It has long been known that wetlands have a natural capacity to clean water. American Indian folklore indicates reeds were considered magical and water flowing downstream of such plants was considered pure.
Time progresses and today these plants offer an effective and alternative way of treating polluted wastewater.
Systems can be self-contained, artificially engineered wetland ecosystems. Designed in a way to optimise the microbiological, chemical and physical processes naturally occurring in the wetland. The reeds transfer atmospheric oxygen down through their roots in order to survive in waterlogged conditions. This creates both aerobic and anaerobic soil conditions, allowing extraordinary microbial species diversity to flourish. Such bacteria and fungi use organic chemical products provided in the waste.
So chemicals are not simply stored in the reed bed, they are actually degraded into harmless components.
Other contaminants, such as metals, are transformed from a toxic state and fixed in the soil via complex chemical reactions. Soil adsorption capacity also provides a buffer for peak and shock effluent loads.
The reeds provide all of the above by dealing with the dissolved organic matter and nutrients through the action of the microbes associated with the substrate media in the bed. The fine soil hosts very large populations of bacteria, fungi and algae - all of which are instrumental in removing the dissolved pollutants in the wastewater. The fine media of the reed bed acts as a filter to entrap floating particles, which are then broken down over time by the micro-organisms.
The basic premise of design is that the reed bed system has the capacity to protect surface and groundwater from the polluting effects of human activity and industry. The system has the ability to adapt quickly to variation in loads and types of flow, in general due to the exponential nature of the bacterial growth and the potential for the soil to absorb pollutants.
Microbes (bacteria, fungi, protozoa) have the ability to utilise a wide range of carbonaceous compounds for respiration and other metabolic activities. It is the promotion and utilisation of these activities within the environment by reed beds that leads to the breakdown of a wide range of compounds by microbial activity. It is also the kinetics of these reactions that determine the area of reed bed required to effect the necessary breakdown.
The greatest strength of this technology is that it has the capacity for self-adaptation; it is fair to assume when designing that there will be microbial populations in the soil that can and will adapt to exist by eating the chemicals in the wastewater. A period of 3 weeks to a month is often quoted, as being sufficient time for an indigenous bacterial population to arise that will feed on the chemicals in the water.
Reed beds are accepted as a cost-effective alternative to conventional treatment methods in a widening circle of industries. This means that more and more performance and design data is available and that the technology is moving from being perceived as experimental into the mainstream market of pollution control.
Reed beds complement the trend towards implementation of effluent control regimes, which minimise emissions and promote the recycling of water. This is due to the fact that they operate most effectively on relatively concentrated effluent streams and because they are designed to treat the effluent to conform to discharge standards.
To achieve successful plant growth initially and to sustain growth subsequently, it is important to note the following: