Associations between persistent organic pollutants and metabolic syndrome in morbidly obese individuals.

BACKGROUND AND AIMS: Persons with "metabolically healthy" obesity may develop cardiometabolic complications at a lower rate than equally obese persons with evident metabolic syndrome. Even morbidly obese individuals vary in risk profile. Persistent organic pollutants (POPs) are widespread environmental chemicals that impair metabolic homeostasis. We explored whether prevalence of metabolic syndrome in morbidly obese individuals is associated with serum concentrations of POPs. METHODS AND RESULTS: A cross-sectional study among 161 men and 270 women with BMI >35 kg/m2 and comorbidity, or >40 kg/m2. Circulating concentrations of 15 POPs were stratified by number of metabolic syndrome components. In multiple logistic regression analysis odds ratios between top quartile POPs and metabolic risk factors versus POPs below the top quartile were calculated adjusting for age, gender, body mass index, smoking status, alcohol consumption and cholesterol concentrations. Age-adjusted concentrations of trans-nonachlor and dioxin-like and non-dioxin-like polychlorinated biphenyls (PCBs) increased with number of metabolic syndrome components in both genders (p < 0.001), while the organochlorine pesticides HCB, ß-HCH and p,p'DDE increased only in women (p < 0.008). Organochlorine pesticides in the top quartile were associated with metabolic syndrome as were dioxin-like and non-dioxin-like PCBs (OR 2.3 [95% CI 1.3-4.0]; OR 2.5 [95% CI 1.3-4.8] and 2.0 [95% CI 1.1-3.8], respectively). Organochlorine pesticides were associated with HDL cholesterol and glucose (OR = 2.0 [95% CI = 1.1-3.4]; 2.4 [95% CI = 1.4-4.0], respectively). Dioxin-like PCBs were associated with diastolic blood pressure, glucose and homeostatic model assessment-insulin resistance index (OR = 2.0 [95% CI = 1.1-3.6], 2.1 [95% CI = 1.2-3.6] and 2.1 [95% CI = 1.0-4.3], respectively). CONCLUSION: In subjects with morbid obesity, metabolic syndrome was related to circulating levels of organochlorine pesticides and PCBs suggesting that these compounds aggravate clinically relevant complications of obesity.

Time trends and congener profiles of PCDD/Fs, PCBs, and PBDEs in Baltic herring off the coast of Finland during 1978-2009.

In Finland, consumption of Baltic fatty fish may lead to high exposure to persistent organic pollutants (POPs), which might have hazardous health effects. Monitoring of POPs in Baltic fish enables the health authorities to keep dietary advice on fish consumption up to date. In this study, which is a compilation of analytical data from earlier studies, time trends and congener profiles of polychlorinated dioxins and furans (PCDD/Fs) and biphenyls (PCBs), and polybrominated diphenyl ethers (PBDEs) in Baltic herring are reported. Altogether 344 samples of Baltic herring from 1978-2009 were collected across the Finnish coast of the Baltic Sea. The chemical analysis was performed in an accredited testing laboratory with high resolution gas chromatography mass spectrometry. During the 31-year period, PCDD/F and PCB concentrations decreased on approximately 80%, from approximately 20 to 5 pg/g fw, expressed as WHO2005 TEQ. The PBDE concentrations experienced a 4-10 fold increase during late 1980s-early 1990s, and declined to 1978s levels of approximately 2 ng/g fw by 2009. The current concentrations of PCDD/Fs, PCBs and PBDEs in Baltic herring are relatively low, and mostly below EU maximum accepted levels, and are expected to continue decreasing. In the future, it may be possible to re-evaluate the consumption restrictions for this specific Baltic fatty fish.

Occurrence of PCDD/F, PCB, PBDE, PFAS, and organotin compounds in fish meal, fish oil and fish feed.

We analysed polychlorinated dibenzo-p-dioxins and furans (PCDD/F, dioxins), and polychlorinated biphenyls (PCB) in 13 fish meal, five fish oil, and seven fish feed samples. Polybrominated diphenyl ethers (PBDE), organotin compounds (OTC), and perfluoroalkylated substances (PFAS) were analysed in ten fish meal, two fish oil, and two fish feed samples. All measured TEQ concentrations of PCDD/F and PCB were below the maximum levels set by Directive 2002/32/EC. There was no correlation between concentrations of WHOPCDD/F-TEQ and indicator PCB in our samples. The most common congeners among PBDEs were BDE-47 and BDE-100. BDE-209 was present in five fish meals of the ten analysed. Tributyltin (TBT) was the predominant congener in all samples except in three fish meals, where monobutyltin (MBT) was the major congener. Perfluorooctane sulphonate (PFOS) was the predominant congener in six fish meals of the ten analysed. There was large variation in concentrations and congener distributions of the studied compounds between our samples. Our results underline a need to pay special attention to the origin and purity of feed raw material of marine origin.

A novel duplication in the FMR1 gene: implications for molecular analysis in fragile X syndrome and repeat instability.

We have observed a 49 bp tandem duplication adjacent to the triplet repeat of the FMR1 gene and have shown it to occur as a variant in Finland. It affects the primers commonly used in molecular analysis of fragile X syndrome by polymerase chain reaction (PCR) methods. One concern is that females with the full mutation and variant alleles might be missed because of the two PCR products generated by the variant. We suggest that the duplication has arisen by a misalignment of the proximal end of the repeat tract and the non-adjacent GGCGGCGGCGG-sequence located 37 bp upstream and may indicate a mutation hot spot. The discovery of this duplication and the previous observations on deletions associated with full mutations in FMR1 indicate that realignment between the repeat tract and dispersed non-adjacent homologous repetitive sequences may also play a role in repeat instability in fragile X.