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Revista mexicana de ciencias agrícolas
Print version ISSN 2007-0934
Rev. Mex. Cienc. Agríc vol.9 n.7 Texcoco Sep./Nov. 2018 Epub Sep 30, 2020
https://doi.org/10.29312/remexca.v9i7.1669
Articles
Use of Saccharomyces cerevisiae to control the quantity and quality of water in white shrimp culture
1Postgraduate School-Campus Veracruz. Manlio Fabio Altamirano, Veracruz, Mexico. CP. 91690. Tel. 01 (229) 2010770. (martha.martinez@colpos.mx; jretam@colpos.mx).
2Postgraduate College-Campus Córdoba. Congregation Manuel Leon, Amatlan de los Reyes, Veracruz, Mexico. CP. 94946. (vicmor@colpos.mx).
3Phileo Lesaffre Animal Care. (bfd-2216@hotmail.com)
4Center for Teaching, Research and Extension in Tropical Livestock-Faculty of Veterinary Medicine and Zootechnics. National Autonomous University of Mexico. Federal Highway Martinez de la Torre-Tlapacoyan km 5.5, Veracruz, Mexico. CP. 93650. (tilapia1@hotmail.com).
We evaluated the effect of BlueEnergyRent product based on yeast Saccharomyces cerevisiae and molasses, on the cultivation of white shrimp Litopenaeus vannamei, determining the impact on water quality parameters, and productive. The experiment was carried out at the Acuilan aquaculture farm, located in La Antigua, Veracruz, Mexico, in 2015. In the shrimp culture, 1.5 g/m3/day of the active molasses-yeast mixture was added as the first treatment and a daily dose adjusted based on the total ammoniacal nitrogen in the second treatment. Both were compared against a treatment with constant water flow. It was observed that BlueEnergyRent did not negatively affect the quality of the water, the productive parameters presented better levels with the treatment based on the total ammoniacal nitrogen, and it was possible to reduce the consumption of water for each kg of shrimp produced to 3.9 m3 kg-1. Healthy organisms with normal growth were harvested with a feed conversion ratio of 1.19. By using BlueEnergyRent the use of water is improved without affecting crop performance.
Keywords: aquaculture; nitrogen compounds; yeast
Se evaluó el efecto de BlueEnergyRent producto a base de levadura Saccharomyces cerevisiae y melaza, en el cultivo de Camarón blanco Litopenaeus vannamei, determinando el impacto en los parámetros de calidad del agua, y productivos. El experimento se llevó a cabo en la granja acuícola Acuilan, ubicada en La Antigua, Veracruz, México, en el año 2015. En el cultivo de camarón se agregó 1.5 g m-3 día-1 de la mezcla activa melaza-levadura como primer tratamiento y una dosis diaria ajustada en base al nitrógeno amoniacal total en el segundo tratamiento. Ambos fueron comparados contra un tratamiento con flujo constante de agua. Se observó que BlueEnergyRent no afectó negativamente la calidad del agua, los parámetros productivos presentaron mejores niveles con el tratamiento en base al nitrógeno amoniacal total, y se logró reducir el consumo de agua por cada kg de camarón producido a 3.9 m3 kg-1. Se cosecharon organismos sanos con crecimiento normal con una tasa de conversión alimenticia de 1.19. Al usar BlueEnergyRent se mejora el uso del agua sin afectar el desempeño del cultivo.
Palabras claves: acuacultura; compuestos nitrogenados; levadura
Introduction
The aquaculture industry has received strong criticism due to the negative environmental and economic effects perceived by excessive water consumption and, at the same time, by the subsequent release of wastewater. Which leads to direct this activity towards a concept of sustainable aquaculture. Although the specific definitions of sustainable aquaculture are varied, the limited use of water is key in any of the definitions and there is an increasing demand on the part of consumers of products grown in systems with environmental responsibility.
At present, numerous efforts have been made to develop recirculation systems and tending to zero water exchange, using chemical and biological filters, which lead to maintaining water quality by eliminating toxic metabolites, such as ammonia (NH3) and nitrite (NO2 -), in addition to ammonia nitrogen (NH3 + NH4 +), which is excreted by organisms and produced by the microbial decomposition of uneaten food (De la Mora et al., 2003).
One option that has been effective in maintaining water quality in aquaculture crops has been the use of beneficial microorganisms such as bacteria and algae, which is known as bio-floc. Serrano and Machuca (2013) in studies with controlled temperature conditions, determined the efficiency of yeasts as a water quality control agent, mainly on the concentration of ammoniacal nitrogen.
The objective of this research was to evaluate the effectiveness of a product based on yeast BlueEnergyRent on the control of the quantity and quality of the culture water, as well as its effect on the production parameters of shrimp Litopenaeus vannamei, one of the culture organisms of greater production and importance in international aquaculture (Plascencia and Almada, 2012).
Material and methods
Location of the experiment
The research was carried out at the aquifer farm Acuilan SPR de RL, located in the Central Region of the state of Veracruz. With location of 19° 22’ north latitude, 96° 22’ west longitude, at an elevation of 20 meters above sea level. It presents an AW2 climate.
Acclimatization of postlarvae
The postlarvae (pL) of white shrimp (L. vannamei) acquired in the laboratory of Camaronera, SA de CV, Alvarado, Veracruz, Mexico was cultivated. The initial size was pL15, with an average weight of 4.6 mg. The postlarvae were transported in two transparent plastic bags with a volume of 28.0 L of water at a salinity of 30 ‰. They were acclimated for 5 days, until obtaining a salt of 2 ‰.
Experimental unit
It consisted of concrete ponds, ten of them with a capacity of 16 m3 and two ponds of 9.6 m3. Each pond had permanent aeration through a 0.5 HP blower, maintaining dissolved oxygen levels in suitable ranges for the culture of 5-15 mgL-1.
Cultivation period
After acclimatization, 60 pl m-3 were sown in each of the 12 concrete ponds with a weight of 19.6 mg. The experimentation began the fourth week of June to the third week of September 2015 completing 86 days of experimentation.
Product to evaluate
The product BlueEnergyRent (BE) was used, formulated with yeast base Saccharomyces cerevisiae together with a mixture of dehydrated molasses, vitamins and minerals, in a ratio of 1:10.
Experimental design
Three experimental treatments were used: the T1 treatment consisted in the application of a daily dose of BE 1.5 mg m-3 and zero water exchanges, the T2 treatment consisted of a dose of BE in proportion to the estimated amount of the total ammonia nitrogen (NAT) present in the water and zero water exchanges, the T3 treatment consisted in not adding BE and maintaining a water exchange of 1.28 m3 h-1. The distribution of the treatments was completely random, each with four repetitions.
To determine the BE dose in T2, the NAT present in the water was calculated as mentioned by Brunty et al. (1997) applying the following formula:
NAT= 0.604*N-food + 3.88
On the recommendation of the BlueEnergyRent supplier, the NAT was multiplied by a factor of 11, based on the C:N ratio in the culture water; both doses were weighed on a portable Braunker® scale, and then hydrated by shaking for 20 minutes in one liter of water.
Feeding
The feeding was distributed in 3 schedules giving 25% at 6:00 am, 25% at 12:00 pm and 50% of the food at 6:00 pm.
Measurement of water quality parameters
Daily the physical and chemical parameters of the water were measured twice a day, morning and evening, with a YSI professional plus® equipment and a Hanna® brand potentiometer. The parameters measured were: temperature (°C), dissolved oxygen (mgL-1), salinity (‰), total ammoniacal nitrogen (mgL-1) and hydrogen potential.
Water use and economic indicators
The following indicators were evaluated: volume of water used (m3), efficiency of water use (m3 kg-1). Production cost ($ MN), utility ($ MN).
Biometrics
Every 8 days, 30 shrimp were caught from each stake and weighed with a portable Braunker® scale, while 10 of these shrimps were measured with a ruler graduated in cm.
In the eleventh biometrics, experimentation was terminated. Each of the ponds was emptied and the final number of shrimp was counted. The 50 organisms from each pond were measured and weighed individually to determine average weight and size.
Results
Parameters of water quality
The five parameters of water quality evaluated showed a significant difference of the treatments T1 and T2 compared with T3 (Table 1).
Table 1 Average value of salinity and pH evaluated in the white shrimp culture (L. vannamei) at 8:00 a.m. and 5:00 p.m. respectively
| Parameters | Hour | Treatment 1 | Treatment 2 | Treatment 3 |
|---|---|---|---|---|
| Salinity ‰ | 8:00 am | 1.73 ±0.12 a | 1.75 ±0.11 a | 2.05 ±0.03 b |
| 5:00 pm | 1.74 ±0.12 a | 1.76 ±0.12 a | 2.05 ±0.03 b | |
| pH | 8:00 am | 9.01 ±0.33 a | 9.06 ±0.37 a | 8.26 ±0.17 b |
| 5:00 pm | 9.28 ±0.23 a | 9.3 ±0.27 a | 8.64 ±0.13 b |
Means with the same letter within columns are significantly equal, according to the Tukey test (p≤ 0.05).
Regarding the temperature obtained, it was observed that during the mornings it remained in the optimum range for shrimp culture, in the afternoon the temperature of the treatments T1 and T2 (without water exchange) exceeded the recommended average (Table 1).
The variations in the levels of O2 were similar in the treatments T1 and T2, remaining in the range of 4.5 mg L-1 and up to 8.5 mg L-1. In the T3 treatment, O2 presented higher levels than the T1 and T2 treatments (Table 1).
Salinity was found within the ranges of survival of the shrimp, the values remained stable in T3. The lowest values were recorded in treatments T1 and T2 as shown in Table 1.
Regarding NAT, it is observed that there is a significant difference between the treatments T1 and T2 compared with T3.
The pH reached high values in the treatments T1 and T3 (without water exchange) staying above 9 from the second day and during most of the experimentation, in the T3 the pH remained constant.
Water use and economic indicators
Regarding the use of water, the T1 and T2 treatments presented greater efficiency (Table 2). The T3 uses 100 times more water with similar performance (Table 3).
Table 2 Water use and economic indicators.
| Characteristics | Treatment 1 | Treatment 2 | Treatment 3 |
|---|---|---|---|
| Water use (m3) | 90.3 a | 90.2 a | 10 011.972 b |
| Water efficiency (m3 kg-1) | 4.19 ±1.46 a | 3.78 ±1.45 a | 438.74 ±303.76 b |
| Production cost ($ kg-1) | 78.52 ±2.24 | 74.74 ±2.02 | 96.32 ±6.6 |
| Utility ($) | 1217.87 | 1439.07 | 882.68 |
Table 3 Production parameters of the white shrimp culture (L. vannamei).
| Parameters | Treatment 1 | Treatment 2 | Treatment 3 |
|---|---|---|---|
| Weight gain g | 7.17 ±1.26 a | 7.96 ±1.54 a | 15.0 ±1.35 b |
| Size cm | 10.27 ±0.79 a | 10.62 ±0.94 a | 13.31 ±0.31 b |
| Daily growth rate | 0.08 ±0.01 a | 0.09 ±0.01 a | 0.17±0.01 b |
| Feed conversion rate | 1.32 ±0.36 a | 1.19 ±0.33 a | 1.42±0.87 a |
| (%) survival | 73.7 ±3.03 a | 66 ±7.91 ab | 45 ±21.01 b |
Means with the same letter within columns are significantly equal, according to the Tukey test (p≤ 0.05).
Treatment T2 had a lower production cost than T1 and T3 (Table 2), this led to a saving of 22.4% compared to treatment T3. Concerning the efficiency in the use of water, the T3 presents significant difference in relation to T1 and T2 (Table 2).
Productive parameters
The productive parameters are presented in Table 3, the treatment T2 with the dose according to the presence of TAN in the water was the one that generated the highest biomass 23.8 kg (Figure 1) maintaining the highest feed conversion rate. The T1 maintained the highest survival percentage with 73.7%. In T3 the organisms obtained the highest size and the highest weight gain, which is reflected in a daily growth rate of 0.17 g.
Discussion
The temperatures in the treatments T1 and T2 exceeded the maximum allowable for the shrimp culture, as recommended by Quiñonez et al. (2010) that mentions that the shrimp of the species L. vannamei maintain their optimum level of cultivation at temperatures of 30 °C because the energy expenditure is not high. The difference between the temperatures of the treatments with zero water exchange and the T3 treatment was due to the fact that the water was stagnant and with direct exposure to the sun, the T3 treatment having a constant flow could maintain its temperature two degrees below (Figure 2).
Dissolved oxygen (OD) presented variations between morning and afternoon due to planktonic activity and the presence of filamentous algae of the genus Cladophora. The T1 and T2 treatments were within the recommended parameters for the shrimp culture, the T3 treatment showed dissolved oxygen saturations in the afternoons (Figure 2). In works carried out with zero water exchange and planting densities similar to those of the present investigation, average values have been recorded in the OD of 6.08 mg L-1 to 6.3 mg L-1 (Audelo-Naranjo et al., 2012; Furtado et al., 2015)
In none of the treatments was below the minimum recommended salinity; however, there was a significant difference between the concentration of salts in T1 and T2 with respect to T3. The amount of dissolved salts in the water was lower in the treatments with zero water exchanges, probably due to the need of the organisms to capture the dissolved minerals and compensate the required salinity. Shrimp require Calcium for the molting process, so this mineral must be taken continuously from the environment (Ceballos et al., 2012).
In all three treatments, the recommended concentration of NAT was exceeded, with significant differences of ±1.5 mg L-1 between morning and afternoon. In the treatments with zero water exchanges the highest concentrations were recorded, the T3 treatment showed the lowest values. The concentration of NAT in the experiment dropped drastically on the seventh day (Figure 3), coinciding with the reports of Luo et al. (2013) where the decrease in 5 days of the NAT levels from 117.285 mg L-1 to 2.5 mg L-1 was observed when adding a carbon source. The high concentrations of nitrogenous compounds in ponds can be attributed to the decomposition of uneaten food and feces (Campaña-Torres et al., 2009).
Figure 3 Fluctuation of total ammonia nitrogen (NAT) in the treatments in the morning and afternoon.
The pH showed a significant difference in value between the treatments with zero replacements and the T3 treatment. In the treatments T1 and T2 pH 9 values higher than the recommended maximum were registered. According to Whetstone et al. (2002) with pH values above 9 organisms can survive with a very slow growth, obtaining an optimal growth when the pH value is in ranges of 6-9. When working with Penaeus monodonPanjaitan (2010) on zero water exchange, using molasses in different doses and preserving the C:N ratio for the bacterial use of nitrogen compounds, the trend was downward in the pH levels, on the contrary in the present investigation there was a rapid increase in pH levels in the T1 and T2 treatments.
In relation to the efficiency in the use of water, treatments T1 and T2 turned out to be the best alternative to T3 (Table 2). The water expenditure in the T3 treatment was considerably high. Chamberlain (2002) mentions that water consumption for shrimp production on an intensive farm in Texas decreased from 37.6 m3 kg-1 to 1.5 m3 kg-1. In the present work, it was possible to reduce from 438.74 m3 kg-1 to 3.78 m3 kg-1.
Regarding economic efficiency, the production cost of the T1 treatments was lower than that recorded in T3 (Table 2). In the productive parameters a marked difference was registered between the final weight gain of the T1 and T2 treatments compared to the T3 treatment, the treatments with zero water exchange reported a lower growth, the obtained weights coincide with those reported in conditions similar to low salinity and with the use of well water in ranges ranging from 15 g to 8.8 g (Nunes and Velásquez, 2001; Miranda et al., 2010; Quiñonez et al., 2010).
Regarding the obtained height, the treatments T1 and T2 showed the lowest growth with an average size of 10.62 cm. González et al. (2008) mention that during its experimentation it was possible to reach lengths of 13 cm in length, coinciding with the sizes reached by the T3 treatment organisms.
The daily growth rate showed a significant difference between the T1 and T2 treatments compared to the T3 treatment, which had the highest daily gain, the growth presented in the treatments with zero water exchange was similar to that reported by González et al. (2008) who obtained 0.9 g per week, equivalent to 0.12 g per day. (Table 3).
With respect to TCA, treatment T2 obtained the best rate of 1.19, treatment T3 presented the highest conversion rate 1.42. Sowers et al. (2006) reports food conversion rates of up to 2.3. In an investigation with a similar seeding density TCA of up to 1.2 has been reported (Manzo, 2000).
The culture represented a percentage of survival of 73% and 66% for the treatments T1 and T2 respectively, this result can be considered important because other authors obtained survival of 60% and 69% at a salinity of 2 ‰ (Atwood et al., 2003). The T3 treatment presented the lowest survival.
Conclusions
In relation to the quality of the water, the experimental conditions tending to the zero exchange show increases in temperature and in pH. Regarding nitrogen, there was the presence of plankton and filamentous algae that contribute to the consumption of nitrogen compounds. BlueEnergyRent insisted on the control of these compounds, as the dose added to the crop was increased.
The use of BlueEnergyRent contributes to reduce the use of water in aquaculture farms, using 110 times less water than in a traditional culture with constant flow.
The low cost of production and significant savings in the use of water that is not only linked to the environmental benefit, but also to the economic benefit in the face of reduced water use.
Obtained visibly healthy organisms, with size and weight appropriate to their stage of life. The use of BlueEnergyRent as a water quality control agent has positive effects on the productive response of white shrimp.
Acknowledgments
To the Acuicola Acuilan farm for facilitating the use of its facilities, To the National Council of Science and Technology for the support of the research project and the Postgraduate School Campus Veracruz, to SAFMEX for the partial financing of the research.
REFERENCES
Atwood, H. L.; Young, S. P.; Tomasso, J. R. and Browdy, C. L. 2003. Survival and growth of pacific white shrimp litopenaeus vannamei postlarvae in low-salinity and mixed-salt environments. J. World Aquac. Soc. 34(4):518-523. [ Links ]
Audelo, N. J. M.; Voltolina, D. and Romero, B. E. 2012. Culture of white shrimp (litopenaeus vannamei boone, 1931) with zero water exchange and no food addition: An eco-friendly approach. Latin Am. J. Aquatic Res. 40(2):441-447. [ Links ]
Brunty, J.; Bucklin, R.; Davis, J.; Baird, C. and Nordstedt, R. 1997. The influence of feed protein intake on tilapia ammonia production. Aquac. Eng. 16(3):161-166. [ Links ]
Campaña, T. A.; Martínez, C. L. R.; Villarreal, C. H.; Hernández, L. J.; Ezquerra, B. J. M. and Cortés, J. E. 2009. Efecto de la adición del rotífero Brachionus rotundiformis (tschugunoff, 1921) sobre la calidad del agua y la producción, en cultivos super-intensivos de camarón blanco del pacífico Litopenaeus vannamei (boone, 1931). Revista Biol. Marina Ocean. 44(2):335-342. [ Links ]
Ceballos, B. J.; Cabrera, M., J. E. and Vega-Villasante, F. 2012. Cultivo tierra adentro de camarón marino litopenaeus vannamei: evaluación del agua de dos granjas acuícolas REDVET - Rev. Electr. Veter. 13(6). [ Links ]
Crab, R.; Kochva, M.; Verstraete, W. and Avnimelech, Y. 2009. Bio-flocs technology application in over-wintering of tilapia. Aquac. Eng. 40(3):105-112. [ Links ]
Chamberlain, G. 2002. Cultivo sostenible de camarón: mitos y realidades. Infofish Internacional. 2(11). http://www.innovacion.gob.sv/inventa/attachments/article/287/Mitos%20 Realidades.pdf. [ Links ]
De la Mora, G.; Villareal, D. E. L.; Arredondo, F. J. L.; Ponce, P J. T. and. Barriga, S. I. D. L. A 2003. Evaluación de algunos parámetros de calidad del agua en un sistema cerrado de recirculación para la acuicultura, sometido a diferentes cargas de biomasa de peces. Hidrobiológica. 13(4):247-253. [ Links ]
Furtado, P. S.; Campos, B. R.; Serra, F. P.; Klosterhoff, M.; Romano L. A. and Wasielesky, W. 2015. Effects of nitrate toxicity in the pacific white shrimp, litopenaeus vannamei, reared with biofloc technology (bft). Aquac. Inter. 23(1):315-327. [ Links ]
González, J. F. A.; Campaña, L. M. F.; Ceja, A. I. and Rubio, Y. G. 2008. Crecimiento de camarón blanco (Litopenaeus vannamei) en un estanque rústico a baja salinidad. AquaTIC: 28:8-15. [ Links ]
Hamlin, H. J.; Michaels, J. T.; Beaulaton, C. M.; Graham, W. F.; Dutt, W.; Steinbach, P.; Losordo, T. M.; Schrader, K. K. and Main, K. L. 2008. Comparing denitrification rates and carbon sources in commercial scale upflow denitrification biological filters in aquaculture. Aquac. Eng . 38(2):79-92. [ Links ]
Luo, G. Z.; Avnimelech, Y.; Pan Y. F. and Tan, H. X. 2013. Inorganic nitrogen dynamics in sequencing batch reactors using biofloc technology to treat aquaculture sludge. Aquac. Eng . 52(1):73-79. [ Links ]
Manzo, D. H. 2000. Efecto de cuatro densidades de siembra sobre el crecimiento de camaron blanco litopenaeus vannamei (boone, 1931) cultivado en estanques rústicos, en manzanillo colima. Facultad de Ciencias Marinas. Universidad de Colima. Manzanillo, Col. 53 p. [ Links ]
Miranda, I.; Valles, J. L.; Sánchez, R. and Álvarez, Z. 2010. Cultivo del camarón marino litopenaeus vannamei (boone, 1931) en agua dulce. Rev. Científ. 20(4):339-346. [ Links ]
Nunes, A. and Velasquez, L. 2001. Low-salinity, inland shrimp culture in brazil and ecuador-economics, disease issues move farms away from coasts. Global Aquaculture Advocate. 4(3):62-64. [ Links ]
Panjaitan, P. 2010. Shrimp culture of penaeus monodon with zero water exchange model (zwem) using molasses. J. Coastal Develop. 14(1):35-44. [ Links ]
Plascencia, A. E. and Almada, M. D. C. B. 2012. La acuicultura y su impacto al medio ambiente. Estudios Sociales. Revista de alimentación contemporánea y desarrollo regional. http://www.redalyc.org/articulo.oa?id=41724972010. [ Links ]
Quiñonez, W. V.; Quiroz, G. R. and Leal, H. M. E. 2010. Cultivo intensivo de camarón blanco Litopenaeus vannamei (boone) en agua de pozo de baja salinidad como alternativa acuícola para zonas de alta marginación. Ra Ximhai. 6(1):1-8. [ Links ]
Serrano, H. B. and Machuca, C. G. 2013. Comparación de la levadura (Saccharomycess cereviceae) y el azúcar, en el control de la calidad del agua en el cultivo de camarón blanco (Penaeus vannamei), en sistema de cultivo cerrado. Facultad de Ciencias Marinas de la UABC, Reportes de laboratorio (comunicación personal, diciembre 2013). [ Links ]
Sowers, A. D.; Tomasso Jr, J. R.; Browdy, C. L. and Atwood, H. L. 2006. Production characteristics of litopenaeus vannamei in low-salinity water augmented with mixed salts. J. World Aquac. Soc. 37(2):214-217. [ Links ]
Whetstone, J. M.; Treece, G. D.; Browdy, C. L. and Stokes, A. D. 2002. Opportunities and constraints in marine shrimp farming. Southern Regional Aquaculture Center. https://agrilifecdn.tamu.edu/fisheries/files/2013/09/SRAC-Publication-No.-2600-Opportunities-and-Constraints-in-Marine-Shrimp-Farming.pdf. [ Links ]
Received: June , 2018; Accepted: October , 2018
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