíz-Lozano, L. Identification of priority conservation actions in marine protected areas: Using a causal networks approach. Ocean. Coast. Manag. 2012, 55, 74–83. [Google Scholar] [CrossRef]
- SEMARNAT. Informe de la Situación del Medio Ambiente en Mexico. Compendio de Estadísticas Ambientales. Indicadores Clave, de Desempeño Ambiental y de Crecimiento Verde; SEMARNAT: Ciudad de Mexico, Mexico, 2016. [Google Scholar]
- Venter, O.; Sanderson, E.W.; Magrach, A.; Allan, J.; Beher, J.; Jones, K.; Possingham, H.; Wood, P.; Fekete, B.; Levy, M.; et al. Sixteen years of change in the global terrestrial human footprint and implications for biodiversity conservation. Nat. Commun. 2016, 7, 12558. [Google Scholar] [CrossRef] [PubMed]
- Hill, D.; Owens, W.; Tchounwou, P. The impact of rainfall on fecal coliform bacteria in Bayou Dorcheat (North Louisiana). Int. J. Envirom Res. Health 2006, 3, 114–117. [Google Scholar] [CrossRef] [PubMed]
- Mijin Seo, L.; Lee, H.; Yongseok, K. Relationship between Coliform Bacteria and Water Quality Factors at Weir Stations in the Nakdong River, South Korea. Water 2019, 11, 1171. [Google Scholar] [CrossRef]
- Thériault, A.; Duchesne, S. Quantifying the fecal coliform loads in urban watersheds by hydrologic/hydraulic modeling: Case study of the Beuport river watershed in Quebec. Water 2015, 7, 615–633. [Google Scholar] [CrossRef]
- Jiménez-Badillo, M.L.; Cruz-Rodas, S.; Lozano-Aburto, M.A.; Rodríguez-Quiroz, G. Problemática ambiental y socioeconómica del Parque Nacional Sistema Arrecifal Veracruzano. Investig. Cienc. 2014, 60, 58–64. [Google Scholar]
- Secretaría de Salud. NOM-242-SSA1-2009, Productos y Servicios. Productos de la Pesca Frescos, Refrigerados, Congelados y Procesados. Especificaciones Sanitarias y Métodos de Prueba; Diario Oficial de la Federación: Ciudad de Mexico, Mexico, 2011. [Google Scholar]
- Cho, K.; Pachepsky, Y.; Oliver, D.; Muirhead, R.; Park, Y.; Quilliam, R.; Shelton, D. Modeling fate and transport of fecally-derived at the watershed scale: State of the science and future opportunities. Water Res. 2016, 100, 38–56. [Google Scholar] [CrossRef] [PubMed]
- SAGARPA-SENASICA. Manual de Buenas Prácticas de Manejo a Bordo en Embarcaciones Menores; SAGARPA: Ciudad de Mexico, Mexico, 2015. [Google Scholar]
- Steffen, R.; Hill, D.; DuPont, H. Traveler’s diarrhea: A clinical review. JAMA 2015, 313, 71–80. [Google Scholar] [CrossRef] [PubMed]
- Salas-Pérez, J.; Salas-Monreal, D.; Monreal-Gómez, M.; Riverón-Enzástiga, M.; Llasat, C. Seasonal absolute acustic intensity, atmospheric forcing and currents in a tropical coral reef system. Estuarine. Coast. Shelf Sci. 2012, 100, 102–112. [Google Scholar] [CrossRef]
- Shawyer, M.; Medina, A. El Uso del Hielo en Pequeñas Embarcaciones de Pesca; Documento Técnico de Pesca; FAO: Roma, Italy, 2005; p. 436. [Google Scholar]
Figure 2.
Variation in the most probable number (MPN) of total coliforms (TC) isolated from: (A) fresh octopus capture in the Enmedio, Chopa and La Gallega reefs, (B) freshwater in post-capture stage in different climatic seasons, (C) boiled and fresh octopus in processing stage and (D) packed-in-ice and boiled octopus from commercialization stage.
Figure 2.
Variation in the most probable number (MPN) of total coliforms (TC) isolated from: (A) fresh octopus capture in the Enmedio, Chopa and La Gallega reefs, (B) freshwater in post-capture stage in different climatic seasons, (C) boiled and fresh octopus in processing stage and (D) packed-in-ice and boiled octopus from commercialization stage.
Figure 3.
Variation in the most probable number (MPN) of fecal coliforms (FC) isolated from: (A) fresh octopus capture in the Enmedio, Chopa and La Gallega reefs, (B) freshwater in post-capture stage in different climatic seasons, (C) boiled and fresh octopus in processing stage and (D) packed-in-ice and boiled octopus from commercialization stage.
Figure 3.
Variation in the most probable number (MPN) of fecal coliforms (FC) isolated from: (A) fresh octopus capture in the Enmedio, Chopa and La Gallega reefs, (B) freshwater in post-capture stage in different climatic seasons, (C) boiled and fresh octopus in processing stage and (D) packed-in-ice and boiled octopus from commercialization stage.
Figure 4.
Anomalies of temperature (A) and salinity (B) in the Veracruz Reef System during 2019. Monthly precipitation anomalies (C) in Veracruz from January 2019 to December 2020. Jamapa River discharge rate (D) expressed in anomalies from January 2019 to August 2020.
Figure 4.
Anomalies of temperature (A) and salinity (B) in the Veracruz Reef System during 2019. Monthly precipitation anomalies (C) in Veracruz from January 2019 to December 2020. Jamapa River discharge rate (D) expressed in anomalies from January 2019 to August 2020.
Table 1.
Results of the Kruskal–Wallis tests, examining the mean differences in the concentration of total coliforms (TC MPN ± σ) isolated in the samples of seawater, freshwater, fresh octopus, octopus boiled, octopus packed in ice, and ice with regard to the space–temporal distribution and the stages of the octopus production chain (capture, post-capture, processing and commercialization). Identical superscript letters mean no significant differences (NS). Asterisks indicate statistically significant differences (p < 0.05).
Table 1.
Results of the Kruskal–Wallis tests, examining the mean differences in the concentration of total coliforms (TC MPN ± σ) isolated in the samples of seawater, freshwater, fresh octopus, octopus boiled, octopus packed in ice, and ice with regard to the space–temporal distribution and the stages of the octopus production chain (capture, post-capture, processing and commercialization). Identical superscript letters mean no significant differences (NS). Asterisks indicate statistically significant differences (p < 0.05).
| Stages | Zone | Climatic Seasons | Sample | TC (MPN ± σ) | N | p |
|---|---|---|---|---|---|---|
| Capture | Southern zone (Enmedio) | Dry | Sea water | 14.4 ± 13.9 a | 6 | 0.2305 NS |
| Rainy | Sea water | 1.8 ± 0 a | 6 | |||
| Windy | Sea water | 8.15 ± 8.19 a | 12 | |||
| Dry | Fresh octopus | 2.4 ± 1.04 a | 3 | 0.0273 * | ||
| Rainy | Fresh octopus | 22 ± 1.73 b | 3 | |||
| Windy | Fresh octopus | 91.1 ± 45.92 c | 6 | |||
| Southern zone (Chopa) | Dry | Sea water | 3.15 ± 1.48 a | 6 | 0.0608 NS | |
| Rainy | Sea water | 1.8 ± 0 a | 6 | |||
| Windy | Sea water | 25.15 ± 25.47 a | 12 | |||
| Dry | Fresh octopus | 3.73 ± 3.00 a | 3 | 0.0141 * | ||
| Rainy | Fresh octopus | 37.33 ± 7.51 b | 3 | |||
| Windy | Fresh octopus | 286.83 ± 447.55 c | 3 | |||
| Northern zone (La Gallega) | Dry | Sea water | 1.8 ± 0 a | 6 | 1 NS | |
| Rainy | Sea water | 1.8 ± 0 a | 6 | |||
| Windy | Sea water | 1.8 ± 0 a | 6 | |||
| Dry | Fresh octopus | 61.33 ± 12.22 a | 3 | 0.0273 * | ||
| Rainy | Fresh octopus | 1373.33 ± 392.59 b | 3 | |||
| Windy | Fresh octopus | 34.73 ±8.81 c | 3 | |||
| Between zones (Southern, Northern) | Fresh octopus | 0.4202 NS | ||||
| Post-capture | Southern zone | Dry | Freshwater | 540 ± 0 a | 3 | 0.0273 * |
| Rainy | Freshwater | 240 ± 0 b | 3 | |||
| Windy | Freshwater | 79 ± 0 c | 3 | |||
| Northern zone | Not applicable | Not applicable | ||||
| Processing | Both zones | Not applicable | Boiled octopus | 226.06 ± 290.82 a | 9 | 0.3063 NS |
| Fresh octopus | 212.53 ± 457.61 a | 36 | ||||
| Commercialization | Both zones | Not applicable | Boiled octopus | 226.06 ± 290.82 a | 9 | 0.003 * |
| Octopus packed in ice | 853.93 ± 463.87 b | 9 | ||||
| Ice | 1600 ± 0 | 9 |
Table 2.
Results of the Kruskal–Wallis tests, examining the mean differences in the concentration of fecal coliforms (FC MPN ± σ) isolated in the samples of seawater, freshwater, fresh octopus, octopus boiled, octopus packed in ice, and ice with regard to the space–temporal distribution and the stages of the octopus production chain (capture, post-capture, processing and commercialization). Identical superscript letters mean no significant difference (NS). Asterisks indicate statistically significant differences (p < 0.05).
Table 2.
Results of the Kruskal–Wallis tests, examining the mean differences in the concentration of fecal coliforms (FC MPN ± σ) isolated in the samples of seawater, freshwater, fresh octopus, octopus boiled, octopus packed in ice, and ice with regard to the space–temporal distribution and the stages of the octopus production chain (capture, post-capture, processing and commercialization). Identical superscript letters mean no significant difference (NS). Asterisks indicate statistically significant differences (p < 0.05).
| Stages | Zone | Climatic Seasons | Sample | FC (MPN ± σ) | N | p |
|---|---|---|---|---|---|---|
| Capture | Southern zone (Enmedio) | Dry | Sea water | 4.5 ± 0 a | 3 | 0.3827 NS |
| Rainy | Sea water | 0 a | 3 | |||
| Windy | Sea water | 1.8 ± 0 a | 3 | |||
| Dry | Fresh octopus | 0 a | 3 | 0.0495 * | ||
| Rainy | Fresh octopus | 6.7 ± 1.91 b | 3 | |||
| Windy | Fresh octopus | 4.7 ± 0 c | 3 | |||
| Southern zone (Chopa) | Dry | Sea water | 0 | 6 | Not applicable | |
| Rainy | Sea water | 0 | 6 | |||
| Windy | Sea water | 0 | 6 | |||
| Dry | Fresh octopus | 1.87 ± 0.12 a | 3 | 0.0201 * | ||
| Rainy | Fresh octopus | 29.67 ±5.77 b | 3 | |||
| Windy | Fresh octopus | 1.3 ± 0.52 c | 3 | |||
| Northern zone (La Gallega) | Dry | Sea water | 0 | 6 | Not applicable | |
| Rainy | Sea water | 0 | 6 | |||
| Windy | Sea water | 0 | 6 | |||
| Dry | Fresh octopus | 56.33 ± 20.03 a | 3 | 0.0273 * | ||
| Rainy | Fresh octopus | 203.33 ± 63 b | 3 | |||
| Windy | Fresh octopus | 14.5 ± 8.89 c | 6 | |||
| Between zones (Southern, Northern) | Fresh octopus | 0.0129 * | ||||
| Post-capture | Southern zone | Dry | Freshwater | 7.8 ± 0 a | 3 | 0.0273 * |
| Rainy | Freshwater | 33 ± 0 b | 3 | |||
| Windy | Freshwater | 12.4 ± 0 c | 3 | |||
| Northern zone | Not applicable | Not applicable | ||||
| Processing | Both zones | Not applicable | Boiled octopus | 18.91 ± 36.27 a | 12 | 0.6566 NS |
| Fresh octopus | 21.50 ± 46.65 a | 29 | ||||
| Commercialization | Both zones | Not applicable | Boiled octopus | 18.91 ± 36.27 a | 12 | |
| Octopus packed in ice | 266.72 ±339.76 b | 12 | 0.0041 * | |||
| Ice | 818.75 ± 816.03 c | 12 |
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
© 2023 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Share and Cite
MDPI and ACS Style
Acuña-Ramírez, S.; Jiménez-Badillo, M.d.L.; Galindo-Cortes, G.; Marval-Rodríguez, A.; Castañeda-Chávez, M.d.R.; Reyes-Velázquez, C.; Rodulfo-Carvajal, H.; De Donato-Capote, M. Environmental and Anthropogenic Influences on Coliform Concentrations in the Octopus insularis Production Chain in the Veracruz Reef System, Gulf of Mexico. Animals 2023, 13, 3049. https://doi.org/10.3390/ani13193049
AMA Style
Acuña-Ramírez S, Jiménez-Badillo MdL, Galindo-Cortes G, Marval-Rodríguez A, Castañeda-Chávez MdR, Reyes-Velázquez C, Rodulfo-Carvajal H, De Donato-Capote M. Environmental and Anthropogenic Influences on Coliform Concentrations in the Octopus insularis Production Chain in the Veracruz Reef System, Gulf of Mexico. Animals. 2023; 13(19):3049. https://doi.org/10.3390/ani13193049
Chicago/Turabian StyleAcuña-Ramírez, Sarai, María de Lourdes Jiménez-Badillo, Gabriela Galindo-Cortes, Angel Marval-Rodríguez, María del Refugio Castañeda-Chávez, Christian Reyes-Velázquez, Hectorina Rodulfo-Carvajal, and Marcos De Donato-Capote. 2023. "Environmental and Anthropogenic Influences on Coliform Concentrations in the Octopus insularis Production Chain in the Veracruz Reef System, Gulf of Mexico" Animals 13, no. 19: 3049. https://doi.org/10.3390/ani13193049
APA StyleAcuña-Ramírez, S., Jiménez-Badillo, M. d. L., Galindo-Cortes, G., Marval-Rodríguez, A., Castañeda-Chávez, M. d. R., Reyes-Velázquez, C., Rodulfo-Carvajal, H., & De Donato-Capote, M. (2023). Environmental and Anthropogenic Influences on Coliform Concentrations in the Octopus insularis Production Chain in the Veracruz Reef System, Gulf of Mexico. Animals, 13(19), 3049. https://doi.org/10.3390/ani13193049
Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.
