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3M Co pfoa
Distributions of plasma <t>PFOA</t> and <t>PFOS</t> levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.
Pfoa, supplied by 3M Co, used in various techniques. Bioz Stars score: 91/100, based on 12 PubMed citations. ZERO BIAS - scores, article reviews, protocol conditions and more
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Average 91 stars, based on 12 article reviews
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pfoa - by Bioz Stars, 2020-09
91/100 stars

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1) Product Images from "Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population"

Article Title: Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population

Journal: PLoS ONE

doi: 10.1371/journal.pone.0056969

Distributions of plasma PFOA and PFOS levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.
Figure Legend Snippet: Distributions of plasma PFOA and PFOS levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.

Techniques Used:

Associations between plasma PFOA and PFOS levels and total cholesterol. The Figure illustrates differences in total cholesterol levels according to eight exposure groups of (A) PFOA and (B) PFOS. The lowest exposure groups are used as reference (open dots). The dots are placed at the median of the eight exposure categories. Models are adjusted (sex, age, years of school attendance, body mass index, smoking status, alcohol intake, egg intake, animal fat intake and physical activity).
Figure Legend Snippet: Associations between plasma PFOA and PFOS levels and total cholesterol. The Figure illustrates differences in total cholesterol levels according to eight exposure groups of (A) PFOA and (B) PFOS. The lowest exposure groups are used as reference (open dots). The dots are placed at the median of the eight exposure categories. Models are adjusted (sex, age, years of school attendance, body mass index, smoking status, alcohol intake, egg intake, animal fat intake and physical activity).

Techniques Used: Activity Assay

2) Product Images from "Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort"

Article Title: Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort

Journal: International Journal of Environmental Research and Public Health

doi: 10.3390/ijerph15091832

Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.
Figure Legend Snippet: Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

Techniques Used:

3) Product Images from "Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort"

Article Title: Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort

Journal: Environmental Health Perspectives

doi: 10.1289/ehp.10506

Birth weight and plasma PFOS ( A ) and PFOA ( B ) concentrations in the first maternal blood samples.
Figure Legend Snippet: Birth weight and plasma PFOS ( A ) and PFOA ( B ) concentrations in the first maternal blood samples.

Techniques Used:

Plasma PFOS ( A ) and PFOA ( B ) concentrations between the first and second maternal blood samples.
Figure Legend Snippet: Plasma PFOS ( A ) and PFOA ( B ) concentrations between the first and second maternal blood samples.

Techniques Used:

4) Product Images from "Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort"

Article Title: Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort

Journal: International Journal of Environmental Research and Public Health

doi: 10.3390/ijerph15091832

Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.
Figure Legend Snippet: Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

Techniques Used:

5) Product Images from "Half-Life of Serum Elimination of Perfluorooctanesulfonate,Perfluorohexanesulfonate, and Perfluorooctanoate in Retired Fluorochemical Production Workers"

Article Title: Half-Life of Serum Elimination of Perfluorooctanesulfonate,Perfluorohexanesulfonate, and Perfluorooctanoate in Retired Fluorochemical Production Workers

Journal: Environmental Health Perspectives

doi: 10.1289/ehp.10009

Semi-log plots of PFOS, PFHS, and PFOA concentrations by time (days) for subjects 1–26. Data points indicate observed values and the line shows predicted value.
Figure Legend Snippet: Semi-log plots of PFOS, PFHS, and PFOA concentrations by time (days) for subjects 1–26. Data points indicate observed values and the line shows predicted value.

Techniques Used:

Half-life (years) of serum elimination for PFOS, PFHS, and PFOA (in ascending order for PFOS) for 26 retired fluorochemical production workers by subject number.
Figure Legend Snippet: Half-life (years) of serum elimination for PFOS, PFHS, and PFOA (in ascending order for PFOS) for 26 retired fluorochemical production workers by subject number.

Techniques Used:

6) Product Images from "The Role of Hepatocyte Nuclear Factor 4-Alpha in Perfluorooctanoic Acid- and Perfluorooctanesulfonic Acid-Induced Hepatocellular Dysfunction"

Article Title: The Role of Hepatocyte Nuclear Factor 4-Alpha in Perfluorooctanoic Acid- and Perfluorooctanesulfonic Acid-Induced Hepatocellular Dysfunction

Journal: Toxicology and applied pharmacology

doi: 10.1016/j.taap.2016.05.001

Predicted activation of upstream regulators in response to PFOA or PFOS
Figure Legend Snippet: Predicted activation of upstream regulators in response to PFOA or PFOS

Techniques Used: Activation Assay

In silico docking studies of PFOA and PFOS to HNF4α
Figure Legend Snippet: In silico docking studies of PFOA and PFOS to HNF4α

Techniques Used: In Silico

Genes upregulated by PFOA or PFOS and NANOG expression
Figure Legend Snippet: Genes upregulated by PFOA or PFOS and NANOG expression

Techniques Used: Expressing

HNF4α regulated genes altered in response to PFOA and PFOS
Figure Legend Snippet: HNF4α regulated genes altered in response to PFOA and PFOS

Techniques Used:

PFOA- and PFOS-induced cytotoxicity
Figure Legend Snippet: PFOA- and PFOS-induced cytotoxicity

Techniques Used:

Human serum concentrations of PFOA and PFOS within different subpopulations of exposure in the United States
Figure Legend Snippet: Human serum concentrations of PFOA and PFOS within different subpopulations of exposure in the United States

Techniques Used:

Genes downregulated by PFOA or PFOS
Figure Legend Snippet: Genes downregulated by PFOA or PFOS

Techniques Used:

PFOA and PFOS ligands docked to HNF4α
Figure Legend Snippet: PFOA and PFOS ligands docked to HNF4α

Techniques Used:

Concentration-response of HNF4α protein expression in hepatocytes exposed to PFOA or PFOS
Figure Legend Snippet: Concentration-response of HNF4α protein expression in hepatocytes exposed to PFOA or PFOS

Techniques Used: Concentration Assay, Expressing

Related Articles

other:

Article Title: Polyfluoroalkyl Compounds in Texas Children from Birth through 12 Years of Age
Article Snippet: In 2002, for example, 3M, a major North American PFC producer, ended production of PFOS-related compounds, the ammonium salt of PFOA, and other perfluorooctanesulfonyl fluoride–based products (3M Company 2000; ).

Article Title: Potential health effects of emerging environmental contaminants perfluoroalkyl compounds
Article Snippet: The global concern over the potential environmental and health impact of long-chain PFCs has led to the phase-out of production of PFOA and PFOS by their major manufacturer (the 3M Company) in 2000, and has facilitated regulatory initiatives to reduce the environmental release of these PFCs in many countries.

Article Title: The Role of Hepatocyte Nuclear Factor 4-Alpha in Perfluorooctanoic Acid- and Perfluorooctanesulfonic Acid-Induced Hepatocellular Dysfunction
Article Snippet: As expected, residents of the areas surrounding cities including Decatur, Alabama and Cottage Grove, Minnesota, where the 3M company manufactured PFOA and PFOS, had higher concentrations in their blood, as a consequence of watershed contamination.

Chromatography:

Article Title: Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population
Article Snippet: .. Concentrations of PFOA and PFOS in plasma were determined using high performance liquid chromatography/tandem mass spectrometry at the 3M Toxicology Laboratory, using the methods described by Ehresman et al. . ..

Article Title: Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort
Article Snippet: .. Exposure assessment We measured plasma concentrations of PFOS and PFOA using high performance liquid chromatography–tandem mass spectrometry in the 3M Toxicology Laboratory ( ). ..

Mass Spectrometry:

Article Title: Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population
Article Snippet: .. Concentrations of PFOA and PFOS in plasma were determined using high performance liquid chromatography/tandem mass spectrometry at the 3M Toxicology Laboratory, using the methods described by Ehresman et al. . ..

Article Title: Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort
Article Snippet: .. Exposure assessment We measured plasma concentrations of PFOS and PFOA using high performance liquid chromatography–tandem mass spectrometry in the 3M Toxicology Laboratory ( ). ..

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    3M Co pfoa
    Distributions of plasma <t>PFOA</t> and <t>PFOS</t> levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.
    Pfoa, supplied by 3M Co, used in various techniques. Bioz Stars score: 91/100, based on 12 PubMed citations. ZERO BIAS - scores, article reviews, protocol conditions and more
    https://www.bioz.com/result/pfoa/product/3M Co
    Average 91 stars, based on 12 article reviews
    Price from $9.99 to $1999.99
    pfoa - by Bioz Stars, 2020-09
    91/100 stars
      Buy from Supplier

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    Distributions of plasma PFOA and PFOS levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.

    Journal: PLoS ONE

    Article Title: Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population

    doi: 10.1371/journal.pone.0056969

    Figure Lengend Snippet: Distributions of plasma PFOA and PFOS levels. (A) Distribution of plasma PFOA levels (ng/mL) of the study population. (B) Distribution of plasma PFOS levels (ng/mL) of the study population.

    Article Snippet: Concentrations of PFOA and PFOS in plasma were determined using high performance liquid chromatography/tandem mass spectrometry at the 3M Toxicology Laboratory, using the methods described by Ehresman et al. .

    Techniques:

    Associations between plasma PFOA and PFOS levels and total cholesterol. The Figure illustrates differences in total cholesterol levels according to eight exposure groups of (A) PFOA and (B) PFOS. The lowest exposure groups are used as reference (open dots). The dots are placed at the median of the eight exposure categories. Models are adjusted (sex, age, years of school attendance, body mass index, smoking status, alcohol intake, egg intake, animal fat intake and physical activity).

    Journal: PLoS ONE

    Article Title: Association between Plasma PFOA and PFOS Levels and Total Cholesterol in a Middle-Aged Danish Population

    doi: 10.1371/journal.pone.0056969

    Figure Lengend Snippet: Associations between plasma PFOA and PFOS levels and total cholesterol. The Figure illustrates differences in total cholesterol levels according to eight exposure groups of (A) PFOA and (B) PFOS. The lowest exposure groups are used as reference (open dots). The dots are placed at the median of the eight exposure categories. Models are adjusted (sex, age, years of school attendance, body mass index, smoking status, alcohol intake, egg intake, animal fat intake and physical activity).

    Article Snippet: Concentrations of PFOA and PFOS in plasma were determined using high performance liquid chromatography/tandem mass spectrometry at the 3M Toxicology Laboratory, using the methods described by Ehresman et al. .

    Techniques: Activity Assay

    Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

    Journal: International Journal of Environmental Research and Public Health

    Article Title: Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort

    doi: 10.3390/ijerph15091832

    Figure Lengend Snippet: Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

    Article Snippet: For study sample 1, plasma concentrations of PFOS and PFOA were measured in the 3M Toxicology Laboratory [ ], and samples in the study sample 2 and 3 were analyzed at the Department of Environmental Science at Aarhus University [ ].

    Techniques:

    Birth weight and plasma PFOS ( A ) and PFOA ( B ) concentrations in the first maternal blood samples.

    Journal: Environmental Health Perspectives

    Article Title: Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort

    doi: 10.1289/ehp.10506

    Figure Lengend Snippet: Birth weight and plasma PFOS ( A ) and PFOA ( B ) concentrations in the first maternal blood samples.

    Article Snippet: Exposure assessment We measured plasma concentrations of PFOS and PFOA using high performance liquid chromatography–tandem mass spectrometry in the 3M Toxicology Laboratory ( ).

    Techniques:

    Plasma PFOS ( A ) and PFOA ( B ) concentrations between the first and second maternal blood samples.

    Journal: Environmental Health Perspectives

    Article Title: Perfluorinated Chemicals and Fetal Growth: A Study within the Danish National Birth Cohort

    doi: 10.1289/ehp.10506

    Figure Lengend Snippet: Plasma PFOS ( A ) and PFOA ( B ) concentrations between the first and second maternal blood samples.

    Article Snippet: Exposure assessment We measured plasma concentrations of PFOS and PFOA using high performance liquid chromatography–tandem mass spectrometry in the 3M Toxicology Laboratory ( ).

    Techniques:

    Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

    Journal: International Journal of Environmental Research and Public Health

    Article Title: Prenatal Exposure to Perfluoroalkyl Substances and Birth Outcomes; An Updated Analysis from the Danish National Birth Cohort

    doi: 10.3390/ijerph15091832

    Figure Lengend Snippet: Odds ratio for low birth weight ( a ) and preterm birth ( b ) according to continuous PFASs values using a restricted cubic spline regression model with three knots at the 10th, 50th and 90th percentiles. The dashed lines represent 95% confidence intervals for the spline model (reference is the 10th percentile of each PFASs level). Model adjusted for a study sample indicator, infant sex, infant birth year, gestational week of blood draw, maternal age, parity, socio-occupational status, pre-pregnancy body mass index (BMI), smoking and alcohol intake during pregnancy. In graph ( a ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and low birth weight were 0.52, 0.43, 0.55, 0.88, 0.35, and 0.05, respectively. In graph ( b ), the p -values for non-linearity for PFOS, PFOA, PFHxS, PFNA, PFHpS and PFDA and preterm birth were 0.10, 0.01, 0.01, 0.05, 0.69, and 0.01, respectively.

    Article Snippet: For study sample 1, plasma concentrations of PFOS and PFOA were measured in the 3M Toxicology Laboratory [ ], and samples in the study sample 2 and 3 were analyzed at the Department of Environmental Science at Aarhus University [ ].

    Techniques: