Saprophytic bacteria and
fungi can convert organic matter into living cell mass, carbon dioxide, water and a range of metabolic by-products. These saprophytic organisms may then be predated upon by
protozoa,
rotifers and, in cleaner waters,
Bryozoa which consume suspended organic particles including viruses and pathogenic bacteria. Clarity of the water may begin to improve as the
protozoa are subsequently consumed by
rotifers and
cladocera. Purifying bacteria, protozoa, and rotifers must either be mixed throughout the water or have the water circulated past them to be effective. Sewage treatment plants mix these organisms as
activated sludge or circulate water past organisms living on
trickling filters or
rotating biological contactors. Aquatic vegetation may provide similar surface habitat for purifying bacteria, protozoa, and rotifers in a pond or marsh setting; although water circulation is often less effective. Plants and algae have the additional advantage of removing nutrients from the water; but some of those nutrients will be returned to the water when the plants die unless the plants are removed from the water. Because of the complex chemistry of
Phosphorus much of this element is in an unavailable form unless decomposition creates anoxic conditions which render the phosphorus available for re-uptake. Plants also provide
shade, a refuge for
fish, and
oxygen for
aerobic bacteria. In addition,
fish can limit
pests such as
mosquitoes. Fish and waterfowl feces return waste to the water, and their feeding habits may increase
turbidity.
Cyanobacteria have the disadvantageous ability to
add nutrients from the air to the water being purified and to generate
toxins in some cases. The choice of
organism depends on the local
climate different
species and other factors. Indigenous species usually tend to be better adapted to the local environment.
Macrophytes The choice of plants in engineered wet-lands or managed lagoons is dependent on the purification requirements of the system and this may involve plantings of varying plant species at a range of depths to achieve the required goal. Plants purify water by consuming excess
nutrients and by providing surfaces upon which a wide range of other purifying organisms can live. They also are effective oxygenators in sunlight. They also have the ability to translocate chemicals between their submerged foliage and their root systems and this is of significance in engineered wet-lands designed to de-toxify waste waters. Plants that have been used in temperate climates include
Nymphea alba,
Phragmites australis,
Sparganium erectum,
Iris pseudacorus,
Schoenoplectus lacustris and
Carex acutiformis. Macrophytes can also remove trace metals and emerging contaminants through adsorption to root surfaces, rhizofiltration, and internal sequestration within plant tissues, often alongside bacteria in the rhizosphere that degrade organic pollutants or alter metal speciation. Constructed or floating wetland systems using species such as Eichhornia crassipes and Lemna minor have shown measurable reductions in metals, pharmaceuticals, and PFAS in lake and reservoir settings by coupling plant uptake with microbial degradation and ion-exchange processes. Where oxygenation is a critical requirement
Stratiotes aloides,
Hydrocharis morsus-ranae,
Acorus calamus,
Myriophyllum species and
Elodea have been used.
Hydrocharis morsus-ranae and
Nuphar lutea have been used where shade and cover are required.
Fish Fish are frequently the top level predators in a managed treatment eco-system and in some case may simply be a mono-culture of herbivorous species. Management of multi-species fisheries requires careful management and may involve a range of fish species including bottom-feeders and predatory species to limit population growth of the herbivorous fish.
Rotifers Rotifers are microscopic complex organisms and are filter feeders removing fine particulate matter from water. They occur naturally in aerobic lagoons, activated sludge processes, in trickling filters and in final settlement tanks and are a significant factor in removing suspended bacterial cells and algae from the water column.
Annelids Annelid worms are essential to the effective operation of trickling filters helping to remove excess bio-mass and enhancing natural sloughing of the bio-film. Supernumerary worms are very commonly found in the drainage troughs around trickling filters and in the final settlement sludge. Annelids also play a key role in lagoon treatment systems and in the effective working or engineered wet-lands. In this environment worms are a principal force in mixing in the upper few centimetres of the sediment layer exposing organic material to both oxidative and anoxic environments aiding the complete breakdown of most organics. They are also a key ingredient in the food-chain transferring energy upwards to fish and aquatic birds.
Protozoa The range of protozoan species found is very wide but may include species of the following: •
Amoeba •
Arcella •
Didinium •
Stylonychia •
Vorticella Insects •
Chironomidae bloodworm larva •
Podura aquatica water springtail •
Psychodidae drain fly or filter fly larva ==Bacteria==