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Preventing Disease Outbreaks in Flowing Aquaculture Systems through Water Flow Management

Introduction

Disease outbreaks are one of the worst and most devastating occurrences in the commercial aquaculture. In the case of producers who maintain running water systems such as raceways, flow-through tanks, and recirculating aquaculture systems (RAS) the flow of water via a common infrastructure can be seen as a highly efficient protective mechanism as well as a possible transmission agent. Knowledge of the biological hazards that these environments present is the critical leading step that can be made to develop successful defense to prevent aquaculture disease.
The flowing aquaculture systems are prone to a wide range of pathogenic organisms. Bacterial disease-causing organisms include some of the most common such as Aeromonas hydrophila, Flavobacterium columnare (the cause of columnaris disease), and Yersinia ruckeri (the cause of enteric red mouth disease) commonly derived in the case of affected salmonid and warmwater fish. The parasite infestations especially Ichthyophthirius multifiliis, white spot or Ich (Ichthyophthirius multifiliis), Gyrodactylus spp, and Trichodina spp. do well in the waters with low water quality and high fish concentration. Salmonid populations can suffer massive impacts that undermine immune responses (Shinn et al., 2015).
 

Flow and Circumference Patterns

Pathogen load, oxygenation, and the efficiency of waste removal all of which establishes the disease risk baseline that the fish population is exposed to are directly dependent on the flow rate and circulation design of a fish-rearing system. When poorly designed flowing system water management, then, the exchanges of water occur sufficiently high to keep a continuous leakage of metabolic waste products, uneaten feed and limit the buildup of pathogen-filled biofilms on the tank surfaces.
Stagnant zones areas with low velocity in which the movement of water is negligible are some of the riskiest characteristics. Dissolved oxygen is depleted more quickly in these dead zones, the organic waste is high and the concentration of the pathogens is higher than in well-flushed regions. By flocking around stagnant areas, fish are also exposed to compounding immunosuppressive stress by having a higher pathogen concentration coupled with a lower oxygen supply. Experiments on the hydraulics of raceway systems and circular tanks had shown that even small asymmetries in the placement of the inlets or where the outlets are located can create surprisingly large dead zones which cannot be detected by standard visual inspection (Summerfelt et al., 2004).
The fish tank disease prevention is most important. Fish tank should be circular and the tangential inlet flow forms a rotating current that moves waste materials to a central outflow, which reduces the formation of dead zones and the overall water quality in the tank is relatively homogenous. Longitudinal flow uniformity can be enhanced in raceways by spacing of baffles and inlet diffusers in a manner that prevents the high oxygen and low waste water quality gradients at the inlet and the low oxygen and high waste water quality gradients at the outlet which have a negative impact on fish in downstream sections. The flow rates are species-specific: Atlantic salmon and rainbow trout are much more active in terms of water exchange rates than tilapia or catfish, as they demand more oxygen and cannot withstand the accumulation of metabolic waste.
Preventing Disease Outbreaks in Flowing Aquaculture Systems through Water Flow Management 1

Oxygenation and Removal of Wastes:

The concentration of dissolved oxygen (DO) is the most significant water quality parameter in flowing aquaculture systems and its control cannot be separated with disease prevention. Fish in which chronically optimum DO levels are kept to levels that are even slightly lower than the saturation level of the species demonstrate suppressive effects on innate immune system, decreased phagocytic performance and a high level of cortisol, all of which compromise bacteria and parasitic infections (Tort, 2011).
DO is added in flowing system by a mix of inflow water, reaeration of the surface and in intensive tasks, by supplemental aeration or injection of pure oxygen. Pure oxygen systems that are capable of supersaturating water up to 150-200 percent saturation enable the operator to keep the target DO levels at extremely high fish biomass densities.
Water chemistry control is equally important in the control of ammonia and nitrite. Un- ionized ammonia produces gill damage, decreased oxygen uptake efficiency, and hypothalamic-pituitary-interrenal stress axis even at 0.02-0.05 mg/L concentrations. The combination of controlling the rate of feeding, flow volumes and biological filtration capacity is critical in ensuring that ammonia is kept at levels that do not affect the health of fish (Wedemeyer, 1996).
 

Tracking Fish Behavior:

Even the most advanced water management systems cannot offer much security when the symptoms of illness are not recognized, and the complete outbreak has already taken place. Early behavioral surveillance can thus be regarded as a requisite part of an all-inclusive disease prevention procedure with flowing systems. Fish express physiological condition via apparent actions way ahead of the gross pathological signs lesions, bloodshed or massive death.
The major behavioral signs of incipient disease or stress are the signs of schooling cohesion, surface-crowding behavior (evidence of hypoxia or pathology in the gills), erratic or spiral swimming, diminished feed response, and abnormal positioning at tank inlets or outlets. Skilled farm personnel performing frequent behavioral evaluations are
able to notice these red flags several hours to days prior to the onset of clinical disease.
Preventing Disease Outbreaks in Flowing Aquaculture Systems through Water Flow Management 2

Biofilters, Sediment Taps, and UV Sterilizers:

The optimal disease-preventive impact of water flow management is attainable when coupled with an integrated set of filtration technology that covers physical, biological as well as microbial aspects of water quality. All filtration elements address a varied group of risks, and the collaboration of the entire process forms a multi-barrier defense that cannot be achieved by flowing water.
As a biological process, biolauration by use of fixed-bed, moving-bed, or drum biofilters forms communities of nitrifying bacteria that transform ammonia into nitrate, keeping the water in the very narrow range of water chemistry that sustains fish immune systems. Surface area and hydraulic loading of biofilters should be selected with great care to match the anticipated amounts of biomass in the system as well as the maximum rates of ammonia release during times of high fish growth or feeding rates; undersized biofilters are another frequent cause of ammonia shoots in the system. (Timmons & Ebeling, 2013).
Mechanical filtration using drum filters, swirl separators, and sediment settling zones is used to remove suspended solids such as pathogen-laden fecal particles. Drum filters with finer mesh and the ability to capture particles as small as 40-60 microns are also useful because they can eliminate parasite cysts and bacteria aggregates that other filters would cause the system to recycle.
The most directed pathogen-control device that has been ever given to the operators of the flowing systems is the ultraviolet (UV) sterilizers. Water that undergoes UV exposure chambers is dotted with ultraviolet radiation that interferes with the DNA of the pathogen and it will be unable to reproduce without the addition of chemical residues into the production environment. UV sterilizers have a wide range of bacteria, viruses and protozoan parasite and are especially useful in the system where water is partially recirculated or where the source of intake water is ambient with a load of pathogens.
 

Conclusion

The prevention of diseases in flowing aquaculture systems is essentially an environmental management activity. It is by designing and operating systems that achieve optimal flow patterns, eliminate any stagnant areas, maintain target water chemistry levels and incorporate and incorporate strong filtration at all levels of the water treatment. The producers can radically reduce the occurrence and severity of disease outbreaks without necessarily having to rely on therapeutic intervention as the main instrument.
The evidence is overwhelming, fish raised in highly oxygenated, low-ammonia, pathogen-reduced systems show higher immune functioning, greater growth rates, and a greatly reduced mortality rate than fish raised in poorly run systems.
We focus on providing professional-level solutions to a contemporary aquaculture business and specialize in the design of RAS systems, painstaking water quality control, and advanced equipment of fish farming. We integrate professional knowledge on the technical aspect together with practical experience gained in the industry to assist aquaculture practitioners in the development of efficient, bio secure, and environmental friendly production systems. We offer the knowledge and specialized services required to succeed in the current stressful aquaculture settings, in both system design as well as operational troubleshooting.

References

Bly, J. E., & Clem, L. W. (1992). Temperature and teleost immune functions. Fish & Shellfish Immunology, 2(3), 159–171. https://doi.org/10.1016/S1050-4648(05)80056-7
Costello, M. J. (2009). The global economic cost of sea lice to the salmonid farming industry. Journal of Fish Diseases, 32(1), 115–118. https://doi.org/10.1111/j.1365-2761.2008.01011.x
Føre, M., Frank, K., Norton, T., Svendsen, E., Alfredsen, J. A., Dempster, T., Eguiraun, H., Watson, W., Stahl, A., Sunde, L. M., Schellewald, C., Skøien, K. R., Alver, M. O., & Berckmans, D. (2018). Precision fish farming: A new framework to improve production in aquaculture.
Biosystems Engineering, 173, 176–193. https://doi.org/10.1016/j.biosystemseng.2017.10.014
Good, C., Davidson, J., Welsh, C., Snekvik, K., & Summerfelt, S. (2009). The effects of ozone on performance, health and welfare of rainbow trout Oncorhynchus mykiss in low-exchange recirculating aquaculture systems. Aquacultural Engineering, 41(3), 87–94.
Liltved, H., & Cripps, S. J. (1999). Removal of particle-associated bacteria by prefiltration and ultraviolet irradiation. Aquacultural Engineering, 20(1), 1–13.
Shinn, A. P., Pratoomyot, J., Bron, J. E., Paladini, G., Brooker, E. E., & Brooker, A. J. (2015).
Economic costs of protistan and metazoan parasites to global mariculture. Parasitology, 142(1), 196–270. https://doi.org/10.1017/S0031182014001437
Summerfelt, S. T., Davidson, J. W., Waldrop, T. B., Tsukuda, S. M., & Bebak-Williams, J. (2004). A partial-reuse system for coldwater aquaculture. Aquacultural Engineering, 31(3–4), 157–181. https://doi.org/10.1016/j.aquaeng.2004.03.007
Timmons, M. B., & Ebeling, J. M. (2013). Recirculating Aquaculture (3rd ed.). Ithaca Publishing Company.
Tort, L. (2011). Stress and immune modulation in fish. Developmental & Comparative Immunology, 35(12), 1366–1375. https://doi.org/10.1016/j.dci.2011.07.002
Wedemeyer, G. A. (1996). Physiology of Fish in Intensive Culture Systems. Chapman & Hall.
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