INTRODUCTION not exactly filtration units but a combination
are many physical and chemical methods to treat air pollution. Bioprocesses
have been very efficient for the treatment of air pollution. The most popular
bioreactor configuration is the conventional biofilter. Biofilters were
initially designed for odour control at wastewater treatment plants, but now
they are becoming renowned for the treatment of volatile organic compounds
(VOCs) and other organic compounds. These gases have bad odour and are
dangerous for humans and animals.
process is preferred over other air pollution control techniques and has gained
popularity because it has economic advantages,
as the energy requirement is significantly low and avoids cross media transfer
of pollutants. This technology can be mainly applied to waste gases to control
air pollution, which have low concentration and readily biodegradable
pollutants. Biofilters utilizes microorganisms to reduce air pollution. Air
pollutants come in contact with microorganisms inside the biofilter, where
microorganisms demean pollutants to produce energy and by-products (C02 and
H20). Biofilter includes a filter material, where microorganisms breed. Biofilm
is a very important part of the biofilter. Biofilm is a thin layer of moisture
where the microorganisms reside. In the process of biofiltration polluted air
is pushed inside the biofilter slowly thereby, the pollutants in the air get
absorbed in the filter media, then as a result the polluted gas is dispersed in
the biofilter and absorbed onto the biofilm.
the escalation of the conventional biofilter, new configurations were developed
for air pollution control which is known as biotrickling filters and bioscrubbers.
A new set of technologies were also introduced for air pollution control such
as membrane bioreactor and rotating biological contractor. A lot of industries
use this biofilter technology for example the food industry, pharmaceuticals,
wood products manufacturing, paint and coatings application, petroleum
industry, sewage treatment etc. Polluted air stream comprises VOCs and many
sulfur compounds. Biofilters require a large area while treating large
airflows, which can be as big as a basketball court. Recent research shows that
biofilters can be used to remove a variety of airborne contaminants which
includes aliphatic and aromatic hydrocarbons, alcohols, aldehydes, organic
acids, acrylate, carbolic acids, amines and ammonia.
The main three bio reactor configurations used for
air pollution control are biofilters, biotrickling filters and bioscrubbers.
The core mechanism is same for all but they make use of microbes in different
phases which may be suspended, fixed or in a liquid state. Biofilters are not
exactly filtration units but a combination of different unit operations such as
absorption, adsorption, degradation and desorption of gas phase contaminants.
Water is added into the biofilter system to control
the moisture content and add essential nutrients. Humidification of gas streams
is generally carried out before feeding it into the system.
BIOFILTER CONFIGURATION AND ELEMENTS
The two categories of biofilters are open bed or
Open bed biofilters are the
ones that are used mostly and its depth varies from about 10 to 18 inches. They
are larger than the closed-bed biofilters. Open bed biofilters are made in such
a way that they are exposed to the weather outside. Closed bed biofilters are
usually surrounded with a small exhaust port to let out the air which is clean.
Closed bed biofilters are commonly used to treat small airflows and tend to have
deeper media approximately (2-3 feet), in order to reduce the space which is
required to attain odour control also it is more expensive as compared to open bed
the conventional biofilter can be referred to a fixed film or packed bed
bioreactor which consists of a natural filter bed, it depicts that inert
packing materials are also successful in a closed bed biofilter. In this biofilter polluted air is let into in
down flow or an up flow manner through the reactor where contaminants of the
waste air are decomposed with the help of biocatalyst which is already present
in the packed bed. Therefore, to treat hydrophobic and water soluble compounds,
this reactor is used. Conventional biofilters are not considered for the
treatment of the pollutants like chlorinated compounds which lead to
acidification because there is no moving liquid present in it. Key elements of
a biofilter are as follow.
1. Filter bed
beds which were initially used in conventional biofilters were made up of
natural materials. Common materials used were soil, compost or peat. Natural
filter beds are still used in some areas. The benefit of using natural filter
beds is the availability of microorganisms and nutrients. Major disadvantage in
using these filters is depletion of essential nutrients over time and increase
in pressure drop due to gradual degradation and compaction. This also causes
decrease in efficiencies over time. New materials have been introduced to
overcome such problems. Inert and synthetic materials are combined with natural
filter beds to regulate the pressure drop across the filter bed. It is
essential to humidify waste gas while using inert materials as, microorganisms
need a significant level of relative humidity for proper functioning. Generally,
in conventional biofilters, continuous liquid phase is not added. Nowadays, filter
beds are fully made up of inert materials in which feeding liquid solution is
necessary to avoid drying of the filter bed which can result in decrease in
performance and reactor failure.
One of the major
issues in a biofilter is to maintain a favourable water content. Regulations
and moisture levels can be smoothly maintained these days with the help sensors
that are cost effective. When the level of loading rates reach a peak point,
the occurrence of adding the liquid phase automatically increases. The
temperature of the filter bed rises with high loading rates. In open biofilters
sprinklers are especially placed while using natural filter beds for maintaining
favourable conditions in accordance to the content of water. This usually takes
place in summer season where the top layer of the bed happens to dry out often.