Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria
Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limi...
Ausführliche Beschreibung
Autor*in: |
Ishmail Kamara [verfasserIn] Gilbert Umaye Adie [verfasserIn] Abdulmoseen Segun Giwa [verfasserIn] |
---|
Format: |
E-Artikel |
---|---|
Sprache: |
Englisch |
Erschienen: |
2023 |
---|
Schlagwörter: |
---|
Übergeordnetes Werk: |
In: Scientific African - Elsevier, 2018, 20(2023), Seite e01613- |
---|---|
Übergeordnetes Werk: |
volume:20 ; year:2023 ; pages:e01613- |
Links: |
---|
DOI / URN: |
10.1016/j.sciaf.2023.e01613 |
---|
Katalog-ID: |
DOAJ088549763 |
---|
LEADER | 01000naa a22002652 4500 | ||
---|---|---|---|
001 | DOAJ088549763 | ||
003 | DE-627 | ||
005 | 20230410113629.0 | ||
007 | cr uuu---uuuuu | ||
008 | 230410s2023 xx |||||o 00| ||eng c | ||
024 | 7 | |a 10.1016/j.sciaf.2023.e01613 |2 doi | |
035 | |a (DE-627)DOAJ088549763 | ||
035 | |a (DE-599)DOAJ61c965628653428a8f50f177a6599ede | ||
040 | |a DE-627 |b ger |c DE-627 |e rakwb | ||
041 | |a eng | ||
100 | 0 | |a Ishmail Kamara |e verfasserin |4 aut | |
245 | 1 | 0 | |a Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
264 | 1 | |c 2023 | |
336 | |a Text |b txt |2 rdacontent | ||
337 | |a Computermedien |b c |2 rdamedia | ||
338 | |a Online-Ressource |b cr |2 rdacarrier | ||
520 | |a Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. | ||
650 | 4 | |a Toxic metals | |
650 | 4 | |a Low-cost toys | |
650 | 4 | |a Polyvinyl chloride | |
650 | 4 | |a Artificial saliva | |
650 | 4 | |a Gastric environment | |
650 | 4 | |a Hazard index | |
653 | 0 | |a Science | |
653 | 0 | |a Q | |
700 | 0 | |a Gilbert Umaye Adie |e verfasserin |4 aut | |
700 | 0 | |a Abdulmoseen Segun Giwa |e verfasserin |4 aut | |
773 | 0 | 8 | |i In |t Scientific African |d Elsevier, 2018 |g 20(2023), Seite e01613- |w (DE-627)1047200163 |x 24682276 |7 nnns |
773 | 1 | 8 | |g volume:20 |g year:2023 |g pages:e01613- |
856 | 4 | 0 | |u https://doi.org/10.1016/j.sciaf.2023.e01613 |z kostenfrei |
856 | 4 | 0 | |u https://doaj.org/article/61c965628653428a8f50f177a6599ede |z kostenfrei |
856 | 4 | 0 | |u http://www.sciencedirect.com/science/article/pii/S2468227623000704 |z kostenfrei |
856 | 4 | 2 | |u https://doaj.org/toc/2468-2276 |y Journal toc |z kostenfrei |
912 | |a GBV_USEFLAG_A | ||
912 | |a SYSFLAG_A | ||
912 | |a GBV_DOAJ | ||
912 | |a GBV_ILN_11 | ||
912 | |a GBV_ILN_20 | ||
912 | |a GBV_ILN_22 | ||
912 | |a GBV_ILN_23 | ||
912 | |a GBV_ILN_24 | ||
912 | |a GBV_ILN_31 | ||
912 | |a GBV_ILN_39 | ||
912 | |a GBV_ILN_40 | ||
912 | |a GBV_ILN_60 | ||
912 | |a GBV_ILN_62 | ||
912 | |a GBV_ILN_63 | ||
912 | |a GBV_ILN_65 | ||
912 | |a GBV_ILN_69 | ||
912 | |a GBV_ILN_70 | ||
912 | |a GBV_ILN_73 | ||
912 | |a GBV_ILN_95 | ||
912 | |a GBV_ILN_105 | ||
912 | |a GBV_ILN_110 | ||
912 | |a GBV_ILN_151 | ||
912 | |a GBV_ILN_161 | ||
912 | |a GBV_ILN_170 | ||
912 | |a GBV_ILN_206 | ||
912 | |a GBV_ILN_213 | ||
912 | |a GBV_ILN_230 | ||
912 | |a GBV_ILN_285 | ||
912 | |a GBV_ILN_293 | ||
912 | |a GBV_ILN_370 | ||
912 | |a GBV_ILN_602 | ||
912 | |a GBV_ILN_2014 | ||
912 | |a GBV_ILN_2086 | ||
912 | |a GBV_ILN_4012 | ||
912 | |a GBV_ILN_4037 | ||
912 | |a GBV_ILN_4112 | ||
912 | |a GBV_ILN_4125 | ||
912 | |a GBV_ILN_4126 | ||
912 | |a GBV_ILN_4249 | ||
912 | |a GBV_ILN_4305 | ||
912 | |a GBV_ILN_4306 | ||
912 | |a GBV_ILN_4307 | ||
912 | |a GBV_ILN_4313 | ||
912 | |a GBV_ILN_4322 | ||
912 | |a GBV_ILN_4323 | ||
912 | |a GBV_ILN_4324 | ||
912 | |a GBV_ILN_4325 | ||
912 | |a GBV_ILN_4326 | ||
912 | |a GBV_ILN_4335 | ||
912 | |a GBV_ILN_4338 | ||
912 | |a GBV_ILN_4367 | ||
912 | |a GBV_ILN_4700 | ||
951 | |a AR | ||
952 | |d 20 |j 2023 |h e01613- |
author_variant |
i k ik g u a gua a s g asg |
---|---|
matchkey_str |
article:24682276:2023----::oaadiacsiltxceasnocscidetyslimjrak |
hierarchy_sort_str |
2023 |
publishDate |
2023 |
allfields |
10.1016/j.sciaf.2023.e01613 doi (DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede DE-627 ger DE-627 rakwb eng Ishmail Kamara verfasserin aut Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q Gilbert Umaye Adie verfasserin aut Abdulmoseen Segun Giwa verfasserin aut In Scientific African Elsevier, 2018 20(2023), Seite e01613- (DE-627)1047200163 24682276 nnns volume:20 year:2023 pages:e01613- https://doi.org/10.1016/j.sciaf.2023.e01613 kostenfrei https://doaj.org/article/61c965628653428a8f50f177a6599ede kostenfrei http://www.sciencedirect.com/science/article/pii/S2468227623000704 kostenfrei https://doaj.org/toc/2468-2276 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 20 2023 e01613- |
spelling |
10.1016/j.sciaf.2023.e01613 doi (DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede DE-627 ger DE-627 rakwb eng Ishmail Kamara verfasserin aut Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q Gilbert Umaye Adie verfasserin aut Abdulmoseen Segun Giwa verfasserin aut In Scientific African Elsevier, 2018 20(2023), Seite e01613- (DE-627)1047200163 24682276 nnns volume:20 year:2023 pages:e01613- https://doi.org/10.1016/j.sciaf.2023.e01613 kostenfrei https://doaj.org/article/61c965628653428a8f50f177a6599ede kostenfrei http://www.sciencedirect.com/science/article/pii/S2468227623000704 kostenfrei https://doaj.org/toc/2468-2276 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 20 2023 e01613- |
allfields_unstemmed |
10.1016/j.sciaf.2023.e01613 doi (DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede DE-627 ger DE-627 rakwb eng Ishmail Kamara verfasserin aut Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q Gilbert Umaye Adie verfasserin aut Abdulmoseen Segun Giwa verfasserin aut In Scientific African Elsevier, 2018 20(2023), Seite e01613- (DE-627)1047200163 24682276 nnns volume:20 year:2023 pages:e01613- https://doi.org/10.1016/j.sciaf.2023.e01613 kostenfrei https://doaj.org/article/61c965628653428a8f50f177a6599ede kostenfrei http://www.sciencedirect.com/science/article/pii/S2468227623000704 kostenfrei https://doaj.org/toc/2468-2276 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 20 2023 e01613- |
allfieldsGer |
10.1016/j.sciaf.2023.e01613 doi (DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede DE-627 ger DE-627 rakwb eng Ishmail Kamara verfasserin aut Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q Gilbert Umaye Adie verfasserin aut Abdulmoseen Segun Giwa verfasserin aut In Scientific African Elsevier, 2018 20(2023), Seite e01613- (DE-627)1047200163 24682276 nnns volume:20 year:2023 pages:e01613- https://doi.org/10.1016/j.sciaf.2023.e01613 kostenfrei https://doaj.org/article/61c965628653428a8f50f177a6599ede kostenfrei http://www.sciencedirect.com/science/article/pii/S2468227623000704 kostenfrei https://doaj.org/toc/2468-2276 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 20 2023 e01613- |
allfieldsSound |
10.1016/j.sciaf.2023.e01613 doi (DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede DE-627 ger DE-627 rakwb eng Ishmail Kamara verfasserin aut Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q Gilbert Umaye Adie verfasserin aut Abdulmoseen Segun Giwa verfasserin aut In Scientific African Elsevier, 2018 20(2023), Seite e01613- (DE-627)1047200163 24682276 nnns volume:20 year:2023 pages:e01613- https://doi.org/10.1016/j.sciaf.2023.e01613 kostenfrei https://doaj.org/article/61c965628653428a8f50f177a6599ede kostenfrei http://www.sciencedirect.com/science/article/pii/S2468227623000704 kostenfrei https://doaj.org/toc/2468-2276 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 20 2023 e01613- |
language |
English |
source |
In Scientific African 20(2023), Seite e01613- volume:20 year:2023 pages:e01613- |
sourceStr |
In Scientific African 20(2023), Seite e01613- volume:20 year:2023 pages:e01613- |
format_phy_str_mv |
Article |
institution |
findex.gbv.de |
topic_facet |
Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index Science Q |
isfreeaccess_bool |
true |
container_title |
Scientific African |
authorswithroles_txt_mv |
Ishmail Kamara @@aut@@ Gilbert Umaye Adie @@aut@@ Abdulmoseen Segun Giwa @@aut@@ |
publishDateDaySort_date |
2023-01-01T00:00:00Z |
hierarchy_top_id |
1047200163 |
id |
DOAJ088549763 |
language_de |
englisch |
fullrecord |
<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000naa a22002652 4500</leader><controlfield tag="001">DOAJ088549763</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230410113629.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230410s2023 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1016/j.sciaf.2023.e01613</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)DOAJ088549763</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-599)DOAJ61c965628653428a8f50f177a6599ede</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="100" ind1="0" ind2=" "><subfield code="a">Ishmail Kamara</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2023</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Toxic metals</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Low-cost toys</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Polyvinyl chloride</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Artificial saliva</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Gastric environment</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Hazard index</subfield></datafield><datafield tag="653" ind1=" " ind2="0"><subfield code="a">Science</subfield></datafield><datafield tag="653" ind1=" " ind2="0"><subfield code="a">Q</subfield></datafield><datafield tag="700" ind1="0" ind2=" "><subfield code="a">Gilbert Umaye Adie</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="0" ind2=" "><subfield code="a">Abdulmoseen Segun Giwa</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">In</subfield><subfield code="t">Scientific African</subfield><subfield code="d">Elsevier, 2018</subfield><subfield code="g">20(2023), Seite e01613-</subfield><subfield code="w">(DE-627)1047200163</subfield><subfield code="x">24682276</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:20</subfield><subfield code="g">year:2023</subfield><subfield code="g">pages:e01613-</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">https://doi.org/10.1016/j.sciaf.2023.e01613</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">https://doaj.org/article/61c965628653428a8f50f177a6599ede</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">http://www.sciencedirect.com/science/article/pii/S2468227623000704</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="2"><subfield code="u">https://doaj.org/toc/2468-2276</subfield><subfield code="y">Journal toc</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_DOAJ</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_11</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_20</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_22</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_23</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_24</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_31</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_39</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_40</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_60</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_62</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_63</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_65</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_69</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_73</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_95</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_105</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_110</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_151</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_161</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_170</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_206</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_213</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_230</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_285</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_293</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_370</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_602</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2014</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2086</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4012</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4037</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4125</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4126</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4249</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4306</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4307</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4322</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4323</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4324</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4325</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4326</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4335</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4338</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4367</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4700</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">20</subfield><subfield code="j">2023</subfield><subfield code="h">e01613-</subfield></datafield></record></collection>
|
author |
Ishmail Kamara |
spellingShingle |
Ishmail Kamara misc Toxic metals misc Low-cost toys misc Polyvinyl chloride misc Artificial saliva misc Gastric environment misc Hazard index misc Science misc Q Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
authorStr |
Ishmail Kamara |
ppnlink_with_tag_str_mv |
@@773@@(DE-627)1047200163 |
format |
electronic Article |
delete_txt_mv |
keep |
author_role |
aut aut aut |
collection |
DOAJ |
remote_str |
true |
illustrated |
Not Illustrated |
issn |
24682276 |
topic_title |
Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria Toxic metals Low-cost toys Polyvinyl chloride Artificial saliva Gastric environment Hazard index |
topic |
misc Toxic metals misc Low-cost toys misc Polyvinyl chloride misc Artificial saliva misc Gastric environment misc Hazard index misc Science misc Q |
topic_unstemmed |
misc Toxic metals misc Low-cost toys misc Polyvinyl chloride misc Artificial saliva misc Gastric environment misc Hazard index misc Science misc Q |
topic_browse |
misc Toxic metals misc Low-cost toys misc Polyvinyl chloride misc Artificial saliva misc Gastric environment misc Hazard index misc Science misc Q |
format_facet |
Elektronische Aufsätze Aufsätze Elektronische Ressource |
format_main_str_mv |
Text Zeitschrift/Artikel |
carriertype_str_mv |
cr |
hierarchy_parent_title |
Scientific African |
hierarchy_parent_id |
1047200163 |
hierarchy_top_title |
Scientific African |
isfreeaccess_txt |
true |
familylinks_str_mv |
(DE-627)1047200163 |
title |
Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
ctrlnum |
(DE-627)DOAJ088549763 (DE-599)DOAJ61c965628653428a8f50f177a6599ede |
title_full |
Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
author_sort |
Ishmail Kamara |
journal |
Scientific African |
journalStr |
Scientific African |
lang_code |
eng |
isOA_bool |
true |
recordtype |
marc |
publishDateSort |
2023 |
contenttype_str_mv |
txt |
author_browse |
Ishmail Kamara Gilbert Umaye Adie Abdulmoseen Segun Giwa |
container_volume |
20 |
format_se |
Elektronische Aufsätze |
author-letter |
Ishmail Kamara |
doi_str_mv |
10.1016/j.sciaf.2023.e01613 |
author2-role |
verfasserin |
title_sort |
total and bio-accessible toxic metals in low-cost children toys sold in major markets in ibadan, south west nigeria |
title_auth |
Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
abstract |
Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. |
abstractGer |
Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. |
abstract_unstemmed |
Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required. |
collection_details |
GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_206 GBV_ILN_213 GBV_ILN_230 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_2014 GBV_ILN_2086 GBV_ILN_4012 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4249 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 |
title_short |
Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria |
url |
https://doi.org/10.1016/j.sciaf.2023.e01613 https://doaj.org/article/61c965628653428a8f50f177a6599ede http://www.sciencedirect.com/science/article/pii/S2468227623000704 https://doaj.org/toc/2468-2276 |
remote_bool |
true |
author2 |
Gilbert Umaye Adie Abdulmoseen Segun Giwa |
author2Str |
Gilbert Umaye Adie Abdulmoseen Segun Giwa |
ppnlink |
1047200163 |
mediatype_str_mv |
c |
isOA_txt |
true |
hochschulschrift_bool |
false |
doi_str |
10.1016/j.sciaf.2023.e01613 |
up_date |
2024-07-03T18:16:16.477Z |
_version_ |
1803582781763092480 |
fullrecord_marcxml |
<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000naa a22002652 4500</leader><controlfield tag="001">DOAJ088549763</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230410113629.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230410s2023 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1016/j.sciaf.2023.e01613</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)DOAJ088549763</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-599)DOAJ61c965628653428a8f50f177a6599ede</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="100" ind1="0" ind2=" "><subfield code="a">Ishmail Kamara</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Total and bio-accessible toxic metals in low-cost children toys sold in major markets in Ibadan, South West Nigeria</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2023</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Toxic metals are usually added to children's toys to improve/impact some intrinsic properties such as colour which attracts children. Some of the toxic metals have life-threatening potentials on children when ingested. There is no specific legislation in Nigeria that monitors and regulates limits of such metals in toys. This study assessed total and bio-accessible concentrations of Pb, Cd, Cr, Ni, and Mn in imported low-cost children's plastic toys sold in popular markets in Ibadan, Nigeria. A total of 22 different toys were purchased and subjected to an indicative test for the presence of polyvinyl chloride (PVC) following the Beilstein method as well as analysing for total recoverable metals and migrated fractions into simulated saliva and gastric environments. Toy samples were crushed, ashed, and dissolved with dilute nitric acid for total recoverable metals while migration studies were carried out using simulated saliva and gastric environments to check bio-accessible fractions that could leach into the human system. Metals in all extracts were determined using flame atomic absorption spectrophotometric technique. The indicative PVC test showed 12 samples positive to PVC and 10 tested negative. Total recoverable metal concentrations (mg/kg) ranged as follows: Pb: Below Detection Limit (BDL) - 4838, Cd: BDL - 44.9, Cr: 0.331–79.8, Ni: 0.273–59.1 and Mn: 0.205–31.0 with Pb and Cr having 18 and 14% of samples higher than EU limits of 90 and 60 mg/kg. Bio-accessible concentrations in artificial saliva were: Pb: BDL - 42.4, Cd: BDL-0.450, Ni: BDL-1.40 and Mn: BDL-0.058 with Pb higher in 70% of samples compared to 2.0 mg/kg migrated EU limit while other metals were within the limits. Furthermore, metal concentrations that migrated to gastric environment were: Pb: 8.24–50.3, Cd: BDL-0.057, Ni: 0.103–1.96 and Mn: BDL-1.37 with Pb in 100% of samples higher than 2.0 mg/kg EU migrated limit. Chromium migration in both environments was BDL. The results of this study suggest that toxic metal contents are present in both PVC and non-PVC made toys, but higher in PVC containing toys. Though the calculated hazard index for health risk assessment of heavy metals was < 1 for all metals, Pb concentration in both total recoverable extract and saliva and gastric environments seem to be problematic and constant monitoring and regulation are required.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Toxic metals</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Low-cost toys</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Polyvinyl chloride</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Artificial saliva</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Gastric environment</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Hazard index</subfield></datafield><datafield tag="653" ind1=" " ind2="0"><subfield code="a">Science</subfield></datafield><datafield tag="653" ind1=" " ind2="0"><subfield code="a">Q</subfield></datafield><datafield tag="700" ind1="0" ind2=" "><subfield code="a">Gilbert Umaye Adie</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="0" ind2=" "><subfield code="a">Abdulmoseen Segun Giwa</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">In</subfield><subfield code="t">Scientific African</subfield><subfield code="d">Elsevier, 2018</subfield><subfield code="g">20(2023), Seite e01613-</subfield><subfield code="w">(DE-627)1047200163</subfield><subfield code="x">24682276</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:20</subfield><subfield code="g">year:2023</subfield><subfield code="g">pages:e01613-</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">https://doi.org/10.1016/j.sciaf.2023.e01613</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">https://doaj.org/article/61c965628653428a8f50f177a6599ede</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="0"><subfield code="u">http://www.sciencedirect.com/science/article/pii/S2468227623000704</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="856" ind1="4" ind2="2"><subfield code="u">https://doaj.org/toc/2468-2276</subfield><subfield code="y">Journal toc</subfield><subfield code="z">kostenfrei</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_DOAJ</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_11</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_20</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_22</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_23</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_24</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_31</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_39</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_40</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_60</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_62</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_63</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_65</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_69</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_73</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_95</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_105</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_110</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_151</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_161</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_170</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_206</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_213</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_230</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_285</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_293</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_370</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_602</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2014</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2086</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4012</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4037</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4125</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4126</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4249</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4306</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4307</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4322</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4323</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4324</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4325</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4326</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4335</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4338</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4367</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4700</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">20</subfield><subfield code="j">2023</subfield><subfield code="h">e01613-</subfield></datafield></record></collection>
|
score |
7.401101 |