What are aerobic, anaerobic and facultative bacteria?

Every bacterium in wastewater falls into one of three groups, defined by whether it needs oxygen. Aerobic bacteria need dissolved oxygen to survive and break down organic material, and go dormant or die off without it. Anaerobic bacteria never use oxygen: they get their energy from other electron acceptors, the substances a cell uses in place of oxygen. Facultative bacteria sit between the two, using dissolved oxygen when it is present and switching to an alternate acceptor the moment it is gone.

In a healthy system, most of the working population is aerobic or facultative, and those two groups are the fastest at breaking down fats, oils, grease and organic solids, because oxygen-based metabolism is the most efficient reaction available. Strictly anaerobic bacteria are slower by comparison, which matters once dissolved oxygen runs out, as it does routinely in a sewer line, a wet well or a lagoon bottom.

What order do bacteria take oxygen in?

Bacteria do not pick an electron acceptor at random. They draw down whatever is available in a fixed order, because each option yields less energy than the one before it, and a cell always uses the most efficient option on hand. Dissolved oxygen goes first, used exclusively as long as it lasts. Once it is gone, bacteria turn to nitrate, a condition called anoxic, and denitrifying bacteria strip oxygen from it and release nitrogen gas.

Once nitrate is also exhausted, bacteria turn to sulfate, an ion present in ordinary wastewater. Sulfate-reducing bacteria strip oxygen from sulfate and leave sulfide behind, which becomes hydrogen sulfide gas the moment it reaches air, usually where the water turns turbulent: a pump discharge, a drop structure or a wet well. If sulfate also runs out, the last acceptor is carbon dioxide, and methane-producing bacteria take over. Each step is slower and yields less energy than the last, which is why anaerobic sludge digests so much more slowly than the same material would aerobically.

Why do treatment plants sometimes want zones without oxygen?

A treatment plant can put the anoxic step to work. Denitrification uses a deliberately oxygen-free zone with nitrate present, so facultative bacteria strip nitrogen out of the water as nitrogen gas rather than releasing it downstream. Biological phosphorus removal uses a separate anaerobic zone earlier in the process, conditioning bacteria to take up phosphorus once oxygen returns. Both are designed, controlled zones, sized and timed for the reaction a plant wants, with the water moving on to an aerated zone right after. Neither is the condition that produces hydrogen sulfide: the nitrogen removal step stops at nitrate and never reaches sulfate.

Why does nobody want a collection system to go anaerobic?

A sewer line, a force main or a lift station has nothing designed into it the way a plant’s anoxic or anaerobic zones are designed. It is simply a pipe, with no basin, no timed cycle and no engineered stopping point. Left long enough, wastewater runs through the same electron acceptor order a plant’s zones use on purpose, but with no control over where it stops: oxygen first, then nitrate, then the sulfate step that produces hydrogen sulfide. In a pipe, that step removes nothing useful. It only makes gas, sulfuric acid on exposed concrete and steel above the waterline, and conditions that let fats, oils and grease settle rather than break down. A collection system going anaerobic is not a designed process; it is oxygen-starved wastewater sitting long enough for the worst step to take over.

Why does aeration have a ceiling?

Aeration, mixing air into water mechanically, is the most direct way to keep bacteria aerobic, and it works well wherever it reaches. But it has two hard limits. Water itself can dissolve only a limited amount of oxygen no matter how hard the blowers run, a property of water, not a shortcoming of the equipment. And aeration only raises dissolved oxygen inside the tank or basin where it is installed. A blower at a plant does nothing for a force main, a wet well or a lagoon bottom miles upstream, exactly where a collection system runs out of oxygen and starts down the sulfate step.

What does supplying usable oxygen upstream mean?

Supplying usable oxygen is a different approach: instead of mixing air into water where equipment happens to be installed, an inorganic compound carries oxygen the bacteria can already use, on the molecule itself, into wherever the water goes. We add no bacteria and no enzymes; the native bacteria do the work. As long as that oxygen is available, the same facultative bacteria keep using it instead of turning to nitrate and then sulfate, so the sulfate step and the hydrogen sulfide it produces are never reached. The compound is consumed as bacteria use its oxygen, so nothing of it remains downstream. We dose it as far upstream as a site’s water and power allow, the practice we call AerobicShift, letting a force main or a wet well stay aerobic instead of sliding down the ladder. It changes nothing about a plant’s own designed zones; those stay exactly what the plant built them to be. How the program is dosed and measured covers the delivery side.

The electron acceptor ladder

Step Electron acceptor Bacteria type What it produces Where it happens
1 Dissolved oxygen Aerobic and facultative Carbon dioxide and water Anywhere dissolved oxygen is present, the fastest step
2 Nitrate (anoxic) Facultative, denitrifying Nitrogen gas A zone with no dissolved oxygen but nitrate present, often designed on purpose
3 Sulfate Anaerobic, sulfate-reducing Sulfide, then hydrogen sulfide (H2S) gas Oxygen and nitrate both used up: a force main, a wet well or a lagoon bottom
4 Carbon dioxide Anaerobic, methane-producing Methane gas Deep sludge or a digester, once sulfate is also exhausted

Summary

  • Bacteria are aerobic, anaerobic or facultative, and most of the useful work in a healthy system is done by aerobic and facultative organisms while oxygen is available.
  • Bacteria draw down electron acceptors in a fixed order, oxygen, then nitrate, then sulfate, then carbon dioxide, and hydrogen sulfide only appears once the sulfate step is reached.
  • A treatment plant puts the nitrate step to work on purpose in designed anoxic zones; a collection system has no such design, so reaching the sulfate step there only makes gas, acid and grease.