Adverse health impacts of cooking with kerosene: A multi-country analysis within the Prospective Urban and Rural Epidemiology Study.

BACKGROUND: Kerosene, which was until recently considered a relatively clean household fuel, is still widely used in low- and middle-income countries for cooking and lighting. However, there is little data on its health effects. We examined cardiorespiratory effects and mortality in households using kerosene as their primary cooking fuel within the Prospective Urban Rural Epidemiology (PURE) study. METHODS: We analyzed baseline and follow-up data on 31,490 individuals from 154 communities in China, India, South Africa, and Tanzania where there was at least 10% kerosene use for cooking at baseline. Baseline comorbidities and health outcomes during follow-up (median 9.4 years) were compared between households with kerosene versus clean (gas or electricity) or solid fuel (biomass and coal) use for cooking. Multi-level marginal regression models adjusted for individual, household, and community level covariates. RESULTS: Higher rates of prevalent respiratory symptoms (e.g. 34% [95% CI:15-57%] more dyspnea with usual activity, 44% [95% CI: 21-72%] more chronic cough or sputum) and lower lung function (differences in FEV1: -46.3 ml (95% CI: -80.5; -12.1) and FVC: -54.7 ml (95% CI: -93.6; -15.8)) were observed at baseline for kerosene compared to clean fuel users. The odds of hypertension was slightly elevated but no associations were observed for blood pressure. Prospectively, kerosene was associated with elevated risks of all-cause (HR: 1.32 (95% CI: 1.14-1.53)) and cardiovascular (HR: 1.34 (95% CI: 1.00-1.80)) mortality, as well as major fatal and incident non-fatal cardiovascular (HR: 1.34 (95% CI: 1.08-1.66)) and respiratory (HR: 1.55 (95% CI: 0.98-2.43)) diseases, compared to clean fuel use. Further, compared to solid fuel users, those using kerosene had 20-47% higher risks for the above outcomes. CONCLUSIONS: Kerosene use for cooking was associated with higher rates of baseline respiratory morbidity and increased risk of mortality and cardiorespiratory outcomes during follow-up when compared to either clean or solid fuels. Replacing kerosene with cleaner-burning fuels for cooking is recommended.

Occupational exposure to petroleum-based and oxygenated solvents and oral and oropharyngeal cancer risk in men: A population-based case-control study in France.

OBJECTIVE: To examine the association between occupational exposure to petroleum-based and oxygenated solvents and the risk of oral and oropharyngeal cancer. METHODS: The ICARE study is a large population-based case-control study conducted in France between 2001 and 2007. This present analysis was restricted to men and included 350 and 543 cases of squamous cell-carcinoma of the oral cavity and oropharynx, respectively, and 2780 controls. Lifetime tobacco, alcohol consumption and complete occupational history were assessed through detailed questionnaires. Job-exposure matrices allowed us to assess occupational exposure to five petroleum-based solvents (white spirits; diesel/fuel oils/kerosene; gasoline; benzene; special petroleum products) and five oxygenated solvents (diethyl ether; tetrahydrofuran; ketones and esters; alcohols; ethylene glycol). Odds-ratios (ORs), adjusted for age, smoking, alcohol consumption and socioeconomic status, and 95% confidence intervals (CI) were estimated using unconditional logistic models. RESULTS: Associations between oral cancer risk and exposure to white spirits and diesel/fuel oils/kerosene were suggested, but there was no exposure-response trend. Concerning exposure to oxygenated solvents, participants with the highest levels of cumulative exposure to diethyl ether had a significant excess risk of oropharyngeal cancer (OR = 7.78, 95%CI 1.42 to 42.59; p for trend = 0.04). Ever exposure to tetrahydrofuran was associated with a borderline significant increased risk of oral cancer (OR = 1.87, 95%CI 0.97 to 3.61), but no exposure-response trend was observed. Additional adjustments for exposure to other solvents did not substantially change the results. CONCLUSION: Our results do not provide evidence for a major role of petroleum-based and oxygenated solvents in the occurrence of oral and oropharyngeal cancers in men.

Executive summary workshop: toward the elimination of the use of solid fuels and kerosene in urban homes in the americas

Household air pollution is one of the principal causes of disease and premature death in low and middle-income countries (LMIC) and is an avoidable health risk. In the Americas, the World Health Organization (WHO) estimated that approximately 82,000 deaths in these countries were attributale to cooking, heating, and lighting with polluting fuels and technologies in 2016. Accelerating the transition to clean energy for all is an urgent and necessary public health intervention in the region of the Americas, to reduce the health risks that primarily affect socially and economically vulnerable populations, to achieve a continent healthier, more equitable and with sustainable development, contributing to the worldwide efforts to achieve the Sustainable Development Goals (SDGs) by 2030. To achieve this result, the health sector should be involved in the design of policy interventions to reduce exposure to indoor air pollution and its effects on health, as well associal inequities. In line with the WHO Indoor Air Quality Guidelines launched in November 2014, the PAHO Strategic Plan 2014-2019 has set itself the objective of helping Member States to reduce the percentage of population by 5% that depends on solid fuels for cooking in countries with a percentage of users equal to or greater than 10% of the population (priority countries). To measure progress, one indicator is the number of countries that are implementing large-scale programs to reduce solid fuel use (SFU) in the home, and a outcome indicator measures progress in the use of energy and clean technology for cooking at home. Evaluating the progress of the countries in the indicator of the Strategic Plan, some of its member states have successfully reduced solid fuel use (SFU) in the households by 5% and have implemented large-scale programs to transition to clean fuels. Nevertheless, in other countries in the region, progress has been almost non-existent. Following the first workshop carried out in Tegucigalpa (Honduras) in 2015, where new indoor air pollution guidelines were launched by the WHO, the workshop "Toward the elimination of solid fuels and kerosene in urban homes in the Americas" was organized and carried out in Mexico City (Mexico) from September 11 to 13, 2018.

Toxicity and occupational exposure assessment for Fischer-Tropsch synthetic paraffinic kerosene.

Fischer-Tropsch (FT) Synthetic Paraffinic Kerosene (SPK) jet fuel is a synthetic organic mixture intended to augment petroleum-derived JP-8 jet fuel use by the U.S. armed forces. The FT SPK testing program goal was to develop a comparative toxicity database with petroleum-derived jet fuels that may be used to calculate an occupational exposure limit (OEL). Toxicity investigations included the dermal irritation test (FT vs. JP-8 vs. 50:50 blend), 2 in vitro genotoxicity tests, acute inhalation study, short-term (2-week) inhalation range finder study with measurement of bone marrow micronuclei, 90-day inhalation toxicity, and sensory irritation assay. Dermal irritation was slight to moderate. All genotoxicity studies were negative. An acute inhalation study with F344 rats exposed at 2000 mg/m3 for 4 hr resulted in no abnormal clinical observations. Based on a 2-week range-finder, F344 rats were exposed for 6 hr per day, 5 days per week, for 90 days to an aerosol-vapor mixture of FT SPK jet fuel (0, 200, 700 or 2000 mg/m3). Effects on the nasal cavities were minimal (700 mg/m3) to mild (2000 mg/m3); only high exposure produced multifocal inflammatory cell infiltration in rat lungs (both genders). The RD50 (50% respiratory rate depression) value for the sensory irritation assay, calculated to be 10,939 mg/m3, indicated the FT SPK fuel is less irritating than JP-8. Based upon the proposed use as a 50:50 blend with JP-8, a FT SPK jet fuel OEL is recommended at 200 mg/m3 vapor and 5 mg/m3 aerosol, in concurrence with the current JP-8 OEL.

Assessment of DNA damage in blood lymphocytes of bakery workers by comet assay.

The comet assay is widely used in screening and identification of genotoxic effects of different substances on people in either their working or living environment. Exposure to fuel smoke leads to DNA damage and ultimately different types of cancer. Using a comet assay, the present study aimed to assess peripheral blood lymphocyte DNA damage in people working in bakeries using natural gas, kerosene, diesel, or firewood for fuel compared to those in the control group. The subjects of this study were 55 people in total who were divided into four experimental groups, each of which comprised of 11 members (based on the type of fuel used), and one control group comprised of 11 members. Using CometScore, the subjects' peripheral blood lymphocytes were examined for DNA damage. All bakers, that is, experimental subjects, showed significantly greater peripheral blood lymphocyte DNA damage compared to the individuals in the control group. There was greater peripheral blood lymphocyte DNA damage in bakers who had been using firewood for fuel compared to those using other types of fuel to such an extent that tail moments (µm) for firewood-burning bakers was 4.40 ± 1.98 versus 1.35 ± 0.84 for natural gas, 1.85 ± 1.33 for diesel, and 2.19 ± 2.20 for kerosene. The results indicated that burning firewood is the greatest inducer of peripheral blood lymphocytes DNA damage in bakers. Nonetheless, there was no significant difference in peripheral blood lymphocyte DNA damage among diesel and kerosene burning bakers.

Lung injury via oxidative stress in mice induced by inhalation exposure to rocket kerosene.

Rocket kerosene (RK) is a new rocket propellant. Toxicity occurs if a high level of RK is inhaled. To study the toxicity of RK in lung and the mechanisms of RK-induced lung jury, a total of 72 male ICR mice (1.5 months, adult) were randomly assigned to the RK exposure group (RKEG) and normal control group (NCG). Mice were whole-body exposed to room air or aerosol of 18000 mg/m3 RK for 4 hours. Histopathological analysis was performed to evaluate the pulmonary lesions. Oxidative stress was assessed by assay of MDA, SOD, GSH-PX and TAOC. Inflammatory response was estimated by detecting inflammatory cell counts, TNF-α and IL-6 protein levels in serum. The results showed that after 2 to 6 hours of RK exposure, pulmonary vascular dilatation, congestion and edematous widening of the alveolar septum were noted. After 12 to 24 hours post-exposure, diffuse hemorrhage in alveolar space were found, along with the progressive pulmonary vascular dilatation and edematous widening of alveolar septum. During 3 to 7 days of RK-exposure, inflammatory cells were scattered in the lung tissue. The pathological alterations of the lung were alleviated after 14 days post-exposure, and showed significant improvement after 21 days post-exposure. After 30 days of RK exposure, the pathological changes in the lung tissue were nearly recovered except the local thickening of the alveolar wall. Compared with NCG, RK inhalation produced a significant increase of MDA levels and a significant decrease of SOD, GSH-Px and TAOC activity in the lung after 2 hours post-exposure (P<0.05). There were significant increases of TNF-α and IL-6 protein levels in serum of mice in RKEG after 2, 6 and 12 hours and 1, 4 and 7 days post-exposure compared with NCG (P<0.05). TNF-α protein levels had a sharp increase after 4 days of exposure. IL-6 protein level was increased at early phase of experiment and then gradually decreased along with the prolonged course of exposure. Considering that the RK-induced lung injury was through the oxidative stress, inhibition of oxidative stress after RK exposure may be urgently needed.

Kerosene: a review of household uses and their hazards in low- and middle-income countries.

Kerosene has been an important household fuel since the mid-19th century. In developed countries its use has greatly declined because of electrification. However, in developing countries, kerosene use for cooking and lighting remains widespread. This review focuses on household kerosene uses, mainly in developing countries, their associated emissions, and their hazards. Kerosene is often advocated as a cleaner alternative to solid fuels, biomass and coal, for cooking, and kerosene lamps are frequently used when electricity is unavailable. Globally, an estimated 500 million households still use fuels, particularly kerosene, for lighting. However, there are few studies, study designs and quality are varied, and results are inconsistent. Well-documented kerosene hazards are poisonings, fires, and explosions. Less investigated are exposures to and risks from kerosene's combustion products. Some kerosene-using devices emit substantial amounts of fine particulates, carbon monoxide (CO), nitric oxides (NO(x)), and sulfur dioxide (SO(2)). Studies of kerosene used for cooking or lighting provide some evidence that emissions may impair lung function and increase infectious illness (including tuberculosis), asthma, and cancer risks. However, there are few study designs, quality is varied, and results are inconsistent. Considering the widespread use in the developing world of kerosene, the scarcity of adequate epidemiologic investigations, the potential for harm, and the implications for national energy policies, researchers are strongly encouraged to consider collecting data on household kerosene uses in studies of health in developing countries. Given the potential risks of kerosene, policymakers may consider alternatives to kerosene subsidies, such as shifting support to cleaner technologies for lighting and cooking.

Acute treatment with kerosene damages the dermal barrier and alters the distribution of topically applied benzo(a)pyrene in mice.

The dermal route is important in many occupational exposures. Some materials may reduce the barrier function of the skin to enhance absorption and effect on internal organs. We have reported previously that kerosene cleaning following treatment with used engine oil increased DNA adduct levels in the lungs of mice compared with animals treated with used oil alone. To investigate what other physiological parameters might be affected by kerosene, we conducted in vitro and in vivo measurements of skin barrier function. We also topically applied (3)H-BAP(100 nM in 25 µL acetone) and washed half the mice with 25 µL kerosene 1 hr after carcinogen application. Groups of four mice were euthanized from 1 to 72 hr after treatment. Skin, lungs, and livers were harvested from each animal and stored separately. Kerosene application reduced the barrier function of the skin in vitro beyond the effect of the acetone vehicle and the vehicle plus BAP. In vivo studies indicated that kerosene treatment reduced the barrier function at 4 and 8 hr post application and that the barrier function recovered at 24 hr after a single treatment. The fraction of the radiolabel remaining in the skin of animals treated with (3)H-BAP and washed with kerosene was significantly less than those not washed, beginning at 24 hr (p< 0.05). Fractional distribution to the lungs and livers of these animals became significantly elevated at this time. Kerosene treatment compromises dermal barrier function and the ability of the skin to retain water, enhances carcinogen absorption, and alters organ distribution. This appears to contribute to the increase in BAP DNA adducts we reported earlier.

Past, present and emerging toxicity issues for jet fuel.

The US Air Force wrote the specification for the first official hydrocarbon-based jet fuel, JP-4, in 1951. This paper will briefly review the toxicity of the current fuel, JP-8, as compared to JP-4. JP-8 has been found to have low acute toxicity with the adverse effects being slight dermal irritation and weak dermal sensitization in animals. JP-4 also has low acute toxicity with slight dermal irritation as the adverse effect. Respiratory tract sensory irritation was greater in JP-8 than in JP-4. Recent data suggest exposure to jet fuel may contribute to hearing loss. Subchronic studies for 90 days with JP-8 and JP-4 showed little toxicity with the primary effect being male rat specific hydrocarbon nephropathy. A 1-year study was conducted for JP-4. The only tumors seen were associated with the male rat specific hydrocarbon nephropathy. A number of immunosuppressive effects have been seen after exposure to JP-8. Limited neurobehavioral effects have been associated with JP-8. JP-8 is not a developmental toxicant and has little reproductive toxicity. JP-4 has not been tested for immune, neurobehavioral or reproductive endpoints. JP-8 and JP-4 were negative in mutagenicity tests but JP-4 showed an increase in unscheduled DNA synthesis. Currently, JP-8 is being used as the standard for comparison of future fuels, including alternative fuels. Emerging issues of concern with jet fuels include naphthalene content, immunotoxicity and inhalation exposure characterization and modeling of complex mixtures such as jet fuels.

Digestive cell turnover in digestive gland epithelium of slugs experimentally exposed to a mixture of cadmium and kerosene.

Slugs, Arion ater (L), have been proposed as sentinel organisms to assess soil health. In slugs under the influence of pollutants, digestive cell loss and the concomitant increase of excretory cells of the digestive gland have been described. The aim of the present work was to determine up to what extent digestive cell loss affects biomarkers and whether the affectation is reversible after exposure to a mixture of metal and organic pollutants. Slugs were dosed with a mixture of cadmium and kerosene in the food for 27 days. Apart from chemical analyses, the volume density of black silver deposits (Vv(BSD)) after autometallography, and acyl-CoA oxidase (AOX) activity were used as biomarkers of exposure to metals and organic compounds, respectively. As effect biomarkers, changes in the volume density of the cell types that constitute the digestive gland epithelium were calculated. Proliferating cells were identified by means of bromodeoxyuridine (BrdU) immunohistochemistry. Results revealed that the mixture of pollutants provoked an increase in Vv(BSD) and AOX activity and a decrease in the number of digestive cells. These changes had no effect in the digestive gland accumulation capacity or in the effect and exposure biomarkers employed. BrdU-labelling showed that exposure to pollutants provoked an enhanced digestive cell proliferation.

[Ecological/hygienic and toxicological evaluation of combustion products of aviation kerosene and liquefied natural gas].

Products of kerosene combustion in the present-day aeroengines contain more than 200 compounds of incomplete combustion, partial oxidation, and thermal decomposition of fuel and oil. Most of these are strong toxicants for humans. Increase of temperature in the turbine engine combustion chamber led to production of very toxic nitrogen oxides. In search for the ecologically safe and less toxic alternative attention of fuel engineers was drawn to liquefied natural gas which compares well and even excels kerosene in ecological, economic and many other respects.

Micronucleus studies in the peripheral blood and bone marrow of mice treated with jet fuels, JP-8 and Jet-A.

The potential adverse effects of dermal and inhalation exposure of jet fuels are important for health hazard evaluation in humans. The genotoxic potential of jet fuels, JP-8 and Jet-A, was investigated in an animal model. Mice were treated dermally with either a single or multiple applications of these jet fuels. Peripheral blood and bone marrow smears were prepared to examine the incidence of micronuclei (MN) in polychromatic erythrocytes (PCEs). In all experiments, using several different exposure regimens, no statistically significant increase in the incidence of MN was observed in the bone marrow and/or peripheral blood of mice treated with JP-8 or Jet-A when compared with those of untreated control animals. The data in mice treated with a single dose of JP-8 or Jet-A did not confirm the small but statistically significant increase in micronuclei reported in our previous study.

Motor inhibition and learning impairments in school-aged children following exposure to organophosphate pesticides in infancy.

Despite the critical role of acetylcholinesterase (AChE) in cortical function and development, no long-term studies have been conducted in humans on the long-term sequelae of the disruption of the cholinergic system in early childhood. We report a neuropsychological assessment of healthy school-aged children, who had been hospitalized in infancy following exposure to organophosphate pesticides, compared with children exposed to other toxins such as kerosene, and age- and sex-matched non-exposed children. Although overall, the children seem to have overcome the acute one-time exposure incident, and they all attend regular schools, a finer assessment of specific cognitive abilities indicates they are impaired compared with the matched controls. Specifically, the children who had been exposed to organophosphate pesticides had a deficit in inhibitory motor control. Children with pesticide or kerosene poisoning had a retrieval deficit on the acquisition phase of a verbal learning task.

JP-8 jet fuel-induced DNA damage in H4IIE rat hepatoma cells.

We investigated the genotoxicity of middle distillate jet fuel, Jet Propulsion 8 (JP-8), on H4IIE rat hepatoma cells in vitro. DNA damage was evaluated using the comet (single cell gel electrophoresis) assay. Cells were exposed for 4h to JP-8 (solubilized in ethanol (EtOH) at 0.1% (v/v)) to concentrations ranging from 1 to 20microg/ml. Exposure to JP-8 resulted in an overall increase in mean comet tail moments ranging from 0.74+/-0.065 (0.1% EtOH control) to 3.13+/-0.018,4.36+/-0.32,5.40+/-0.29,7.70+/-0.52 and 11.23+/-0.77 for JP-8 concentrations 3, 5, 10, 15 and 20microg/ml, respectively. Addition of DNA repair inhibitors hydroxyurea (HU) and cytosine arabinoside (Ara-C) to cell culture with JP-8 resulted in accumulation of DNA damage strand breaks and increase in comet tail length. Inclusion of 4mM HU and 40microM Ara-C with 3, 5, 10 and 20microg/ml JP-8 concentrations resulted in increased mean tail moments to 5.94+/-0.43,10.12+/-0.72,17.03+/-0.96,and29.25+/-1.55. JP-8, in the concentrations used in this study, did not result in cytotoxicity or significant apoptosis, as measured using the terminal deoxynucleotidyl transferase (TDT)-mediated dUTP-X nick end labeling (TUNEL) assay. These results demonstrate that relevant exposures to JP-8 result in DNA damage to H4IIE cells, and suggest that DNA repair is involved in mitigating these effects.

Effects of short-term JP-8 jet fuel exposure on cell-mediated immunity.

The U.S. Air Force has implemented the widespread use of JP-8 jet fuel in its operations, although a thorough understanding of its potential effects upon exposed personnel is unclear. Exposure to environmental toxicants such as JP-8 may have significant effects on host physiology. Jet fuel exposure has been shown to cause human liver dysfunction, abnormal electroencephalograms, shortened attention spans, and decreased sensorimotor speed. Previous studies have shown that short-term, low-concentration JP-8 exposure had significant effects on the immune system; e.g., decreased viable immune cell numbers, decreased immune organ weights, and loss of immune function that persisted for extended periods of time (i.e., up to 4 weeks post-exposure). In the current study, an in-depth analysis of the effects of JP-8 exposure on cellular immunity was performed. Short-term (7 days, 1 h/day), low-concentration (1000 mg/m3) exposures were conducted in mice, and T cell and natural killer (NK) cell functions were analyzed 24 h after the last exposure. The exposure regimen was found to almost completely ablate NK cell function, as well as significantly suppress the generation of lymphokine-activated killer (LAK) cell activity. Furthermore, JP-8 exposure suppressed the generation of cytotoxic T lymphocyte (CTL) cells from precursor T cells, and inhibited helper T cell activity. These findings demonstrate that JP-8 jet fuel exposure has significant detrimental effects on immune functions of exposed individuals. JP-8 jet fuel should be considered a potential and significant immunotoxicant. Chronic exposure to JP-8 may have serious implications to the long-term health of exposed individuals.

Proteomic analysis of the renal effects of simulated occupational jet fuel exposure.

We analyzed protein expression in the cytosolic fraction prepared from whole kidneys in male Swiss-Webster mice exposed 1 h/day for five days to aerosolized JP-8 jet fuel at a concentration of 1000 mg/m3, simulating military occupational exposure. Kidney cytosol samples were solubilized and separated via large-scale, high-resolution two-dimensional electrophoresis (2-DE) and gel patterns scanned, digitized and processed for statistical analysis. Significant changes in soluble kidney proteins resulted from jet fuel exposure. Several of the altered proteins were identified by peptide mass finger-printing and related to ultrastructural abnormalities, altered protein processing, metabolic effects, and paradoxical stress protein/detoxification system responses. These results demonstrate a significant but comparatively moderate JP-8 effect on protein expression in the kidney and provide novel molecular evidence of JP-8 nephrotoxicity. Human risk is suggested by these data but conclusive assessment awaits a noninvasive search for biomarkers in JP-8 exposed humans.

Investigation of in vitro toxicity of jet fuels JP-8 and Jet A.

The in vitro cytotoxicity and electrophysiological toxicity of Jet Propulsion-8 (JP-8 jet fuel) on four cell types: H4IIE liver cell line, NIH Swiss 3T3 cell line, neuroblastoma x glioma NG108-15 cells, and embryonic hippocampal neurons were investigated. H4IIE cells exposed to Jet A (a commercial fuel) and JP-8 demonstrated identical toxicity with an IC50 of 12.6 +/- 0.4 micrograms/ml for the two fuels. Comparison of H4IIE and NIH/3T3 toxicity to JP-8 revealed that NIH/3T3 cells were more sensitive to JP-8 than H4IIE cells, with an IC50 8.5 +/- 0.1 micrograms/ml. JP-8 exposure for the hippocampal neurons proved to be highly toxic (IC50 of < 2 micrograms/ml), while in contrast, the NG108-15 cells were much less sensitive. Electrophysiological examination of NG108-15 cells showed that administration of JP-8 at 1 microgram/ml did not alter significantly any of the electrophysiological properties. However, exposure to JP-8 at 10 micrograms/ml during a current stimulus of +46 pA decreased the amplitude of the action potential to 83 +/- 7% (n = 4), the rate of rise, dV/dtMAX to 50 +/- 8% (n = 4), and the spiking rate to 25 +/- 11% (n = 4) of the corresponding control levels. These results demonstrate JP-8 induced cytotoxic varies among cell types. The possible mechanisms underlying these observations are presented.

Modulation of bronchial epithelial cell barrier function by in vitro jet propulsion fuel 8 exposure.

The loss of epithelial barrier integrity in bronchial and bronchiolar airways may be an initiating factor in the observed onset of toxicant-induced lung injuries. Acute 1-h inhalation exposures to aerosolized jet propulsion fuel 8 (JP-8) have been shown to induce cellular and morphological indications of pulmonary toxicity that was associated with increased respiratory permeability to 99mTc-DTPA. To address the hypothesis that JP-8 jet fuel-induced lung injury is initiated through a disruption in the airway epithelial barrier function, paracellular mannitol flux of BEAS-2B human bronchial epithelial cells was measured. Incubation of confluent cell cultures with non-cytotoxic concentrations of JP-8 or n-tetradecane (C14), a primary constituent of JP-8, for a 1-h exposure period resulted in dose-dependent increases of paracellular flux. Following exposures of 0.17, 0.33, 0.50, or 0.67 mg/ml, mannitol flux increased above vehicle controls by 10, 14, 29, and 52%, respectively, during a 2-h incubation period immediately after each JP-8 exposure. C14 caused greater mannitol flux increases of 37, 42, 63, and 78%, respectively, following identical exposure conditions. The effect on transepithelial mannitol flux reached a maximum at 12 h and spontaneously reversed to control values over a 48-h recovery period, for both JP-8 and C14 exposure. These data indicate that non-cytotoxic exposures to JP-8 or C14 exert a noxious effect on bronchial epithelial barrier function that may preclude pathological lung injury.

Toxicity of middle distillates from dermal exposure.

This report focuses on recent studies that investigated the effects of kerosine dermal exposure on neurotoxicity and reproductive/developmental toxicity. Background toxicity information will also be reviewed for kerosine range mid distillates. The kerosine range mid distillates have a carbon range of C9-C16 and have a boiling range of 302-554 degrees F (150-290 degrees C). This category includes kerosine, aviation fuels (e.g., Jet A, JP-5 and JP-8), no. 1 fuel oil and diesel fuel oil. In general, the kerosine range mid distillates demonstrate relatively low acute toxicity by any route of exposure. High inhalation exposures can induce central nervous system depression characterized by ataxia, hypoactivity and prostration. Kerosines are known to cause skin irritation and inflammation under conditions of acute and repeated exposure in animals and humans, but are only slightly irritating to the eye and are not skin sensitizers. In addition, the absorption of kerosine range mid distillates through the skin has been demonstrated to be fairly rapid, but limited to approximately 10-15% of the applied dose after 24 hours. The kerosine range mid distillates are generally inactive in genetic toxicity tests although positive studies have been reported. Positive results, while at times equivocal, have been reported for straight run kerosine and jet fuel A in the mouse lymphoma assay with metabolic activation, and hydrodesulfurized kerosine (mouse) and jet fuel A (rat) in the bone marrow cytogenetic assay. Effects on the nervous and reproductive systems have been reported in humans and experimental animals under conditions where inhalation and dermal exposure to specific kerosine type fuels are sometimes difficult to separate. Recent laboratory studies have addressed this point and examined the effects of dermal exposure. In these studies, rats were exposed to hydrodesulfurized kerosine by skin application to determine the potential of dermal contact to cause reproductive/developmental toxicity (OECD Guideline 421) or neurotoxicity (TSCA Guidelines on subchronic inhalation and neurotoxicity studies). These studies demonstrated that the highest dose level of kerosine does not induce reproductive/developmental or neurotoxicity effects by skin exposure in rodent studies. The dermal NOEL for HDS kerosine in rats was > or = 494 mg/kg for both neurotoxicity, and reproductive/developmental toxicity.