Abstract:
Although molecular toxins and emission of particulates from the thermal degradation of biomass
materials such as meat is a complex area of study, it has become necessary to investigate this
phenomenon and determine how it affects biological functions and as precursors for cancer,
degenerative diseases that stress the respiratory landscape. Accordingly, this study describes the
pyrolysis of goat meat in the temperature range 300-525 ˚C. Goat meat sample of 10±0.2 g was
heated under atmospheric conditions in an air depleted environment in a thermal degradation
reactor (volume ~ 1.6 cm3) and the smoke effluent passed through a transfer column and
collected over 10 mL dichloromethane and kept in crimp top amber vials. Evolution of selected
molecular toxins was monitored using an in-line Gas Chromatography hyphenated to a mass
spectrometer (GC-MS) while the particulate nature and morphology of particulate emissions was
investigated using a scanning electron microscope (SEM). GC-MS analysis was carried out using
an Agilent Technologies 7890A GC system coupled to an Agilent Technologies 5975C mass
selective detector (MSD). The density functional theory (DFT) and Chemissian softwares were
used to explore the thermochemistry and molecular geometries of 2-(ethylthio)phenol,
2,3-dimethylhydroquinone, and 1,1’-biphenyl. The major organic volatiles detected from GCMS were phenol, 2,3-dimethyl hydroquinone, 2-(ethylthio)phenol, indole and 1,1’-biphenyl. At a
pyrolysis temperature of 500 ˚C, the mean particle size of particulates was found to be
7.72 ± 0.61 µm while at 700 ˚C, the particulate size of emissions was found to be 3.52 ± 0.31
µm. This particles are small in sizes and are possible to get into the lungs and cause respiratory
problems Moreover, a kinetic model for the thermal destruction of indole, 2,3-
dimethylhydroquinone, and 2-(ethylthio)phenol within a temperature region of 450 ˚C and 525
˚C using pseudo-first order reaction kinetics has been proposed at a residence time of 2.0 s.
Consequently, the temperature dependent rate constants for the destruction of 2,3 dimethylhydroquinone, 2-(ethylthio)phenol, and indole were estimated to be, k x Tn x e RT411 101726310.s-1, k x Tn x e RT110 1019283 38..s -1, and k 130 x 1021Tn x e RT 315 76 . . s -1 respectively. The electron density maps as well as the toxicity index of 2-(ethylthio)phenol are also reported in this study. The fundamental finding of this study is that most bio-hazardous byproducts were evolved in high yields above 300 ˚C.