Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole
Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tr...
Ausführliche Beschreibung
Autor*in: |
Vetter, W. [verfasserIn] |
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Format: |
E-Artikel |
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Sprache: |
Englisch |
Erschienen: |
2004 |
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Schlagwörter: |
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Anmerkung: |
© Springer Science+Business Media New York 2004 |
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Übergeordnetes Werk: |
Enthalten in: Archives of environmental contamination and toxicology - New York, NY : Springer, 1973, 48(2004), 1 vom: Dez., Seite 1-9 |
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Übergeordnetes Werk: |
volume:48 ; year:2004 ; number:1 ; month:12 ; pages:1-9 |
Links: |
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DOI / URN: |
10.1007/s00244-004-0049-5 |
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Katalog-ID: |
SPR002731681 |
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100 | 1 | |a Vetter, W. |e verfasserin |4 aut | |
245 | 1 | 0 | |a Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
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520 | |a Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. | ||
650 | 4 | |a PCBs |7 (dpeaa)DE-He213 | |
650 | 4 | |a TCDD |7 (dpeaa)DE-He213 | |
650 | 4 | |a Aryl Hydrocarbon Receptor |7 (dpeaa)DE-He213 | |
650 | 4 | |a Aryl Hydrocarbon Receptor Ligand |7 (dpeaa)DE-He213 | |
650 | 4 | |a EROD Induction |7 (dpeaa)DE-He213 | |
700 | 1 | |a Hahn, M. E. |4 aut | |
700 | 1 | |a Tomy, G. |4 aut | |
700 | 1 | |a Ruppe, S. |4 aut | |
700 | 1 | |a Vatter, S. |4 aut | |
700 | 1 | |a Chahbane, N. |4 aut | |
700 | 1 | |a Lenoir, D. |4 aut | |
700 | 1 | |a Schramm, K.-W. |4 aut | |
700 | 1 | |a Scherer, G. |4 aut | |
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10.1007/s00244-004-0049-5 doi (DE-627)SPR002731681 (SPR)s00244-004-0049-5-e DE-627 ger DE-627 rakwb eng Vetter, W. verfasserin aut Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer Science+Business Media New York 2004 Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 Hahn, M. E. aut Tomy, G. aut Ruppe, S. aut Vatter, S. aut Chahbane, N. aut Lenoir, D. aut Schramm, K.-W. aut Scherer, G. aut Enthalten in Archives of environmental contamination and toxicology New York, NY : Springer, 1973 48(2004), 1 vom: Dez., Seite 1-9 (DE-627)253390052 (DE-600)1458449-9 1432-0703 nnns volume:48 year:2004 number:1 month:12 pages:1-9 https://dx.doi.org/10.1007/s00244-004-0049-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 48 2004 1 12 1-9 |
spelling |
10.1007/s00244-004-0049-5 doi (DE-627)SPR002731681 (SPR)s00244-004-0049-5-e DE-627 ger DE-627 rakwb eng Vetter, W. verfasserin aut Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer Science+Business Media New York 2004 Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 Hahn, M. E. aut Tomy, G. aut Ruppe, S. aut Vatter, S. aut Chahbane, N. aut Lenoir, D. aut Schramm, K.-W. aut Scherer, G. aut Enthalten in Archives of environmental contamination and toxicology New York, NY : Springer, 1973 48(2004), 1 vom: Dez., Seite 1-9 (DE-627)253390052 (DE-600)1458449-9 1432-0703 nnns volume:48 year:2004 number:1 month:12 pages:1-9 https://dx.doi.org/10.1007/s00244-004-0049-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 48 2004 1 12 1-9 |
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10.1007/s00244-004-0049-5 doi (DE-627)SPR002731681 (SPR)s00244-004-0049-5-e DE-627 ger DE-627 rakwb eng Vetter, W. verfasserin aut Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer Science+Business Media New York 2004 Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 Hahn, M. E. aut Tomy, G. aut Ruppe, S. aut Vatter, S. aut Chahbane, N. aut Lenoir, D. aut Schramm, K.-W. aut Scherer, G. aut Enthalten in Archives of environmental contamination and toxicology New York, NY : Springer, 1973 48(2004), 1 vom: Dez., Seite 1-9 (DE-627)253390052 (DE-600)1458449-9 1432-0703 nnns volume:48 year:2004 number:1 month:12 pages:1-9 https://dx.doi.org/10.1007/s00244-004-0049-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 48 2004 1 12 1-9 |
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10.1007/s00244-004-0049-5 doi (DE-627)SPR002731681 (SPR)s00244-004-0049-5-e DE-627 ger DE-627 rakwb eng Vetter, W. verfasserin aut Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer Science+Business Media New York 2004 Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 Hahn, M. E. aut Tomy, G. aut Ruppe, S. aut Vatter, S. aut Chahbane, N. aut Lenoir, D. aut Schramm, K.-W. aut Scherer, G. aut Enthalten in Archives of environmental contamination and toxicology New York, NY : Springer, 1973 48(2004), 1 vom: Dez., Seite 1-9 (DE-627)253390052 (DE-600)1458449-9 1432-0703 nnns volume:48 year:2004 number:1 month:12 pages:1-9 https://dx.doi.org/10.1007/s00244-004-0049-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 48 2004 1 12 1-9 |
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10.1007/s00244-004-0049-5 doi (DE-627)SPR002731681 (SPR)s00244-004-0049-5-e DE-627 ger DE-627 rakwb eng Vetter, W. verfasserin aut Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer Science+Business Media New York 2004 Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 Hahn, M. E. aut Tomy, G. aut Ruppe, S. aut Vatter, S. aut Chahbane, N. aut Lenoir, D. aut Schramm, K.-W. aut Scherer, G. aut Enthalten in Archives of environmental contamination and toxicology New York, NY : Springer, 1973 48(2004), 1 vom: Dez., Seite 1-9 (DE-627)253390052 (DE-600)1458449-9 1432-0703 nnns volume:48 year:2004 number:1 month:12 pages:1-9 https://dx.doi.org/10.1007/s00244-004-0049-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 48 2004 1 12 1-9 |
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English |
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Enthalten in Archives of environmental contamination and toxicology 48(2004), 1 vom: Dez., Seite 1-9 volume:48 year:2004 number:1 month:12 pages:1-9 |
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Vetter, W. @@aut@@ Hahn, M. E. @@aut@@ Tomy, G. @@aut@@ Ruppe, S. @@aut@@ Vatter, S. @@aut@@ Chahbane, N. @@aut@@ Lenoir, D. @@aut@@ Schramm, K.-W. @@aut@@ Scherer, G. @@aut@@ |
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Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. 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|
author |
Vetter, W. |
spellingShingle |
Vetter, W. misc PCBs misc TCDD misc Aryl Hydrocarbon Receptor misc Aryl Hydrocarbon Receptor Ligand misc EROD Induction Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
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1432-0703 |
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Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole PCBs (dpeaa)DE-He213 TCDD (dpeaa)DE-He213 Aryl Hydrocarbon Receptor (dpeaa)DE-He213 Aryl Hydrocarbon Receptor Ligand (dpeaa)DE-He213 EROD Induction (dpeaa)DE-He213 |
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misc PCBs misc TCDD misc Aryl Hydrocarbon Receptor misc Aryl Hydrocarbon Receptor Ligand misc EROD Induction |
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misc PCBs misc TCDD misc Aryl Hydrocarbon Receptor misc Aryl Hydrocarbon Receptor Ligand misc EROD Induction |
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misc PCBs misc TCDD misc Aryl Hydrocarbon Receptor misc Aryl Hydrocarbon Receptor Ligand misc EROD Induction |
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Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
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Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
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Vetter, W. |
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Archives of environmental contamination and toxicology |
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Archives of environmental contamination and toxicology |
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2004 |
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Vetter, W. Hahn, M. E. Tomy, G. Ruppe, S. Vatter, S. Chahbane, N. Lenoir, D. Schramm, K.-W. Scherer, G. |
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48 |
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Elektronische Aufsätze |
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Vetter, W. |
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10.1007/s00244-004-0049-5 |
title_sort |
biological activity and physicochemical parameters of marine halogenated natural products 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole and2,4,6-tribromoanisole |
title_auth |
Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
abstract |
Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. © Springer Science+Business Media New York 2004 |
abstractGer |
Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. © Springer Science+Business Media New York 2004 |
abstract_unstemmed |
Abstract Physicochemical parameters (vapor pressure, water solubility, Henry’s law constant) and biological activities of two halogenated natural products frequently detected in marine samples and food were determined. Synthetic 2,3,3′,4,4′,5,5′-heptachloro-1′-methyl-1,2′-bipyrrole (Q1) and 2,4,6-tribromoanisole (TBA) were available in pure form. The physicochemical parameters were in the range of anthropogenic chlorinated compounds of concern. The aqueous solubilities at 25°C ($ S_{w,25} $) of Q1 and TBA were 4.6 μg/L and 12,200 μg/L, respectively, whereas subcooled liquid vapor pressures were 0.00168 Pa (Q1) and 0.06562 Pa (TBA) as measured by the gas chromatographic–retention time technique. Q1 was negative by established test systems for the determination of ethoxyresorufin-O-deethylase (EROD) induction and by sulforhodamine B assay. EROD induction potency was at least $ 10^{−7} $ times lower than that of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). At a relatively high concentration (20 μM), Q1 inhibited specific binding of 2 nM [3H]TCDD to the in vitro-expressed human aryl hydrocarbon receptor (AHR) by 18%; lower concentrations showed no effect. Molecular modeling showed that Q1 is nonplanar, consistent with its relatively modest affinity as an AHR ligand. When tested for cell-growth inhibitory/cytocidal activity in human tumor cells, Q1 was only marginally, if at all, active with an $ IC_{50} $ value >50 μM compared with five to ten times lower $ IC_{50} $ values for potent cytotoxins tested in the test system used. Furthermore, standard pesticide tests on insecticidal, herbicidal, and fungicidal activity did not provide any significant activity at highest concentrations. For TBA, the results in all tests were comparable with Q1. The SRB assay was also applied to the halogenated natural product 4,6-dibromo-2-(2′,4′-dibromo)phenoxyanisole, but no toxic response was found. Although it was apparent that Q1 and TBA had been proven to have relatively low biological activity in all tests performed, further research is necessary to clarify whether metabolites of the compounds eventually may possess a risk to humans or other living organisms. Nevertheless, the role of Q1 in nature remains uncertain. © Springer Science+Business Media New York 2004 |
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title_short |
Biological Activity and Physicochemical Parameters of Marine Halogenated Natural Products 2,3,3′,4,4′,5,5′-Heptachloro-1′-Methyl-1,2′-Bipyrrole and2,4,6-Tribromoanisole |
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https://dx.doi.org/10.1007/s00244-004-0049-5 |
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Hahn, M. E. Tomy, G. Ruppe, S. Vatter, S. Chahbane, N. Lenoir, D. Schramm, K.-W. Scherer, G. |
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Hahn, M. E. Tomy, G. Ruppe, S. Vatter, S. Chahbane, N. Lenoir, D. Schramm, K.-W. Scherer, G. |
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score |
7.4028063 |