Abstract

Cooking methods have been linked with the presence of PAHs in some foods. Mud fish is one of the major components of delicacies in Western part of Nigeria. It is either cooked or smoked for consumption. Not much study has been carried out to determine the effect of methods of preparation on the level of PAHs concentration in mud fish. Fresh mud fish was purchased in Ogbomoso and smoked for 1, 2, 3 and 4h respectively at a temperature range of 200 oC – 210 oC with the use of Azadirachta indica wood and charcoal. A representative portion of about 10 g of sample was taken from the homogenized sample and extracted with ultrasonicator using three solvent systems: methanol, methanol: dichloromethane (1:1v/v) and dichloromethane. The aromatic and the free fatty acid fractions were subsequently analyzed with Gas Chromatography (GC/FID). PAHs and FFA were quantified and used to monitor the impact of the type of biomass used in smoking the mud fish. The result showed that 24 PAHs were detected in all the samples except in firewood smoked mud fish (FSMF) 1hr and charcoal smoked mud fish (CSMF) 1h – 4h where benzo[j]fluoranthene was below detection limit. The total PAHs found in all smoked mud fish in this study were higher than what was found in fresh [control] fish. Amount of PAHs in samples smoked with wood was significantly different from samples smoked with charcoal. The main compounds of free fatty acids present in the samples were myritic acid, palmitic acid, stearic acid and linoleic acid. The concentration of PAHs with 2 – 3 rings were less than the PAHs with 4 – 6 rings, with pyrene, benzo[c]phenanthrene and indeno(1,2,3 – cd) pyrene being the most abundant compounds. The phenanthrene/anthracene ratio for FSMF ranged from 0.27 – 9.02 and 0.72 – 1.66 for CSMF which suggests the source of the PAHs was pyrolitic. Also, Fluoranthene/fluoranthene + pyrene ratio ranged from 0.00 – 0.54 in FSMF and 0.01 – 0.99 for CSMF samples which equally suggests a pyrolytic source. From the proximate analysis results, the crude protein for the UPMF is 28.27 which increases gradually to 47.7 % in FSMF 4h and increased to 65.94 % in CSMF 4h. The crude fiber of all the samples both processed and unprocessed were generally low than expected. The percentage composition of fat increased from 1.01 % in fresh sample to 6.04 % in CSMF 4h.

Highlights

  • Polycyclic Aromatic hydrocarbons (PAHs) are hazardous organic chemicals consisting of two or more benzenoid group [1]

  • It can be implied that smoking for short time and low temperature will lead to high concentration of PAHs in smoked fish, whereas higher time of smoking and high temperature will lead to decrease in the total PAHs in the smoked fish

  • Among all the 24 PAHs detected in the samples, Benzo(a)fluorathene was below detection limit in firewood smoked mud fish (FSMF) 1hr and in charcoal smoked mud fish (CSMF) 1h, 2h, 3h and 4h

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Summary

Introduction

Polycyclic Aromatic hydrocarbons (PAHs) are hazardous organic chemicals consisting of two or more benzenoid group [1]. Those containing up to four benzene rings are known as light PAHs (L-PAHs) and those containing more than four benzene rings are known as heavy PAHs (H-PAHs). H-PAHs are more stable and toxic than L-PAHs [2]. They are ubiquitous pollutants in the environment. Some have been demonstrated to be mutagenic and carcinogenic for humans [4]. Those PAHs that are considered to be less toxic may even increase the carcinogenicity of other PAHs [3, 5]. Sixteen of the PAHs that are considered as priority by the American Environmental Protection Agency (AEPA) are; naphthalene, acenaphthylene, acenaphthene, fluorene, anthracene, phenanthrene, fluoranthene, chrysene, benzo (a) anthracene, pyrene, benzo (k) fluoranthrene, benzo (b) fluoranthene, benzo (a) pyrene, dibenzo (a,h) anthracene, indeno(1,2,3-cd) pyrene and benzo (g, h, i) perylene [1]

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