Exposure opportunity models for Agent Orange, dioxin, and other military herbicides used in Vietnam, 1961–1971

Nearly 19.5 million gallons of herbicides were sprayed on the Republic of Vietnam between 1961 and 1971 for military purposes. Amounts of spray and patterns of applications are available in an electronic file called HERBS that contains records of 9141 defoliation missions, including detailed coordinates of US Air Force Ranch Hand aircraft flight paths, along with chemical agent and gallonage sprayed. Two classes of models for use in epidemiological and environmental studies that utilize the HERBS data for estimating relative exposure opportunity indices are presented: a discrete “hits” model that counts instances of proximity in time and space to known herbicide applications, and a continuous exposure opportunity index, E4, that takes into account type and amount of herbicide sprayed, distance from spray application, and time interval when exposure may have occurred. Both direct spraying and indirect exposure to herbicide (or dioxin) that may have remained in the local environment are considered, using a conservative first-order model for environmental disappearance. A correction factor for dermal versus respiratory routes of entry has been incorporated. E4 has a log-normal distribution that spans six orders of magnitude, thus providing a substantial amount of discrimination between sprayed and unsprayed areas. The models improve on earlier ones by making full use of the geometry of the HERBS spray flight paths of Ranch Hand aircraft. To the extent possible so many decades after the War, the models have been qualitatively validated by comparison with recent dioxin soil and biota samples from heavily contaminated areas of Vietnam, and quantitatively validated against adipose dioxin obtained in epidemiological studies of Vietnamese. These models are incorporated within a geographic information system (GIS) that may be used, as one would expect, to identify locations such as hamlets, villages, and military installations sprayed by herbicide. In a novel application, the GIS also facilitates quantitative risk assessment in epidemiological and ecological studies by applying the models within a framework of historical reconstruction of exposure history of individuals based upon their location histories.

[1]  M. Chipman Herbicides in Vietnam. , 1973, Science.

[2]  T. B. Curbishley,et al.  AgDrift®: A model for estimating near‐field spray drift from aerial applications , 2002, Environmental toxicology and chemistry.

[3]  D. Cyranoski US and Vietnam join forces to count cost of Agent Orange , 2002, Nature.

[4]  Luís Bragança,et al.  A methodological approach , 2005 .

[5]  KIRK R SMITH,et al.  Place makes the poison: Wesolowski Award Lecture — 1999 , 2002, Journal of Exposure Analysis and Environmental Epidemiology.

[6]  L. Abenhaim,et al.  Correlation between dioxin levels in adipose tissue and estimated exposure to Agent Orange in south Vietnamese residents. , 1994, Environmental Research.

[7]  L. Dwernychuk,et al.  Dioxin reservoirs in southern Viet Nam--a legacy of Agent Orange. , 2002, Chemosphere.

[8]  A. Schecter,et al.  Recent Dioxin Contamination From Agent Orange in Residents of a Southern Vietnam City , 2001, Journal of occupational and environmental medicine.

[9]  R. Frank,et al.  Occupational exposure of herbicide applicators to herbicides used along electric power transmission line right-of-way. , 1984, American Industrial Hygiene Association journal.

[10]  Steven D. Stellman,et al.  The extent and patterns of usage of Agent Orange and other herbicides in Vietnam , 2003, Nature.

[11]  J. Stellman,et al.  Estimation of exposure to Agent Orange and other defoliants among American troops in Vietnam: a methodological approach. , 1986, American journal of industrial medicine.

[12]  J. Stellman,et al.  A geographic information system for characterizing exposure to Agent Orange and other herbicides in Vietnam. , 2002, Environmental health perspectives.

[13]  Ryan S. Miller,et al.  Identifying populations potentially exposed to agricultural pesticides using remote sensing and a Geographic Information System. , 1999, Environmental health perspectives.

[14]  J. C. Street,et al.  Applicator exposure to 2,4-D, dicamba, and a dicamba isomer. , 1982, Journal of environmental science and health. Part. B, Pesticides, food contaminants, and agricultural wastes.

[15]  D. M. Sassone,et al.  Comparison of extremely low frequency (ELF) magnetic field personal exposure monitors , 2002, Journal of Exposure Analysis and Environmental Epidemiology.

[16]  J. Behren,et al.  Agricultural pesticide use in California: pesticide prioritization, use densities, and population distributions for a childhood cancer study. , 2001, Environmental health perspectives.

[17]  I M Abbott,et al.  Worker exposure to a herbicide applied with ground sprayers in the United Kingdom. , 1987, American Industrial Hygiene Association journal.

[18]  J. W. Barry,et al.  FSCBG: An aerial spray dispersion model for predicting the fate of released material behind aircraft , 1993 .

[19]  S. Melly,et al.  Using GIS and historical records to reconstruct residential exposure to large-scale pesticide application , 2002, Journal of Exposure Analysis and Environmental Epidemiology.

[20]  J. B. Greig Veterans and Agent Orange: Health Effects of Herbicides Used in Vietnam , 1995 .

[21]  E. Schaeffner,et al.  Use of an Asbestos Exposure Score and the Presence of Pleural and Parenchymal Abnormalities in a Lung Cancer Case Series , 2001, International journal of occupational and environmental health.

[22]  Peggy Reynolds,et al.  Childhood cancer incidence rates and hazardous air pollutants in California: an exploratory analysis. , 2002, Environmental health perspectives.

[23]  L. Abenhaim,et al.  Agent Orange and the risk of gestational trophoblastic disease in Vietnam , 1996 .

[24]  J. Stellman,et al.  Combat and herbicide exposures in Vietnam among a sample of American Legionnaires. , 1988, Environmental research.