Tap water as the source of a Legionnaires' disease outbreak spread to several residential buildings and one hospital, Finland, 2020 to 2021.

In Finland, all microbiology laboratories notify findings and physicians notify Legionnaires' disease (LD) cases to the National Infectious Disease Register. All cases are interviewed, and water samples obtained from potential places of exposure. isolates from humans and water are compared by whole genome sequencing (WGS).

Public health impacts of city policies to reduce climate change: findings from the URGENCHE EU-China project.

Background: Climate change is a global threat to health and wellbeing. Here we provide findings of an international research project investigating the health and wellbeing impacts of policies to reduce greenhouse gas emissions in urban environments.

Methods: Five European and two Chinese city authorities and partner academic organisations formed the project consortium.

Building-related health impacts in European and Chinese cities: a scalable assessment method.

Background: Public health is often affected by societal decisions that are not primarily about health. Climate change mitigation requires intensive actions to minimise greenhouse gas emissions in the future. Many of these actions take place in cities due to their traffic, buildings, and energy consumption.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) increases bilirubin formation but hampers quantitative hepatic conversion of biliverdin to bilirubin in rats with wild-type AH receptor.

In haem degradation, haem oxygenase-1 (HO-1) first cleaves haem to biliverdin, which is reduced to bilirubin by biliverdin IXα reductase (BVR-A). The environmental pollutant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes hepatic accumulation of biliverdin in moderately TCDD-resistant line B (Kuopio) rats. Using line B and two TCDD-sensitive rat strains, the present study set out to probe the dose-response and biochemical mechanisms of this accumulation.

Immediate and highly sensitive aversion response to a novel food item linked to AH receptor stimulation.

Aversion to novel food items was studied in male rats and mice after 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure using chocolate consumption as an indicator. The correlation of this phenomenon with susceptibility to acute toxicity and CYP1A1 induction was examined by determining the dose-response of chocolate aversion in differently dioxin-sensitive rat lines after TCDD (0.01-10 μg/kg).

Hepatic effects of a highly purified 2,2',3,4,4',5,5'-heptachlorbiphenyl (PCB 180) in male and female rats.

PCB 180 (2,2',3,4,4',5,5'-heptachlorobiphenyl) is a persistent and accumulating polychlorinated biphenyl abundantly present in food and the environment. In this study, we used highly purified PCB 180 (dioxinlike impurities: 2.7 ng TEQ(WHO)/g PCB 180) in a 28-day toxicity study in young adult Sprague-Dawley rats.

Effect of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on heme oxygenase-1, biliverdin IXalpha reductase and delta-aminolevulinic acid synthetase 1 in rats with wild-type or variant AH receptor.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) causes hepatic accumulation of biliverdin and its monoglucuronide in moderately TCDD-resistant line B rats, but not in highly TCDD-resistant line A rats. In the mammalian heme degradation process, heme is cleaved to biliverdin by the rate-limiting enzyme heme oxygenase-1 (HO-1). Subsequently, biliverdin IXalpha reductase (BVRA) catalyzes the reduction of biliverdin to bilirubin.

Differences in acute toxicity syndromes of 2,3,7,8-tetrachlorodibenzo-p-dioxin and 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin in rats.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is the most potent congener of polychlorinated dibenzo-p-dioxins. The potency of 1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (HxCDD) is only 10% of that of TCDD for typical aryl hydrocarbon receptor (AHR)-mediated effects. Acute lethality, macroscopic effects, and liver toxicity of TCDD and HxCDD were compared in male rats of the strain Han/Wistar (Kuopio; H/W), and of the lines A and B.

Evaluation of various housekeeping genes for their applicability for normalization of mRNA expression in dioxin-treated rats.

Quantitative reverse transcription-polymerase chain reaction (qRT-PCR) is an extremely sensitive, convenient and rapid method to measure mRNA levels in cells and tissues, and is gaining popularity in toxicology. To correct for sample-to-sample variation, normalization of the expression data is required. The conventional way to perform normalization is to select a reference gene whose expression is believed to remain stable across all experimental conditions, then relate the concentrations of gene(s) of interest to those of this housekeeping gene.

TGF-beta induces the expression of SAP30L, a novel nuclear protein.

Background: We have previously set up an in vitro mesenchymal-epithelial cell co-culture model which mimics the intestinal crypt villus axis biology in terms of epithelial cell differentiation. In this model the fibroblast-induced epithelial cell differentiation from secretory crypt cells to absorptive enterocytes is mediated via transforming growth factor-beta (TGF-beta), the major inhibitory regulator of epithelial cell proliferation known to induce differentiation in intestinal epithelial cells. The aim of this study was to identify novel genes whose products would play a role in this TGF-beta-induced differentiation.

2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced accumulation of biliverdin and hepatic peliosis in rats.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a widespread, persistent, and highly toxic environmental pollutant. The most TCDD-sensitive and the most TCDD-resistant rat strains (Long-Evans [Turku/AB] and Han/Wistar [Kuopio], respectively) were crossbred to separate the alleles of two genes (Ahrand an unidentified gene "B") mediating resistance against TCDD toxicity. During crossbreeding, a new type of toxicity in livers of both sexes was detected, characterized macroscopically by intense dark green to black color and swelling that appeared most frequently after a large dose (300 micro g/kg or more as a single intragastric dose) and a follow-up period of more than three weeks.