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Three plasticizers, namely bis (3,5,5-trimethylhexyl) phosphate (TMHPh), di(propylene glycol) dibenzoate (DiPGDB), and tri-n-butyl trimellitate (TBTM), were recently identified and reported in high concentrations in indoor dust from Belgian homes. In this study, their behavior within the human body was investigated by generating Phase I biotransformation products for the first time. Human liver microsomes (HLMs) were used following an in vitro assay and liquid chromatography time of flight mass spectrometry (LC-QTOF-MS) was employed for the analysis. Biotransformation products were identified for TMHPh as products of hydroxylation reactions that took place in one or two positions in the structure of the substrate. For DiPGDB, biotransformation products were formed after hydrolysis of carboxylic esters and oxidative-O-dealkylation. For TBTM, biotransformation products were formed through hydrolysis of the different carboxylic esters of the molecule, in agreement with studies on structurally similar compounds. The generated results can contribute to biomonitoring studies creating new knowledge on human exposure to emerging compounds and on the metabolism of xenobiotics.

A novel analytical method for the monitoring of four newly identified plasticizers, namely di-propylene glycol dibenzoate (DiPGDB), tri-n-butyl trimellitate (TBTM), isooctyl 2-phenoxyethyl terephthalate (IOPhET) and bis 3,5,5-trimethylhexyl phosphate (TMHPh), in handwipes based on pulverization was developed and in-house validated. In total, 164 handwipe samples (paired with house dust and human urine) were collected during winter (n = 82) and summer (n = 82) 2019 from adults and toddlers living in Flanders, Belgium. Method LOQs ranged from 1 to 200 ng/g. The ranges of Σplasticizers were 70–5400 ng/g for winter and 70–3720 ng/g for summer. The detection frequencies were 39% for DiPGDB, 27% for TBTM and

Plasticizers are a category of chemicals extensively used in consumer products and, consequently, their presence is ubiquitous in the indoor environment. In the present study, an analytical method has been developed for the quantification of plasticizers (7 legacy phthalate esters (LPEs) and 14 alternative plasticizers (APs)) in indoor floor dust based on ultrasonic and vortex extraction, Florisil fractionation and GC-(EI)-MS analysis. Dust samples (n = 54) were collected from homes, offices, and daycare centers from different EU countries (Belgium, the Netherlands, Ireland and Sweden). Method LOQs ranged from 0.2 to 5 mu g/g. Tri-n-hexyl trimellitate (THTM) was not detected in any sample, whereas dimethyl phthalate (DMP), diphenyl phthalate and acetyl triethyl citrate (ATEC) were detected only in 6, 2 and 1 out of 54 samples, respectively. The highest concentrations of plasticizers were measured in Swedish offices, at a mean concentration of total plasticizers of 1800 mu g/g, followed by Swedish daycare centers at 1200 and 670 mu g/g for winter and spring sampling, respectively. Generally, the contribution of APs was slightly higher than for LPEs for all indoor environments (mean contribution 60% and 40%, respectively based on contributions per indoor environment). For the APs, main contributors were DINP in Belgian homes (28%), Swedish offices (60%), Swedish daycare centers (48%), and Dutch offices (31%) and DEHT in Belgian (28%), Irish (40%) and Dutch homes (37%) of total APs. The predominant LPE was bis-2-ethylhexyl-phthalate (DEHP) with a mean contribution varying from 60% to 85% of total LPEs. Human exposure was evaluated for dust ingestion and dermal absorption using hazard quotients (HQs) of plasticizers (ratio between average daily doses and the reference dose). None of the HQs of plasticizers exceeded 1, meaning that the risk for adverse human health effects from these plasticizers via dust ingestion and dermal absorption is unlikely.

In recent years, several changes have been made to the composition of various products which are used indoors. Plenty of new chemical additives have been incorporated to materials to comply with current legislation and safety rules. Consequently, the emission profiles of contaminants detected indoors may change over time, requiring continuous monitoring. In this study, dust samples were collected from 25 homes located in the Flemish region of Belgium during different seasons (winter and summer). Our aim was the development of a suspect screening workflow for the identification of new chemicals which might have been applied to indoor goods, released into the indoor environment, and accumulated in dust. An in-house suspect list was curated including selected groups of compounds, namely “phthalates”, “phosphates”, “terephthalates”, “citrates”, “trimellitates”, (di-, tri-, tetra-) “carboxylic acids”, “adipates”, “azelates”, “sebacates”, (di-)“benzoates”, and “succinates”. 63 chemicals were prioritized based on their level of identification and detection frequency in samples. Seasonal comparison was tested, indicating that higher temperatures of summer might facilitate the release of few chemicals from the products into the indoor environment. Seven chemicals, to the best of our knowledge not previously reported, were selected out of the 63 listed and identified for structure confirmation using high-resolution mass spectrometry. Tributyl trimellitate (TBTM), bis (3,5,5-trimethylhexyl) phosphate (Bis-3,5,5-TMHPh), iso-octyl 2-phenoxy ethyl terephthalate (IOPhET), dimethyl azelate (DMA), dimethyl sebacate (DMS), dipropylene glycol dibenzoate (DiPGDB) and 3,5-di-tert-butyl-4-hydroxybenzaldehyde (BHT-CHO) were detected at frequencies ranging from 8 to 52% in winter and 4–56% in summer dust.

Indoor dust has been extensively used for assessment of indoor contamination, especially for semi-volatile organic compounds (SVOCs). In the present study, the occurrence of four groups of SVOCs, i.e. organophosphorus flame retardants (PFRs), emerging PFRs (ePFRs), legacy phthalates (LPs), and alternative plasticizers (APs), was investigated in the indoor dust and air collected from floors, table surfaces, windows, and air conditioner (A/C) filters in bedrooms and offices in Guangzhou, South China. In bedrooms, A/C filter dust showed the highest median concentrations of PFRs (4670 ng/g) and ePFRs (586 ng/g), whilst the highest median concentrations of LPs and APs were found in floor (240,880 ng/g) and window dust (157,160 ng/g), respectively. In offices, A/C filter dust showed the highest median concentrations for PFRs (6750 ng/g) and APs (504,520 ng/g), while the highest ePFR median level was found in PC table dust (5810 ng/g) and LPs in floor dust (296,270 ng/g). Median air concentrations of PFRs, ePFRs, LPs, and APs were measured at 4.6, 0.12, 399, and 25 ng/m3 in bedrooms, and at 8.0, 0.05, 332, and 43 ng/m3 in offices, respectively. Tris(1-chloro-iso-propyl) phosphate (TCIPP) was the predominant PFRs/ePFRs in both dust and air. Di(2-ethylhexyl) phthalate (DEHP), di-iso-decyl phthalate (DIDP) and di-iso-nonyl phthalate (DINP) were the main LP/AP compounds in dust, whilst di-iso-butyl phthalate (DIBP) and di-n-butyl phthalate (DNBP) were the most abundant LPs/APs in air. A significant correlation (p < 0.05) was found between dust and air levels for chemicals with log Koa < 14, indicating that equilibrium was achieved for these chemicals but not for those with log Koa > 14. Among the investigated human exposure pathways (i.e. dust ingestion, dermal absorption, and air inhalation), dust ingestion was the predominant one for all chemicals. Human exposures of this magnitude to these chemicals through the investigated pathways was unlikely to present a health risk in the present study.

Six newly identified compounds, dimethyl azelate (DMA), dimethyl sebacate (DMS), di-propylene glycol dibenzoate (DiPGDB), tri-n-butyl trimellitate (TBTM), isooctyl 2-phenoxyethyl terephthalate (IOPhET) and bis3,5,5-trimethylhexyl phosphate (TMHPh), were quantified in residential dust using a modified and in-house validated method. The method was based on vortex and ultrasonic extraction, Florisil fractionation and liquid chromatography with tandem mass spectrometry (LC-MS/MS) analysis. Fifty paired dust samples were collected from homes located in the Flemish region of Belgium, during winter (n = 25) and summer (n = 25) of 2019. Method LOQs ranged between 3.8 and 94 ng/g. The ranges of total concentrations of targeted compounds were 0.6-89 mu g/g for winter and 0.8-130 mu g/g for summer samples. DiPGDB was the dominant compound, with 88% and 92% contribution in dust samples per season, followed by TBTM > TMHPh > DMA (less than 10% contribution in both seasons) and DMS, detected only in the summer samples. Human exposure was evaluated for inadvertent dust ingestion using the oral derived no effects level values (DNEL) where available in ECHA, for (I) the hypothesis, where the total concentration of the chemical is considered bio-accessible, (II) the hypothesis where the bio-accessible fraction is defined by the theoretical bio-accessibility, calculated based on logKow values. In both scenarios, DiPGDB, TBTM and TMHPh had the most important contribution to human exposure, with toddlers being more exposed than adults. No risk for adverse human health effects was derived from the comparison with DNELs.

Organophosphorus flame retardants (PFRs) and emerging PFRs (ePFRs) are two groups of compounds used as replacements for brominated flame retardants (BFRs). They have already been detected in indoor dust (mainly in homes and offices). To date, few studies investigated the occurrence of FRs in car dust and the information of possible health risks is still limited. The present study reports on the investigation of the levels and profiles of eight target PFRs: tris(2-ethylhexyl) phosphate (TEHP), tris(2-chloroethyl) phosphate (TCEP), tris(2-butoxyethyl) phosphate (TBEP), triphenyl phosphate (TPHP), 2-ethylhexyl diphenyl phosphate (EHDPHP), tris(1-chloro-2-propyl) phosphate (TCIPP), tri cresyl phosphate (TCP), tris(1,3-dichloro-2-propyl) phosphate (TDCIPP) and four target ePFRs; 2,2-bis(chloromethyl)propane-1,3-diyltetrakis(2-chloroethyl)bisphosphate (V6), isodecyl diphenyl phosphate (iDDPHP), resorcinol bis(diphenylphosphate) (RDP) and bisphenol A-bis(diphenyl phosphate) (BDP) in car dust from Greece. The samples were collected from the interior of 25 private cars in Thessaloniki, Greece, with different years of manufacture (1997–2015) and continents of origin. After ultrasonic extraction and Florisil fractionation, the PFR analysis was carried out by GC-EI/MS, whereas the ePFRs were analyzed by LC-MS/MS. Levels of Σ8PFRs varied from 2000 to 190,000 ng g−1, with mean and median concentrations of 20,000 and 11,500 ng g−1, respectively. The concentrations of Σ4ePFRs ranged from 44 to 8700 ng g−1, with mean and median values at 1100 and 190 ng g−1, respectively. Estimations of human exposure showed that toddlers are more exposed than adults to both PFRs and ePFRs. Yet, the intake via dust ingestion and dermal absorption was several orders of magnitude lower than the corresponding reference doses.

Brominated flame retardants (BFRs) are organobromine compounds with an inhibitory effect on combustion chemistry tending to reduce the flammability of products. Concerns about health effects and environmental threats have led to phase-out or restrictions in the use of Penta-, Octa- and Deca-BDE technical formulations, increasing the demand for Novel BFRs (NBFRs) as replacements for the banned formulations. This study examined the occurrence of legacy and NBFRs in the dust from the interior of private cars in Thessaloniki, Greece, aged from 1 to 19 years with variable origin and characteristics. The determinants included 20 Polybrominated Diphenyl Ethers (PBDEs) (Di-to Deca-BDEs), four NBFRs such as Decabromodiphenylethane (DBDPE), 1,2-bis(2,4,6-tribromophenoxy)ethane (BTBPE), 2-ethylhexyl2,3,4,5-tetrabromobenzoate (TBB), and bis(2-ethylhexyl)-3,4,5,6-tetrabromophthalate (TBPH), three isomers of hexabromocyclododecane (HBCD), and tetrabromobisphenol A (TBBPA). The concentrations of Sigma(20)1313DE ranged from 132 to 54,666 ng g(-1) being dominated by BDE-209. The concentrations of Sigma(4)NBFRs ranged from 48 to 7626 ng g(-1) and were dominated by DBDPE, the major substitute of BDE-209. HBCDs ranged between

To assess the impacts of e-waste regulations on environmental pollution, the levels, compositions, and human exposure assessment of organophosphorus flame retardants (PFRs), emerging PFRs (ePFRs), phthalate esters (PAEs), and alternative plasticizers (APs) were investigated in indoor dust samples collected from homes in a former e-waste dismantling area in 2013 and in 2017, 4 years after the implementation of legislation and regulations governing e-waste dismantling activities in this area. The median concentrations of sigma PFRs, sigma ePFRs, sigma PAEs, and sigma APs in dust decreased from 5680, 1650, 167,200, and 140,600 ng/g in 2013 to 1210, 476, 95,000, and 45,300 ng/g in 2017, respectively, suggesting that the national and local regulations prohibiting primitive e-waste dismantling activities is effective in mitigating the pollution status for these chemicals. In the analyzed dust samples, tris(1-chloro-2-propyl) phosphate (TCIPP), triphenyl phosphate (TPHP), resorcinol bis(diphenylphosphate) (RDP), and bisphenol A-bis(diphenyl phosphate) (BDP) were the major PFRs/ePFRs, contributing to 77% and 76% of the total PFRs/ePFRs in 2013 and 2017, respectively. Di(2-ethylhexyl) phthalate (DEHP), di-iso-nonyl phthalate (DINP), di-iso-decyl phthalate (DIDP), and di-n-butyl phthalate (DNBP) were the major PAEs/APs, with contributions of 89% and 95% for the total PAEs/APs in 2013 and 2017, respectively. The results of the human exposure assessment demonstrated that exposure to these levels of the target chemicals via dust ingestion and dermal contact was unlikely to cause health concerns for local residents.