Aerobic biological waste treatment processes rely on microorganisms that perform aerobic respiration to degrade organic pollutants. In aerobic respiration:
- Organic matter (e.g., carbohydrates, proteins, fats in wastewater) serves as the primary source of electrons (electron donor) and carbon for microbial growth.
- Microorganisms oxidize this organic matter to extract energy.
- The electrons removed from the organic matter are passed down an electron transport chain.
- Molecular oxygen (O$_2$) acts as the terminal (or final) electron acceptor in this chain. When oxygen accepts these electrons (along with protons), it is reduced to water (H$_2$O).
This use of oxygen as the terminal electron acceptor is the defining characteristic of aerobic respiration and, consequently, aerobic treatment processes (e.g., activated sludge process, trickling filters). Other options:
- Carbon dioxide (CO$_2$): Can be a carbon source for autotrophs or a product of respiration, but not typically the primary terminal electron acceptor in organic matter degradation for energy by heterotrophs. Some microbes (methanogens, acetogens) can use CO$_2$ as an electron acceptor in anaerobic conditions, but this is not typical for aerobic waste treatment.
- Nitrate (NO$_3^-$): Can serve as a terminal electron acceptor in anaerobic respiration (denitrification).
- Sulfate (SO$_4^{2-}$): Can serve as a terminal electron acceptor in anaerobic respiration (sulfate reduction).
Therefore, in aerobic processes, oxygen is the primary electron acceptor. \[ \boxed{\text{Oxygen}} \]