Avaliação da presença do 3-monocloro-1, 2-propanediol e glicidol em óleos vegetais comestíveis utilizando GC/MS/MS e seu risco toxicológico / Evaluation of the presence of 3-monochloro-1, 2-propanediol and glycidol in edible vegetable oils using GC/MS/MS and its toxicological risk

Cloropropanóis são um grupo conhecido de contaminantes relacionados ao processamento de alimentos. Eles são formados na reação entre lipídeos e cloretos quando submetidos ao tratamento térmico, e podem ser encontrados na forma livre ou ligada. O 3-monocloro-1,2-propanediol (3-MCPD), é classificado pela IARC como possível carcinógeno humano (grupo 2B). O glicidol (e seus ésteres), é classificado também pela IARC como uma substância provavelmente carcinogênica para seres humanos (grupo 2A), e, recentemente, vem sendo encontrado em alimentos. O objetivo deste trabalho foi avaliar a presença do 3-MCPD e do glicidol em óleos vegetais comestíveis utilizando a cromatografia gasosa com detector de massa triplo quadrupolo MS/MS. A técnica utilizada foi a preconizada pela AOCS Cd 29c-13, sendo uma análise indireta, e foi possível adaptá-la visando as determinações do 3-MCPD e glicidol através da construção de curvas de calibração e análises de amostras de referência. O método foi validado e os resultados indicaram o limite de detecção do composto 3-MCPD, de 42,4 µg/kg e o limite de quantificação de 50 µg/kg, e para o Glicidol indicaram o limite de detecção de 43,5 µg/kg e limite de quantificação de 50 µg/kg. Os resultados para 3-MCPD obtidos nos ensaios da curva de calibração e linearidade demonstraram que o método foi capaz de expressar resultados com boa linearidade (0 - 10 mg/kg , r2, = 0.9991). Os resultados obtidos nos ensaios de exatidão obedeceram aos critérios de 70 a 120% de recuperação, e ±20% de variação entre os resultados de acordo com SANTE (2017). O método em questão demonstrou ser seletivo, uma vez que não foram observados picos interferentes nos tempos de retenção dos compostos estudados. Os ensaios de precisão nos níveis baixos, médio e alto e robustez demonstraram que o método é robusto e preciso, portanto a validação foi considerada adequada ao uso pretendido. Foram analisadas 368 amostras de óleos vegetais (76 amostras de óleo de canola, 48 amostras de óleo de milho, 69 amostras de óleo de algodão, 33 amostras de óleo de palma, 10 amostras de óleo de palmiste, 50 amostras de oleína de palma, 30 amostras de óleo de soja e 51 amostras de óleo de girassol). As concentrações das amostras analisadas apresentaram resultados para 3-MCPD com valores médios entre 203 a 1205 µg/kg. Para o Glicidol os valores foram de 2 a 1198 µg/kg, com elevado o desvio padrão entre os resultados analíticos, onde o óleo de palma apresentou a maior variação de 1600 a 5260 µg/kg. Através da avaliação do risco realizada para o composto 3-MCPD foi possível detectar, utilizando o critério do pior cenário de exposição e resultados analíticos, os valores diários de consumo de óleo de algodão de 0,044 µg/kg p.c., de óleo de girassol 0,045 µg/kg p.c., óleo de canola 0,18 µg/kg p.c., óleo de palma de 0,28 µg/p.c, óleo de milho de 0,0462 µg/kg p.c., e o óleo de soja, de maior consumo no Brasil (72%) apresentou o valor de 0,27 µg/kg p.c. O consumo de todos estes óleos, pela a população brasileira, pode ser considerado seguro ao comparar com o valor de TDI Ingestão Diária Tolerável - de 2µg/kg p.c.. Através da avaliação do risco realizada também utilizando o critério de pior cenário de exposição e e resultados analíticos para o composto glicidol foi possível verificar que os valores diários de consumo de óleo de algodão de 0,061 µg/kg p.c., de óleo de girassol 0,03 µg/kg p.c., óleo de canola 0,13 µg/kg p.c. e de óleo de palma de 0,57 µg/p.c, de óleo de milho de 0,11 µg/kg p.c, e o óleo de soja de maior consumo no Brasil (72%) não ultrapassam o valor de 0,288 µg/kg p.c indicando consumo seguro destes óleos para a população brasileira baseado na TDI de 1000µg/kg p.c

Chloropropanols are a known group of contaminants related to food processing. They are formed during the reaction process between lipids and chlorides when submitted to heat treatment and can be found in free or bound form. The 3-monochloro-1,2-propanediol (3-MCPD), is classified by IARC as a possible human carcinogen (group 2B). Glycidol (and its esters), also classified by IARC as a substance likely to be carcinogenic to humans (group 2A), has recently been found in food. The present study aims to evaluate the presence of 3-MCPD and glycidol in edible vegetable oils using gas chromatography with triple quadrupole MS/MS mass detector. The technique applied is recommended by AOCS, guide Cd 29c-13, an indirect analysis, and allows quantification of 3-MCPD and glycidol by building the calibration curves and analysis of reference samples. The method was validated and the detection limit of the contaminant 3-MCPD of 42,4 µg/kg and the quantification limit of 50 µg/kg was established. For Glycidol the detection limit of was 43,5 µg/kg and quantification limit was 50 µg/kg. The results obtained in the calibration and linearity curves demonstrated that the method could express results with good linearity (0 10 mg/kg, r2, = 0.9991). The results obtained in the trueness trials agreed to the criteria of 70 to 120% of recovery, and ± 20% of variation between the results according to what is preconized by SANTE (2017). The method showed to be selective, since no interfering peaks were observed in the retention times of the studied compounds. The tests performed on low, medium and high values demonstrated the robustness and precision of the method, so the validation was considered completed and suitable for the purpose. A total of 368 vegetable oil samples were analyzed (76 samples of canola oil, 48 samples of corn oil, 69 samples of cottonseed oil, 33 samples of palm oil, 10 samples of kern palm oil, 50 samples of palm olein, 30 samples of soybean oil and 51 samples of sunflower oil). The results found in samples for 3-MCPD were within mean values between 203 and 1205 µg/kg. The results found in samples for glycidol were within mean values between 2 to 1198 µg/kg where palm oil presented the highest variation for glycidol from 1600 to 5260 µg/kg. Through the risk assessment for the contaminant 3-MCPD it was possible to detect the values based on exposed worst case scenario and analytical results. The results for cottom oil were 0,044 µg/kg bw, sunflower 0,045 µg/kg bw, canola 0,18 µg/kg bw and palm oil 0,28 µg/kg bw, corn oil 0,0462 µg/kg bw, and for soybean, which is the most consumed oil in Brazil (72%) the value of 0,27 µg/kg bw. These results indicates safe consumption for these oils based in the Theoretical Daily Ingestion - TDI of 2µg/kg bw. The risk assessment for the glycidol based on exposure worst case scenario and analytical results presented for cottom oil the value of 0,061 µg/kg bw, sunflower 0,03 µg/kg bw, canola oil 0,13 µg/kg bw , palm oil 0,57 µg/kg bw, corn oil 0,11 µg/kg bw and for soybean, which is the most consumed in Brazil - 72% the value of 0,27 µg/kg bw. These results indicates safe consumption for these oils based in the TDI of 1000µg/kg bw

Development of gas chromatography-mass spectrometry for determination of fatty acid esters of chloropropanols in milk powder and the pollution level of infant formula / 中华预防医学杂志

<p><b>OBJECTIVE</b>To establish a method for determination of fatty acid esters of chloropropanols (chloropropanols esters) in milk powder by isotope dilution-gas chromatography-mass spectrometry (GC-MS), and to acquire the pollution level of chloropropanols esters in infant formula and evaluate the dietary exposure risk of chloropropanols esters in infant formula for infants.</p><p><b>METHODS</b>A total of 111 infant formula samples were collected from supermarkets in Beijing, and the infant formula with no chloropropanols esters detected was served as the blank sample. The samples were ultrasonically extracted with hexane, followed by ester-bond cleavage reaction with sodium methylate-methanol and purification by matrix solid-supported liquid-liquid extraction, then being derivatived with heptafluoro butyrylimidazol. After extracted by sodium chloride solution, the derivatives were determined by GC-MS. The concentration of chloropropanols esters were quantified using the deuterium chloropropanols esters as the internal standards. The accuracy of the method was assessed by the recoveries of the blank spiked samples, and the relative standard deviations (RSD) of the recoveries represent the precision of the method. The contamination level of chloropropanols esters and the intake amount of the infant formula of the 6-month infant were used to estimate the dietary exposure assessment, and x (95% CI) and P97.5 of the contamination level of chloropropanols esters were used to represent the average dietary exposure and the high-end dietary exposure.</p><p><b>RESULTS</b>The satisfied linear correlations in the range of 0.010-0.800 mg/L was acquired for 3-MCPD esters, 2-MCPD esters, 1,3-DCP esters and 2,3-DCP esters with coefficient correlations of 0.999 9, 0.999 8, 0.999 5 and 0.999 6, respectively. The limits of detection (LOD) and the limits of quantitation (LOQ) for 3-MCPD esters, 2-MCPD esters, 1,3-DCP esters and 2,3-DCP esters were 0.005, 0.005, 0.015, 0.015 mg/kg, and 0.015, 0.015, 0.045, 0.045 mg/kg. The average recoveries of the four chloropropanols esters spiked at 0.025, 0.050 and 0.100 mg/kg in blank matrix were in a range from 80.3% to 111.9%, with relative standard deviations (RSD) less than 11.4%. Of the 111 infant formula samples, the detection rates and the contamination levels of 3-MCPD esters and 2-MCPD esters were 77.5% (86/111), 11.7% (13/111) with the contamination levels in the range of ND-0.230 mg/kg and ND-0.039 mg/kg, respectively, and χ (95% CI) and P97.5 of 3-MCPD esters and 2-MCPD esters were 0.020 (0.003-0.113) and 0.006 (0.005-0.025) mg/kg, 0.113 and 0.025 mg/kg, respectively. 1,3-DCP esters and 2,3-DCP esters were not detected in the 111 samples. x (95% CI) and P75 of the six-month old infants to 3-MCPD esters were 0.304 (0.038-1.735) and 1.735 µg · kg⁻¹ · d⁻¹, respectively, which accounted for 15.2% and 86.7% of the PMTDI (2 µg · kg⁻¹ · d⁻¹) of 3-MCPD.</p><p><b>CONCLUSION</b>This GC-MS method was accurate and rugged for the determination of chloropropanols esters in milk powder. Based on the exposure assessment results, the health risk of chloropropanols esters for infants caused by the intake of infant formula was acceptable.</p>

Spermatotoxic effects of alpha-chlorohydrin in rats / 한국실험동물학회지

This study was conducted to investigate the potential effects of alpha-chlorohydrin (ACH) on epididymal function and antioxidant system in male rats. The test chemical was administered to male rats by gavage at doses of 0, 3, 10, and 30 mg/kg/day for 7 days. Twenty-four male rats were randomly assigned to four experimental groups, with six rats in each group. Spermatotoxicity was assessed by measurement of reproductive organ weight, testicular sperm head count, epididymal sperm motility and morphology, histopathologic examination, and oxidative damage analysis in rats. At 30 mg/kg/day, an increase in the incidence of clinical signs, epididymis weight, and gross necropsy findings of the epididymis, a decrease in the sperm motility, and an increased incidence of histopathological changes of the epididymis were observed in a dose-dependent manner. At 10 mg/kg/day, an increased incidence of clinical signs and histopathological changes and decreased sperm motility were observed. In the oxidative damage analysis, an increase in the malondialdehyde concentration and a decrease in the glutathione content and glutathione peroxidase and catalase activities in the epididymal tissue were detected at > or =3 mg/kg/day. The results show that graded doses of ACH elicit depletion of the antioxidant defense system and that the spermatotoxicity of ACH may be due to the induction of oxidative stress.

Study on the absorption, distribution and excretion of 3-chloro-1,2-propandiol in rats / 中华预防医学杂志

<p><b>OBJECTIVE</b>To explore the absorption, distribution and excretion of 3-Chloro-1,2-propandiol (3-MCPD) in healthy male SD rats after oral administration.</p><p><b>METHODS</b>3-MCPD was administrated with a single oral dosage of 75 mg/kg BW to each rat. Samples of blood, tissues (including liver, kidney, brain and testicle) and excreta were then collected, and analyzed by the GC-MS method to determine 3-MCPD concentrations. The reported value is the mean value of three rats.</p><p><b>RESULTS</b>At 2 h after the administration, 3-MCPD concentrations in blood, testicle and kidney were (67.46 +/- 7.72), (78.37 +/- 5.15) and (56.21 +/- 3.64) microg/g, respectively. At 24 h, however, the corresponding values changed to (1.07 +/- 0.97) microg/g, (49.43 +/- 28.18) microg/g and (11.41 +/- 2.55) microg/g. During the 24-hour period, 9.74 +/- 3.05% of the given parent compound was excreted in urine, whereas 0.56 +/- 0.22% and 0.28 +/- 0.03% were excreted in feces and bile, respectively, which implies that kidney is a major organ for excretion 3-MCPD.</p><p><b>CONCLUSIONS</b>3-MCPD was quickly absorbed through the alimentary tract and quickly distributed into a number of tissues, and then accumulated in the target organs, especially in the testicle. The excretion of the parent compound was largely through the kidney. It was inferred that 3-MCPD was mainly metabolized in the liver.</p>

Conformational features of reduced and disulfide intact forms of hen egg white lysozyme in aqueous solution in presence of 3-chloro-1, 2-propanediol and dioxane: implications for protein folding intermediates.

Conformational features of reduced and disulfide intact hen egg white lysozyme in aqueous 1,4-dioxane and 3-chloro-1, 2-propanediol solutions have been examined using circular dichroism and fluorescence spectroscopy. We find that in presence of 1, 4-dioxane, reduced lysozyme assumes a relatively compact conformational form with secondary structure closer to native state and no tertiary structure as judged by peptide and aromatic CD spectra and ANS binding studies monitored by fluorescence. Further, in presence of 40% (v/v) 3-chloro-1, 2-propanediol, disulfide intact lysozyme (DI-lysozyme) assumes a conformational form with native like secondary structure and no tertiary structure akin to a molten globule state. We correlate our results to kinetic hydrogen- deuterium exchange NMR results of the refolding of lysozyme available in literature and suggest that the conformational forms observed in our study could be models for kinetic intermediates in the refolding of lysozyme.