Do Carpets Impair Indoor Air Quality and Cause Adverse Health Outcomes: A Review.

Several earlier studies have shown the presence of more dust and allergens in carpets compared with non-carpeted floors. At the same time, adverse effects of carpeted floors on perceived indoor air quality as well as worsening of symptoms in individuals with asthma and allergies were reported. Avoiding extensive carpet use in offices, schools, kindergartens and bedrooms has therefore been recommended by several health authorities. More recently, carpet producers have argued that former assessments were obsolete and that modern rugs are unproblematic, even for those with asthma and allergies. To investigate whether the recommendation to be cautious with the use of carpets is still valid, or whether there are new data supporting that carpet flooring do not present a problem for indoor air quality and health, we have reviewed the literature on this matter. We have not found updated peer reviewed evidence that carpeted floor is unproblematic for the indoor environment. On the contrary, also more recent data support that carpets may act as a repository for pollutants which may become resuspended upon activity in the carpeted area. Also, the use of carpets is still linked to perception of reduced indoor air quality as well as adverse health effects as previously reported. To our knowledge, there are no publications that report on deposition of pollutants and adverse health outcomes associated with modern rugs. However, due to the three-dimensional structure of carpets, any carpet will to some extent act like a sink. Thus, continued caution should still be exercised when considering the use of wall-to-wall carpeted floors in schools, kindergartens and offices, as well as in children's bedrooms unless special needs indicate that carpets are preferable.

DNA damage and DNA damage responses in THP-1 monocytes after exposure to spores of either Stachybotrys chartarum or Aspergillus versicolor or to T-2 toxin.

We have characterized cell death in THP-1 cells after exposure to heat-treated spores from satratoxin G-producing Stachybotrys chartarum isolate IBT 9631, atranone-producing S. chartarum isolate IBT 9634, and sterigmatocystin-producing Aspergillus versicolor isolate IBT 3781, as well as the trichothecenes T-2 and satratoxin G. Spores induced cell death within 3-6 h, with Stachybotrys appearing most potent. IBT 9631 induced both apoptosis and necrosis, while IBT 9634 and IBT 3781 induced mostly necrosis. T-2 toxin and satratoxin G caused mainly apoptosis. Comet assay +/- formamidopyrimidine DNA glycosylase showed that only the spore exposures induced early (3h) oxidative DNA damage. Likewise, only the spores increased the formation of reactive oxygen species (ROS), suggesting that spores as particles may induce ROS formation and oxidative DNA damage. Increased Ataxia Telangiectasia Mutated (ATM) phosphorylation, indicating DNA damage, was observed after all exposures. The DNA damage response induced by IBT 9631 as well as satratoxin G was characterized by rapid (15 min) activation of p38 and H2AX. The p38 inhibitor SB 202190 reduced IBT 9631-induced H2AX activation. Both IBT 9631 and T-2 induced activation of Chk2 and H2AX after 3 h. The ATM inhibitor KU 55933, as well as transfection of cells with ATM siRNA, reduced this activation, suggesting a partial role for ATM as upstream activator for Chk2 and H2AX. In conclusion, activation of Chk2 and H2AX correlated with spore- and toxin-induced apoptosis. For IBT 9631 and satratoxin G, additional factors may be involved in triggering apoptosis, most notably p38 activation.

Involvement of NADPH oxidase and iNOS in rodent pulmonary cytokine responses to urban air and mineral particles.

We have investigated the potential of two complex mineral particles (feldspar and mylonite), quartz (Min-U-Sil), and suspended particulate matter (SRM-1648) (SPM) from urban air to induce inflammatory cytokine responses in primary rat alveolar type 2 cells and alveolar macrophages, and the involvement of cellular formation of free radicals in these responses. All particle types induced an increased release of interleukin (IL)-6 and macrophage inflammatory protein (MIP)-2 from type 2 cells. Diphenyleneiodonium chloride (DPI), a selective inhibitor of NADPH-oxidase, reduced the IL-6 and MIP-2 responses to quartz, SPM and mylonite. N-(3-[Aminomethyl] benzyl) acetamidine (1400W), a selective inhibitor of inducible nitric oxide synthase (iNOS), significantly reduced the Il-6 response to SPM and feldspar in the type 2 cells. The macrophages displayed significantly increased TNF-alpha and MIP-2 release upon exposure to quartz or SPM. Here, DPI significantly reduced the tumor necrosis factor (TNF)-alpha and MIP-2 responses to quartz, and the MIP-2 response to SPM. No significant effect of 1400 W was detected in the alveolar macrophages. The role of particle-induced cellular generation of free radicals in lung cytokine responses was further elucidated in mice that lacked either NADPH-oxidase or iNOS as well as in wild-type (wt) mice. All particles were able to elicit increased cytokine levels in the bronchoalveolar lavage (BAL) fluid of the mice, although the levels depended on particle type. The NADPH-oxidase knockout (KO) mice demonstrated a significantly lower IL-6 and MIP-2 responses to SPM compared to their respective wt mice. The iNOS KO mice displayed significantly reduced IL-6, TNF-alpha, and MIP-2 responses to SPM. The overall results indicate the involvement of cellular free-radical formation in the pulmonary cytokine responses to particles of varying composition.

Estrogenic effects of environmental chemicals: an interspecies comparison.

The development of various in vitro screening methods has led to identification of novel estrogenic chemicals of natural and anthropogenic origin. In this study, the (anti)estrogenic potential of several environmental chemicals were compared in an array of in vitro test systems comprising: (i) competitive binding to estrogen receptors derived from the human breast cancer cell line MCF-7 (hER) and rainbow trout (Oncorhynchus mykiss) (rtER), (ii) a proliferation assay with MCF-7 cells (E-SCREEN), and iii) induction of vitellogenin (rtVtg) in isolated rainbow trout hepatocytes. The results showed substantial differences in assay sensitivity for potent estrogens like 17beta-estradiol, diethylstilbestrol and zearalenone (ranking order of sensitivity: E-SCREEN > hER approximately rtER approximately rtVtg). Chemicals like 4-n-nonylphenol and bisphenol A had higher relative binding affinity to the hER, whereas 4-t-butylphenol and 4-n-butylphenol showed highest affinity to the rtER. Zearalenone and the novel estrogen 4-t-butylhexanol displayed a considerable higher relative potency in the E-SCREEN than the rtVtg assay, whereas alkylphenols and the novel estrogen mimic 4-t-butyl-nitrobenzene were most potent in fish cells. Correlation analysis of data from the test systems suggest that interspecies differences is largely due to inter-assay variation of the ER-dependent cellular responses, whereas binding to the ER are fairly similar in the two species tested.

Effects of the environmental oestrogens bisphenol A, tetrachlorobisphenol A, tetrabromobisphenol A, 4-hydroxybiphenyl and 4,4'-dihydroxybiphenyl on oestrogen receptor binding, cell proliferation and regulation of oestrogen sensitive proteins in the human breast cancer cell line MCF-7.

Bisphenol A is extensively used in the manufacturing of epoxy resins and polycarbonate plastics, whereas several brominated and chlorinated analogues are used as flame retardants and intermediates in the plastic industry. Due to the structural relationship between these chemicals and the high production volumes, we wanted to characterize and compare their potential oestrogen-like potency using several end-points in MCF-7 cells: induction of pS2 protein and progesterone receptor, reduction of oestrogen receptor level, and stimulation of cell growth. Bisphenol A, tetrachloro- and tetrabromo-bisphenol A, 4-hydroxybiphenyl and 4,4'-dihydroxybiphenyl all showed oestrogen-like properties in MCF-7 cells. The chemicals tested had affinity to the oestrogen receptor isolated from MCF-7 cells, although their EC50s were 1,000 to 80,000 times higher than the EC50 of 17beta-oestradiol. Bisphenol A and 4-hydroxybiphenyl induced cell growth in MCF-7 cells, and the highest test concentrations induced responses, apparently exceeding the cell growth induced by 17beta-oestradiol. The other chemicals tested induced less than 50% of the maximum 17beta-oestradiol-stimulated cell growth. Bisphenol A, 4-hydroxybiphenyl, tetrabromobisphenol A and tetrachlorobisphenol A all increased the level of the oestrogen-regulated proteins, progesterone receptor and pS2, whereas 4,4'-dihydroxybiphenyl showed no such effect. Bisphenol A was the only chemical tested that clearly mimicked 17beta-oestradiol in its ability to reduce the level of cytosolic oestrogen receptors in MCF-7 cells. By measuring several oestrogen-dependent endpoints it seems that some xeno-oestrogens cause an imbalanced oestrogen-response. Their ability and potency in mimicking 17beta-oestrogen in one parameter is not necessarily accompanied by a similar effect in another oestrogen-linked parameter.

Brominated phenols: characterization of estrogen-like activity in the human breast cancer cell-line MCF-7.

A large number of halogenated phenols are detected in the blood of humans, fish and wild-animals. We have characterized the estrogen-like activity of phenol, 4-bromophenol (4-BP), 2,4-dibromophenol (2,4-DBP), 2,4,6-tribromophenol (2,4,6-TBP) and 4-tert-butylphenol (tert-BP) using the estrogen-dependent human breast cancer cell line MCF-7. 4-BP, 2,4-DBP and 4-tert-BP all bind to the estrogen receptor (ER) with approximately 10,000-fold less affinity than 17 beta-estradiol (17 beta-E). 2,4,6-TBP was only able to displace 43% of radiolabelled estrogen when tested at concentrations up to 1 microM, whereas phenol had no affinity for the ER. 4-tert-BP stimulated cell growth and induced estrogen-regulated proteins such as the progesterone receptor (PgR) and pS2. The brominated phenols, however, although binding to the ER, did not stimulate cell growth or increase the levels of the PgR or pS2, or reduce the level of 17 beta-E induced pS2. On the contrary, 4-BP, 2,4-DBP and partly 4-tert-BP reduced 17 beta-E-stimulated cell growth apparently by an ER independent mechanism.