1. Natural conglomerate of microorganism in suspension. The feature of bacteria to agglutinate is commonly used in the microbiologic depuration processes of waste water and is activated by polysaccharide extracells production. Bio Floc BFC technology

2. Activated sludge are a suspension in water of activated biomass ( bacteria, saprophyte, protozoa, amoeba, rotifers and other microorganism) commonly in a form of floc. This sludge is the basic of activated sludge oxidation systems, the most frequent traditional depuration plants or waste water treatment. The role of such a biomass ( above all available in a form of sedimentable floc made of organic matter and colonies of bacteria they feed from) in the depuration process is to use biodegradable organic matter of the waste and decompose into smaller and less dangerous compound, which in part are used by microorganis as food and for their reproduction.

3. Bioflocculation is due to formation of suspended organic matter gelatinous flocs, few mm sized. Aggregation of the flocs is probably activated by superficial electric load of organic molecules, many of them of colloidal nature and from presence of filamentous bacterial forms (Spheromixya sp., Micotrix sp.) to make up a real internal shell, the floc cohesion depend from. Bio degradation of soluble matter, from eterogeneous aerobic bacteria population, lead to formation of CO 2, H 2 O, NH 4 +, NO 2 -, NO 3 - and other molecules. Bacteria are selected by global conditions, so that in environment with high concentration of protein we would find type of di Alcaligens, Flavobacterium, Bacillus, while in enrironment rich of carbohydrate we will find Pseudomonas, and at low concentration of O 2 and organic matter Nitrosomonas e Nitrobacter.Pseudomonas Nitrosomonas

4. Part of decomposition occur in the activated sludge where a catalithic demolition is generated by esoenzimes on polimerich organic molecules. The need to keep both reactions requires a compromise to the internal turbulence of the waste to allow the formation of the floc but also a suitable water oxygenation to favour the aerobic metabolism The oxidation pond is o be oxygenated as much as possible taking care not to destroy the sludge floc and the agglomerated microorganism.

5. Bio floc in aquaculture Bio floc is the main character to purify water and production of natural feed..  Bio floc system reduces problems with patogens..  This aggregate of bacteria and organic particles comprise an important part of the natural diet of shrimp and fish.  The floc contain an average of 45 % of protein, which is nearly double the protein level of the feeds

6. Nutritional Value of Algae The principal advantage of an algae-based production system is the nutritional value of phytoplankton – HUFAs – Carotenoids & other pigments Nutritional value depends upon species – Diatoms best source of HUFAs Managing species composition may be important Cambia foto Altre info sui valori nutrizionali

7. Bio floc intensive shrimp pond culture

10. In a very short time the pond is dryed and ready to be refilled and stocked

11. > Light  Feed  Waste  Aereation ( air or pure oxigen ) -Circulation -Turbolence  Bacteria -Cyanobacteria -Green algae -Diatoms -Dinoflagellates  Chemoautotrophs - photoautotrophs - heterotrophs  Biosecurity  Supplemental nutrition  Water quality  Waste managment - water reuse - waste conversion Complex Dinamic Microbial community 45% proteins content

12. Mixing and aeration are key features of BFC technology > Supply oxygen to water Aeration  Generate turbulence  Degass CO2 from water For biomass over 4 kg/m2 pure oxygen is required > Keep Biofloc in suspension > Provide vertical circulation

15. . Ammonia removal in aquaculture. > unlike nitrifying batteria that produce nitrite and nitrate, heterotrophic bacteria Incorporate ammonia nitrogen directly into microbial biomass.  When using feed, only 1/3 of the dissolved organic carbon required by the hetrotrophic bacteria is available from the feed.  This means that the additional organic carbon must be added for the heterotrophic bacteria to use all available ammonia generated by the shrimp

16. Mixing and aeration are key features of BFC technology * Needed to reduce sludge deposition * Suspend organic waste for digestion by bacteria * Prevent anaerobic zone  Circulation velocity from 10 to 20 cm per sec.  Below 10 cm per sec. sedimentation can occur

17. Production: bibliograpy data tilapia 100 kg per cubic meter shrimp 300 to 700 stocking density with pure oxigen over 4 kg per square meter Oxygen is a limiting factor in nitrification. To nitrify completely 1 gr of ammonia nitrogen 4,57 gr of oxigen are required. Kg o2/kg feed =28 gr NH4-N x 4,47 gr O2 = 128 gr O2/kg feed for nitrification Rule of thumb for total oxygen consumption: Oxygen requirement is sum of fish and bacterial oxygen consumption: 0,25 kg O2 consumed by fish 0,12 kg 02 by bacteria 0,37 kg 02 ---------------------------------------- + -------------------------------- = --------------- kg feed kg feed kg feed It should be considered that the oxygen demand increase after feeding associated with digestion and assimilation of food. In the range 0f 1.1 kg of oxyigen per kg feed

18.  Autotrophic system (photoautotrophic) green algaee low density production  Heterotrophic system………………………….. Brown algae medium density production  Chemo autotrophic system………………… high density Heterotrophic system  Heterotrophic bacterial growth is affected by the system’ s C/N ratio, temperature DO, PH, salinity.  Increase in microbial biomass production is 40 times greater than the biomass generated from the nitrification process and consumption of O» is also much higher. > CO» production of hetereotrophic floc also is higher than autotrophic nitrifiers. Danger parameters. CO2 danger zone, (illustrted:(CO2)> 20 mg/L  NH3 danger zone as a f ( temperature, salinity, PH) (Illustrated : (NH3 )> 0.0125 mg/l & TAN 0,2 mg/L  Green zone defines a preferred PH- (Alk) regime (illustrated : PH 7,4 – 8,1 & (Alk)) 75 – 175 ppm CaCO3 ….keep the system out the danger zone Brown algae

19. Stocking density over 130 - 150 pl m2 Aeration 28 32 hp ha Belize 48 hp Produzione 13,500 kg ht 550 kg x hp Biofloc 643 kg hp Semi bio floc 540 kg hp Traditional 480 kg hp

20. Solids removal and control are very important tools to manage BFC systems -Dominance of heterotrophs bacteria as grow faster than authotrophs bacteria, lead to variation in water quality  High number of protozoans feed on heterotrophic bacteria  Generates: high Bod, high CO2, low Ph Foam Fractionator Protein Skimmer Settling tank

22. Pre growing  Raceway  Round ponds

23. Products applications  Hatchery  Pregrowing Eco2 : aeration, degassing, circulation, 3 interchangeable nozzles air or pure oxygen injector Splash. Degassing, CO2 removal Force 7 : highest O2 transfer rate Flash. upside down vertical aeration and circulation

24. Culture: indoor and green houses

25. Products applications  Indoor  Greenhouses Splash Flash

26. Growing in small square concrete tanks Growing in small round concrete tanks

27. Growing in outdoor raceway

28. Growing.. Medium size lined pond 2000 m2

29. Growing.. Medium size lined pond 2000 m2 Product application Force 7 Brio44

30. 10.000 square meters pond

32. Products application Force 7 Combo

33. Average stocking density 300/350 kg per hp Pump operated nozzle aerator

34. Biofloc require oxygen and degassing Force 7 offers:  Best oxygen transfer rate  Degassing  Propeller design according to specific target to prevent anaerobic area

35. Biofloc must be kept in suspension. Sedimentation has to be avoided. Water circulation is a must. Rio: Low power consumption Highest volume of water Combo: Best oxygen transfer rate Incomparable to any other system

36. Brio 44/ 47  Degassing  Huge splashed water  Steady circulation

37. Flash Concentrate oxygen dissolution Splash  Co2 stripping  Degassing  Oxygen transfer rate

38. Protos Skim Skim One  Foam fractionatorion to rigenerate old floc with new ones  Degassing  Reduce nitrate  Balance PH

40. Water recycling