Agriculture and Agri-Food Canada / Agriculture et Agroalimentaire Canada -- spacer --
Agriculture and Agri-Food Canada / Agriculture et Agroalimentaire Canada Government of Canada / Gouvernement du Canada
français -- spacer -- Contact Us -- spacer -- Help -- spacer -- Search -- spacer -- Canada Site
-- spacer --
AAFC Online -- spacer -- Links -- spacer -- Newsroom -- spacer -- What's New -- spacer -- Site Index
-- spacer --
National Science Programs Home Page blank button Agriculture and Agri-Food Canada
-- blue spacer --
National Science Programs
-- orange spacer --
Scientists
-- orange spacer --
Industry
-- orange spacer --
Media
-- orange spacer --
Youth
-- orange spacer --
Online Publications
-- orange spacer --
Centres
-- orange spacer --
-- blue spacer --

Other odors

Ammonia is only one of the gases released from farms that has an unpleasant odor. Many other gases also irritate the human nose. Some of these are not only unpleasant but also dangerous. Perhaps the most noteworthy is hydrogen sulfide (H2S), a poisonous gas with the smell of rotten egg. High concentrations of this gas can be released when liquid pig manure in tanks is stirred. It can be fatal to humans, though only at high concentrations produced where ventilation is poor. Many other compounds, although not known to be poisonous, have an objectionable odor; more than 150 such compounds have been identified in pig manure alone.

To date, people have perceived farm odors only as nuisances, but awareness of this problem is now growing. Indeed, some countries have already established regulations regarding allowable odor intensities.

Odor-causing gases can come from many sources. Some of the most offensive arise from organic substances decaying in the absence of oxygen. The decomposing matter may be manure, effluent from manure piles, silage, plant debris, or a wide range of other organic materials. When decomposed without an adequate oxygen supply, they are not completely broken down into CO2 and simple salts but rather are released as various intermediates such as organic acids, alcohols, aldehydes, sulfides, and CH4. Of these, the compounds with the most offensive odors are the volatile organic acids.

Many odor-causing compounds come from the same source and therefore occur together. For example, volatile organic acids are often found with NH3 and H2S. Given the many compounds involved, odors are not easily measured and quantified. Indeed, the most sensitive and reliable sensor is still the human nose. One way to measure odor intensity is to count the number of times an air sample has to be diluted with fresh air before its odor becomes nearly imperceptible. A panel of human evaluators is used to determine the number of "dilutions to the threshold" (DT), which may range from 0 to 200 or more. On this scale, a reading of 170 DT or higher would be considered "unacceptable." The lowest value achievable within a feedlot operation is about 7 DT.

A variation on this approach is to compare the air sample with known concentrations of a reference compound, like butanol. With this method, the intensity of odor is reported in terms of equivalent concentrations of butanol. The scale normally ranges from 0 to 80 ppmv butanol (the highest intensity to which the nose is responsive). Most ambient odors have a rating of less than 60 ppmv butanol.

Researchers have used these techniques to evaluate the odor from various types of farms. Odors from pig farms usually rate "high" to "very high," whereas poultry and cattle operations normally rate "high," comparable to that of paper mills, petrochemical plants, and oil refineries. Of course, odor intensity varies considerably depending on wind speed, air stability, humidity, and distance from source.

Composting

Gases emitted during composting of organic waste may include CO2, NH3, CH4, N2O, and NO. Smaller quantities of reduced sulfur and nitrogen compounds may also be produced in anaerobic microsites. The form and quantity of gaseous compounds emitted during composting depends on the material being composted and the method used. Odor-producing compounds can be virtually eliminated with a properly designed aeration system. A biofilter system in enclosed composting facilities also ensures odor-free exhaust air.

Methane emission can also be eliminated with adequate aeration. Ammonia emission is controlled by the available C:N ratio of the composting material and by the aeration system used. When NH3 emission occurs, it is usually early during the composting process. Ammonia may be captured using a scrubber. The factors influencing N2O and NO emissions during composting are not well understood. Researchers are working toward a better understanding of N2O emissions during composting and strategies to minimize emissions. A well-designed compost facility should not negatively affect the health of our air.

Photo: Composting

(J. Paul, AAFC)

Producers can reduce the intensity of odors from farms in several ways. The most obvious, perhaps, is to plan the farm layout carefully, placing sources of odor, like barns and lagoons, downwind and far from dwellings. Other methods include cleaning and washing barns frequently, aerating stored manure (although this action may favor NH3 release), injecting slurries, and immediately incorporating solid manures after they are applied. Finally, various chemicals and bacterial cultures have been proposed for odor control, but their cost is often high and their efficacy limited. One possible approach is to add calcium bentonite, a clay with high absorption capacity, to animal diets. This additive has even been found to enhance weight gain under some conditions.

Go to Top of Page



Date Modified: 2003-08-27