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Suspended Solids Effects In Shrimp Biofloc Systems

24 March 2014, at 12:00am

The use of biofloc systems for shrimp culture requires monitoring of water quality parameters, particularly suspended solids levels, writes Carlos Gaona et al, Universidade Federal do Rio Grande. Taken from the Global Aquaculture Advocate, a Global Aquaculture Alliance publication.

The use of lined tanks increases the confinement of biofloc in the culture environment and restricts the organic particles in the water column from being recycled completely.

When a production cycle begins with a well-stocked biofloc inoculum, the concentrations of ammonia and nitrite are relatively low, but concentrations of suspended solids tend to be higher in this phase. Generally, nitrite concentrations rise as suspended solids levels increase. At dissolved-oxygen concentrations above 5 mg/L, excess suspended solids were not a problem for shrimp respiration.

Marine shrimp aquaculture systems that incorporate biofloc technology often experience a high density of suspended solids within the systems. The injection of air at the bottoms of culture tanks promotes both the diffusion of oxygen in the water column and mixing of suspended material. The use of lined tanks increases the confinement of biofloc in the culture environment and restricts the organic particles in the water column from being recycled completely.

Suspended Solids

Suspended solids consist mainly of organic matter, which is comprised of microbial forms that when decomposing exert a high demand for oxygen. This demand can decrease the dissolved-oxygen concentrations in the culture system to reach levels below the recommended concentration for the cultivated species. An increase in suspended solids can also reduce the water quality within the system (Table 1). Overall, these less-than-optimal conditions reduce system performance.

These conditions can occur throughout the different stages of the marine shrimp production cycle, depending on whether the system starts a cycle with mature biofloc inoculum. However, the use of biofloc inoculum relates to the suspended solids concentration in the water column.

At the beginning of a cycle, interactions among the nitrogenous compounds, ammonia and nitrite are most notable when biofloc is forming in the culture. The reduction of ammonia occurs with the establishment of ammonium-oxidizing bacteria, which does not require the use of organic carbon, and with the absorption of heterotrophic bacteria. Therefore, the nitrite accumulation occurs due to the slow growth of nitrite-oxidizing bacteria.

Total suspended solids levels constantly increase, and consequently nitrite concentrations increase. In contrast, when a cycle begins with a well-stocked biofloc inoculum, the concentrations of ammonia and nitrite are relatively low. However, the concentrations of suspended solids are higher in this phase. Both situations require management of suspended particulate matter within the culture system.

Experimental Work

In experiments conducted with Litopenaeus vannamei shrimp in biofloc systems at the Marine Aquaculture Station of the Federal University of Rio Grande in southern Brazil, the best growth performance occurred in a study where suspended solids were removed for the maintenance and control of the total suspended solids concentrations in culture inoculated with biofloc.

In another experiment, concentrations of nitrogen compounds differed when compared to different total suspended solids (TSS) concentrations during the formation of biofloc. Higher TSS concentrations resulted in higher concentrations of nitrite.

In another experiment that used the biofloc inoculum, it was observed that when the concentration of dissolved oxygen was maintained above 5 mg/L, the suspended solids excess was not a problem for the respiration of the reared shrimp. Considering the interactions of water quality parameters listed above, maintenance of the suspended solids levels is required for better water quality. Values for common water quality parameters measured under two average TSS concentrations are shown in Table 2.

Monitoring, Intervention

Figure 1. Settling chambers use gravity to settle particles. The arrows indicate water flow. Water from the culture tank enters via a central pipe, which reduces velocity and turbulence, and returns after settling.

Figure 2. Total suspended solids concentrations in study with and without clarification. The arrow indicates the seventh week since the start of the solids removal process.

Measurements of suspended solids were made using the gravimetric method, which measures total suspended solids and settleable solids within an Imhoff cone. Various techniques can be applied to reduce and maintain suspended solids concentrations, such as the use of a settling chamber or clarifier to remove solids. Set up in straightforward settling chambers, clarifiers rely on gravity to move particles to the bottom (Figure 1).

The radial water flow in the settling chamber can be adjusted based on prior analysis of biofloc sedimentation in an Imhoff cone, increasing the efficiency of the method. This method allows the control of TSS and keeps the concentrations near the recommended values (Figure 2). Another advantage of this method is maintaining a constant flow during the application of settling, so a small amount of water is sufficient for removing suspended solids.

Further Reading

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March 2014

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