Furan Isomers Research Articles

Chlorinated dibenzo-p-dioxin and dibenzofuran levels in human adipose tissue and milk samples from the north and south of Vietnam

Although 2,3,7,8-TCDD has been found to be extremely toxic to a variety of laboratory aminals, human epidemiology studies, where exposure to 2,3,7,8-TCDD has been less well characterized than in animal toxicologic studies, have been less conclusive in characterizing the extent of toxicity. In order to determine whether the newly refined techniques of human adipose tissue biopsy including isomer specific and sensitive measurement of PCDDs and PCDFs might be able to assist in finding populations within the same country with high and low levels of dioxins, adipose tissue samples were taken and levels analyzed from the north and south of Vietnam. It seemed reasonable, based on previous work, that high levels of 2,3,7,8-TCDD might still be found in adipose tissue in selected patients living in areas sprayed with Agent Orange and other 2,3,7,8-TCDD containing herbicides, and that lower levels should be found in patients not exposed to 2,3,7,8-TCDD from herbicides or other sources, such as persons who had always resided in the north of Vietnam. Of 9 specimens from patients hospitalized in Hanoi who had never been south, none had detectable adipose tissue levels of 2,3,7,8-TCDD at a detection limit of 2 or 3 ppt on a wet weight basis. Of 15 specimens from Ho Chi Minh City hospitalized patients the mean of positive specimens (12 of 15) was 28 on a lipid basis. The mean of the positive values from the south is about 2 to 3 times higher than found in the North American Continent control patients where the mean is about 6–10 ppt and much higher than in the north of Vietnam. In the northern specimens, the levels were non-detectable with a sensitivity of between 2 and 3 ppt. Other PCDD and PCDF isomers not found in Agent Orange, the penta- through octachlorinated dibenzo-dioxins and dibenzofurans, were similar in isomer type and quantity in the south of Vietnam to what we previously reported in North America. Adipose tissue from the north of Vietnam contained the lowest levels of four through eight chlorinated dioxins and furans thus far reported. The initial data suggests that populations exist in the south of Vietnam with elevated levels of 2,3,7,8-TCDD at the present time, fourteen years after the last known 2,3,7,8-TCDD (Agent Orange) application, superimposed on a preexisting body burden of dioxins and dibenzofurans from sources other than Agent Orange such as technical grade pentachlorophenol or products of incineration contaminated with higher chlorinated PCDDs or PCDFs. In light of the recent finding that unexpected levels of PCDDs and PCDFs exist in the general adult population of industrialized countries, ca. 1,000 to 1,200 ppt, wet weight of total dioxin and furan isomers in adipose tissues, it seems reasonable that the extent of human toxicity of dioxins may be more readily characterized in Vietnam than in industrialized countries. Because 2,3,7,8-TCDD was applied in 1962–1970, although not yet cleaned up, the levels of 2,3,7,8-TCDD in the environment, the food chain, and in humans, would be expected to decrease with time. Therefore, if studies are not initiated in a timely fashion, the opportunity to better characterize the extent of the toxicity of TCDD to humans as well as the persistence of TCDD in the environment in Vietnam may be lost.

The Binghamton state office building PCB, dioxin and dibenzofuran electrical transformer incident: 1981–1986

The Binghamton State Office Building (BSOB) polychlorinated biphenyl (PCB) and chlorinated benzene containing electrical transformer arcing and fire incident of February 5, 1981, was the first recognized incident of its kind. A surge of excess electricity led to an electrical panel malfunction at 5:30 AM. For about 30 minutes intense heat was generated as electrical arcing occurred. Dense smoke containing polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzo-p-dioxins (PCDDs) as well as biphenylenes billowed up through air shafts and contaminated all areas of the building later tested for these chemicals. This incident was the first outside a laboratory setting to demonstrate the conversion of PCBs, in the presence of oxygen and heat, to PCDFs, and of the chlorinated benzenes to PCDDs. It demonstrated a hitherto unsuspected potential health hazard of PCB and chlorinated benzene containing electrical transformers, and by implication, capacitors, when not properly separated from areas of buildings used by workers and public. The building has been shut since then and an estimated $40,000,000 may be spent on direct cleanup and rehabilitative costs prior to reopening of the building, if it is to be reopened. Elevated levels of serum PCBs were detected in workers, eg., firefighters initially involved in the fire, which stabilized at lower levels later in the year. Elevated penta- and hexa- chlorinated furan isomers corresponding to isomers found in the soot (and identical to some Yusho isomers) were found in some cleanup workers. Electron microscopy of percutaneous liver biopsies of three patients chemically exposed from the incident showed lesions similar to those seen in guinea pigs fed the soot, which was biologically quite active. This incident, and others occurring afterward, has led the US Environmental Protection Agency to ban PCB containing transformers from similar buildings.

Humoral immunotoxicity of polychlorinated diphenyl ethers, phenoxyphenols, dioxins and furans present as contaminants of technical grade pentachlorophenol

Previous studies have demonstrated that the humoral immune response in mice as measured by the splenic IgM response to sheep erythrocytes (SRBC) is highly sensitive to suppression by technical grade (86%) pentachlorophenol (T-PCP) whereas analytical grade (> 99%) PCP is not immunosuppressive. In the present studies, we have examined several contaminant fractions and purified isomers from T-PCP for their humoral immunosuppressive effect. C57BL/6 mice were treated with a single oral dose of the various contaminants 2 days prior to SRBC challenge and the peak splenic IgM antibody response was measured 5 days later. Under these exposure conditions, T-PCP produced a dose-related suppression of the antibody response whereas analytical grade PCP was without effect. The dose of T-PCP producing 50% immunosuppression relative to the vehicle-treated control (ID 50) was 83 mg/kg. Results from studies using contaminant fractions extracted from T-PCP indicated that a chlorinated dioxin/furan fraction was significantly immunosuppressive, whereas a chlorinated phenoxyphenol fraction and a chlorinated diphenyl ether fraction were without effect when administered at dose levels expected to occur in the ID 50 dose of T-PCP. Several purified phenoxyphenol isomers representing the major pre- and isopredioxins in T-PCP were also not immunosuppressive, nor was octachlorodibenzo- p-dioxin. The 1,2,3,6,7,8-hexachlorodioxin (HxCDD), 1,2,3,4,6,7,8-heptachlorodioxin (HpCDD), and 1,2,3,4,6,7,8-heptachlorofuran (HpCDF) isomers were all significantly immunosuppressive. The single, oral ID 50s were 7.1, 85 and 208 μg/kg for HxCDD, HpCDD and HpCDF, respectively. Coadministration of HxCDD and HpCDD produced an additive immunosuppresive effect suggesting that the toxic dioxin and furan isomers present in T-PCP function in concert to produce the degree of immune suppression observed following T-PCP exposure. When analytical grade PCP was coadministered with HpCDD, the degree of immune suppression was equivalent to that produced by HpCDD alone, indicating no significant influence of PCP on dioxin-induced immunosuppression. The enhanced susceptibility of Ah-responsive C57BL/6 mice to T-PCP induced immune suppression as compared to Ah-nonresponsive DBA/2 mice and the correlation of immune suppression with P 1-450 associated monoxygenase induction provided further evidence for the role of the toxic Ah-interactive dioxin and furan contaminants in T-PCP as the mediators of T-PCP immunotoxicity.