Pentachlorophenol dermal absorption and disposition from soil in swine: effects of occlusion and skin microorganism inhibition

Novel Insights into the Dermal Bioaccessibility and Human Exposure to Brominated Flame Retardant Additives in Microplastics

In this study, we optimized and applied an in vitro physiologically based extraction test to investigate the dermal bioaccessibility of polybrominated diphenyl ethers (PBDEs) and hexabromocyclododecane (HBCDD), incorporated as additives in different types of microplastics (MPs), and assess human dermal exposure to these chemicals. The dermal bioaccessibility of PBDEs in polyethylene (PE) MPs was significantly higher (P < 0.05) than in polypropylene (PP) MPs. Both log K_ow and water solubility influenced the dermal bioaccessibility of PBDEs. For HBCDDs in polystyrene MPs, the dermally bioaccessible fractions were 1.8, 2.0, and 1.6% of the applied dose for α-, β-, and γ-HBCDDs, respectively. MP particle size and the presence of cosmetic formulations (antiperspirant, foundation, moisturizer and sunscreen) influenced the bioaccessibility of PBDEs and HBCDDs in MP matrices at varying degrees of significance. Human exposure to ∑PBDEs and ∑HBCDDs via dermal contact with MPs ranged from 0.02 to 22.2 and 0.01 to 231 ng (kg bw)^-1 d^-1 and from 0.02 to 6.27 and 0.2 to 65 ng (kg bw)^-1 d^-1 for adults and toddlers, respectively. Dermal exposure to PBDEs and HBCDDs in MPs is substantial, highlighting for the first time the significance of the dermal pathway as a major route of human exposure to additive chemicals in microplastics.

Dermal bioaccessibility of flame retardants from indoor dust and the influence of topically applied cosmetics

Despite extensive literature on their potential adverse health effects, there is a lack of information on human dermal exposure to organic flame retardant chemicals (FRs). This study applies an in vitro physiologically based extraction test to provide new insights into the dermal bioaccessibility of various FRs from indoor dust to synthetic sweat/sebum mixture (SSSM). The bioaccessible fractions of α-, β- and γ-hexabromocyclododecane (HBCD) and tetrabromobisphenol A (TBBPA) to 1:1 (sweat/sebum) mixture were 41%, 47%, 50% and 40%, respectively. For Tris-2-chloroethyl phosphate (TCEP), tris (1-chloro-2-propyl) phosphate (TCIPP) and tris-1,3-dichloropropyl phosphate (TDCIPP), bioaccessible fractions were 10%, 17% and 19%. Composition of the SSSM and compound-specific physicochemical properties were the major factors influencing the bioaccessibility of target FRs. Except for TBBPA, the presence of cosmetics (moisturising cream, sunscreen lotion, body spray and shower gel) had a significant effect (P<0.05) on the bioaccessibility of the studied FRs. The presence of cosmetics decreased the bioaccessibility of HBCDs from indoor dust, whereas shower gel and sunscreen lotion enhanced the bioaccessibility of target PFRs. Our bioaccessibility data were applied to estimate the internal exposure of UK adults and toddlers to the target FRs via dermal contact with dust. Our worst-case scenario exposure estimates fell far below available health-based limit values for TCEP, TCIPP and TDCIPP. However, future research may erode the margin of safety for these chemicals.

Bioaccessibility of pesticides and polychlorinated biphenyls from house dust: in-vitro methods and human exposure assessment

Semi-volatile chemicals like pesticides and polychlorinated biphenyls (PCB) tend to accumulate in house dust. This may result in residues of some parts per million (p.p.m.), closely associated with health impairments and diseases like cancer. To explain these associations, we must establish whether a relevant absorption from house dust into human organisms occurs, and most crucially the release of chemicals, that is, their bioaccessibility. Digestive as well as dermal bioaccessibilities were examined using in-vitro methods. On average, the digestive bioaccessibility was ~40% for the pesticides and ~60% for the PCB. The dermal penetration availability reached ~60% for the pesticides and ~70% for the PCB (percentages of the concentrations in the dust). Based on the bioaccessibility, an estimate of internal exposure was calculated and expressed as percentages of acceptable or tolerable daily intake (ADI/TDI) values. Exposure via the respiratory tract proved to be very low. Exposure via the digestive tract had maximum values of 4% for pesticides and 12% for PCB. Dermal exposure was much higher. Even for average concentrations in house dust (≈0.5 p.p.m.), children exposed to DDT and PCB showed up to 300% of the ADI/TDI values, and adults about 60%. With high concentrations of contaminants in house dust, the maximum doses absorbed through the skin reached 5000%.

Dermal absorption of environmental contaminants from soil and sediment: a critical review

Risk assessment of hazardous wastes sites may require characterization of the dermal availability of chemical contaminants in soil and/or sediment. Current U.S. Environmental Protection Agency guidance for assessment of dermal exposures to contaminants in water and soil was finalized in 2004 as a supplement (Part E) to the Risk Assessment Guidance for Superfund (RAGS). The soil protocol presented in RAGS Part E is less sophisticated than the water protocol and is supported by less empirical data. Investigations of dermal absorption of soil and sediment-borne contaminants that have been conducted to date include in vitro and in vivo experiments using both human and surrogate skin. A review of that literature was conducted with attention to relevant criteria including consideration of layering effects, degree of chemical saturation of soil, appropriateness of particle size distribution employed, soil-chemical contact time, and continuity of soil-skin contact (in in vivo studies). Most studies published to date are deficient by virtue of execution or reporting on one or more of the selected criteria. In addition the lack of methodological standardization evident in the literature hinders systematic evaluation of results. Since additional experimental work is needed, general agreement on acceptable approaches would be useful. Recommendations for good practice are presented.

An observational study of the potential exposures of preschool children to pentachlorophenol, bisphenol-A, and nonylphenol at home and daycare

The Children's Total Exposure to Persistent Pesticides and Other Persistent Organic Pollutants (CTEPP) study investigated the potential exposures of 257 preschool children, ages 1 1/2-5 yr, and their primary adult caregivers to more than 50 anthropogenic chemicals. Field sampling took place in selected counties in North Carolina (NC) and Ohio (OH) in 2000-2001. Over a 48-h period in each child's daycare center and/or home, food, beverages, indoor air, outdoor air, house dust, soil, participants' hand surfaces and urine were sampled. Additional samples-transferable residues, food preparation surface wipes, and hard floor surface wipes-were collected in the approximately 13% of the homes that had pesticide applications within the 7 days prior to field sampling. Three phenols were among the measured chemicals: pentachlorophenol (PCP), bisphenol-A [2,2-bis(4-hydroxyphenyl)propane], and nonylphenol (4-n-nonylphenol). Nonylphenol (NP) was detected in less than 11% of the samples in any medium. Among samples that were collected at all participants' homes and daycare centers, PCP was detected in >50% of indoor air, outdoor air, house dust, and urine samples; bisphenol-A (BPA) was detected in >50% of indoor air, hand wipe, solid food, and liquid food samples. The concentrations of the phenols in the sampled media were measured, and the children's potential exposures and potential absorbed doses resulting from intake through the inhalation, dietary ingestion, and indirect ingestion routes of exposure were estimated. The children's potential exposures to PCP were predominantly through inhalation: 78% in NC and 90% in OH. In contrast, their potential exposures to BPA were predominantly through dietary ingestion: 99%, for children in both states. The children's estimated exposures to PCP, calculated from the amounts excreted in their urine, exceeded their estimated maximum potential intake, calculated from the multimedia PCP concentrations, by a factor greater than 10. This inconsistency for PCP highlights the need for further research on the environmental pathways and routes of PCP exposure, investigation of possible exposures to other compounds that could be metabolized to PCP, and on the human absorption, metabolism, and excretion of this phenol over time periods longer than 48 h.

Principles for characterizing the potential human health effects from exposure to nanomaterials: elements of a screening strategy

The rapid proliferation of many different engineered nanomaterials (defined as materials designed and produced to have structural features with at least one dimension of 100 nanometers or less) presents a dilemma to regulators regarding hazard identification. The International Life Sciences Institute Research Foundation/Risk Science Institute convened an expert working group to develop a screening strategy for the hazard identification of engineered nanomaterials. The working group report presents the elements of a screening strategy rather than a detailed testing protocol. Based on an evaluation of the limited data currently available, the report presents a broad data gathering strategy applicable to this early stage in the development of a risk assessment process for nanomaterials. Oral, dermal, inhalation, and injection routes of exposure are included recognizing that, depending on use patterns, exposure to nanomaterials may occur by any of these routes. The three key elements of the toxicity screening strategy are: Physicochemical Characteristics, In Vitro Assays (cellular and non-cellular), and In Vivo Assays. There is a strong likelihood that biological activity of nanoparticles will depend on physicochemical parameters not routinely considered in toxicity screening studies. Physicochemical properties that may be important in understanding the toxic effects of test materials include particle size and size distribution, agglomeration state, shape, crystal structure, chemical composition, surface area, surface chemistry, surface charge, and porosity. In vitro techniques allow specific biological and mechanistic pathways to be isolated and tested under controlled conditions, in ways that are not feasible in in vivo tests. Tests are suggested for portal-of-entry toxicity for lungs, skin, and the mucosal membranes, and target organ toxicity for endothelium, blood, spleen, liver, nervous system, heart, and kidney. Non-cellular assessment of nanoparticle durability, protein interactions, complement activation, and pro-oxidant activity is also considered. Tier 1 in vivo assays are proposed for pulmonary, oral, skin and injection exposures, and Tier 2 evaluations for pulmonary exposures are also proposed. Tier 1 evaluations include markers of inflammation, oxidant stress, and cell proliferation in portal-of-entry and selected remote organs and tissues. Tier 2 evaluations for pulmonary exposures could include deposition, translocation, and toxicokinetics and biopersistence studies; effects of multiple exposures; potential effects on the reproductive system, placenta, and fetus; alternative animal models; and mechanistic studies.

Systemic uptake and cutaneous disposition of pentachlorophenol in a sequential exposure scenario: effects of skin preexposure to benzo[a]pyrene

Characterizing interactions caused by sequential skin exposures to various environmental toxicants can be critical for a meaningful risk assessment. To assess sequential chemical exposure effect on chemical cutaneous disposition and systemic uptake of a toxicant, [(14)C]pentachlorophenol (PCP) was topically administered in three porcine skin models (in vivo, ex vivo, and in vitro) at 40 micro g/cm(2) with or without skin preexposure to benzo[a]pyrene (BaP), a known human carcinogen and cutaneous cytochrome P-450 (CYP450) inducer. In the mass balance studies, BaP skin preexposure was found to enhance (14)C absorption in all three models with detectable in vivo effect during the first several days. Total 8-h absorption was tripled by skin preexposure to BaP in the ex vivo (1.1 to 3.2%) and in vitro (0.20 to 0.66%) systems. As seen in the extended in vivo studies, total absorption was 50-57% regardless of exposure conditions, suggesting the prolonged observation period may conceal existing impact of potentially modified disposition processes, such as cutaneous metabolism, on systemic absorption. Skin preexposure to the skin CYP450 inducer BaP largely changed label penetration depth and distribution pattern in cutaneous tissues and decreased (14)C concentration in skin and fat. Additionally, BaP preexposure altered (14)C systemic tissue disposition, suggesting that altered cutaneous PCP disposition may eventually change the toxicity profile (cutaneous vs. systemic risk). The preliminary tissue distribution and systemic absorption data suggested that skin preexposure to BaP may considerably modify cutaneous biotransformation rate and thus deserves further investigation. The dermal model-dependent impacts of expected skin biotransformation manipulation by preexposure to chemicals such as BaP on cutaneous disposition and systemic uptake of environmental toxicants such as PCP need to be considered in risk assessment.

Soils: their implications to human health

This paper reviews how the health of humans is affected by the world's soils, an association that to date has been under appreciated and under reported. Soils significantly influence a variety of functions (e.g. as a plant growth medium; its importance on the cycling of water; as a foundation for buildings) that sustains the human population. Through ingestion (either deliberate or involuntary), inhalation and dermal absorption, the mineral, chemical and biological components of soils can either be directly beneficial or detrimental to human health. Specific examples include: geohelminth infection and the supply of mineral nutrients and potentially harmful elements (PHEs) via soil ingestion; cancers caused by the inhalation of fibrous minerals or Rn gas derived from the radioactive decay of U and Th in soil minerals; and tetanus, hookworm disease and podoconiosis caused by skin contact and dermal absorption of appropriate soil constituents. Human health can also be influenced in more indirect ways as soils interact with the atmosphere, biosphere and hydrosphere. Examples include: the volatilisation of persistent organic pollutants (POPs) from soils and their subsequent global redistribution that has health implications to the Aboriginal people of the Arctic; the frequent detrimental chemical and biological quality of drinking and recreational waters that are influenced by processes of soil erosion, surface runoff, interflow and leaching; and the transfer of mineral nutrients and PHEs from soils into the plants and animals that constitute the human food chain. The scale and magnitude of soil/health interactions are variable, but at times a considerable number of people can be affected as demonstrated by the extent of hookworm infection or the number of people at risk because they live in an I-deficient environment. Nevertheless, it can often be difficult to establish definite links between soils and human health. This, together with the emergence of new risks, knowledge, or discoveries, means that there is considerable scope for research in the future. Such investigations should involve a multidisciplinary approach that both acquires knowledge and ensures its dissemination to people in an understandable way. This requires an infrastructure and finance that governments need to be responsive to.

Enhanced systemic tissue distribution after dermal versus intravenous 3,3',4,4'-tetrachlorobiphenyl exposure: limited utility of radiolabel blood area under the curve and excretion data in dermal absorption calculations and tissue exposure assessment

As a dioxin-like polychlorinated biphenyl (PCB), 3,3',4,4'-tetrachlorobiphenyl (TCB) is receiving increasing research and regulatory interest due to its high toxicity and persistence in the environment. (14)C-TCB was administered at an identical dose of 300 microg via the intravenous (iv) or dermal route to swine to examine the exposure route dependency of the relationship between tissue exposure and blood area under the curve (AUC) and the relationship between dermal absorption and excretion of radiolabel. After iv and dermal exposure, blood, urine, and feces samples were collected during the 11-day in vivo studies. At the end of the experiments, full mass balance studies were conducted to characterize tissue distribution of label. On average, over 70% of the applied dermal and iv doses were recovered. As expected, more than a 10-fold increase in blood AUC (0.49 vs 0.031, h x % dose/ml), plasma AUC (0.40 vs 0.038, h x % dose/ml), urine excretion (29 vs 2.3% of the applied dose), and fecal (30 vs 3.0% of the applied dose) excretion was determined after iv exposure compared to dermal exposure. However, we unexpectedly found that the tissue residue following iv exposure (8.0% of the applied dose) was only half that following dermal exposure (16% of the applied dose). Significantly larger (20- to 30-fold) ratios of blood AUC:tissue residue and excretion:tissue residue were observed after iv exposure compared to dermal exposure. This may indicate a route-related concentration-dependent blood-to-tissue partition process of pooled label, unique skin metabolism, or saturable hepatic metabolism of TCB. Thus, a long-term, low-input exposure pattern similar to this dermal exposure could be more harmful to systemic tissues than a short-term, high-dose exposure similar to this iv exposure. One should be aware that greater absorption, higher blood concentrations, greater blood and plasma AUCs, and greater excretion of label do not necessarily result in a greater overall tissue exposure and that some conventional approaches using label determination in blood and excreta without full mass balance studies may underestimate dermal absorption of chemicals similar to TCB.

Dermal absorption and tissue disposition of 3,3',4, 4'-tetrachlorobiphenyl (TCB) in an ex-vivo pig model: assessing the impact of dermal exposure variables

TCB is one of the dioxin-like polychlorinated biphenyls (PCBs). This research was designed to help assess the risk of occupational and environmental TCB exposure. To evaluate exposure variables' effects on dermal absorption and cutaneous disposition, 14C-TCB (40 microg/cm(2)) in acetone, methylene chloride, a water-acetone mixture, and a soil-based mixture were applied in an ex-vivo pig-skin-flap model (n = 4-5/treatment). Dermal absorption (0.11-0.66%, 8 hr) and penetration (1.14-2.48%) varied according to exposure conditions. Acetone and methylene chloride vehicles differed in absorption profiles and skin penetration patterns but were similar in absorption amounts. Adding water to the acetone did not change absorption but did alter the penetration pattern. The non-occluded soil-based mixture showed more absorption than did the liquid vehicles (p<0.05), but occlusion significantly (p<0.05) decreased that absorption (0.66-->0.29%, 8 hr) and penetration (2.48-->1.11%). In conclusion, dermal absorption data from liquid-organic or aqueousorganic mixtures may underestimate the risk of exposure to TCB-contaminated soil.

Absorption, metabolism, and disposition of [14C]SDZ ENA 713, an acetylcholinesterase inhibitor, in minipigs following oral, intravenous, and dermal administration

PURPOSE

SDZ ENA 713 (rivastigmine) is an acetylcholinesterase inhibitor intended for therapeutic use in Alzheimer's disease. The present study compared the pharmacokinetics of [14C]SDZ ENA 713 after intravenous, oral, and dermal administration to male minipigs, and also examined the effects of dose level and skin abrasion on transdermal absorption.

METHODS

Four groups of 3 minipigs each received a single intravenous (0.1 mg/kg), single oral (1.0 mg/kg), or topical doses of 18 mg or 54 mg of [14C]SDZ ENA 713. Topical doses were administered as dermal patches on two occasions 10 days apart. On Study Day 1, test patches were applied to a virgin skin site. Placebo patches were applied to a separate skin site and were replaced daily during Days 1-10. On Study Day 11, test patches were applied to the site on which the placebo patches had been previously applied. After each dose, serial blood and quantitative urine and feces were collected at designated intervals for 7 days. Concentrations of radioactivity, parent drug, and metabolite ZNS 114-666 were measured in whole blood. Radioactivity was also determined in excreta, skin application sites (at study termination), and on used dermal patches (at 24 hr after application).

RESULTS

Oral doses of [14C]SDZ ENA 713 were rapidly (tmax = 0.83 hr) and efficiently (ca. 93%) absorbed, although the bioavailability of the parent drug was low, ca. 0.5%, apparently due to extensive first-pass metabolism. Radioactivity was excreted mainly in the urine (approximately 90%) with a half-life of 56 hr, slightly longer than that observed after an intravenous dose, 46 hr. After dermal administration of [14C]SDZ ENA 713 to a virgin skin site, absorption was 8% at both dose levels investigated. Following daily application of placebo patches for 10 days, absorption from a [14C]SDZ ENA 713 dermal patch increased by approximately twofold, 17% and 19% of the 18 mg and 54 mg doses, respectively. The increase is possibly due to hydration or abrasion of the skin as a result of repeated application and removal of the adhesive patches. Whereas total absorption from the dermal dose was smaller than that from the oral dose, essentially all of the absorbed drug via the dermal route reached the systemic circulation intact, thus yielding a SDZ ENA 713 bioavailability 20-40 times greater than that of the oral dose. Metabolite ZNS 114-666 was rapidly formed and accounted for <4% of total drug-related material in the systemic circulation.

CONCLUSIONS

Dermal administration in minipigs provided a markedly greater bioavailability of SDZ ENA 713 than the oral route. The extent of absorption was independent of dose within the range tested, and appeared to be enhanced by hydration or abrasion of the skin application site.