AFU Common Entrance Exam study materials
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Dawn oxygen crash in a 1.4 ha tilapia pond

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Dawn oxygen crash in a 1.4 ha tilapia pond

A farmer owns a 1.4 ha pond, average depth 1.2 m, stocked with 4,200 Nile tilapia averaging 320 g. He feeds a 28% protein pellet at 3% of biomass daily, split into two feeds. Over the past week daytime temperatures have reached 29–31 °C and the water is dark green with a thick Microcystis scum on the downwind shore; Secchi depth is 18 cm. Four days ago he broadcast 200 kg of raw chicken manure. At 05:30 today, dissolved oxygen was 2.0 mg/L at the surface and 0.6 mg/L at the bottom; about 40 fish are dead and many are gulping at the surface. He has one 2.2 kW paddlewheel aerator, a diesel generator and 20 litres of fuel, and no grid electricity. A nearby irrigation canal can supply a partial water exchange. Market-size fish will fetch a good price in six weeks.

1. Rank your actions for the next 12 hours, with a fuel budget. Justify each action and say what you would refuse to do today.

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Understanding the emergency. The pond is carrying roughly 4,200 × 0.32 kg ≈ 1,340 kg of fish, plus a heavy algal bloom and a fresh load of manure. At 05:30 DO has been falling all night: algae and fish respire without photosynthesis from dusk to dawn, so the lowest point of the day is first light. Surface 2.0 mg/L is already below the ~3 mg/L stress threshold for tilapia, and 0.6 mg/L at the bottom is lethal. The stock is not in a stable state - it is on the edge of a total crash.

Ranked actions

  1. Stop feeding immediately. Feed is direct oxygen demand: uneaten pellets decompose and fish metabolise more at high intake. Even 24–48 hours without feed costs far less than a kill.
  2. Run the aerator through the night and dawn, not midday. With 2.2 kW at roughly 1 litre/hour, 20 litres buys about 20 running hours. Spend them 20:00–08:00 across the next two nights, positioned in the deepest water away from the scum. Daytime mechanical aeration is wasted: the bloom is already supersaturated then.
  3. Partial water exchange from the canal, 10–20% of pond volume if the canal water is cooler and oxygenated. Screen the inlet against wild fish and predators, and do not exchange so fast that you shock the fish with a temperature drop.
  4. Remove dead fish now and dispose of them away from the pond. Do not sell them.
  5. Do not add lime, manure or 'oxygen powder' as a substitute for aeration. Agricultural lime does not oxygenate water.

Refuse today: any algaecide, any further manure, any handling or netting of stressed fish, and any increase in feed once the fish recover within the first 48 hours.

2. Explain why dosing the pond with copper sulfate or another algaecide now could kill the entire stock, even though the bloom is the underlying problem.

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The bloom is the oxygen source and the oxygen sink. In daylight, dense Microcystis produces oxygen; at night it consumes it. Killing the bloom removes the daytime production and simultaneously creates a large mass of dead organic matter that bacteria decompose - and bacterial decomposition consumes oxygen in exactly the same water column the fish are already short of.

The sequence after an algaecide dose

  1. Algae die and sink within hours to days.
  2. Bacterial breakdown of that biomass exerts a heavy oxygen demand, typically driving dawn DO towards zero.
  3. Many cyanobacteria (including Microcystis) release toxins when cells lyse, which damage fish gills and liver even if oxygen holds.
  4. The pond has no oxygen reserve to buffer this: at 2.0 mg/L surface and 0.6 mg/L bottom, the margin is already gone.

Copper-specific risks. Copper toxicity to fish depends strongly on water hardness and alkalinity, which the farmer has not measured. In soft, low-alkalinity water the same dose that kills algae can kill tilapia; the safe margin is narrow and unknowable without a test. Copper also accumulates in sediment and can suppress the beneficial bacteria and zooplankton that help stabilise the pond.

The correct alternative is mechanical: aerate, exchange water, stop feeding, and physically remove surface scum from the downwind shore with a net or pump. If an algicide is ever used, it is used preventively on a small, early bloom, with aeration running, never as an emergency measure in a pond already at 2 mg/L at dawn.

3. Set out a three-week recovery plan and the stocking and feeding changes you would recommend for the next cycle. Support your recommendations with numbers.

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Days 1–3: stabilise

  • No feed for 48 hours, then 1% of biomass per day (about 13 kg/day) for three days, then 1.5–2%.
  • Aerate every night 20:00–08:00 until dawn DO stays above 4 mg/L for three consecutive mornings.
  • Measure DO at dawn and at 15:00 daily with a meter, not by watching fish behaviour - by the time fish gulp, the damage is done.
  • Remove scum mechanically; do not pump it back into the pond.

Days 4–14: reduce the load

  • Harvest the largest fish early if the market will take them. Cutting standing biomass from 1,340 kg to around 800–900 kg cuts oxygen demand by roughly a third and brings the pond back within the aerator's realistic capacity.
  • Water exchange of 10–15% on two or three occasions rather than one large flush.
  • Stop all manure. If manure is used later, compost it first and apply no more than about 50 kg/ha per week (about 70 kg for this pond), never raw and never in bulk.

Days 15–21 and next cycle

  • Aeration capacity is the real constraint. A common working rule is about 0.75 kW per 400 kg of fish, so 1,340 kg needs roughly 2.5 kW - the 2.2 kW unit is marginal, and a second unit or a larger pond-side power supply is the single best investment. At minimum, budget fuel for nightly running rather than emergencies.
  • Feeding: 3% of biomass of a 28% pellet is generous for a pond this fertile; 2–2.5% with a floating pellet and feeding to satiation observation reduces waste and sludge.
  • Transparency: keep Secchi depth at 30–40 cm. At 18 cm the bloom is far too dense; the target should be achieved by managing nutrient input, not by algicides.
  • Stocking: if aeration cannot be upgraded, reduce stocking or plan a mid-cycle partial harvest so peak biomass never again coincides with hot, still weather.