Plasticizers and bisphenol A, in packaged foods sold in the Tunisian markets: study of their acute in vivo toxicity and their environmental fate
Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products,...
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| Vydané v: | Environmental science and pollution research international Ročník 24; číslo 28; s. 22382 - 22392 |
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| Hlavní autori: | , , , , , , , , |
| Médium: | Journal Article |
| Jazyk: | English |
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Berlin/Heidelberg
Springer Berlin Heidelberg
01.10.2017
Springer Nature B.V |
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| ISSN: | 0944-1344, 1614-7499, 1614-7499 |
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| Abstract | Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream
Sparus aurata
. In fact, chemical analysis showed the contamination of wild
S. aurata
by BBP from Sousse Coast (1.5 mg/kg) and wild
S. aurata
from Monastir Coast (0.33 mg/kg). |
|---|---|
| AbstractList | Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream Sparus aurata. In fact, chemical analysis showed the contamination of wild S. aurata by BBP from Sousse Coast (1.5 mg/kg) and wild S. aurata from Monastir Coast (0.33 mg/kg). Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream Sparus aurata. In fact, chemical analysis showed the contamination of wild S. aurata by BBP from Sousse Coast (1.5 mg/kg) and wild S. aurata from Monastir Coast (0.33 mg/kg).Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream Sparus aurata. In fact, chemical analysis showed the contamination of wild S. aurata by BBP from Sousse Coast (1.5 mg/kg) and wild S. aurata from Monastir Coast (0.33 mg/kg). Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream Sparus aurata . In fact, chemical analysis showed the contamination of wild S. aurata by BBP from Sousse Coast (1.5 mg/kg) and wild S. aurata from Monastir Coast (0.33 mg/kg). Today, processed and packaged foods are considered as among the major sources of human exposure to plasticizers and bisphenol which migrate from plastic packing. In the present study, a wide range of food products sold on the Tunisian market such as grain and grain products, milk and dairy products, fats and oil, drink, fish, and sweets have been analyzed firstly in order to identify the presence of phthalates and bisphenol. Then, the identified chemical molecules were studied for their environmental fate and tested in vivo for its toxicity in mice models. The food products analyzed using GC-MS/MS indicated the presence of the benzyl butyl phthalate (BBP), dibutyl phthalate (DBP), bis(2-ethylhexyl) phthalate (DEHP), diisodecyl phthalate (DiDP), diisononyl phthalate (DiNP), and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINC) and which using UPLC-MS/MS demonstrated the presence of bisphenol A of all food products. However, compared to other phthalates, BBP was found at high concentrations in the puff pastry (123 mg/kg), milk (2.59 mg/kg), butter (1.5 mg/kg), yogurt (2.23 mg/kg), oil (6.94 mg/kg), water (0.57 mg/kg), candy 1 (2.35 mg/kg), candy 2 (0.81 mg/kg), orange juice (1.25 mg/kg), peach juice (1.26 mg/kg), fruit juices (0.4 mg/kg), and chocolate (0.884 mg/kg). The obtained data in vivo clearly showed that the acute administration of BBP caused hepatic and renal damage as demonstrated by an increase in biochemical parameters as well as the activities of plasma marker enzymes such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase, lactate dehydrogenase, blood urea nitrogen, glucose, urea, creatinine, and uric acid when compared to the control group. By the same occurrence, the histopathological study revealed that BBP strongly modified the structure of hepatic and renal tissues. In addition, the plasticizers and BBP will therefore discharge via wastewater treatment plants in aquatic system and could reach marine organisms such as fish. We have followed the fate of BBP in bream Sparus aurata. In fact, chemical analysis showed the contamination of wild S. aurata by BBP from Sousse Coast (1.5 mg/kg) and wild S. aurata from Monastir Coast (0.33 mg/kg). |
| Author | Machreki, Monia Reyns, Tim Mansour, Hedi Ben Di Bella, Giuseppa Ghazouani, Lakhdar Feriani, Anouar Van Loco, Joris Beltifa, Asma Ghorbel, Asma |
| Author_xml | – sequence: 1 givenname: Asma surname: Beltifa fullname: Beltifa, Asma organization: Research Unit of Analysis and Process Applied to Environmental (APAE) UR17ES32 Higher Institute of Applied Sciences and Technology Mahdia, “ISSAT”, University of Monastir, Laboratory of Chemical Residues and Contaminants, Direction of Food, Medicines and Consumer Safety, Scientific Institute of Public Health, Faculté des Sciences Mathématiques, Physiques et Naturelles Université Tunis El Manar – sequence: 2 givenname: Anouar surname: Feriani fullname: Feriani, Anouar organization: Unité de Biochimie Macromoléculaire et Génétique, Faculté des sciences de Gafsa – sequence: 3 givenname: Monia surname: Machreki fullname: Machreki, Monia organization: Research Unit of Analysis and Process Applied to Environmental (APAE) UR17ES32 Higher Institute of Applied Sciences and Technology Mahdia, “ISSAT”, University of Monastir – sequence: 4 givenname: Asma surname: Ghorbel fullname: Ghorbel, Asma organization: Hygiene Laboratory/Toxicology Unit Hedi CHAKER Hospital – sequence: 5 givenname: Lakhdar surname: Ghazouani fullname: Ghazouani, Lakhdar organization: Unité de Biochimie Macromoléculaire et Génétique, Faculté des sciences de Gafsa – sequence: 6 givenname: Giuseppa surname: Di Bella fullname: Di Bella, Giuseppa organization: Dipartimento di ScienzeBiomediche, Odontoiatriche e delleImmaginiMorfologiche e Funzionali of the University of Messina – sequence: 7 givenname: Joris surname: Van Loco fullname: Van Loco, Joris organization: Laboratory of Chemical Residues and Contaminants, Direction of Food, Medicines and Consumer Safety, Scientific Institute of Public Health – sequence: 8 givenname: Tim surname: Reyns fullname: Reyns, Tim organization: Laboratory of Chemical Residues and Contaminants, Direction of Food, Medicines and Consumer Safety, Scientific Institute of Public Health – sequence: 9 givenname: Hedi Ben surname: Mansour fullname: Mansour, Hedi Ben email: hdbenmansour@gmail.com organization: Research Unit of Analysis and Process Applied to Environmental (APAE) UR17ES32 Higher Institute of Applied Sciences and Technology Mahdia, “ISSAT”, University of Monastir |
| BackLink | https://www.ncbi.nlm.nih.gov/pubmed/28801775$$D View this record in MEDLINE/PubMed |
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| ContentType | Journal Article |
| Copyright | Springer-Verlag GmbH Germany 2017 Environmental Science and Pollution Research is a copyright of Springer, (2017). All Rights Reserved. |
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| Keywords | Marine organisms Bisphenol A Plasticizers Biochemical analysis Food contamination Acute toxicity |
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| References | Fromme, Gruber, Schlummer, Wolz, Boehmer, Angerer, Mayer, Liebi, Bolte (CR2) 2007; 33 CR6 Moghaddam, Samarghandians, Farkhndeh (CR10) 2015; 25 CR8 Ahmed, Moselhy, Nabil (CR1) 2015; 14 CR18 Giboney (CR3) 2005; 71 Hanioka, Jinno, Tanaka-agawa, Nishimura, Ando (CR5) 2000; 41 Moon, Kim, Jug, Koo, Ann, Lee, Kim, Yoon, Ch, Park, Jang, Park (CR11) 2012; 27 Mourad, Khadrawy (CR12) 2012; 2 Nakagawa, Tayama (CR13) 2000; 74 Wroblewski (CR17) 1995 Wormuth, Scheringer, Vollenweider, Hungerbuchler (CR16) 2006; 26 Sangai, Verma, Trivedi (CR15) 2012; 30 Goulas, Zygoura, Karatapanis, Georgantelis, Kontominas (CR4) 2007; 45 Reitman, Frankel (CR14) 1957; 28 Kavlock, Boekelheide, Chapin, Cunningham, Faustman, Foster, Golub, Henderson, Hinberg, Little, Seed, Shea, Tabacova, Tyl, Williams, Zacharewski (CR7) 2002; 16 Marmugi, Lasserre, Beuzelin, Duckeix, Huc, Polizzi, Chetivau, Pineau, Martin, Guillou, Mselli-Lakhal (CR9) 2014; 5 9861_CR8 AE Goulas (9861_CR4) 2007; 45 9861_CR6 N Hanioka (9861_CR5) 2000; 41 WMS Ahmed (9861_CR1) 2015; 14 M Wormuth (9861_CR16) 2006; 26 A Marmugi (9861_CR9) 2014; 5 R Kavlock (9861_CR7) 2002; 16 NP Sangai (9861_CR15) 2012; 30 S Reitman (9861_CR14) 1957; 28 HS Moghaddam (9861_CR10) 2015; 25 MK Moon (9861_CR11) 2012; 27 PT Giboney (9861_CR3) 2005; 71 Y Nakagawa (9861_CR13) 2000; 74 9861_CR18 IM Mourad (9861_CR12) 2012; 2 H Fromme (9861_CR2) 2007; 33 F Wroblewski (9861_CR17) 1995 10879814 - Chemosphere. 2000 Oct;41(7):973-8 23024108 - Toxicol Ind Health. 2014 Aug;30(7):581-97 25168180 - Toxicology. 2014 Nov 5;325:133-43 22888396 - Oxid Med Cell Longev. 2012;2012:194829 13458125 - Am J Clin Pathol. 1957 Jul;28(1):56-63 23359474 - PLoS One. 2013;8(1):e55387 22690096 - J Korean Med Sci. 2012 Jun;27(6):644-52 17610953 - Environ Int. 2007 Nov;33(8):1012-20 26376105 - Toxicol Mech Methods. 2015;25(7):507-13 15791889 - Am Fam Physician. 2005 Mar 15;71(6):1105-10 16834635 - Risk Anal. 2006 Jun;26(3):803-24 23821587 - Hum Exp Toxicol. 2013 Jul;32(7):675-86 17141933 - Food Chem Toxicol. 2007 Apr;45(4):585-91 12406493 - Reprod Toxicol. 2002 Sep-Oct;16(5):489-527 10839477 - Arch Toxicol. 2000 Apr;74(2):99-105 |
| References_xml | – volume: 28 start-page: 56 year: 1957 end-page: 63 ident: CR14 article-title: Colorimetric method for the determination of serum glutamic oxaloacetic and glutamic pyruvic transaminases publication-title: Am J Clin Pathol doi: 10.1093/ajcp/28.1.56 – volume: 27 start-page: 644 year: 2012 end-page: 652 ident: CR11 article-title: Bisphenol impairs mitochondrial function in the liver at doses below the n observed adverse effect level publication-title: J Korean Med Sci doi: 10.3346/jkms.2012.27.6.644 – ident: CR18 – volume: 25 start-page: 507 year: 2015 end-page: 513 ident: CR10 article-title: Effect of bisphenol A on blood glucose, lipid profile and oxidative stress indices in adult male mice publication-title: Toxicol Mech Methods doi: 10.3109/15376516.2015.1056395 – volume: 33 start-page: 1012 year: 2007 end-page: 1020 ident: CR2 article-title: Intake of phthalates and di (2-ethylhexyl) adipate: results of the integrated exposure assessment survey based on duplicate diet samples and bio monitoring data publication-title: Environ Int doi: 10.1016/j.envint.2007.05.006 – volume: 71 start-page: 1105 year: 2005 end-page: 1110 ident: CR3 article-title: Mildly elevated liver transaminase levels in the asymptomatic patient publication-title: Am Fam Physician – volume: 45 start-page: 585 year: 2007 end-page: 591 ident: CR4 article-title: Migration of di(2-ethylhexyl) adipate and acetyltributyl citrate plasticizers from food-grade PVC film into sweetened sesame paste (halawa tehineh): kinetic and penetration study publication-title: Food Chem Toxicol doi: 10.1016/j.fct.2006.10.003 – volume: 16 start-page: 489 year: 2002 end-page: 527 ident: CR7 article-title: NTP center for the evaluation of risks to human reproduction: phthalates expert panel report on the reproductive and developmental toxicity of di-nbutyl phthalate publication-title: Reprod Toxicol doi: 10.1016/S0890-6238(02)00033-3 – volume: 14 start-page: 228 year: 2015 end-page: 238 ident: CR1 article-title: Bisphenol A toxicity in adult male rat’s hematological, biochemical and histological approach publication-title: Glob Vet – start-page: 115 year: 1995 end-page: 118 ident: CR17 publication-title: La Due JS Colorimetric method for LDH in Wootton IDP microanalysis in medical biochemistry – ident: CR6 – volume: 41 start-page: 973 year: 2000 end-page: 978 ident: CR5 article-title: Interaction of bisphenol A with rat hepatic cytochrome P450 enzymes publication-title: Chemosphere doi: 10.1016/S0045-6535(99)00529-9 – volume: 5 start-page: 133 year: 2014 end-page: 143 ident: CR9 article-title: Adverse effects of long-term exposure to bisphenol A during adulthood leading to hyperglycemia and hypercholesterolemia in mice publication-title: Toxiclogy doi: 10.1016/j.tox.2014.08.006 – volume: 26 start-page: 803 year: 2006 end-page: 824 ident: CR16 article-title: What are the sources of exposure to eight frequently used phtalic acid esters in Europeans? publication-title: Risk Anal doi: 10.1111/j.1539-6924.2006.00770.x – ident: CR8 – volume: 2 start-page: 19 year: 2012 end-page: 28 ident: CR12 article-title: The sensitivity of liver, kidney and testis of rats to oxidative stress induced by different doses of bisphenol publication-title: Int J Life Sci Pharma Res doi: 10.5963/LSMR0202002 – volume: 74 start-page: 99 year: 2000 end-page: 105 ident: CR13 article-title: Metabolism and cytotoxicity of bisphenol A and other bisphenol in isolated rat hepatocytes publication-title: Arch Toxicol doi: 10.1007/s002040050659 – volume: 30 start-page: 581 year: 2012 end-page: 597 ident: CR15 article-title: Testing the efficacity of quercetin in mitigating bisphenol A toxicity in liver and kidney of mice publication-title: Toxicol Ind Health doi: 10.1177/0748233712457438 – volume: 25 start-page: 507 year: 2015 ident: 9861_CR10 publication-title: Toxicol Mech Methods doi: 10.3109/15376516.2015.1056395 – volume: 30 start-page: 581 year: 2012 ident: 9861_CR15 publication-title: Toxicol Ind Health doi: 10.1177/0748233712457438 – volume: 26 start-page: 803 year: 2006 ident: 9861_CR16 publication-title: Risk Anal doi: 10.1111/j.1539-6924.2006.00770.x – volume: 2 start-page: 19 year: 2012 ident: 9861_CR12 publication-title: Int J Life Sci Pharma Res doi: 10.5963/LSMR0202002 – volume: 14 start-page: 228 year: 2015 ident: 9861_CR1 publication-title: Glob Vet – ident: 9861_CR8 doi: 10.1371/journal.pone.0055387 – volume: 27 start-page: 644 year: 2012 ident: 9861_CR11 publication-title: J Korean Med Sci doi: 10.3346/jkms.2012.27.6.644 – volume: 45 start-page: 585 year: 2007 ident: 9861_CR4 publication-title: Food Chem Toxicol doi: 10.1016/j.fct.2006.10.003 – ident: 9861_CR6 doi: 10.1155/2012/194829 – start-page: 115 volume-title: La Due JS Colorimetric method for LDH in Wootton IDP microanalysis in medical biochemistry year: 1995 ident: 9861_CR17 – volume: 28 start-page: 56 year: 1957 ident: 9861_CR14 publication-title: Am J Clin Pathol doi: 10.1093/ajcp/28.1.56 – ident: 9861_CR18 doi: 10.1177/0960327112464796 – volume: 74 start-page: 99 year: 2000 ident: 9861_CR13 publication-title: Arch Toxicol doi: 10.1007/s002040050659 – volume: 33 start-page: 1012 year: 2007 ident: 9861_CR2 publication-title: Environ Int doi: 10.1016/j.envint.2007.05.006 – volume: 41 start-page: 973 year: 2000 ident: 9861_CR5 publication-title: Chemosphere doi: 10.1016/S0045-6535(99)00529-9 – volume: 5 start-page: 133 year: 2014 ident: 9861_CR9 publication-title: Toxiclogy doi: 10.1016/j.tox.2014.08.006 – volume: 71 start-page: 1105 year: 2005 ident: 9861_CR3 publication-title: Am Fam Physician – volume: 16 start-page: 489 year: 2002 ident: 9861_CR7 publication-title: Reprod Toxicol doi: 10.1016/S0890-6238(02)00033-3 – reference: 10879814 - Chemosphere. 2000 Oct;41(7):973-8 – reference: 12406493 - Reprod Toxicol. 2002 Sep-Oct;16(5):489-527 – reference: 25168180 - Toxicology. 2014 Nov 5;325:133-43 – reference: 17141933 - Food Chem Toxicol. 2007 Apr;45(4):585-91 – reference: 10839477 - Arch Toxicol. 2000 Apr;74(2):99-105 – reference: 23359474 - PLoS One. 2013;8(1):e55387 – reference: 17610953 - Environ Int. 2007 Nov;33(8):1012-20 – reference: 15791889 - Am Fam Physician. 2005 Mar 15;71(6):1105-10 – reference: 13458125 - Am J Clin Pathol. 1957 Jul;28(1):56-63 – reference: 23024108 - Toxicol Ind Health. 2014 Aug;30(7):581-97 – reference: 26376105 - Toxicol Mech Methods. 2015;25(7):507-13 – reference: 16834635 - Risk Anal. 2006 Jun;26(3):803-24 – reference: 22690096 - J Korean Med Sci. 2012 Jun;27(6):644-52 – reference: 22888396 - Oxid Med Cell Longev. 2012;2012:194829 – reference: 23821587 - Hum Exp Toxicol. 2013 Jul;32(7):675-86 |
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| Title | Plasticizers and bisphenol A, in packaged foods sold in the Tunisian markets: study of their acute in vivo toxicity and their environmental fate |
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