| ODOUR POLLUTION AND ITS CONTROL |
7.0
LAWS AND REGULATIONS
Generally,
most regulatory organizations/municipal authorities resort to nuisance prevention
law to abate odour, but it is being followed more in breach than in practice.
Perhaps the most effective method of overcoming the problem is to have regulation,
which can be directed towards specific emissions from specific industries. For
example, regulation of pulp mills odours which limits emission of mercaptans.
The development of odour measurement, regulation and
control technique has been greatly progressed in most of the countries. In Australia,
several states are reviewing the existing regulations on the control of odour
from various source based on a forthcoming Australian–New–Zealand standard of
odour measurement using dynamic olfactomerty. In Europe, the official standard
for odour measurement is expected to be published in 2002.
In
the USA, odour has been listed as one of the key area to be dealt with the Agriculture
Air Quality Task Force. There are some State regulations in the US to address
the odour from some specific sources. In Minnesota, the Feedlot Hydrogen
Sulfide Program administered by the Minnesota Pollution Control Agency is in vougue
since July 1997. The hydrogen sulfide standard works in the following way: each
gas sample represents an average value of the gas over a continuous 30-minute
period. A violation occurs if the hydrogen sulfide ambient air quality exceeds
30 and 50 ppb within certain time period. Iowa’s "manure law"
was enacted in 1995, to create a system of setback distances for lagoons and buildings,
depending on the nature of the surrounding area. Also Iowa Department of Natural
Resources has proposed new regulations for swine producers, which require manure
injection rather than spreading.
There are more activities in
in addressing gaseous and odour problems from large-scale swine facilities. Europe
has focussed on two primary areas of concern – nitrogen emissions and odour prevention.
The Netherlands has "an extremely strict approach" for regulating
nitrogen emissions. By 2010, farmers must reduce their emissions by 70 % of 1980
levels, with an assumption that a 10 % reduction rate in ammonia emissions will
result in a 7 % reduction of odour. In Denmark, odour laws were established
during 1950 to 1980. These laws required ventilation chimneys and setback distances
from houses. By the end of 1980s, it was felt that the general code of good agricultural
practice had not reduced odour to acceptable levels. The Ministry of Environment
then imposed restrictions on the construction and location of manure storage and
swine buildings, as well as on the land application of manure. Germany
focuses more on managing nutrients than on paying specific attention to ammonia
odour emissions. The Fertilizer Ordinance enacted in July, 1996, requires manure
to be worked into non-tilled soils immediately after application. Producers have
to send records of both manure storage and cropland application to the government.
There are strict controls on lagoons as well – they must be lined, covered and
equipped with underground pipes for the detection of leaks.
In
India, Schedule II and Schedule VI (General standards for discharge of effluents)
under Environmental (Protection) Rules, 1986 prescribes that all efforts shall
be made to remove unpleasant odour as far as practicable. Nonetheless, there are
only two industries, wherein industry specific standards under Schedule I of these
Rules mandate odour removal. These are the fermentation industries and the natural
rubber industries. The standards for many other major odour pollution causing
industries such as pulp and paper mills, tanneries, meat processing industries,
bulk drug and pharmaceutical units, food and fruit processing units, dairies and
milk plants etc. do not specify odour control.