A total of 331 different VOCs and fixed gases from swine facilities in Nort
h Carolina were identified by gas chromatography and mass spectrometry (GC/
MS). Of these. 203 were found in air samples adsorbed onto Tenax((R)), 112
were found in air samples adsorbed onto cotton material, and 167 different
compounds were identified in the lagoon samples. The compounds identified w
ere diverse, and included many acids, alcohols, aldehydes, amides, amines,
aromatics, esters, ethers, fixed gases, halogenated hydrocarbons, hydrocarb
ons, ketones, nitriles, other nitrogen-containing compounds, phenols, sulfu
r-containing compounds, steroids, and other compounds. The vast majority of
these compounds were present at concentrations below published odor and ir
ritation thresholds. Yet human assessments indicated that odors land irrita
nt sensations) in the immediate vicinity of the swine houses land even at d
istances beyond 1000 ft) were strong. Comparison of the findings from chemi
cal and human assessments points to the importance of the cumulative effect
s of hundreds of compounds in producing odor and irritation downwind of swi
ne operations. Many GC peaks from the samples were too small to allow ident
ification of the compounds, but their presence may also contribute signific
antly to the odor and irritation. Several methodological difficulties were
associated with the human odor assessments. Odorous air evaluated in the fi
eld was simultaneously collected in Tedlar((R)) bags for evaluation in the
laboratory; however, intensity ratings in the held were higher than those i
n the laboratory. This is due to the fact that organic dust (dried fecal ma
terial and feed) adheres to Tedlar((R)) bags and the tubing of collection/d
elivery systems; therefore, only VOCs from the vapor phase (but not the dus
t) reach the nose of the panelists in sniffing air samples obtained in Tedl
ar((R)) bags. Future collection and measurement techniques need to be devel
oped that can evaluate odors from dust and vapor phases simultaneously in t
he laboratory. Dispersion models also need to be developed that account acc
urately for odor intensities downwind of animal operations. Finally. safety
standards for odor exposures need to be determined that consider the risk
of simultaneous exposure to hundreds of low level compounds. (C) 2001 Elsev
ier Science B.V. All rights reserved.