1 15 34 Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 027 Folder The folder containing the original item. 0409 Series The series number of the original item. Series III Subseries I Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Source A related resource from which the described resource is derived Nature Date A point or period of time associated with an event in the lifecycle of the resource April 10 1980 Title A name given to the resource News in Brief: US agency denies Agent Orange cover up; News in Brief: Australia orders Agent Orange inquiry Subject The topic of the resource VA AVHS government liability Agent Orange controversy ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 028 Folder The folder containing the original item. 0447 Series The series number of the original item. Series III Subseries I Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Aldred, J. E. Description An account of the resource Corporate Author: Consultative Council on Congenital Abnormalities in the Yarram District Date A point or period of time associated with an event in the lifecycle of the resource September 26 1978 Title A name given to the resource Report of the Consultative Council on Congenital Abnormalities in the Yarram District Subject The topic of the resource AVHS congenital birth defects ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 034 Folder The folder containing the original item. 0695 Series The series number of the original item. Series III Subseries I Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Hall, Peter Ben Selinger Source A related resource from which the described resource is derived Nature Date A point or period of time associated with an event in the lifecycle of the resource July 23 1981 Title A name given to the resource Letter to the Editor: Australian 2,4,5-T Subject The topic of the resource dioxin AVHS ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 036 Folder The folder containing the original item. 0786 Series The series number of the original item. Series III Subseries I Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Jessop, D. S. Source A related resource from which the described resource is derived Senate Date A point or period of time associated with an event in the lifecycle of the resource November 25 1982 Title A name given to the resource Standing Committee on Science and the Environment: Report on Pesticides and the Health of Vietnam Veterans Subject The topic of the resource AVHS government liability ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 038 Folder The folder containing the original item. 0858 Series The series number of the original item. Series III Subseries I Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Lee, Charles Source A related resource from which the described resource is derived The Medical Journal of Australia Date A point or period of time associated with an event in the lifecycle of the resource June 30 1979 Title A name given to the resource Dioxin (Dilemma)? Subject The topic of the resource dioxin AVHS herbicide regulation ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 053 Folder The folder containing the original item. 1407 Series The series number of the original item. Series III Subseries II Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Program: 1985 Annual Summer Toxicology Forum, Aspen, Colorado, 15-19 July 1985 Subject The topic of the resource AVHS risk assessment dioxin ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 054 Folder The folder containing the original item. 1415 Series The series number of the original item. Series III Subseries II Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Date A point or period of time associated with an event in the lifecycle of the resource February 17 1986 Title A name given to the resource The Toxicology Forum 1986 Annual Winter Meeting Subject The topic of the resource AVHS dioxin ao_seriesIII https://www.nal.usda.gov/exhibits/speccoll/files/original/4cad9e104281ea21aa6d58077c25dc9a.pdf 6089c4098b1b8003a618435654fe0d69 PDF Text Text Item ID Number 01474 Author Corporate Author ROpOrt/ArtlOlO TltlO Typescript: Notes and diagrams regarding TCDD exposure Journal/Book Title °°00 Year Month/Day Color n OOSOrfptOD NOtOS Typescript and diagrams regarding TCDD exposure, Australian Senate Committee on Science and the Environment, Ranch Hand versus Marine exposure Tuesday, May 15, 2001 Page 1474 of 1514 �PARAMETERS OF TCDD EXPOSURE HERBS TAPE ACCURACY ENVIRONMENTAL FATE OF TCDD PERSONNEL PROXIMITY TO SPRAY VIA RECORDS REVIEW ECOLOGIC MODELING �ISSUE: CAN A VALID HERBICIDE ORANGE (TCDD) EXPOSURE ALLOCATION BE MADE FOR EACH INDIVIDUAL (GROUP) IN PREPARATION FOR A STUDY OF GROUND PERSONNEL? EXPOSURE ALLOCATION OUTCOMES STUDY OUTCOMES VALID TRUTH MISCLASSIFIED INDETERMINANT BIASED POSITIVE OR NEGATIVE NOT TRUTH �EXPOSURE ALLOCATION METHODS SUBJECTIVE MEANS: * QUESTIONNAIRE TECHNIQUES OPINION: INTENTIONAL MALATHION EXPOSURE BY SIMILAR AIRCRAFT IN RVN HAS CREATED A POSITIVE IRREVOCABLE BIAS ® SOLICITATION FOR "EXPOSED" VOLUNTEERS OPINION: UNCORRECTABLE SELECTION BIAS �EXPOSURE ALLOCATION METHODS OBJECTIVE MEANS: e RECORD REVIEWS IN SELECTED OCCUPATIONAL GROUPS OPINION: BIAS, MISCLASSIFICATION POSSIBLE, SMALL SAMPLE SIZE ASSURED ® PROBABILISTIC DETERMINATION VIA HERBS TAPES AND RECORD REVIEW FOR TIME/DISTANCE ESTIMATES OPINION: MISCLASSIFICATION ASSURED; SELECTION BIAS PROBABLE, TRUE ERROR RATES IMPOSSIBLE TO MEASURE; VALIDITY COMPROMISED �PROCESS OF EXPOSURE ALLOCATION INFLUENCES: > COHORTS (STUDY AND COMPARISON) TO BE SELECTED > METHOD(S) OF COHORT SELECTION > SAMPLE SIZE OF COHORTS » STATISTICAL POWER > OPERATION OF CONFOUNDERS (MALATHION, COMBAT STRESS, ETC.) \ SCIENTIFIC/LAY ACCEPTANCE OF STUDY �SOME STUDY OPTIONS BASED ON EXPOSURE DILEMMA 9 PERFORM A "RVN EXPERIENCE STUDY" ® DECLARE AGENT ORANGE STUDY NOT DOABLE ' © BOTH OPTIONS ABOVE » DETERMINE FEASIBILITY OF USING OCCUPATIONAL GROUPS • CONDUCT AGENT ORANGE STUDY BASED UPON PROBABILISTIC EXPOSURE • ABOVE OPTION, ADD COHORT(S) FOR "RVN EXPERIENCE STUDY" �OPINION BASED UPON $ WORLD LITERATURE: ZERO TO LOW INCIDENCE OF HEALTH CONSEQUENCES, RARE OR DIFFICULT TO MEASURE CLINICAL ENDPOINTS ® FACT OF UNESTIMATABLE ERROR "RATES FOR EXPOSURE ALLOCATION IN GROUND TROOPS BASED UPON HERBS TAPES @® YIELDS A STUDY OF UNKNOWN ABILITY (POWER) TO DETECT A EFFECT USE OF PROBABILISTIC MEANS TO DETERMINE EXPOSURE IS SCIENTIFIC HOKUM �AUSTRALIAN SENATE COMMITTEE ON SCIENCE AND THE ENVIRONMENT CONCLUSIONS LITTLE LIKELIHOOD AUSTRALIAN TROOPS WERE DIRECTLY OR INDIRECTLY EXPOSED TO HERBICIDES DIRECT EXPOSURE TO MALATHION WAS HIGHLY PROBABLE IN THE MAJORITY OF CASES EXPOSURE TO ANTIMALARIAL DRUGS WAS ROUTINE ANY ADDED CARCINOGENIC/TERATOGEN1C.BURDEN ON AUSTRALIAN TROOPS WAS RELATIVELY SMALL ' BASED ON CURRENT DATA, "THERE IS NO CONVINCING EVIDENCE THAT BIRTH ABNORMALITIES, PSYCHIATRIC DISORDERS AND MORTALITY ARE EXCESSIVE AMONG VIETNAM VETERANS." ALL FUTURE AUSTRALIAN GOVERNMENT STUDIES WILL ADDRESS THE ISSUE OF VIETNAM SERVICE, NOT SPECIFIC CHEMICAL EXPOSURE �KEY ITEMS OF CONSIDERATION MARINE STUDY RELATIVE TO RANCH HAND STUDY "EXPOSED " MARINES RECEIVED AN AVERAGE EXPOSURE 1/1000 THE AVERAGE DOSE RECEIVED BY RANCH HAND PERSONNEL MARINE EXPOSURE ALLOCATIONS BASED ON DISTANCE FROM SPRAY PATHS LEAD TO SERIOUS MISCLASSIFICATION OR BIAS MARINE EXPOSURE ALLOCATIONS BASED ON TIME IN A SPRAY AREA SUBSTANTIALLY ALTER THE SIZES OF THE STUDY AND CONTROL POPULATIONS AND LEAD TO SERIOUS MISCLASSIFICATION �CONCLUSIONS RANCH HAND VERSUS OR PLUS THE MARINE POPULATION • OVERWHELMING ALLOCATION PROBLEMS FOR "EXPOSURE-NONEXPOSURE" IN MARINES - MISCLASSIFICATION BY 6AO 8RITERIA = OILUTIONAL EFFECT - ALLOCATION BY PERSONAL HISTORY = BIAS • MARINE EXPOSURE 1/1000 OF RANCH HAND EXPOSURE « MARINE - RANCH HAND POPULATIONS DIFFER BY HOST FACTORS; AGE, RACE, EDUCATIONAL LEVEL, ETC •• BY CONSIDERATION OF EXPOSURE DIFFERENTIAL AND MISCLASSIFICATION, RANCH HAND STUDY FAR MORE POWERFUL THAN INDEPENDENT MARINE STUDY OR ADDITIVE STUDY TO INCLUDE MARINES •• ADDITION OF MARINE POPULATION TO RANCH HAND POPULATION = UNACCEPTABLE SCIENCE �MORTALITY ANALYSIS POWER COMPARISON OF THE RANCH HAND STUDY TO THE MARINE POPULATION CONSIDERING MISCLASSIFICATION AND RELATIVE EXPOSURE * POWER TABLE MARINE STUDY POWER ANCK HAND POWER 1-B % MISCLASSIFiCATION EXPOSURE LEVELS RELATIVE TO RANCH HAND • 1/10 1/20 1/100 1/1000 .87 0 10 25 ASSUMPTIONS: RH STURY POP. 1,200; 6,000 (1:5) MARINE STUDY POP. 21,900: 196,100 NORMAL INCIDENCE OF DISEASE =0.001 DISEASE INCIDENCE IN RH - 0.004 LINEAR DOSE - RESPONSE MISCLASS OF MARINE CONTROLS EXCLUDED .38 .33 .26 .17 .15 .13 .07 .06 .06 .05 .05 .05 * INCORRECT POPULATION NUMERICS BASED ON ENVIRONMENTAL FATE OF TCDD � Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 055 Folder The folder containing the original item. 1474 Series The series number of the original item. Series III Subseries II Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Typescript: Notes and diagrams regarding TCDD exposure Subject The topic of the resource human exposure AVHS Ranch Hand Marine Corps exposure ao_seriesIII https://www.nal.usda.gov/exhibits/speccoll/files/original/eb6debf974ce03cc4e2b945c807897f6.pdf b9dc095475ed57983dee2a445bd57420 PDF Text Text Item ID Number 01497 Author O'Keefe, Barry Corporate Author Report/Article TitlO Typescript: Chapter/: Soft Tissue Sarcoma: Law, Science and Logic, An Australian Perspective Journal/Book Title Year 0000 Month/Day Color Number of Images DOSCrlptOU NotOS Tnis manuscript is a draft version of a chapter or section from the following book: Agent Orange and its Associated Dioxin: Assessment of a Controversy. Young, A. L. and G. M. Reggiani, eds. New York: Elsevier, 1988. This book is available in the NAL collection, call no.: RA1242 T44 A3. "This chapter deals with the Final Report of the Royal Commission on the use and effects of chemical Agents on Australian Personnel in Vietnam, July 1985. It is based on the transcript of the examination and cross-examination of Professor Olav Axelson and Dr. Lennart Hardell as expert witnesses concerning chemically caused cancer, their published papers and the submissions made to the Royal Commission in relation to the subject as well as the Report itself." Tuesday, May 15, 2001 Page 1497 of 1514 �CHAPTER 7 SOFT TISSUE SARCOMA Law, Scien'ce and Logic (*) An Australian Perspective Barry O'Keefe Q.C. - Sydney - Australia Introduction The Royal Commission conducted by the Australian Federal Judge, the Hon. Mr. Justice Evatt D.S.C., presented an excellent opportunity for close examination of a number of studies relied upon by some statutory agencies and others in support of claims that 2,4-D, 2,4,5-T and the contaminant dioxin in Agent Orange are carcinogenic in man and induce male-mediated birth defects. The data and methodology involved as well as the conclusions reached in such studies were able to be examined in an objective, logical and disinterested manner by a Royal Commission wellequipped to make an accurate assessement of the reliability and scientific value of such studies. (*) This chapterdeals with the Final Report of the Royal Commission on the use and effects of chemical Agents on Australian Personnel in Vietnam, July 1985. It is based on the transcript of the examination and cross-examination of Professor Olav Axel son and Dr. Lennart Hardell as expert witnesses concerning chemically caused cancer, their published papers and the submissions made to the Royal Commission in relation to the subject as well as the Report itself. �- 2- A claim made repeatedly by those who represented the members of the Australian Vietnam Veterans Association or who purported to speak on behalf of the veterans was that Agent Orange had caused and was causing cancer in Vietnam Veterans. One type of cancer in particular (soft tissue sarcoma , a generic term for several types of rare cancer), was the focus concern because of surveys of Swedish agricultural, forestry and railway workers by the Swedish investigators Axelson and Hardell. Both published several scientific papers, produced a number of documents for use in courtrooms, gave newspaper and radiointerviews and appeared on television. Both were identified in local and other media with the scientific work which was seeking to link specific cancer types with the use of phenoxy herbicides. This was more manifest in relation to Hardell. Since these studies are the main epidemiological evidence relied upon to support an association between exposure to phenoxy herbicides and an increase of the relevant types of cancer, the Royal Commission examined these data very closely. This involved not only a close examination of the background of their research but also a careful analysis of their data case by case and of their methodology. �- 3 - Epidemiological methodology - The case control study. Epidemiology is said to be the science dealing with the environmental causes of diseasesof humans as inferred from observations of human beings. Whilst the discipline of epidemiology can be used to assess the risk of individuals in a human population developing a particular disorder or to demonstrate an apparent association or lack of association between an observed health phenomenon and a given substance or substances by the mathematical testing of a possible association between the observed health phenomenon and the postulate source of that phenomenon, such a demonstration cannot of itself be used as proof of causal relationship. It merely demonstrates statistical association. This may be a true association or only an indirect or artifactual association. In this regard the problems of confounding and of bias (whether of the selection or observational kind) are important because they can invalidate the conclusions. �- 4- Observational bias may take different forms. It may be bias of the subject arising, for example, out of memory problems or it may be bias in the investigator himself. People who are suffering from a particular disease are more apt that health people to think about their condition and to try and find an explanation, for example, in exposure to various situations or agents which they believe may have caused their disease. This can affect the accuracy of the data obtained. Likewise the accuracy of data obtained may be affected by the subject having knowledge of the result which the investigator is seeking to achieve, just as it may be affected by the data collector being made aware of the object of the data collection. Positive evidence (unless due to confounding) is important. Negative human evidence may not carry, unless it relates to prolonged and heavy exposure. If however it is related and is consistent in a variety of correlation studies over time (cohort studies of exposed individuals and/or case-control studies of affected patients) negative human evidence may justify the conclusion that for practical purposes the agent may be considered as not constituting a risk to human health. In assessing the result of a particular epidemiological study the strength of the association: demonstrated, the duration and degree of exposure, the presence of a dose/response relationship, confirmation or replication of the result by others and the specific �- 5- nature of the response are all relevant factors. So too is the knowledge that the data on which the result is based are accurate. If the data on which a study is based are subject to doubt, then the conclusions of the study must be treated as doubtful at best. In proper epidemiological practice the events which generate an hypothesis should be kept separate from the events used to test that hypothesis. The case control study is one of the methods which can be used for an epidemiological study to assess cancer association and is the one which has been used by Dr. Hardell. A case control study is a retrospective study where one sample of a selected population is compared with another regarding one or more characteristics of interest. The case-control study method has become widely used and refined during the last 50 years due to the increasing importance of chronic diseases where the low incidence and long interval between cause and effect are not well suited for other epidemiological approaches. �- 6- Given the extension of case control studies it is more than ever important to recognize the limitations of the method. In the case of herbicides the case control study is an investigation of the exposure frequencies of two groups of subjects selected on the basis of their status with respect to exposure to the chemical or chemicals in question. The method is valuable because it permits us to see back through time, commencing with the effect back to a postulated cause. It has advantages in relation to other methods: it is relatively inexpensive and requires little time; it is very well suited to the study of rare diseases; it allows the evaluation of several etiologic factors both as independent and interacting causes. The method has also a number of important limitations; it is not suitable for the study of exposures which occur only rarely; it allows estimation of relative rates but not of absolute rates; and finally it is susceptible to bias. Bias, especially selection and recall bias, is the most serious potential problem in case control studies. There are many kinds of selection bias: selective admission to the group; selective survival and death; selective detection; selective response �- 7- and participation. There are other tuasis and confounding factors which can make the conclusions of a study untenable. There can also be demographic bias due to age and sex, which can be risk factors in cancer. There can be clinical bias when a person is genetically predisposed to a specific disease. There is finally the anamnestic recall bias of the interviewed subject. In this case the disease itself acts a&a stimulus which makes the subject concentrate his attention to the possibility or to the degree of an antecedent exposure. There is also the problem of defining the exposure. Taking, for example, an industrial exposure which has occurref 20 years ago and which lasted only a few days, it is extremely difficult, perhaps verging on the impossible, to assess the validity of the information. Efforts should be made to stimulate the memory of the control group of to check the statements made by both the cases and the controls. �- 8- A methological standard which is used to lesten the possibility of bias is the interview with each single member of the group. However the interviewer should be "blinded". In many studies the interviewer who inquires about whether or not the patient was exposed to the causel agent is aware of the research hypothesis or of the subject's identity as a subject or as a control. This can lead to a preconception on the fact of the interview, which is another source of bias. All these factors were thoroughly dealt with in the course of the testimony of Prof. Axel son and Dr. Hardell and considered in detail in the report of the Royal Commission. Prof. Olav Axelson In late 1971 and early 1972 Professor 0. Axelson undertook a study (first analysis) of cancer mortality amongst railway workers because of rumors of excess lung cancer mortality amongst those exposed to 2,4-D and 2,4,5-T (1). In an endeavour to determine if the rumors were justified he examined mortality amongst a cohort of 348 railway workers, inclusion in which cohort depended upon a workers having a given duration of exposure to herbicides during the period from 1951 to 1971. On analysis of the data Professor Axelson �- 9- found a total of 18 deaths from all causes compared with 20.54 expected and a total of 6 deaths from tumors compared with 4.88 expected when a zero latency period was allowed for. For tumors, therefore, the relative risk was close to unity (namely 1.2) and certainly not statistically significant. As far as deaths from lung cancer were concerned, 0.83 have been expected and 2 were found. Neither of these occurred in the sub-cohort said to be exposed to phenoxy acids and both of them (cases 256 and 257) occurred in people who have been smokers for a long time, perhaps decades. From this analysis Professor Axel son concluded that: "There seems to be a possible association between excess tumor mortality and exposure to amitrol and its combinations, especially if a latent period is considered. On the contrary in the cohort exposed to phenoxy acids and .combinations a fairly good agreement is found between the exposed and observed deaths indipendent of the latent period" (4 ). Not only did his first analysis not demonstrate an association between phenoxy herbicides and an increase in cancer incidence but Professor Axelson expressed the view that his conclusion was: "as close as one can get to a negative epidemiologically". �- 10 - After becoming aware of observations by Dr. Hardell i.e. "the first clinical report about soft tissue sarcoma and phenoxy herbicide-exposure" Professor Axelson reanalysed his data (re-analysis). Two (2) cancer cases which in his first analysis had been classified as having been exposed to amitrol were now stated to be cases in which "it is possible that phenoxy acid exposure alone may have occurred"/2 J . When these cases were reclassified in this way i.e. the possibility was converted to a fact and used as an assumption in the re-analysis, an excess of mortality from tumors was obtained amongst individuals with phenoxy acid exposure, as redefined/i) . Thus to produce an excess of -tumors in the relevant subcohort a change in classification had to be effected and the excess found in that cohort depended on only two (2) cases - the two who were re-classified. It is no doubt because of considerationssuch as these that the Axelson re-analysis concedes that: 1) "the material is unsatisfactorily small"; 2) " the exposure pattern is complex" and 3) "it is not possible to clearly select any special herbicide as carcinogenic", and they explain why the conclusion in the �- 11 - re-analysis are so nebulous in relation to the subcohort said to have been exposed to phenoxy acids: "certain indications suggest that an excess tumor mortality may also be referable to phenoxy acids", and "on the basis of these investigations it is not possible to select any special herbicide as carcinogenic but the suspicion against phenoxy acids as a group \ of preparations may have become somewhat increased". Subsequently, using the same exposure data as before, Professor Axel son followed the cohort through to October 1978 and undertook yet another analysis (update). This time, however, he introduced a latency period of 10 years and reached a conclusion which was different from the conclusion in his first analysis. There are two (2) reports of his update (£|). Whilst they are not identical both versions contain the following statement: "tumor incidence was also updated but provided little additional information. The incidence data have therefore been omitted from this presentation". The omission of the incidence data is interesting since, in his first analysis, Professor Axelson had stated that: the "tumor incidence data, however, may be more relevant than the mortality data...." �- 12 - It would seem reasonable to conclude that nothing abnormal was found in the update in relation to tumor incidence - an indicator which Professor Axel son had regarded as "more relevant" than mortality. In his update Professor Axel son concluded that: 1) "no specific type of tumor is predominating; 2) "the aspects of causal relationship are rather unclear"; 3) "those exposed in 1962 or later did not show a clear excess mortality"; 4) "this finding might be interpreted in different ways, i.e. the variety of herbicides during the early period could be of importance and/or the work conditions may have been more primitive and the herbicide handling more careless resulting in a higher degree of exposure". Thus the findings from the update do not single out phenoxy acidi . Indeed the comment in (4) above together with the discussion concerning Table I in reference (1) (below) and the absence of any other data as to the herbicides used by the Swedish railways, support the inference-1 that Professor Ayeison's work in fact exculpates 2,4,5-T. As the Royal Commission found: "At the very least, there are serious problems in his work arising from confounding factors". �- 13 - Because it has been suggested by some that Professor Axel son's first analysis, re-analysis and update in some way support Dr. Harden's later findings, they should be examined. In carrying out this examination it is desirable to look at: 1) methodological flaws; 2) the lack of expertise of those engaged in Axelson's study; 3) the inaccuracy of uncertainty of the data involving problems in the selection of the cohort, in the determination of exposure and arising from wrong diagnoses; 4) the weakness of the conclusions; and 5) the difference between the results obtained by Professor Axelson and those obtained by Dr. Harden. 1) Methological flaws In proper epidemiological practice the events which generate an hypothesis should be kept separate from the events used to test that hypothesis. As Professor Axelson himself agreed: "To my understanding there is a tendency for some statisticians to take the view that one should not use individuals or such observations that have started - yes, started the study - I would not say generated the hypothesis because that is generated from the facts as well". �- 14 - However, his study breached this basis principle, as is clear from the fact that what generated the study was an assertion of three lung cancer amongst the railway workers. One of those was subsequently excluded and leaving Professor Axelson with two cases and they were included as cases in his study. 2) Lack of expertise A questionnaire was sent out as part of the data gathering process. At the time the questionnaire was designed and sent out and at the time the data were gathered, Professor Axelson had neither university qualifications nor professional training in either epidemiology or statistics. He was not a mathematician and his only training in epidemiology was self-training - by reading books. True it is that in 1972 he attended 14 days of lectures in Finland but that, as he conceded, "did not have any effect because it came later".(5; Lack of training and experience may well explain the absence of a written protocol for the study as well as the absence of any formal development of a plan in which the design and purpose of the study and how it would be carried out were detailed (6). �- 15 - 3) Inaccuracy of the data Inaccuracy of the data about exposure can affect the correctness of the conclusions in a study in which exposure to a given substance is the variable. The collection of the data which were used for the first analysis was undertaken at a time there was a good deal of controversy in Sweden about the use of phenoxy herbicides, particularly 2,4,5-T, and a lot of adverse publicity both in the newspapers and on television (7). In addition, rumors were current about an association between cancer and use of such herbicides by railway workers (8). Thus the climate in the communitiy generally and in the study population in particular raises a serious question of possible information bias. This possibility was conceded by Professor Axelson in his evidence to the Royal Commisison. The problem was heightened amongst railway workers by the distribution of questionnaires, in which the first question was : "Have you experienced any health problems which you relate to herbicides?" (9). The questionnaires were sent first to the Chief Physician of the Swedish Railways. From him they went to the various districts in the railway network and then from each district to the men of that district (10). Professor Axelson did not know �- 16 - who had actually filled out the questionnaires (|O). However, it is clear that they went to the bulk of the workers who were included in the cohort as well as to others. All of those to whom the questionnaires went had asked for health check-ups, as appears from Professor Axel son's evidence both before the Royal Commission and the EPA (1980) deposition. The questionnaires were distributed at the very time when lists of the workers said to have been exposed to herbicides in the period 1951 to 1972 were being compiled, or had been requested from, the Swedish railways. An examination of a copy of the questionnaire (3) reveals that no information was sought concerning the extent of exposure to any particular herbicide or chemical and that the instructions which formed part of the questionnaire did not differentiate between different herbicides, all of which were grouped together as "weed and brush killers". In view of the form of the instructions which appeared at the head of the questionnaire, and the first question in it, it is not surprising that Professor Axelson conceded that it was: "fairly clear what the investigation was all about" and that: " we did not camouflage that at all", �- 17 - Despite the fact that the distribution of the questionnaires at such a sensitive time was likely to have exacerbated the problem of recall bias, the information obtained from them in relation to exposure was not used (10). The cohort was in fact compiled from exposure information derived from lists supplied by the Swedish railways. Thus the problem of information bias was made more severe by the adoption of a procedure which produced no countervailing positive or beneficial effect on the study. It took a nember of attempts to compile the study cohort. In the first attempts information as to exposure was sought from the Swedish railway authorities. They provided information in lists which were the result of a "joint assessement of exposure from the railway company and from the trade union representatives". That first or basic set of lists proved to be of little use "because we got in material which was fai'r/y bad from some districts", and "therefore we repeated the whole procedure once more". So instructions were given for the compilation of another set of lists: "At least in this respect, because we had a bad experience there from the first attempts,., we had to be more detailed in the second one before we gave up". �- 18 - There has been therefore a first set of lists from the Railways which were rejected because they were inclomplete and inconsistent, due to differences in the various data provided from different districts. A second set of lists was then compiled and in respect of that Professor Axelson made some mechanical exclusions i.e. everybody who had only exposure up to and including 45 days. The manuscript submitted by Professo Axelson to the Health Board of Occupational Safety and Health became the subject of media publicity. This led to a number of persons coming forward claiming that they should have been in the study. This new group of claimants who came forward to the Railways led to the compilation of a third set of lists. In the compilation of the second set of lists there were instances in which the union insisted that the names of particular workers be added and, after discussion, addition were made for this reason. The lists were then signed as "mutually agreed" between the railways and the unions, although they probably included the names of workers who did not appear from the rail ways' records as persons who had been exposed for 45 days or more. �- 19 - How many of the workers fell into this category was and remains unknown. The employees at the Swedish railways who gathered the material had not training in data collection. The potential for inaccuracy created by this circumstances was compounded by the fact that the exposure was determined by the people compiling the list looking at the salaries that were paid to the various workers, from those salaries deducing what work tasks were undertaken by the various workers and then implying what exposure they could have had. The process involved in the collection of exposure data was conceded by Professor Axel son to be "a sort of guessing". The extend to which any particular person may have been exposed was "guesstimated". Professo Axel son agreed during the examination that in the railway records there was no indication in relation to any individual of any particular preparation or preparations of a chemical nature which were in fact involved in his job. Thus the compilation of the lists relating to exposure was fraught with problems. No checking of exposure was ever undertaken by Professor Axel son or his assistants. The data which were provided in the second and thrird sets of lists were accepted with "not even a spot check in relation to one or some random number", and "..except �- 20 - for excluding persons who are (sic) exactly 45 days of alleged exposure and some accidental inclusions of those who were under 45 days (Professor Axelson) took no part in the selection of the cohort" In these circumstances it is understandable that Professor Axelson did not attest the accuracy of the exposure data. Professor Axel son's reservations about the accuracy of the data are highlighted by his decision to "modify the cohort selection basis after the data had been gathered" by increasing it from a minimum of 45 days exposure to a minimum of 46 days of exposure. This modification of the basis of selection of the cohort was regarded by the Royal Commission as being perhaps somewhat naive, As indicated above the data relating to phenoxy herbicide exposure used in the first analysis, the re-analysis and the update were obtained from the lists supplied by the Swedish railways. These lists categorised potential exposure under three headings namely, Group A, Group 0 and Group F. Professor Axelson said that 'A1 in the Group A heading stood for amitrol. However, an examination of his document (10) shows that a number of specific herbicides are referred to by name under and included within that heading. �- 21 - The heading for Group 0 was "other herbicides". The heading for Group F was said by Professor Axel son to stand for "phenoxy acids". However it turned out that this was not so. It emerged that Group F was "all brush killers". Professor Axelson conceded that the word "brush killers" meant all chemicals of that the description. The description "brush killers" is not apt for 2,4-D and is certainly a category much wider than phenoxy herbicides. Therefore the fact that a person was included in the lists under the heading of Group F did not mean he had been exposed to phenoxy acids even if it be accepted (for the sake of argument) that it meant anything in relation to exposure to a herbicide. It could mean, for example, that the worker was exposed to a phenoxy acid in combination with another herbicide or other herbicides or that he had no exposure to phenoxy acids at all. This latter possibility was accepted by Professor Axelson as was the fact that : "The exposure data did not come from the men claiming to be exposed", "it came from railway officials which may or may not have had personal knowledge of exposure of any individual", "in conjunction with union people who may or .may not have personal knowledge of any such expsure", "and it was derived substantially by way of inference from the category of employment revealed by the employment record". �- 22 - It should be noted that the herbicides which fell within Group F included Primatol D43, Totalex extra, Uridal and MPCA ( None of these contains 2,4-D, 2,4,5-T or TCDD. Ino. Table included in his publication (1) on the exposure of the railway workers Professor Axel son reported the total quantity of specific herbicides "consumed" in 1957-1961 on the Swedish railways over the whole of Sweden. The records did not reveal any use of certain of these herbicides for some of the years 1957 to 1961 inclusive. Professor Axelson sought to avoid the consequences of the implication of this absence of evidence of use of phenoxy herbicides by saying that the word "consumed" really meflnt "purchased from suppliers" but not necessarly used in any given year. However the word "used" which appears in the •footnote to the Table is clearly a synonym for "consumed" and not for "purchased". It is difficult to understand Professor Axelson's reason for including the Table in his study unless he were of the belief that it showed the amount of herbicide actually "consumed" i.e. "used" throughout Sweden by the Swedish railways in the years against which entries are made. Either the Table (and the records on which it was based) indicated the amount of herbicides used in the years dealt with or it does not. If the records do so indicate, then they are de_structive of the conclusions set out in the update. If they do not in fact so indicate then there are two further possibilities, namely Professor Axelson either believed �- 23 - that they did so indicate of he did not so believe. It is unconceivable that he did not believe that Table (and the relevant records) showed what the heading said it showed. If he did not so believe, the inclusion of the Table in his study would amount to a gross departure from the proper standards of scientific honesty. However, even accepting that he did believe the contents of the Table to be accurate (although his oral testimony indicates that they are not accurate) this very situation highlights the loose, untrained and unexperienced approach which was involved in the study and emphasizes the totally unsatisfactory nature of his exposure data. The significance of Professor Axel son's change of stance in relation to this matter prompted the Royal Commissioner to ask: "THE COMMISSIONER: I mean, I am rather shattered to find that in that Table there that I have studied in some depth - to find that it has got nothing to do with the price of fish if I may use a colloquial!ism of this country. I had assumed the men had been exposed, or there was potential exposure, to that amount of that chemical and I find I am wrong in making such an assumption?". "A-Yes". Professor Axel son admitted in his answer that the Table does not tell explicity the exposure of the men in question. �- 24 - A little later, however, Professor Axelson said that the records "reflect indirectly at least how much of herbicide that was used" The Table sKo»o$that no herbicides containing 2,4,5-T or any substance that could potentially contain 2,3,7,8-TCDD were used by the Swedish Railways prior to 1963. When Professor Axelson undertook the updating of his data he ascertained that two cases (Nos. 268 and 334) which had previously been classified as having cancer ("f ) had not had their diagnoses of cancer confirmed by the National Central Bureau of Statistics (3). These cases were therefore excluded from the update (3) on the grounds of misdiagnosis. The proposition that error in diagnosis can be quite important in a study in which the numbers involved are small is clearly applicable to the work of Professor Axelson. The "other exposures*1 of the workers involved in the analysis, the reanalysis and the update were unknown (3)- In this regard the update expressely stated that: "It should be made clear that the recognized exposure have been mixed with other unknown exposures; unfortunately there is no possibility of sub-dividing the material in this regard" (3). �- 25 - The Royal Commission observed in relation to Professor Axel son's work that: "It was carried out by untrained and inexperienced people; there was no protocol; it was based on a cohort, the selection of which was completely outside the control and supervision of those conducting study; no responsibility for the accuracy of the exposure data was accepted; those conducting the work used data the accuracy of which they themselves doubted; the data on which the work was based were inaccurate"; and then conluded that: "(a) it was carried out by untrained and inexperienced people; (b) there was no proper protocol; (c) exposure data were obtained in a climate of considerable controversy about the very subject of the study; (d) the questionnaires distributed made apparent to the subjects the purpose of the information sought; (e) in a number of cases the data relating to exposure were little more than a guess; (f) persons who were counted as having been exposed to phenoxy acids may not have any such exposure; (g) the number and extent of confounding factors was unknown; (h) there was inaccuracy in diagnosis data." 4.- Weakness of the conclusions The three conclusions reached by Professor Axelson in relation �- 26 - to the effects of phenoxy herbicide exposure are different. The first is negative. The second raises a fairly nebulous possibility if a particular assumption as to exposure is adopted. The third is dependent on small numbers, involves a lack of specificity and the accuracy of the exposure data is questionable. On their own these considerations would be adequate to justify the conclusion that Professor Axel son's work does not make any real contribution in relation to the problem of whether there is an association between exposure to phenoxy herbicides and the incidence of cancer. But such considerations do not stand alone. There are other factors within Professor Axelson's material which support the conclusion just expressed. In his first analysis Professor Axelson used a maximum latency pariod of 5 year. In his later analysis he changed the latency period to 10 years so as to bring it "more in line with standard epidemiological approaches". Such a period "seemed to be a reasonable latency or induction period" according to Professor Axelson. After being questionned at length Professor Axelson agreed that if he had adopted the same latency period in his first analysis as he had in the update, the total number of tumors observed in the cohort said to have been exposed to �- 27 - phenoxy acids and combinations would be reduced from five (5) to three (3) viz. Cases 173, 328 and 388 - the only cases who had both the potential for exposure to phenoxy acids and combinations as well as the necessary minimum latency period. This reduced number of three (3) is to be compared with 2.83 expected: "And the relative risk then is 1.06 which is insignificant in any case." This conclusion would flow through to the re-analysis (2). When a minimum latency period of 10 years is adopted and the consumption data set out in Professor Axel son's publication are accepted as correct, the number of tumors observed in the so called "phenoxy acid" sub-cohort in the update is reduced to three (3) compared with 3.14 expected (1). The relative risk is then 0.95. Whilst the figure of 3.14 for the number of tumors expected would need some reduction, the extent of the reduction could not, according to Professor Axelson, be calculated from the data available. Although he was not able to agree that the adjustment would probably result in a figure of between 2.22 and 2.44 (Relative Risk of 1.35 and 1.22) such figures can fairly be derived from the data presented and are a reasonable indication of number of tumors to be expected. �- 28 - As can be seen from Table I there is only one instance (Case 328 \- cancer of the prostate) in which the first exposure occurred after 1963. TABLE I (*) Case first year of exposure No. assigned by Axelson 127 1957 172 1958 173 1958 268 1960 317 1958 328 1967 388 1961 113 1960 In the original analysis, the re-analysis and the update the numbers from which the relative risks for the subcohort said to have been exposed to phenoxy acids and combinations were calculated are small and the existence of an excess depends (*) From Reference No. 1 �- 29 - entirely on the classification as to exposure which is assigned to given cases. However, as the Royal Commission found, "the exposure data are inadequate, unreliable and non-specific" Its final word in relation to the value of his work is worthy of note. The Royal Commission concluded that: "because of number of faults, together with the extent of uncertainty or error in the data, Professor Axelson's doubful positive conclusions * should be given little or no weight". Jr^ Lennart Ha.rdell The relevant studies undertaken by Dr. Lennart Hardell in relation to the effects of herbicide exposure on various populations in Sweden are as follows: 1) the North Sweden Study concerning the incidence of soft tissue sarcoma (X-^/12,1$, 11+, Js). 2) the South Sweden Study also concerning the incidence of soft tissue sarcoma 3) the Malignant Lymphoma Study 4) the Nasopharyngeal Cancer Study (19); �- 30 - 5) the Colon Cancer Study (I3>) which had as its essential purpose the verification of the conclusions in the studies referred to in paragraph (1), (2) and (3) above (2.0). Before undertaking his North Sweden study Dr. Hardell published the preliminary clinical observations which had caused him to undertake that study in North Sweden (2A}. These clinical observations had been made during the first three (3) months after he had gone to the Umea Regional Hospital in 1976. A like course was taken by him prior to undertaking his malignant lymphoma study (22). Since Dr. Hardell's studies constitute the main body of epidemiological evidence which supports an association between exposure of humans to phenoxy acids and an increased incidence of soft tissue sarcoma and malignant lymphoma they will be examined in some detail. However, as Judge Weinstein noted in his judgment of 8 May, 1985 in the Agent Orange Product Liability Litigation, Hardell's studies "were widely recognised as flawed" (Gibbs et al.y Dow et a!. U.S. District Court, Eastern District of New York MDL 381 at page 48). This statement by Judge Weinstein adopts the conclusion of Mr. Justice Nunn in the Nova Scotian case of Palmer & Ors v Stora Kopparbergs Bergslags Aktiebolag trading as Nova Scotia Industries £tl983j 60 Nova Scotia Reports (2d) 271) in which His Honour referred �- 31 - to the Harden studies as "unacceptable as proof of the results claimed" and found "that they cannot be taken at face value" (supra at page 352). 1) The Nort Sweden Study In August 1977 Dr. Hardell reported on clinical observations either made by him in his first three (3) months at the hospital or deduced from the earlier hospital records. These related to seven (7) initial and two (2) other instances of soft tissue sarcoma found amongst persons said to have been exposed to phenoxy herbicides during the 10 or 20 years preceding diagnosis and observed in the Oncological (Cancer) Centre at the Umea Regional Hospital between 1970 and 1976 (23). He treated the initial seven (7) of these cases as "a series1.1 In this first report (24) Dr. Hardell states that between 1970 and 1976 a total of 87 patients with malignant mesenchymal tumors (soft tissue sarcomas - STS) had attended the Umea Oncological Centre. Fifty five of these (68%) were men and of these 43 were still working. Nine (9) of the men who were still working were forestry workers, four (4) worked in agriculture and forestry and six (6) at saw mills or in the pulp industry - a total, of 19 or 42.2%. Such a mix of occupations is not surprising in view of the geographic situation of Umea in Sweden's North and extent to which �- 32 - forestry, activities associated with forestry and, to a lesser extent, agricultural pursuits are undertaken in the region , In the report of his clinical observations concerning the seven (7) initial cases Dr. Hardell states that "the exposure was quite massive in all cases" (21) and that the exposure of five (5) of them was "direct" (2.1). In his North Sweden study these seven (7) initial cases are described as "a series of patients with soft tissue sarcomas and massive exposure to phenoxy acids" (2lj). Examination of the histories of these patients as ascertained by Dr. Hardell shows that these statements are far from accurate. His use of the word "massive" in fact reveals a good deal about his approach to exposure data as also, perhaps, does the form of his editing of the case histories of the seven (7) cases extracted from the hospital records. Case I had sprayed with 2,4,5-T for barely one week in 1963 and 1964, two weeks in 1965, one month in 1966, one month in 1967 and 2 weeks in 1968. He was diagnosed as suffering from STS in 1976. Adopting, as both Professor Axelson and Dr. Hardell did, a minimum latency period of ten years the relevant exposure for Case I should be taken as that arising from something less than three weeks of herbicides spraying. The longer the latency �- 33 - period adopted the less the relevant exposure, falling into nil if 15 years is adopted. Case 2 sprayed for 3 weeks in each of three or four summers during the 1950's and 1960. He was diagnosed as suffering from STS in 1976. Thus his exposure was a maximum of twelve weeks spread over twenty years. Case 3 was diagnosed as suffering from STS in 1976. His only association with herbicides was that "thousand of litres of phenoxy acid" were stored for about eleven months each year in the workshop in which he was employed. Some of these had been "stored partly in open containers" so that he could smell the material and it is stated that he "had also handled the preparation". In what circumstances or for what period the containers were left open (e.g. whether this was only when they were being handled), the extent and manner of handling of "the preparation" (singular) by the patient, what "the preparation" handled was or what the "phenoxy acids" (plural) were is not revealed. Similarly whether or not the man was wearing gloves or other protective clothing when he handled herbicide is not stated' in the report and remains unknown. Such an absence of detail itself suggests that there was no great extent of exposure. Since Dr. Hardell saw his patient and appears to have taken a part in his extended treatment the data must have been known to �- 34 - Dr. Hardell and, if substantial, surely would have been revealed by him either in one of his publications or in the course of his evidence to the various tribunals before which he has testified. This has never been done, indeed Dr. Hardell was unable to supply any further details about these relevant matters although he was expressly afforded such an opportunity. However it is known, that case No. 3 never sprayed and that this case was classified as unexposed when Dr. Hardell undertook his North Sweden study (24). Case 4 was exposed to unspecific phenoxy acids for about twenty days per annum in the years between 1961 and 1966. As the date of his diagnosis is not stated, the precise extent of his relevant exposure cannot be calculated. However, taking the date of Dr. Hardell's observations (i.e. 1976) as the latest date of diagnosis, the maximum relevant period would appear to be low. If 15 years is adopted as the latency period the relevant exposure of this case falls to nil. Case 5 was exposed to herbicides for a total of six weeks in 1945 and 1946. The nature of those herbicides is not revealed but having regard to the fact that 2,4-D and 2,4,5-T were introduced into Sweden after 1950 it is improbable that such early exposure would have involved phenoxy acids, Case 5 did spray phenoxy �- 35 - acids for two weeks in each of the years 1960 to 1968. He was diagnosed as suffering from STS in 1974. Adopting a latency period of ten years, his relevant exposure is that arising from a maximum of eight weeks spraying spread over four years. His relevant exposure falls to nil if a latency period of 15 years (or more) is adopted. Case 6 was diagnosed in 1972 as having STS. The only evidence that he had any exposure was that "over 4-5 summers in the fifties... he cut and removed grass along the verges sprayed by the Highway Department" and that "he had worked and lived in forests sprayed with phenoxy acids" (2-1). In Dr. Hardell's report of this case neither the relationship between the time of cutting of the grass and the time of herbicide spraying nor the actual herbicide/s involved is revealed. However, it is unlikely that 2,4,5-T would have been used for grass killing since it is unsuitable for such a purpose. It is used for trees and for woody, tree-like growth. It is also inherently improbable that the grass would have been cut before such herbicide sprays as had been used would have had time to take effect. There is no point in spraying herbicide on grass an4 then immediately cutting the grass. This conclusion was accepted by Dr. Harden, �- 36 - Dr. Hardell also admitted that as far as the possibility of exposure of this man as a result of having lived and worked in the forest was concerned, he did not know the relationship between his place of residence and the location where spraying occurred, or the relationship between the time of spraying and when he worked in the forest. Nor did Dr. Hardell have any data as the whether the case was ever actually been in contact with the substances which had been sprayed or as to when and how often the spraying had occurred. In addition there was nothing to indicate that the man in question had carried out spraying himself, indeed it was not suggested that he had ever done so. Case 7 was diagnosed as having STS in 1970. However symptoms had been manifest in mid-1969. His only association with phenoxy acids was that he "had worked in forests up to 1970" (21) where "he carried out thinningin the phenoxy acids prayed areas from 1956 to the beginning of the 1960's (21). Whilst it is hardly likely that he would have been carrying out thinning immediately after spraying had taken place, the report is silent about any such temporal association and Dr. Hardell was unable to provide any further information on this subject in the course of his evidence before the Royal Commission. The only other possible source of exposure for this patient was that he had worked "in conjuction with spraying a few years later" (21). What this involved remains �- 37 - obscure as does the description of the spray or sprays used. There may in fact have been no exposure whatsoever. However, deficient as it is, the information set out above in relation to this man was agreed by Dr. Hardell to be "... a fair summary of the total information you were able to get about exposure of this man". Once again, if a 15 years latency period is adopted, this man would have no relevant exposure. From the foregoing it can be seen that it is doubtful whether there was any exposure of Cases 3,6 and 7 and that, insofar as there may have been any exposure at all, it was minimal at most. If a latency period of 15 years is adopted then Cases 1, 4 and 5 would also be excluded because of absence of relevant exposure. Dr. Hardell's description of the extent of exposure of the cases include in the series as "massive" and "quite massive" was found by the Royal Commission to be both "inaccurate" and "highly emotive". It is the language of the advocate rather than the language of the detached scientist. In his role as advocate Dr. Hardell manifested a readiness to adapt his evidence in the light of cross-examination. His description of the exposure of the initial seven (7) cases referred to in his clinical observations (21), the special meaning �- 38 - he ascribed to the word "massive" in his Agent Orange deposition, his realization in the course of giving evidence that this created problems for him and his change in position when it was clearly demonstrated that he had been inaccurate in his description of the extent of exposure, all demonstrate his approach. A ban on the use of 2,4,5-T was imposed in Sweden (25) in or about April 1977. This was done for reasons which were political rather than scientific. At that time phenoxy herbicides were the subject of intense debate and there was grave concern amounting to alarm about 2,4,5-T (25), indeed so great was the intensity of the controversy in the North of Sweden that it led to accusations that an academic from the Umea area, Professor Rappe, was a liar because he defended the use of Hormoslyr, one of the constituents of which was 2,4,5-T (2S). It was against such a background that Dr. Hardell's clinical observations were published. With the active co-operation of Of, Hardell they received widespread publicity (2&). He gave a number of newspaper and radio interviews and also appeared on television ( ) . He was increasingly identified in local and other £) media as involved in the scientific work which was seeking to link specific cancer types with the use of phenoxy herbicides (29). �- 39 - He became a prominent figure of the then current controversy. (25,26,27,28,29,30). The publicity which he and his clinical observations received and the extent to which he was identified with the controversy concerning phenoxy herbicides are relevant in relation to the problem of information bias in his studies. Because of the extent and heat of the controversy which surrounded the use of phenoxy herbicides in Sweden, information bias was always likely to be a problem, however,thi's problem was accentuated by Dr. Hardell's involvement and prominence in 4n£- controversy. Thus a climate which was already unsuitable for epidemiological research in relation to the possible association between phenoxy herbicides and cancer was made even worse by Dr. Hardell's actions. Indeed, it was admitted by him that at the material time there were "very few topics in the environmental debate... discussed as much as phenoxy acids. The debate was concerned with both the possible carcinogenic properties and the teratogenic properties" (24). �- 40 - Dr Harden recognized that in a climate which was already conductive to information bias "it would be most undesirable for a researcher who was going to undertake a study to do anything that would exacerbate or make worse the situation which existed at that time". However that is precisely what he did. Not only did he give newspaper interviews, appear on radio and television and pose for photographs, he also took part in public meetings and generally ensured that his work was put before the Swedish public. A number of criticisms of Dr. Hardell's studies have been advanced!. These include: 1) the inclusion within the studies of • the data which generated the hypothesis which the studies were intended to test; 2) information bias as a result of: a) selective recall by the cases because of the prevailing publicity and other factors including a preliminary phone call from Dr. Hardell; b) a difference in the completeness of the histories of exposure s of cases when compared with those of controls; c) interviewer bias arising out of the fact that the interviewers knew the purpose of the various studies; 3) inadequate and unsatisfactory exposure data; 4) methological problems arising from: �- 41 - a) the inadequacy of the instructions for the telephone interviewer; b) the form of the questionnaires which required only "Yes" of "No" answers and gave no opportunity for a "Don't know" reply or for explanations (25, 30, 31). c) the use of the Oncological Centre's letterhead and the requirement that the questionnaire be returned to the Centre at Umea: 5) the linking by the results of 12 different histological types of sarcoma with exposure -- a unique and improbable situation, the previous highest link being three (3) sites in human (See Palmer & Qrs v Stora Kopparbergs Bergs lags Aktiebolag at page 307) ; 6) the presence of confounding factors for which no adjustment was, or could on the available data be made. After a lengthy and careful examination of the evidence the Royal Commission concluded that "each of these criticisms is validly applied to Dr. Hardell's North Sweden Study and most of them also apply to his later studies". Dr. Hardell 1 s North Sweden Study was a case control study of 52 male patients aged from 26 to 80 years. Each had been diagnosed as suffering from soft tissue sarcoma and all had been treated at the Umea Oncological Centre between 1970 and 1977. Each case was matched for sex, age and town of residence with four (4) controls. Dr. Hardell then contacted all subjects by �- 42 - telephone. This was followed by a letter and a printed questionnaire (32,33). The letter was signed by Dr. Hardell and was on the letterhead of the Umea Onclogical Canter (24). The questionnaire was headed "Umea Regional Hospital Oncological Centre" (33). North Sweden is a fairly sparsely populated area and although Umea is a relatively small place (80-90.000 people) it is a centre for the north. Its hospital is a specialist hospital dealing with cancer and is the only such hospital in the north of Sweden. All soft tissue sarcomas would be referred to it and so its cancer section would be well known to the people of the region. Although a proper application of the principles of epidemiology requires that hypothesis generating data and hypothesis testing data be kept separate, Dr. Harden included the hypothesis generating cases in his North Sweden Study. There were 13 patients with soft tissue sarcoma included in the Study as exposed cases. At least six (6) of these were drawn from the seven (7) initial cases in the hypothesis generating material referred to in Dr. Hardell's clinical observations (21). The number drawn from the hypothesis generating data and included amongst the exposed cases in the study may well havebeen as high as eight (8) from the nine (9) cases referred to in his published clinical observations (21). �- 43 - Of the initial seven (7) cases who were clearly included in the Study onl} one (1), namely Case 3, was treated as unexposed. Thus six (6) out of 13 of the exposed cases, and possibly as many as eight (8) of such cases, were derived from the hypothesis generating data. In view of this the Royal Commision found that: "The first criticism of Dr. Hardell's studies is clearly justified in re]ation to the North Sweden Study". In addition to the publicity which preceded Dr. Hardell's North Sweden Study and his prominence in the debate which was then raging about phenoxy herbicides; every case "had already been if treated in the Department of Oncology at the University of Uinea, so the fact that the letter accompanies the questionnaire as well as the questionnaire itself were linked with the Oncological Centre at Umea is highly material. The questionnaire: a) specifically referred to Hormoslyr in question 10, 14 and 28; b) included seven (7) questions out of a total of 31 which were either concerned with the spraying of herbicide a herbicide; nominated �- 44 - c) contained 20 questions which expressely referred to exposure to some form of chemical or chemicals; d) included as its remaining questions, eight (8) which were concerned only with occupation or place o-f work, one (1) which dealt with medical details, one (1) which asked about cigarettes and one (1) at the end of the questionnaire, namely question V, which gave the subject an opportunity to add any "additional information", i An examination of the questionnaire clearly shows that its major concern was with exposure to chemicals, the emphasis being on herbicides, particularly Hormosylr (2,4,5-T). In the context of the then current controversy about 2,4,5-T the subject matter of the inquiry by Dr. Hardell would have been patent to anyone who received the letter and questionnaire and even more obvious to those who had been treated at the Onclogical Centre at Umea. Having regard to all these considerations it is perhaps not surprising that Dr. Hardell finally agreed that: "there could be a recall bias which probably is in our study" and that the Royal Commission decided that : "clearly information bias taints the study..." �- 45 - The question of exposure to phenoxy herbicides had been expressly raised with each of the patients referred to in the clinical observations (21) and the diagnosis of cancer and its associations with the patient's history of exposure discussed in detail with the patient. In taking the history the connection between the patient's cancer and its exposure to phenoxy herbicides was said to have been "probed". At least one of those initial cases "spontaneously told me (i.e. Dr. Harden) about his work as a forestry man and that he constantly talked about spraying within the occupation". No such probing or volunteering of association can be found in relation to the controls. Each questionnaire revealed the name of the relevant patient when it went out. Numbers were assigned to the cases only after interviews had taken place. The telephone interviewer (Miss Damber) had no written instructions in respect of the interview and Dr. Harden had no direct knowledge of her mode of questionning. It appears that she was not experienced in such studies. The exposure data relating to the cases included in the story were described by the Royal Commission as "both unsatifactory and inadequate". In the first instance the statement about exposure contained in the study says that: "Exposure to phenoxy �- 46 - acids of chlorophenol was admitted by 36.5% of the patient group..." (24). However, the words "phenoxy herbicides do not appear in the questionnaire. For the purposes of the Study exposure was defined by Dr. Hardell as including "working in a freshly sprayed moist area". However, whether a person had worked in such an area of1 had "wet contact" was not asked in the questionnaire (24). The only question which touched upon this subject was question 14 that asked whether a person had "worked in treated area". However Dr. Harden conceded that the answer to this question did not inform as to whether the area had been sprayed five minutes, five days or five months before the exposure had occurred. It is clear from the use of the seven (7) original cases referred to in the clinical observations (21) that no uniform approach to exposure was maintained (e.g. see above regarding Cases 6 and 7 in the clinical observations). In addition Dr. Hardell said that questionnaires were sent to the employers of all those cases and controls who had been working in forestry i.e. 50 persons in total (16) and "we could only get answers from twenty persons since c'ne employers did not keep the records". As a result the information was regarded by Dr. Hardell as "weak data and nothing I can set up on a scientific basis and argue about". �- 47 - Some of the data on which the North Swedish Study is based are included in a paper which was published in 1979 (l6). This paper is very revealing since the additional data relating to exposure and the substances involved can be analysed to some extent. It is not possible, however, to relate the numbers assigned to the cases in that publication with those assigned in Dr. Hardell's clinical observations (21). Dr. Hardell was unable to do this when he gave evidence and, although the material was going to be forwarded by him to the Royal Commission, it was not forthcoming. What is known is that at least six (6) of the original seven (7) cases and possibly as many as eight (8) of the initial nine (9) cases observed by Dr. Hardell were included as exposed cases in the North Sweden Study. The North Sweden Study contains details relating to the 13 soft tissue sarcoma cases who are said to have been exposed to phenoxyacetic acids, It. is worthwhile looking in more detail at six of these cases, namely Cases 160, 180, 390, 490, 510 and 520. In cross-examination it emerged that Case 390 had only two (2) days of exposure at some time between nine (9) and 19 years prior to diagnosis. This occurred while he was mist blowing with a chemical the nature of which was undefined but was perhaps 2,4-D. �- 48 - 2,4-D does not contain 2,3,7,8-TCDD. Case 160 was stated in the Study to have seven (7) days exposure 19 years prior to diagnosis. However, it emerged that the only information available about the exposure of this case was that he had worked as a supervisor and whilst so working he had either sprayed the material himself or had got it on himself or on his clothes. It should be noted that if only two (2) cases had been wrongly included in this sample the findings would not be statistically significant, i.e. the result depends on a claimed excess of only two (2) soft tissue sarcomas. Cases 390 and 160 could properly be treated as unexposed. In addition it is worthwhile looking at some of the cases who were included in the Study and to examine their latency periods: 1.- Case 180 was said to have had seven (7) days of exposure to MCPA alone at some time between 13 and 15 years before the study. MCPA does not contain 2,3,7,8-TCDD. 2.- Case 490 had a latency of between five (5) and 10 years. 3.- Case 510 had an exposure of five (5) months "somewhere between 3 and 9 years before the date of diagnosis". The maximum latency period for this case was thus nine (9) years, a period saic| to be "improbably short". �- 49 - 4.- Case 520 had a latency period which was between eight (8)and - 12 years, Thus in relation to the 13 "exposed" cases included in the Study the Royal Commission pointed out that: a)"at least six (6) and perhaps as many as eight (8) formed part of the hypothesis generating data; b) three (3) had either doubtful or minimal exposure; c) one (1) had a clearly inadequate latency and another one (1) of even two (2) had a latency period which was barely adequate." Dr. Hardell did not dispute that of the 13 cases included as many as eight of them could be cases he had referred to in his clinical observation and that in two (2) cases (Case 490 and 510) had a latency period significantly less than that usually attributed to soft tissue sarcoma and the same is probably true for Case 520. Thus even adopting a 10 years latency period, 10 or even 11 of the 13 cases could properly be excluded on grounds of wrong classification or as irrelevant to the question of causation. Looking at a best case (from Dr. Hardell's point of view) exclusions would not be fewer than: - six (6) because they formed part of the hypothesis generating data; �- 50 - - one (1) because of no real evidence of exposure to phenoxy herbicides; - one (1) with a latency period which was clearly inadequate. There are then only five (5) cases remaining if a 10 years latency period is adopted and fewer if a 15 year period is adopted. Five (5) cases would not give rise to a result which was statistically significant. If the proper principles of epidemiology were applied and the initial 7 (7) cases referred to in the clinical observations (2j) were excluded from the Study it was admitted by Dr. Hardell that the relative risk would fall "to something just below 3'! Dr. Hardell did not have material from which the precise figure could be calculated. However he offered to forward copies of relevant data to the Royal Commission. This was not done so his claim has not been able to be verified. The above reduction in the relative risk is achieved by eliminating only one (1) of the sources of error in the Study, namely the inclusion in the study of the hypothesis generating data. However, even the reduced figure is still influenced by the effects of subject recall bias, interviewer bias and the presence of confounding factors for which no adjustement has been made in the Study. �- 51 - Another matter which is worthy of note is that exposure to phenoxyacetic acids alone cannot be determined although Dr. Harden asserted in the report of his study that he had analysed "exposure to phenoxy acids alone" (24), and obtained a relative risk of 5.3 in relation to such exposure. It is apparent both from the Study itself and from Dr. Hardell's oral testimony that no such analysis was done. The study states that: "It is impossible... to assess the effects of the individual chemical substances separately since practically all patients may have been exposed to chlorinated dioxins as well, including tetrachlorodibenzodioxin (TCDD)... and also to other compounds" (24). In that part of Dr. Hardell's publication in which the results of the so-called analysis of "exposure to phenoxy acids alone" are set out (24) persons who had also been.-exposed to chlorophenols are included. In this context it should be remembered that Dr. Hardell claims that exposure to chlorophenols is associated with a relative risk for soft tissue sarcoma of 6.6, so such exposure constitutes a confounding factor of importance. Yet another consideration which is relevant to the accuracy or adequacy of the exposure data on which the study is based is the unsuccessful attempt to verify exposure to particular substances with employers, the results of which were: "uncertain �- 52 - and difficult to evaluate. Records of individual working manuals had not been kept, and the answers were mainly based upon reminescence. Replies from the employers were obtained for 20/50 persons involved" (14). Thus the exposure data for the 13 cases said to have been exposed to phenoxyacetic acids alone depend very much on the outcome of the interviews for which there were no written instructions and which were carried out by a lady who had had no a prior experience whatsoever in conducting interviews for epidemiological studies. An examination of the effect of interview on rejection of study subjects and on relative risk assessement (see Tables II and III below) reveals that the relative risk of the cases when compared with controls more that doubled after interview. There is also a marked disparity in the effect of interview on the percentage of controls rejected when compared with cases - nearly 4:1. Thus not only is there justification for the criticisms which assert that the circumstances gave rise to the possibility of interviewer bias, but Dr. Hardell's own later analyses provide material which, the Royal Commssion found "suggests that this, in fact occurred". All cases were given the suffix 0. Controls were given suffixes of 1, 2, 3 or 4. The consequence was that those classifying the subjects in the study "knew just by lookina whether a person was a case or a control" - yet another avenue for information bias. �- 53 - A preliminary classification of the subjects was carried out by Or. Hardell and his assistant and then discussed with others. These included Professor Axel son. The classifying process was carried out with knowledge of the numbers which had been assigned to the subjects who were to be classified, so "there was no question as to classification being blind" For some deceased subjects that fact that their next of kin who washed their clothing said that the clothes of the deceased smelt was sufficient to result in them being classified as exposed, The Study itself admits the presence of a number of confounding factors such as: diesel oil - about which there was insufficient information for a proper evaluation, and other pesticides - about which no information was available (\fc). It is relevant to the problem of confounding to note that Dr. Hardell conceded that none of the 13 exposed cases of soft tissue sarcoma in the study were exposed to phenoxyacetic acids alone. One of the 13 had high grade of exposure to chlorophenols and Dr. Hardell was unable to say how many had been exposed to organic solvents, but he conceded that a number had been and that no calculation whatsoever could be made about the effect of organic �- 54 - solvents because no data were available on them. It is interesting to note the limited conclusion to which Dr. Hardell came as a result of his North Sweden Study. These are set out in the Royal Commission Report. The Royal Commission noted these, commented upon the fact that Dr. Hardell was influenced by an anxiety to prove the integrity of his study and concluded that: "The North Sweden Study is open to criticism and... that is is rightly regarded as flawed and unacceptable as proof of the result claimed". 2.- The South Sweden Study Following the completion of his North Sweden Study, Dr. Hardell undertook an investigation into "the potential effects of MCPA, 2,4-D and the analogous phenoxy propionic acids" all of which were widely used in agriculture in the southern areas o£ Sweden (16) The study was commenced in February 1979 and;as in the case of the North Sweden Study, the data gathering took place in the spring, with the telephone interviews for this particular study ben conducted in May/June 1978. The study involved 110 patients diagnosed between 1974 and 1978 as suffering from 12 different types of soft tissue sarcoma (16). These were matched with 219 controls. �- 55 - The gathering of exposure data involved advance contact with people by telephone, then sending them a nine page questionnaire and later supplementing the information derived from the responses by means of selective telephone interviews of these respondents who had worked in agriculture, forestry or horticulture during the relevant period. In some instances (unspecified) the interviewer also contacted employers, neighbours and others "to elucidate possible exposure" (16). Exposure to phenoxy acids of less that one day was not considered nor was exposure within five (5) years before the year of diagnosis i.e. a latency period of only five (5) years was adopted. As an aside it is worth referring to the Swedish railway workers dealt with in thi's'Study - in relation to whom it is stated that: "the embankments of the Swedish State Railways have been sprayed mainly with amitrol, but pesticides including phenoxy acids have also been used. It is not possible to determine completely all the substances to which individuals had been exposed, despite contact with the people themselves, their workmates, or their employers. Therefore, railway workers who reported exposure to pesticides were regarded as unexposed to phenoxy acids". (16). This is to be contrasted with the approach adopted by Professor Axelson in his Study (A). �- 56 - Eighty five (85) of the 100 cases (i.e. 77,3%) were not exposed to any phenoxy acids of chlorophenols. Of the remaining 25, seven (7) are said to have been exposed to phenoxy acids other than 2,4,5-T and 11 to chlorophenols alone. This left only seven (7) cases who were exposed to 2,4,5-T as well as to other phenoxy acids and other known and unknown chemical substances, included amongstmwhich were organic solvents. Based upon these seven (7) cases and one control Dr. Harden calculated the point estimate of the relative risk of exposure to 2,4,5-T and other phenoxy acids as 17.0 (16). The Royal Commission regarded this as "an extraordinary figure" and "so far out of step as to lack credibility". Relative risks in the South Sweden Study (16) were stated to be as follows: - exposure to phenoxy acids or chlorophenosl: 53; - exposure to all phenoxy acetic acids: 6.8; - exposure to all phenoxy acetic acids excluding 2,4,5-T: 4.2; - exposure to chlorophenols alone: 3.3. An examination of a different print of South Sweden Study (15) is revealing. It includes material which does not appear in versions of the same study published elsewhere (11 - 16). �- 57 - In the publication under examination (15) Dr. Hardell concedes that "when exposure data are collected via questionnaires and interviews a certain possibility exists that the cases will have a greater interest in the questions than the healthy controls do". This concession is not included in later published versions of the Study. Also, for a reason which is unexplained, the results reported in the two versions differ. Thus in Table 6 to reference 15 the relative risk amongst agriculture/ forestry workers exposed to phenoxy acids is calculated at 6.4 based upon 13 cases and five (5) controls. On the same data i.e. 13 cases and five (5) controls, a relative risk of 5.7 is reported in Table 7 of reference 16. The very conclusion of the study would seem to reflect a concern, even a reservation, on the part of Dr. Hardell about the accuracy of the results because, despite the high relative risk reported, the conclusion is expressed in very guarded terms: "this investigation has indicated that exposure to phenoxy acids and chlorophenols might constitute a risk factor in the development of soft tissue sarcomas" (13). Except for the fact that no hypothesis generating data were included in the South Sweden Study, the problems with and criticisms which can be levelled at it are similar to those dealt with in relation to the North Sweden Study. In addition, �- 58 - the media publicity which the North Sweden Study attracted in Sweden is likely to have accentuated the problem of information bias. Having examined the South Sweden Study and the author's testimony about it, the Royal Commision was of the view that the study "has properly been widely regarded as flawed, unacceptable as proof of the results claimed and such that it cannot be taken at face value" 3.- The Maiignant Lymphoma Study In January 1979 Dr. Hardell published his preliminary clinical findings relating to 17 male patients who were suffering from malignant lymphoma (2*2.). As a result of the findings he undertook his third study, the Malignant Lymphoma Study. In it Dr. Hardell deals with 169 patients aged between 25 and 85 who were diagnosed in the period from 1974 to 1978 . <«» &u$Wr«£ from either Hodgkin's Disease or non-Hodgkin's lymphoma. The cases included the 17 patients referred to in the preliminary findings who formed the group from which the hypothesis to be tested was generatepf(22), Cases were matched for sex, age, place of residence and year of death with a total of 338 controls. �- 59 - Information about exposure to various chemicals including organic solvents, chlorophenols and phenoxy acetic acids was obtained by questionnaire. However, there were severe problems about identifying the substances to which any individual had been exposed. Indeed Dr. HardeH conceded in cross-examination that he could not present any separation of figures which showed the number of cases exposed to phenoxy acid alone. On Dr. Harden's analysis of the data the relative risk for exposure to phenoxy acetic acids or chlorophenols was 6.0', to phenoxy acetic acids 4.8 and to chlorophenols 4.6 (18). However, in view of the concession-above it is difficult to understand how the relative risk of 4.8 was calculated, or to know what it really means. A fivefold increased risk of malignant lymphoma was found for those exposed to phenoxy herbicides and chlorophenols. The increased risk for those with high grade exposure to chlorophenols was eightfold and threefold for those with low grade of exposure . An increased risk was also found for those exposed to organic solvents. The study did not reveal any difference between the risk of Hodgin's Disease and non-Hodgkin's lymphoma despite the fact �- 60 - that Hodgkin's Disease seems to occur in two peaks, one affecting the young and one affecting the old and there is thought to be some viral; association in the etiology of Hodgkin's Disease, at least as far as the younger group is concerned. Whilst the etiologies of Hodgkin's Disease and non-Hodgkin's lymphoma appear to be different, Dr. Hardell (18) does not differentiate between the two. He groups them together and, in addition, includes lymphomas which are unclassifiable. At page 10 of reference 18 it is stated that "exposure to phenoxy acid was analysed separately excluding all persons who had high grade exposure to chlorophenols". However, this is just not correct, because Dr. Harden agreed in crossexamination that a number of them may have been exposed to low grade chlorophenol and five (5) of them had been exposed to high grade chlorophenol. Table 3 to reference 18 had a heading which was held by the Royal Commission to be "inaccurate and misleading". It reported on cases and controls exposed to phenoxy acids after those exposed to chlorophenols were excluded. However a number of the persons included in the Table had low grade exposure to chlorophenols and five (5) had high grade exposure. �- 61 - Thus the relevant data is not looking at those cases which were exposed only to chlorophenols. It includes cases who were exposed to phenoxy acids, fourteen (14) who were exposed to a low level of chlorophenols and five (5) instances of exposure to a high level of chlorophenols. Dr. Hardell was also asked about the subdivision of cases as reported in label 5 to reference 18 . That table is headed "Exposure to organic solvents in cases and controls after matching was dissolved and those exposed to phenoxy acids (F) or with high grade exposure to chlorophenols (K) were excluded, assuming there was no joint exposure". Exposure to organic solvents was characterized as low grade (1) and high grade (2). In Table 5 there are 23 cases who had both phenoxy acid exposure and high grade chlorophenol exposure. Dr. Hardell could not say how many cases were exposed just to phenoxy acids and nothing else. This was despite the fact that Dr. Hardell "set out in this paper to examine the relationship between phenoxy acid exposure and lymphoma". In addition, he did not publish a figure in respect of phenoxy acid exposure alone. He said in his testimony that he had carried out such an analysis but that he had no submitted it for publication. The result was not produced to the Royal Commission although Dr. Hardell was afforded an opportunity to do so. His published conclusion �- 62 - namely: "The present investigation... suggests... that exposure to organic solvents, chlorophenoly and/or phenoxy acids constitutes a risk factor for the incidence of malignant lymphoma", certainly gives no scientific support for the proposition that phenoxy acetic acids cause malignant lymphoma. It can thus be seen that not only is the Study misleading in the form in which some of its data are presented but there are also very serious, multiple confounding factors which have not (and cannot) be adjusted for. The Study is also subject to the same criticisms as the North Sweden Study, including the fact that hypothesis generating data were used in it. No one has been able to replicate the findings in Dr. Harden's studies relating to soft tissue sarcoma and malignant lymphoma and the results of his three studies are contrary to the findings obtained by others. This absence of replication, the absence of specific outcome (i.e. 12 types of soft tissue sarcoma, non Hodgkin's malignant lymphoma and Hodgkin's Disease), admitted information bias, the presence of significant confounding factors which are not adjusted for, the unrealibility of the exposure data and the other factors detailed above led the Royal Commission to conclude that "the statistical associations asserted by Dr. Hardell are suspect" and that it could not "accept them as �- 63 - supporting an inference of causal connection between soft tissue sarcoma, malignant lymphoma and exposure to phenoxy herbicides". 4.- The Nasopharyngeal Cancer Study In 1981-82 in conduction, inter alia with Professor Axelson, Dr. Hardell undertook a case-control study of nasal and nasopharyngeal cancer and their relation to phenoxy acid or chlorophenol exposure. The Study (('•J) dealt with 71 patients (being 44 cases of nasal cancer and 27 of nasopharyngeal cancer) who were aged between 25 and 85 years, who had been reported to the Swedish Cancer Registry in the years 1970-1979 and who were resident in the three most northern counties of Sweden at the time of diagnosis. These cases were matched with 541 controls. A questionnaire which was identical with that used in previous studies was sent to the cases, or the next-of-kin of deceased cases. It is claimed by Dr. Hardell that the Study in question "follows the methodological design" of the previous studies undertaken by him. The controls had been used in earlier studies in North Sweden, but no further contact was made with them for the purposes of this Study. On analysis of the data "no significant association was found" between the cancers of interest and phenoxy herbicides �- 64 - Dr. Hardell claimed that this Study could be used as a verification of previous studies. However, despite the assertion that this and previous studies used the same procedures, there are a number of differences between the procedures for the Nasopharyngeal Cancer Study and those used in Dr. Hardell 's earlier studies. In the Nasopharyngeal Cancer Study: a) no contact was made by telephone with the cases before they received the questionnaire; b) there was no publicity linking phenoxy herbicides and nasal cancer at the time the study was undertaken and the debate about phenoxy herbicides had no doubt abated with the banning of 2,4,5-T in 1977; c) no hypothesis generating cases were included amongst the cases examined in the Study; d) the interviewer who made telephone contact with the cases was "blind", since the questionnaires for this study were mixed with identical questionnaires from the Colon Cancer Study The existence of differences in the procedures adopted for this Study means that it cannot be used as a verification of the earlier studies. The fact that a negative result was obtained in relation to exposure to phenoxy herbicides may even be �- 65 - regarded as further evidence supporting the criticisms advanced in respect of Dr. Hardell's first three (3) studies. It is also of interest to note that, contrary to what had been done by Professor Axelson in his study of Swedish Railway workers, employees of the Swedish Railways who were reported as exposed to pesticides: "were considered unexposed to phenoxy acids, since the type of preparation could not betstablished with certainty". In summary therefore it can be said that the Nasopharyngeal Cancer Study not only produces a negative result in relation to phenoxy herbicide exposure but it may even reinforce the criticisms of Dr. Hardell's earlier studies. 5.- The Colon Cancer Study The Colon Cancer Study (l2>) Involved 157 male colon cancer patients who had been extracted from the Swedish Cancer Registry and were resident in northern Sweden. Each was sent a questionnaire and interviewed. The group which had been used as a control group for the studies previously carried out by Dr. Hardell in relation to soft tissue sarcoma and malignant lymphoma was used as the control group for this �- 66 - study, but not further contact was made with the controls. The results show no difference in the incidence of colon cancer amongst those exposed to phenoxy acids and it is argued by Dr. Hardell that this verifies that there was no information bias in his earlies studies. There are, however, differences in the methodology for the Colon Cancer Study when compared with the earlier studies. For example the cases were not telephoned by Dr. Hardell before they receive a questionnaire,'the interviewer did not have knowledge either of the object of the Study or of the classification of patients (as the interviewer in the previous studies had) and there had been no publicity linking colon cancer with phenoxy herbicides. In the course of his testimony, Dr. Hardell was shown a document which had been produced by him in Washington in the 1980 EPA proceedings as a true analysis of his previous studies. This document shows that before interviews were conducted: - in the North Sweden Study, 28.8% of the 52 cases of soft tissue sarcoma (i.e. 15 cases) had originally been classified as exposed and 13.6% of the 206 controls (i.e. 28 controls) had been so classified; - in the South Sweden Study, 16.4% of the 110 cases of soft tissue sarcoma (i.e. 18 cases) had been classified as exposed and 4.6% of the 209 controls (i.e. 10 controls) had been so classified; �- 67 - - in the Malignant Lymphoma Study, 24,9% of the 169 cases of soft tissue sarcoma (i.e. 42 cases) had been classified as exposed and 11% of the 335 controls (i.e. 37 controls) had been so classified. After interview 13 cases and 14 controls classified as exposed remained in the North Sweden Study,. In the South Sweden Study 14 cases and a mere five (5) controls remained after interview. In the Malignant Lymphoma Stdy 41 cases remained after interview but only 24 controls. These results are set out in label II below. TABLE II EFFECT OF INTERVIEW ON REJECTION OF STUDY SUBJECTS North Sweden STS Study South Sweden STS Study Malignant Lymphoma Study Controls - Before Interview „„ 10 37 Controls - After Interview ,. 5 24 Reduction Cases - Before Interview Cases - After Interview Reduction Comparative) Effect of ) interview ) Controls ) v. ) Cases ) 50% 35% 50% 15 18 42 13 14 41 13% 3.8:1 22% 2.27:1 2.1% 16.66:1 �- 68 - The differential effect of the interview on cases and controls is both obvious and telling. At the very lowest, it "is at least suggestive of interviewer bias" as the Royal Commission put it. A comparison of documents tendered to the Royal Commission shows that the percentage of exposed cases in the Malignant Lymphoma Study in the former version is 24.9. However, in a later one it is shown as 27.2% (13). When this difference was pointed out to Dr. Hardell he said that this change had taken place after he had been cross-examined in the EPA proceedings and that the change was effected because he "must have overlooked some exposure (sic) ones which he had not noticed before". Dr Hardell then conceded that by changing that figure he had built up the relative risk from 2.7 to 3. That such a mistake should have had escaped not only him but also the four people who had gone through the data concerning the Malignant Lymphoma Study is curious to say the least. Dr. Hardell explained the difference by saying that "different criteria for exposure were discussed. The first part says all phenoxy acid exposure and that means exposure that has been notified somehow in the questionnaire or by interviews, but during the evolution of the exposure it has turned out that these people are not exposed". �- 69 - However, when pressed on his answer he admitted that this explanation was wrong since th,e document in question was dealing with information derived from questionnaires alone, unadjusted by any value judgements made in the assessement process and unaffected by the results of the interview i.e. not taking into account the effect of interview. When data derived from the questionnaires alone are used, a point estimate for the relative risk revealed by the study is 2.6 compared with 5.3 when the effects of ther interviews are taken into account. If for each of Dr. Hardell's first three (3) studies a comparison is made between the point estimates obtained using data from the questionnaire alone and the point estimates obtained when the effects of the interviews on the data are taken into account, the relative risks are: 2.6 for the North Sweden Study - compared with 5.3 as published; 4.1 for the South Sweden Study - compared with 6.8 as published; 2.7 for the Malignant Lymphoma Study - compared with 4.8 as published. If the data are changed in the way which a comparison of tendered documents reveals, the figures becomes 3 compared with 4.1 for the Malignant Lymphoma Study. �- 70 - TABLE III RELATIVE RISKS - EFFECT OF INTERVIEW North Sweden South Sweden STS Study STS Study Malignant Lymphoma Study RR* - Before Interview 2.6 4.1 2.7 RR - After Interview 5.3 6.8 4.8 Increase in RR following Interview 103.8% 65.8% 77.1 *Relative Risk (References 21, 34, 18, 20) When Dr. Hardell was cross examined on Table I of the Colon Cancer Study, the heading to which is "Exposure Frequencies to Phenoxy Acids", he conceded that these cases were not exposed only to phenoxy acids but some cases also had exposure to chlorophenols and organic solvents. At this point it is relevant to return to the 13 exposed cases of soft tissue sarcoma included in the North Sweeten Study. Dr. Hardell agreed that none of the cases were exposed to phenoxy acids only. One of them in fact had high grade chlorophenol exposure and there was an unknown number who had low grade chlorophenol exposure and whilst Dr. Hardell was unable �- 71 - to say how many were exposed to organic solvents, he agreed that some of them were. Although Dr. Hardell claimed that organic solvents had been / excluded from the analysis of the North Sweden Study (>M) when he was asked to clarify this he referred to a passage at page 715 of reference 12 . However, this passage makes no reference to organic solvents. When this was pointed out to Dr. Hardell he said they were included "with the emulsifiers which contain organic solvents In the end, however, he conceded that organic solvents had not been dealt with in the paper . It is also clear from Dr. Harden's cross-examination that the heading to Table IV in the North Sweden Study (11) is not accurate when it refers to exposure to "phenoxy acetic acids only" since the persons included under that heading were exposed to chlorophenols and to organic solvents as we!1. It is not possible to make any calculation about or allowance for the confounding effect of exposure to organic solvents. Dr. Hardell was then asked about information bias as a result of which response from the subject may be inaccurate and differ between case to control and he said that the existence �- 72 - Of a controversy and of publicity may have influence on the interviewer with consequent difference in classification of the cases. This interview could influence the result and lead to a distortion in the risk ratio. 5) Inconsistencies between Axelson and Hardell a) Hardell claims that there is an increased risk of soft tissue sarcoma and malignant lymphoma both of the Hodgkins and non-Hodgkins types from exposure to pehnoxy herbicides. In Axel son's work there were no cases of soft tissue sarcoma or of non-Hodgkin's lymphoma found and only one case of Hodgkin's Disease. b) It is claimed that Hardell's work indicates specificity in the type of tumor produced by phenoxy herbicide exposure namely, soft tissue sarcoma and malignant lymphoma. However, in his update Axelson concludes that: "no specific type of tumor can be considered as predominating". (3) c) Hardell asserts relative risks in excess of 4 for the association of cancer and phenoxy herbicide exposure. In Axelson's first analysis nis finding in relation to the "phenoxy acids and combination" subcohort wasqs. close to a negative as one can get. In his re-analysis, even when �- 73 - the exposure classification was changed for two (2) cases so as to produce an excess of tumors observed over those expected in the subcohort exposed to phenoxy acids and combinations, the relative risk was still only 1.6 and not statistically significant. In his update the relative risk when properly determined (i.e. with exclusion of wrong diagnoses, adoption of a ten years latency period and using the data detailed in Table I to reference 3> ) lies close to unit and is certainly not statistically significant. Thus far from supporting Dr. Hardell, Professor Axelson's work and his conclusions are different from and, destructive of Dr. Hardell's conclusions. The Axel son Technique Both Dr. Hardell and Professor Axel son sought to rely upon a mathematical calculation undertaken by Professor Axel son in an endeavour to demonstrate that the procedures adopted by Dr. Hardell in his early studies did not give rise to information bias (35, 36). Dr. Hardell was asked about the Axelson Technique and from his cross examination on this topic �- 74 - it emerged that the Axel son technique depends upon a number of assumptions: 1) both cases and controls will have like recall on the subject of exposure and such recall will be accurate; 2) the classification of workers into categories of agriculture and forestry (AF) on the one hand and other occupations (0) on the other hand is accurate; 3) there will be an equality of incidence in the soft tissue sarcoma amongst the unexposed members of the AF group and the 0 unexposed members of the group; 4) there is no other factor which operates in one group and does not operate in the other. It would seem that the technique assumes the result sought to be proved. Certainly, as Professor Allan Smith pointed out "there seems to be little basis for the assumption that there would be differential recall as between cases and controls". In addition Professor Smith stated that it is possible on a theoretical, i.e. mathematical basis "that diminution due to recall bias in the proper number of unexposed cases employed in agriculture or forestry could be compensated for and masked by an increased incidence of the disease amongst the workers in agriculture or forestry not exposed to phenoxy herbicides but exposed to other �- 75 - environmental factors prevalent in their industry". Professor Smith also expressed the view that there was "little value to be found in the application of the Axelson technique especially in relation to the South Sweden Study" and that such technique was "not a reliable indicator of the absence of recall bias in that Study". This view was accepted by the Royal Commission. CONCLUSION The conclusion of the Royal Commssion in relation to the Hardell studies is worth setting out verbatism since it is in marked contrast to the way in which one statutary agency in the United States has recently dealt with in the same studies: "...absence of replication, the absence of specific outcome (i.e. 12 types of soft tissue sarcoma, non-Hodgkin's malignant lymphoma and Hodgkin's Disease), admitted information bias, the presence of significant confounding factors, the unreliability 1 of the exposure data and the other factors detailed above all indicate that the statistical association asserted by Dr. Hardell are suspect. TheCommission cannot, on the balance of probability, accept them as supporting an inference of causal connection between soft tissue sarcoma, malignant lymphoma and exposure to phenoxy herbicides." �- 76 " . . . the Commission does not accept the Hardell studies as proving, on the balance of probabilities, any causal association between Soft Tissue Sarcoma and Lymphoma and exposure to 2,4-D, 2,4,5-T, and TCDD." The conclusion of the Australian Royal Commission in relation to the Hardell studies is congruent with the judicial conclusions reached in relation to those same studies in the United States in the Agent Orange Product Liability Litigation (Gibbs et al. versus Dow et al.: U.S. District Court, Eastern District of New York MDL 381/14; 1985, Weinstein C.J.) and in Canada in the forest spraying litigation (Palmer & Ors versus Stora Kopparbergs Bergslags Aktiebolag trading as Nova Scotia Industries, 1983, 60 Nova Scotia Reports, 2d, 271; Nunn J.). It is also significant that others have not confirmed Dr. Hardell's findings. The epidemiologic studies on soft tissue sarcoma and cancer risk among agricultural and forestry workers as well as factory workers with exposure to the relevant herbicides or their manufacturing processes which have been carried out in Sweden (42,43,44), in Finland T45, 46), in New Zealand (47,48,49,50,51), in the United States of America (52,53,54,55,56,57,58,59,60,61,62,63,64) and in the United Kingdom (65,66,67,68,69) have not confirmed Ilardell's results. The Hardell Studies should now be laid to rest. Perhaps an appropriate epitaph is that written by the eminent epidemiologist Sir Richard Doll, of Green College, Oxford. In a letter (70) written to Hon. Mr. Justice Philip Evatt, the Australian Royal Commissioner, on December 4, 1985, he gave his view on Hardell's studies as follows: "your review of Hardell's work with the additional evidence obtained directly from him at interview shows that many of his published statements were exaggerated or not supportable and that there were many opportunities for bias to have �- 77 - been introduced in the collection of his data. His conclusions cannot be sustained, and, in my opinion, his work should no longer be cited as scientific evidence." �-73LIST OF REFERENCES 1 AXELSON, 0. and Sundell, L. Herbicide Exposure. Mortality and Tumor Incidence. An Epidemiological Investigation On Swedish Railroad Workers. Work Environ. Health. Vol. 11 (1). 1974; pp 21-8. 2 AXELSON, 0. and Sundell, L. Phenoxy Acids and Cancer. Translated for EPA and revised in accordance with comments by Dr. Axelson. Lakartidningen. Vol 74. 1977. pp 2887-8. 3 AXELSON, 0. et al. Herbicide Exposure and Tumor Mortality: An Updated Epidemiological Investigation oh Swedish Railroad Workers. Scand. Jnl. Work Environ. Health. Vol. 6 (1). Mar. 1980; pp 73-79. 4 AXELSON, 0. Sweden. Document. Document Digest 1974 Railroad Workers Study 1974. 23 pages. 5 Axelson, Olav. Curriculum Vitae & List of Publications 13.8.84, 9 pages. AXELSON, 0. EPA Transcript. In the Matter of the Hearing-of 2,4,5-T and Silvex. The Dow Chemical Company, et al. 7.7.80. Washington pp 8821-9100 and Appendices. Evidence of Prof. Olav Axelson. R.C. Transcript 3375 and see for example FOLKBLAD. Copy of Swedish Newspaper No. 190. Torsdag 18 August 1977 and English translation labelled Clipping 9. Umea doctor with the cancer report. 2 pages. See reference 1 at p. 21 and see for example FOLKBLADET. Copy of Swedish Newspaper. Torsdag 18 August 1977 and English translation labelled Clipping 10. The doctor who investigates the cancer cases. 4 pages. AXELSON, 0. Sweden. Questionnaire in Swedish to all railroad workers in the cohort under study headed "Document Digest" 4 pages. (i) �-79- 10 11 AXELSON, 0. Sweden. Document Digest 1974. Railroad Workers Study, 1974. 23 pages. ERIKSSON, M. et al. Soft-tissue Sarcomas and Exposure to Chemical Substances: a Case Referent Study. British Journal of Industrial Medicine, Vol. 38, 1981: pp 27-33. 12 HARDELL, L. & Sandstrom, A. Case-Control Study: Soft Tissue Sarcomas and Exposure to Phenoxyacetic Acids or Chlorophenols. British Jnl of Cancer 1979. Vol. 39 pp 711-717. 13 HARDELL, L. Relation of Soft Tissue Sarcoma, Malignant Lymphoma and Colon Cancer to Phenoxy Acids, Chlorophenols and other Agents.Scandinavian Jnl. of Work, Environment & Health. Vol 7, 1981 pp 119-130. 14 ERIKSSON, M. et al. Soft-Tissue Sarcomas and Exposure to Chemical Substances: A Case Reference Study. British Jnl. of Industrial Medicine, Vol. 13, 1981. pp 27-33. la ERIKSSON, M. Hardell, L. Ber<j, N.O. MolU-r, T. Axelson, 0. Case Control Study on Malignant Mosoncliyiiial Tumors of Soft Tlssuo and Exposure to Chemical Substances translated for EPA. Originally in Ukartdningen Vol, 76, 1979. |jp 3872-75. 16 HARDELL, L. et al. Malignant Lymphoma and Exposure to Chemicals, especially Organic Solvents, Chlurophenols and Phenoxy Acids: A Case-Control Study. British Jnl. of Cancer 1981. Vol 43. pp 169-176. 17 18 19 HARDELL, L. et al. Malignant Lymphoma and Exposure to chemicals especially Organic Solvents, Chlorophenols and Phenoxy Acids. Case Control Study in Br. Jnl. of Cancer Vol. 43, 1981, pp 169 HARDELL, L. et al. Malignant Lymphoma and Exposure to Chemical Substances especially Organic Solvents, Chlorophenols and Phenoxy Acids in Lakartidningen Vol. 77 (4), 1980. pp 208-210. HARDELL, L. et al. Epidemiological Study of Nasal and Nasopharyngeal Cancer and their Relation to Phenoxy Acid or Chlorophenol Exposure. American Jnl of Industrial Medicine 3, 1982. pp 247-257. �20 HARDELL, L. On the Relation of Soft Tissue Sarcoma, Malignant Lymphoma and Colon Cancer to Phenoxy Acids, Chlorophenols and other Agents. Scand. J. Work Environ. Health 7; 119-130; 1981. HARDELL, L. Clinical Observations regarding Malignant Mesenchymal Tumors, in Lakartidningen (the Doctor's Journal) No. 33 of 1977 pp 2753-2754 (Study 1 in Green Book). 21 22 HARDELL, L. Malignant Lymphoma of Histiocytic Type and Exposure to Phenoxyacetic Acids of Chlorophenols. Lancet, Vol. 1 (8106) January 1979: pp. 55-56 23 HARDELL, L. Epidemiological Studies on Soft-Tissue Sarcoma and Malignant Lymphoma and Their Relation to Phenoxy Acid of Chlorophenol Exposure. Umea, Univ. Press, 1981. 139 pages. 24 HARDELL, L. & Sandstrom A. Malignant Tumors and Exposure to Phenoxy Acids of Chlorophenols (Case Control Study). Br. J. Cancer: 39; 711-17; 1979. 25 26 SWEDEN. Swedish Telex of 16.8.77 - Stockholm 27 SWEDEN. Newspaper. Vasterbottens-Kuriren, 18.8.77. Undersokningen Pekar pa Samband Men ar Inget Bevis. 28 FOLKBLAD. Copy of Swedish Newspaper No. 190. Torsdag 18 August 1977 and English translation labelled Clipping 9. Umea doctor with the cancer report. 2 pages. 29 FOLKBLADET. Copy of Swedish Newspaper. Torsdag 18 August 1977 and English translation labelled Clipping 10. The doctor who investigates the cancer cases. 4 pages. �• 31 AXELSON, 0. Umea Regional Hospital, Northern Sweden Questionnaire B. Undated 12 pages. 32 AXELSON, 0. Umea Regional Hospital, Northern Sweden, Questionnaire A, Undated 11 pages. 33 SWEDEN. Oncology Centre. Questionnaire in Swedish from Regionsjukhuset I Umea (Northern Sweden). Undated. 8 pages. 34 ERIKSSON, M. Hardell, L. Berg, N.O. Holler, T. Axel son, 0. Case Control Study on Malignant Mesenchymal Tumors of Soft Tissue and Exposure to Chemical Substances translated for EPA. Originally in Lakartdningen Vol. 76, 1979. pp 3872-75. 35 AXELSON, 0. Some comments on the Swedish Experiences from Studies of Cancer and Exposure to P.henoxy Acid Herbicides and Chlorophenols - largely an extension and updating of a presentation by 0. Axel son, Hardell at a conference on Health Hazards of Chlorophenols in Vancouver, May 16-17, 1984. 25 pages 36 37 AXELSOH, 0. A case-referent epidemiology. Environmental note on observational bias in studies in occupational health Scandinavian Jnl. of Work & Health 6, 1980, pp 80-82. Smith A.H.: Outline of additional testimony of 25.9.1984. 6 pages. (iv) �-82- 38.r Cole, P. Direct testimony of Dr. Philip Cole Before the Environmental Protection Agency of the United States of America. In Re: The Dow Chemical Company, et al, FIFRA Docket Nos. 415, et al. (Exhibit 860) Appearance Date: November 6, 1980. 39.- Anonymous. Further review of the safety for use in the U.K. of the herbicide 2,4,5-T, Advisory Committee on Pesticides, Ministry of Agriculture, Fisheries and Food (December 1980). 40.- Rt. Hon. Peter Walkers, M.P., Minister of Agriculture, Fisheries and Food, In: Advisory Committee on Pesticides; Report on Phenoxy Acid Herbicides. London: Ministry of Agriculture, Fisheries and Food, February 7, 1983. 41.- Cook, R.R. Soft Tissue Sarcomas: Clues and Caution. Tucker, R.E., Young, A.L. and Gray, A.P., Eds. Human and Environmental R|sks of Chlorinated Dioxins and Related Compounds. New York: Plenum, 1983. pp. 613-618. 42.- Eklund G.: Does occupational exposure to chemical pesticides increase the risk of cancer. Weed and plant protection conferences. Uppsala, Sweden, 1983. pp 6-12. 43,-Wiklund K, and Holm I.E.: Soft Tissue Sarcoma risk in Swedish agricultural and forestry workers. Journal of National Cancer Institute. In press. 44.- Stenbeck G., and Wiklund K.: Multiple myeloma in Swedish agricultural workers. Int. Journal of Epidemiology. In press. 45.- Riihimaki, V., Asp, S, and Hernberg, S. Mortality of 2,4-dichlorophenoxyacetic acid and 2,4,5-trichlorophenoxyacetic acid herbicide applicators in Finalnd. Scandinavian Journal of Work Environment and Health 8:37-42, 1982 46.- Riihimaki, V., Asp, S., Pukkala, E. and Hernberg, S. Mortality and cancer morbidity among chlorinated phenoxyacid applicators in Finland. Chemosphere, Vol. 12. No. 4/5. pp. 779-784, 1983! 47.- Smith A.H., Fisher D.O., Giles H.J. and Pearce N.: The New Zealand Soft Tissue Sarcoma Case-Control Study: Interview Findings Concerning Phenoxyacetic Acid'Exposure. Presented at 3rd International Symposium on Chlorinated Dioxins and Related Compounds, October 12-14, 1982, Salzburg, Austria. �-8348.- Smith A.H., Fisher D.O., Pearce N.E. and league C.A.: Do Agricultural Chemicals Cause Soft Tissue Sarcoma? Initial Findings of a Case-Control Study in New Zealand. Community Health Studies 6: 114-119, 1982. 49.- Smith A.H., Pearce N.E., Fisher D.O., Giles H.J., league C.A.: Soft Tissue Sarcoma and exposure to phenoxy herbicides and chlorophenols in New Zealand. I.N.C.I. 73; 1111-17, 1984. 50.- Smith A.H., Pearce N.E.: Update on Soft Tissue Sarcoma and Phenoxy herbicides in New Zealand. 5th International Symposium on chlorinated dioxins and related compounds. Septmber 16-19, Bayreuth, F.R.G., 1985. v 51.- Pearce N.E., Smith A.H., Howard J.K., Giles H.J.: Case Control Study of non Hodgkin's Lymphoma and exposure to phenoxy herbicides, chlorophenol, fencing work and meat employement. British Journal of Indutrial Medicine. In press. 52.- Zack J.A. and Suskind R.S.: The Mortality Experience of Workers Exposed to Tetrachlorodibenzodioxin in a Trichlorophenol Process. Journal of Occupational Medicine 1980: 22:11-14. 53.- Ott M.G., Holder B.B. and Olson R.D.: A Mortality Analysis of Employees Engaged in the Manufacture of 2,4,5'Trichlorophenoxyacetic Acid. Journal of Occupational Medicine 1980; 22:47-50. 54.- Cook R.R., Towsend J.C. and Ott M.G.: Mortality.Experience of Employees Exposed to 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD). Journal of Occupational Medicine 1980; 22:530-532. 55.- Zack J.A. and Gaffey W.R.: A Mortality Study of Workers Employed at the Monsanto Company Plant in Nitro, West Virginia. Environmental Science Research 1983; 26:575-591. 56.- Suskind R.R.: Long Term Health Effects of Exposure to 2,4,5-T and/or its Contaminants. Chemosphere, Vol. 12 No. 4/5, p 769, 1983). 57.- Cook R.R. and Cartnill J.B.: Soft Tissue Sarcoma and Dioxins. Putting the data onto perspective. Symposium on public health risk of dioxin. October 19-20, 1983, New York, N.Y. 58.- Fingerhut M.A., Halterin W.E., Honchar P.A., Russel W.O.: Review of exposure and pathology data for seven cases reported as soft tissue sarcoma among persons occupationally exposed to dioxin-contarninated herbicides. Symposium on public health risks of the dioxins. October 19-20, New York, N.Y. (vi) �59.- Fingerhut M.A., Halperin W.E., Honchar P.A., Smith A.B., Groth D.H., Russel W.O.: An evaluation of reports of dioxin exposure and soft tissue sarcoma pathology among chemical workers in the United States. Scand. J. Work Environ Health 1984; 10(5): 229-303. 60.- Milham S.J.: Herbicides, Occupation and Cancer. Lancet 1; 1464-65, 1982. 61.- Zack J.A. and Suskind R.R.: The Mortality Experience of Workers Exposed to Tetrachlorodibenzodioxin in a Trichlorophenol Process Accident. Journal of Occupational Medicine 22: 11-14, 1980. 62.- Cook R.R., Towsend J.C., Ott M.G. and Silverstein L.G.: Mortality Experience of Employees Exposed to 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD). Journal of Occupational Medicine 22: 530-532, 1980. 63.- Cook R.R.: Dioxin, Chloracne and Soft Tissue Sarcoma. Lancet 1: 618-619, 1981. 64.- Zack J.A. and Gaffey W.A.: A Mortality Study of Workers Employed at the Monsanto Company Plant in Nitro, West Virginia. Tucker R.E., Young L.A. and Gray A.P., Eds. Human and Environmental Risks of Chlorinated Dioxins and Related Compounds. New York: Plenum, 1983. pp. 575-591. 65.- Balarajan R., Acheson E.D.: Soft tissue sarcomas in agriculture and forestry workers. Journal of Epidemiology and Community Health 1984; 38:113-116. 66.- May G.: TCDO: A Study of Subjects 10 and 14 years After Exposure. Chemosphere, Vol. 12, No. 4/5, pp 771-778, 1983. 67 Coggon D. Acheson E.D.: Do phenoxy herbicides cause cancer in man? Lancet: 1; 1057-1059; 1982. 68 Gallagher R.P. Threlfall N. J.: Cancer and occupational exposure to chlorophenols. Lancet 11; 48; 1984. 69 Olsen J.H. Mbller Jensen 0.: Nasal cancer and chlorophenols. Lancet 1 1 ; 47-48; 1984. 70 Doll Richard: Director, Imperial Cancer Research Fund, Cancer Epidemiology and Clinical Trials Unit, Green College, Oxford, U.K.; Letter to Hon. M. Justice Philipp Evatt, Australian Royal Commission on the use and effects of chemical agent on Australian personnel in Vietnam. Page of this volume. � Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 056 Folder The folder containing the original item. 1497 Series The series number of the original item. Series III Subseries II Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource O'Keefe, Barry Title A name given to the resource Typescript: Chapter 7: Soft Tissue Sarcoma: Law, Science and Logic, An Australian Perspective Subject The topic of the resource AVHS ao_seriesIII https://www.nal.usda.gov/exhibits/speccoll/files/original/56d514a7011f45363c2d2088fb18f434.pdf ceebfb72a56e554f4b0099f140c7d89c PDF Text Text Item ID Number 01874 Author Corporate Author ROPQPt/ArtlCiO TitlO "ineraryf°r Mr. K. D. A. Medbury, Commissioner, Australian Repatriation Commission, Department of Veterans Affairs, Australian Government, March 3-4, 1980 Journal/Book Title Year 000 ° Month/Day Color Number of Images 2 Doscripton Notes Wednesday, July 18, 2001 Pago 1874 of 1908 �ITINERARY for MR. K. D. A. MEDBURY Commissiorir-r, Australian RepatriaLion Commission Department of Veterans Affairs Australian Government MONDAY. 3 March 1980 0!OO Colonel Lathrop and Lt Colonel Moynahan meet Mr. Medbury at VIP Suite 240. Escort to Officers' Mess for breakfast. 085fj Transport to Headquarters, Aerospace Medical Division (Bldg 150) 0900 Meet with Colonel Mohr (Bldg 150) 0930 Meet with Colonel Enders (Rldg 125) 0955 Transport to Eplcenrioloyy Division (Bldg 930) 1000 Introduction to Project RANCH HAND II (Colonel Lathrop) 1015 U.S. Air Force Experience with Herbicide Orange (Major Young) 1015 Break 1100 Environmental Fate of Herbicide Orange (Major Young) il'jfj Transport to Officers' Mess 15:00 Lunch - Officers' Mess l?f>5 Transport to Epidemiology Division (Bldg 930) I.';30 Literature Review (Major Sauri) 1400 L'pideriiiolofiic Approach (Lt Colonel Wolfe) l'-30 Break IMS Data Collection (Lt Colonel Moynahan/ Captain Pennington) l!»l'i Physical Examination (Lt Colonel Wolfe) IM r > Statistical Methodology (Dr. Albanese) 16T) Resources (Major Daves) \Wh Transport U> Officers' Mess 1630 Social Hour - Officers' Mess �TUESDAYj. 1 —~" March""J 9fJO - - - ""' ~~ -™™ 1 •" 0800 Colonel Lathrop and Lt Colonel Moynahan meet Mr. Medbury at VIP Suite 240. Escort to Officers' Mess for breakfast. OR55 Transport to Headquarters, USAI" School of Aerospace Medicine (Bldg 125} 0900 -USAF School of Aerospace Medicine Briefing (Bldg 125, Conference Room) and tour of facilities (Mr. Berry) 4 112b Transport to Officers' Mess 1130 Lunch - Officers' Moss 12J.5 Transport to Epidemiology Division (Bldg 930) 1300 Sunmary/Questions and Answers (Colonel Lathrop) Transportation on standby � Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 069 Folder The folder containing the original item. 1874 Series The series number of the original item. Series III Subseries IV Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Itinerary for Mr. K. D. A. Medbury, Commissioner, Australian Repatriation Commission, Department of Veterans Affairs, Australian Government, March 3-4, 1980 Subject The topic of the resource international cooperation AVHS Air Force Health Study ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. 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Source A related resource from which the described resource is derived Wellington, The Evening Post Date A point or period of time associated with an event in the lifecycle of the resource January 18 1980 Title A name given to the resource Vietnam Veterans Attribute Aliments to Agent Orange: Defense Department Survey Subject The topic of the resource AVHS questionnaire ao_seriesIII https://www.nal.usda.gov/exhibits/speccoll/files/original/6e5160597f40b1e483a4fe74fb41335a.pdf 74ff90e8a94b18099e2ce8b0db4eb704 PDF Text Text Item ID Number 01885 Author Corporate Author RUpOrt/ArtiClB TltlB Submission to the Scientific Advisory Committee, Australian Veterans Herbicide Studies, 3rd Meeting to be held in Sydney 3 & 4th March 1981. Journal/Book Title Year 1981 Month/Day February 26 Color ! Number of Images 64 Descrlpton Notes Wednesday, July 18, 2001 Pago 1885 of 1908 �26th February, 1901 SUBMISSION TO THE! SCIENTIFIC ADVISORY COMMITTEE AUSTRALIAN VETERANS HERBICIDE STUDIES 3rd Meeting to be held in Sydne.y 3 & 4th March 1981 SECTIONS: 1. Pilot Study FJroposa3 . • 2. Progress Report on Exposure Lstiiuatiun * 3. Revised Plans ?.nd Estimates for ths Study �SECTION 1 ^ : ' " - . : ' • -. •• PILOT STUDY PROPOSAL Page 1. AUSTRALIAN VETERANS HERBICIDE STUDIES • . 1 • 1.1 EJackground 1.2 Postulated effects of herbicides 2. AIMS AND OBJECTIVES OF THE PILOT STUDY 7 2.1 General Aims .2.2 Specific Objectives ' 3. RESEARCH PLAN ' _ " - • " A." METHODS OF DATA COLLECTION TO RE TESTED FOR THE FAMILY SURVEY 8 13 A.I Data collection methods to be tested A. 2 The questionnaire Zf."3" Data collection by Questionnaire - A.A Coding and data entry for Questionnaire • A.5 Medical history and examination 5. VALIDATION OF fCDICAL DATA '• • " . . ' . " 19 5.1 Overviev/ / 5.2 Methodology 5.3 Conditions to ba validated 5.A Service Medical Records 5.5 Non-Service Records 6. COKTIDIKTIALITY AM) PRIVACY ISSUES '"' 23 6.1 Confidentiality 6.2 Privccy 7. STATISTICAL AfiALYSIS G;r 1i!F. PILOT STUDY 25 8. ATrNDJCES 28 ' 8.3 SI rue I urc; of tht1 lnte::vicv//C?Jf->stionr!£iirc fi.? Structui-R of •:•'.? t-tjo'.ical Hirtory and Modical Examination of Adu3ts B.3 MedJcal Cxor:i.i.n::;.iur-; of Children �> • • -1- • . 1. AUSTRALIAN VETLMhS HERDiCIDC STUDIES I.I Kackground . ' . . . ' • In its report of its second meeting he.ld in Sydney 14th September, 1980 the Scientific Advisory Cormjittcc (SAC) considered a research protocol which set out the broad long-tern 'strategy proposed by the investigators from the Commonwealth Institute of Health. The Committee reported that it "considered these planned investigations to cover fairly completely the possibilities for epidorniological investigation in Australia of the effects of herbicide exposure in Vietnam during the Vietnam war". T!" . Committee identified measurement of exposure to herbicides and the comparability of Vietnam veterans and a proposed control group as two key issues which must be clarified before the scientific viability of the whole study could be assessed. The Committee also recommended expanded pilot studies to provide the data necessary for a fully informed choice of the best method within a spectrum ranging from a mailed self-administered questionnaire (SAQ) to interview and medical examination of all-veterans and their progeny. It was considered that as far as possible these preliminary investigations should be incorporated into a single pilot study to avoid the delays of a sequential approach. It was noted that there may be advantage to all concerned if the Committee were to review plans for the pilot study prior to their commencement. Work is currently proceeding according to a plan drawn up for the pilot survey. Due to limited resources in personnel end shortage of'time it has not been possibJe to provide completed documentation for all aspects of the pilot study. The present submission is a summary which has been prepared to meet a deadline. Further development, particularly of data collection instruments, is proceeding rapidly cr.ci more information could be-nade available to the Conndttee during its meeting, if so desired. A progress report on exposure estimation .is subr.iittex' in section 2 and revised plans and estimates for the investigation are submitted in section 3. �* • - 2 - . . . I'2 Posiulolnci effects of herbicides* The terms of reference as given by the Department of Veterans' Affairs to the now Commonweal th Institute of Health concerned the possible effects of contact v/ith or exposure to Agent Orange and subsequent disabilities in Australian veterans, or in complications of pregnancy in their spouses and the occurrence of congenital malformations in their offspring. Although the possible effects of Agent Orange remain the primary concern of the investigators, the possible effects of exposure to other herbicides such as Agent Blue (cacog'ylic acid) will also be actively sought in the investigation. Agent Orange consisted of a mixture of 2,4-D and 2,4,5,-T. The latter is contaminated during manufacture with TCOD (2,3,7,8-tetrachlorodibanzo-para-dioxin). The pharmaco-dynamics and toxicology of these chemicals has recently been reviewed by the Department of Health. 2,4-D may be absorbed from the gastrointestinal tract or by •inhalation. Little absorption occurs directly though the skin. Absorbed 2,4-D is quick] y excreted from the body, mostly in urine as the free acid. It does not accumulate in the body. There are many reports of consumption of •sublethal doses of 2,4-D without any apparent ill-effects. However, occupationally exposed workers have complained of rcn-specific symptoms such as excessive fatigue, epigastric pains, anorexia (loss of appetite), occasional upper respiratory tract symptoms and impaired taste sensitivity. Medical investigation has not implicated 2,4-D as the cause of all symptoms but did suggest indications of increased incidence of liver disc9.se among workers with chronic exposure to herbicides. Isolated cases of peripheral neuropathy and contact dermatitis following exposure to 2,4-D have been reported. 2,4, 5- T is readily ah; orbed from the gastrointestinal tract after incjGstion and probably aftcr_ inhalation. Skin absorption, however. is slight. Like 2,/t-D it is readily excreted and is not stored in the: body. .Stove rnetaoolism does occur in animz-.ls but the bulk is secreted unchanged in the urine, "iho oral dose required to produce symptoms in man is probably three to four grains. Medical exyrcination of workers engaged in the manufacture of 2,4,5-T has shown increased incidence of chloracne which could be attributed to the presence of TCDD as an impurity. It should be noteci that increased incidences of urinary por'phyria, chloracnc and nirrutisrii have been demonstrated in workers employed in n^nufc.cturing chlorinated phenols such an Z/ijS-trichlorophonol, the precursor of 2,4,5-T. Again, the responsible agent could be TCDf), and most reports do not distinguish its effect from possible: effects cf 7,4,5-T. 2,4,5-T has been shown to csuse toratogenic effects in animals which cannot be wholly attributed to the; presence of toxic impurities such r.s TCOE.). Who the v or not 2,4,5-T is carcinogenic cannot be deduced conclusively from results reported to date. 2,'i,5--T, like 2,4-D, does not- increase mutation rates nor stimulate mutc'C^nic responses in rats r.nd mice. Jt does, hov/ever, produce chromatic! a bnorma lilies, j.n vitro in cultured n-jiioi lyriipiujcylos and affect the cf).ccn.os;o!::«j!S onrj j.eproUuclivG Riec-lianisms of dioui-e si/j hamster bone narrow cells. It shcvjjd I: -2 r.Jclefl, however; that these effects may IKIVO been due to cellular toxicity lather than ^etTit.ic ol.tei Information in tl-.ir; section has been obtoinscl Riciniy from ur,[rjb}is!ii-cl doc%;.i:writi, preparcci tiy tf-o ii;:parLi".t:nt of Health, �•- . -3- • . ' TCDD was present in Agent Orange and Agent Purple used by U.S. military forces in South Vietnam. Kr.av/Jeclge of the toxic effects of TCDD in man comes mainly from medical assessment of occupation-ally exposed workers engaged, in the production of chlorinated phenols and their derivates. Limited data are available from known episodes of exposure of the general population. Table 1.1 lists known toxic effects attributed to TCDD in TABLE 1.1 TOXIC EFFECTS OF TCDD IN MAN Dermatologi ca1; Chloracne Porphyria cutanea tarda Hyperpigmentation and hirsutism Internal: , "~ ~ Psychifit3.\ic: Liver damage (mild fibrosis, fatty changes, haernofuscin deposition and parenchymai-cell degeneration) Raised serum hepatic enzyme levels Disorders of fat metabolism Disorders of carbohydrate metabolism Cardiovascular disorders Urinary tract disorders Rc'spiratory tract disorders Pancreatic disorders Polyneuropathies Sensory impairments (sight, hearing, . ' 'smell, taste) Neurasthenic or depressive syndromes Source: Horcberger, E. Reggi&ni, Ci. Sarnbreth, 3. and Wipf, U.K., ^J.CL.J^9.u;Pj_jJyil- ^2» 2273 (1979) Expos2cJ individuals may develop a variety of medical conditions with chloracne, n-?LirologicRl and behavioural changes, liver end fat metabolism disorders end signs of porphyria cutanea t&rda (a disorder of porphyrin metabolism) arr.ong the most frequently rej.iort»d toxic effects. Reports from Sweden have shown recently a statistically significant c'ssociation between human exposure to chlorc;:f;enoxy acids and chj orophcnols end increased incidence of certain soft, tissue sorccr-iata snci lymphomata. �Table 1.2 summarises the results of some toxicological experiments with TCOD in laboratory animals. TABLE 1.2 TCDD - EXPERIMENTAL TOX1CITY •A Dose LDtjQ for laboratory animals Systemic lesions (liver, blood, skin, etc) and clinical chemistry abnormal findings at chronic administration Embryotoxicity, foetotoxicity, postnatal growth retardation Reproduction, fertility Immunodeficiency (atrophy of lymphoid tissue) Enzyme induction Carcinogenicity Mutagerdcity (?) (0.6-ll5)ug/kg 0.1 ug/kg 0.25 ug/kg 0.01 ug/kg 0.1 ug/kg 1 ug/kg 0.1 ug/kg 2 ug/ml (1) Indicative-; values Note: lug = O.OOlmg Source: Homberejer, Regggiani, fi. Sambreth. J. and V/ipf, U.K., 22, 3273 (1979) Chronic toxicity of TCDD is most often manifested as hop::tic necrosis (death of liver cells) and thymic and lymphojd atrophy. The degree of hepatic involvement appears to be dose and species related. Suprossion of the thyniu-; and lyrnphoid tissue leads to decreased iraiune responses in mice, rats and guinea pigs. Acne of increasing severity v/as produced when AS'Creasing doses of TCOD were applied to 7?abbit's ears. A total close of 0.002 to 6.C03 mo/kg over a nine month period produced severe hstmotoJogical changes F.rsci death in rhesus monkeys, making these among the most TCOD-susceptible animals tested. TCOO is o potent teratogen which causes increased fetal mortality in animals. It pio^uces cleft palate snd kidney rbnormalities in mice at doses as low as 0.001 r.ig/ky whilst di?pres»s?ci fetal v/eight t-nd visoral Ic-sions, occur in rats ot O.CC05> to 0.003 nig/kg. Teratolcigical effects in rhcsuc- rnoniwys h&vs not bee;i demonstrated. Studies on the corcinorjenic potentifil of TCTJi) h.r.ve bc.-cn Jess conclusive. The potential r;iutacenicity of 1CDD in hun;ans has not bjen cttcr^inecl. reeding studies with i-ats tiavc not sh.own iT.utag3n.ic effucU-. but TCiJi) has b&en 5-.!N.o\vn to induce rnutagrnic changes in so.'i-;-: stjains of bscterici, in common with many other substances. �Cacodylic scid • . • When used as a herbicide cacodylic acid has the potential for absorption by inhalation and through the skin. No human data arc known to be available on its dermal absorption and very little is known about human pulmonary absorption of organic arsenicGls. Ingested seafood arsenic is apparently absorbed from the gastrointestinal tract. Whilst no data are available on the distribution of organic arsenic compounds in humans, studies with forestry workers exposed to cacodylic acid have demonstrated its rapid urinary clearance form the body. • Study of the biotransformation of cacodylic scid in living rats has shown that it is fairly stable i_n .vivo and is not converted to inorganic arsenic. Any in vivo transformation of cacodylic acid in other species is not clear. Little data are available on the chronic toxicity of cacodylic acid in humans. Toxic effects of these organic arsenicals used as drugs are mainly manifested in ths central nervous system and include encephalopathy and optic atrophy. Other less frequent side effect include dermatitis, liver damage and disturbances of the haemopoetic system. Cacodylic acid has been considered as a source of intcxication of domestic animals leading to symptoms similar to those produced by chronic ingestion of inorganic arsenic. Chronic feeaing of cacodylic acid to rats and beagle dcgs has produced..no significant effects on body weigh1;, food consumption, organ weights, urinslysis or haematoionical system. Organic arsenr'.cals have no known rnutagenic or teratogenic effects in man or animals and no conclusive evidence cf carcinogenic activity in laboratory animals is known. N'-j epidemic]ogical investigations r.re known to have: been conducted on the carcinogenicity of cacodylic acid or other organic arsenic compounds. There are only three reported studies of the toxic effects to humans of cacodylic acid end its salts in the recent literature. The most extensive documentation of Cc'coclylic acid tox.icity in humans is that of Peoples £t «J_. (I97i0. Tncse authors reviewed 3/i uncontroIJed cases of occupational exposure finioogst CaHfornian agricultural workers which occurred bc-twcen 197J5--7?. exposure cccurrod as a result of misuse, accident or equipment tfH.1function. Basically, cscodylic acid noted as a chemical irritant. Ir.gsstiun produced nausea, coJic vr;;;iiting and diarrhriee;. Application to ths fcye prc'Ciuceci ir.jjcj conjunctivitis whilst der.r.al application produced a contact dermatitis or an alJergic response, The worst ca.se was that of a spray-rig operator who received particularly heavy exposure by drenching of rhis cJothing and by splashing of he.rbio.icie so.luLicr, into his mouth. H J was hospitalised with "paralysis, irregular :rer.pir:-ition, nur-ibner-? anc! f^inti.r^g". Investigation revealed no orcpn dr.rriare a. ici recovery was spontaneous. F'ull rt-(,civory \.-)s always pvfrrpt in tfie yth;:r casc-s, anc! blood arsenic levels al'./ctys rcn:air:r;'d nonr^l. No chronic effects were reported. �[rir)rQ:inic Arsnnic Chronic exposure tc rnco'icir.al inorganic arsenics such as Fowlers' solution produces a characteristic syndrcr.se of tv/perpi client ntion followed by keratoses and, infrequently, dermal neoplasia. "this distinctive clinical syndrome has lead to general agreement that srsciiic can cause skin cancer. There have been numerous reports and several epitieraiclocjical studies of the incidence of cancer amongst workers occupational! y exposed to arsenic in nining and metallurgy, in the chemical industry end in agriculture. The cpidcmiological data are ccnsistcnt with but do not demonstrate a causal relationship between inorganic arsenic and cancer of the skin and respiratory tract. • There is nothing in the recent literature to suggest that cacodylic acid is degraded to inorganic arsenic _in vivo. Indeed there is ample evidence that such a process wculd be contrary to the established metabolic fate of arsenic compounds in r.i£rr.;nals. Halclicsin (Malelhion) Maidiosin is an organophosphorus insecticide of moderate mammalian toxicity. It is rapidly rr;staboliscc! to a variety of products and excreted laroc-'ly .in the urine. It is not cumulative in body tissues. Sublethai exposure can cause depression of plasma colincsterasc activity but this requires a high intake. Spontaneous recovery occurs after cessation of exposure. • " r* Other insecticides used in Vietnam include DDT. The chronic toxicity of DOT to fi.an has been thoroughly .investigated. Massive chronic exposure produces orJy a mild 3tiniu.lat.ian of tho rnicrosomal enzymes of the .liver. In this investigation the major postulated effects are those related to TCi'JD, since- this is the.- potentially ruost toxic contaminant in Agent Orange which comprised a very higi'i pioportiGn of'herbicide usad in Vietnam. �42. ' -- /.'-..•• AIMS AND OBJECTIVES OF THE PILOT STUDY 2.1 General Aims § . - . The purpose of the Pilot Study is to assist in planning the mainsurvey. It addresses rnethodcJonical issues related to study design including the comparability of Vietnam veterans snd the proposed control group and, methods of data collection. It is not expected to provide data on the effects of herbicide exposure in Vietnam but is expected to test methodology and provide a basis for logical decision as to the best and most acceptable methods 'if the conducting the main survey. .2.2 The specific objectives of the pilot stuoy are as follows: 2.2.1. Tojrihqs_e t2etween_sever£l methods of data cohloctien. The choice vail "be maae primarily on the response rate and quality of data, although the cost and duration of data collection will also be a consideration. 2.2.2. Cotnparability of Veteran jand Coritro.l Groups The pilot study will obtain data on comparability additional to that available a priori from existing records. 2.2.3. TesJ_o/_Prcced_ur8S_ toJ-'e_uspd As far eis possible the procedures to be used in the family survey will be .tested during the pilot study. The greatest eipphssis will be on data collection and analysis related to the specific objectives of the pilot study. �3. RESEARCH PLAN 3.1. Vietnam Veterans nnci Contro^ Grouos 1. About 40,000 male army personnel served in Vietnam. About 11,000 male personnel served in the Army during the period of the Vietnam War but were not sent to Vietnam. It has been decided to restrict the study at this stags to male Arrny personnel for the following reasons: (a) To avoid the introduction of possible confounding factors. This means the veteran and control groups should be as homogeneous as possible. The minimal medical standards of en cry into the three Forces were not the same. The Army had a far larger contingent of National Servicemen than either the Navy or Air Force and the usual Service experiences (e.g. diet, living conditions, combat conditions) of members of each Force were presumably quite different. It was therefore decided to drew the veteran and control groups from within a single Force. (b) The possible herbicide effects could be very Final 1. As large as possible a sample of veterans and controls should be considered so as to maximise the chances of detecting such effects. The Army was the largest Force and also contained the highest number of potentially exposed individuals. It was therefore preferred to the Navy or Air Force. (c) There are only a few hundred potentially exposed female Army personnel. Btcause of marriage and the subsequent change of surname it would be difficult to contact these individuals. rurVh-.Tii'ore, even if all could be contacted a few hundred is toe few for the lively detection of the types of effects to bo. considered ir- the family survey. It was decided to District the , study, at. least in;u.a!ly; to nisle servicemen. Australian involvement in Vietnam ceased at the r;nd of 1972. It was decided that only nale servicemen who enlisted pre-1573 and who served -in the Army at some period during the Vietr.cm War years would be included in the study. Of this group those who went to Vietnam will be known as the V grou.o, those who did not v.-ill be known as the C group. Before undertaking & statistics! analysis of the possible effect cf herbicide exposure, it is necessary to compare the V and C groups. Significant differences bstw&en the group? should IK-. noted and, whsre possible, corrected for in the final analysis, "So date it hus been possible1 to compare the V and C groups on the basis of ac:a at en] is twin I:, tirns spont in Avir.y and f,'atiorinl/i<egujar service.-. The two groups jn:e str.ilcliccilly significantly different (p 0.01) with lecipect to each of these three variables. Figure 1 illustrates the results. - The (.'ifferencn in the age at on.liii.ment' dJrlriL-u lions. of the V rind C groups (fig 3.J (a)) is dun to the-: feet that, although there are none of the C group in the GL" ':>•'• category, their; o.rc: 417 of the V group in this category. In the othe/: /i age at f;nl}.:;rnK:nt catec;o?-ios abivjl 85"; fa 12 in the V cjvoufj and ]55c ;'o t!:e C QLOUO. Tho effects of c-ijo v.v:: '.•.icll--doc:uf'ientf.sd Jn tha cpide.-niolc-jici-J l::tc.rati.ri?: ?.p.d it i-i'iajld bo j:c«3'jiblc to adjust for thi.:; �Figure 3.1 (b) shows that, for the V group there is a higher percentage of Regular servicemen than of National servicemen. Exactly the opposite is true of the C group. It is not so obvious how one should adjust for this difference between the groups. This matter needs close attention. The psychological scores in the entrance medical exam could • be of assistance in this regard as could further information to be obtained via the pilot study questionnaires. Figure 3.1 (c) shows that the V group is different from the C groups in so far as a much larger proportion of the former remained in the Army for more than six years (this being the shortest optional sign on period for a Regular serviceman). This difference is probably largely attributable to the fact that more of the V group were Regular servicemen making a career of the Army. However other effects could also be operating and the data to be collected from the pilot study should be studied closely with regard to this difference. •The results of the pilot study will be needed before the question of comparability csn be addressed more fully. This will give information on other variables such as ethnicity, socio-economic status, rural/urban living, together with a self-assessment of the reason for not going to Vietnam. It is planned that Army medical records of the entrance physical examination will be used to give medical and psychological status at the time of enlistment. 3.3 fission of the Pilot Study Twenty three Sydney metrcpolitpn electorates h^vn been selected. Six hundred individuals are; to be drawn from these electorates, 300 frcm the V group r.nd 300 from the C group. Three different interview modes (self-administered (SA), telephone (T) and face-to face (fF)) are to be assessed. One'hundred individuals; from both the V and C groups will be interviewed under each method. Figure 3.2 illustrates the egc at enlistment, length of service and Rcgulcr/Mc-tional service profiles of the V and C subgroups in the selector! Sydney electorates. Those should be compared with the Austrcilia-wjoe profiles illustrates in figure 3.1. It ic clear that, at leai-t on the basis of these; three variables, the chosen Sydney electorates are representative of the whole of Australia for V and C groups. Since; age at enlistment, length of service end Regular/National service rtetus have been slicv;n to be important variables, it was decided to strsi'.ify v<t.sn selecting trie pilot survey sample. To ensure that there are a i-ufrlcionl nur-.ihsr of individuals in each stratum, some of the ck;t'?! have b:,an cropped. Subject to the coritrainls in-posed by the overall numbers ?;v?liable in the ehosc-r, Sydney electorates in each stratum, the: design tio.s been chosen to be as "balan^d" as possible with respect to th'j V ar.rj C groups. Table. 3.1 below FI-.CWS the i'.umbers to be. sampled from each s'-rfiliuTi �-10- Mjmber of Veterans and Controls to be selected at random from each stratum by service status ?.nd time in the Army. Service Time in Status Army Vietnam (V) non-Vietnam (C) Age at enlistment Ago at enlistment LE 20 GT 20 Regular GT 2 yr. Army , 38 38 ' 42 National GT 2 yr. 37 Service LE 2 yr. GT 20 43* 42 LE 2 yr. LE 20 MARGINAL TOTAL * 40* 16* 25* 14* 2* 37 41 48 89 150 150 150 150 the maximum possible number so far indentified as resident in the Sydney study area. �-II -- tiirinjii -(*)'-••...Qfi^l.^^JLhLS.1.''. ._ . .........i_..i_..,. ,,..j ...,.. ..—(...., ...... . . ... . ___ .,...... r; . - -, , , . _ . . - . . - . . _,~.t . —i.-., »_ i.-l. . - fe I -L . : : • [ - i • , . •. „ _ . . .:. . , . .:. - > _• .,--.- _J ...J -j. -:-!..-., i » , . -.1- -!•-••• - t -J i- :- . h • i ,- .-I.-.-.-, ..,. ._.,. , . . r . , -1 -i -1 ..!. ',..; iori^ ."2..iZlLL:irj./:lJJliJjJ\!JJ : ccx^vc.u':".;'.:"". - -rrTi.. j"::!"..! ."!".!"• j.:r.i"j":.":"."'.:' • L • !. :..._. .._----.,.-?- 1j -.-|- J -,--•;••, T • ••? -i: • • • : • i i i i • -_ - » ---- - ........ \: / . l - : ——^ — _;.•:!•:;: -*- . -J -, —--~ ;.: .'_;.: J.j ^ '|: VjTiT-L::VTj:;: "!:•:;:.:. ." i '_ i ;. 1 1 _ _1 _ _ . .......... ... .._ i : ••; | '|~jj;"7". "• '! , ~~" j T ", "\ ~\ ';"": '•"!"~ {"'"! • " ; 1 '•""";"""•" 1 r::::!.;.rp";'.ri"::"; i.CMi:..,": ::".!"!":"!-.!.!- --..:-" "• ' : !! T: - i :' v • " '• - i - ' V . .. ^ . . v ^ f ^__'"* ...^ . _ . " . . - L i . .^:" : „ „ . „ . . ' . .•::::.U:::L-••.::;.!:;.; ..,... ! —v1 . Figure 3.1 I'VofiJca by (a) a^o, (l>) RCI-VJCG .'.-.tc.tui- and (c) '}.C:!;£'r.h of * service: for Lho total population oT the V and C croups .if. /'.'U-;l.;v.O.:i.f-.. �:r.l.1:|:i:hv.rJT!j ri '..Li-!.:, .i. ...:_.i-U ..-l T. . _ ^,_,__ ...j ... :l::j:!'4jj.:r.i.r - r r"! f-rri ; ; ! i ' • . \ • i ' • • i i i i ! • i " • ' i j r i i / I — . f . ... :-;_.. ^ ;..., J. -:-i-.-r ;.---.:.,-.. -.-;-;-; ;- -} -j-| ;- |- I -i -; ^-f tX;l- ;- |^ ^ ^-- -^» ^^ jr . - • r <; .........j r..^,.,,T. ..._„.....!..-r-;-.- -,.r-u-._.... ,....._L :-:-.--;-V;-•'•••---~-I^^~^-. .... .,..„,.,.. ,\--: — - : r,-J .--.-*r - • - : - • > - [ T - i - j - t - t - • ; -I"| "i -il'i"; " r-:" 1 : . ". . -^ . . _ . "i"! ! . i-,. a---.-., i'l'l , . 1 I I I I ! I :n:j i-jfl: :::Ll:L run h-i-r iir!"j!liii!;j4--r-'J-l-i^ i!"^".?-t"".!"irii '_''" :~*~\ | ;---;--|"'-:--;--;—--|-;-^--;^-f-|-i -j j • . _ /|a,\ . '. . (N«.i,0"*l A ;.._..:..: J_:_:.!..:."'..Li.j_i.|.i'.l4.'-;....._j..,_f .... :.; i • / - ., A.»«tYic«•/•.,_: - ui.i.:..:. .1 !.;.j..J-..:.r ... .1 :..:_] . ..-.{.:.: -:--:-} . - i - i - i - i | - : J ...i^lJ/lL^^.-^rdji^CfO.^^^^};,.^1;?;^ dihi:$?!H:fc; 3.? I •onioi- by (a) r.-^o, (b) service status rind (c) for vhe iilj.cn v.o be i--:i;rij)J.od d n the Tilot Si-udy. of :?cr ice �V' '•! *v ' - . • -5"?-*••>- 4. METHODS OF DATA COLLECTION ID .BE TESTED FOR THE: FAMILY SURVEY * ! Data Collection Methods to be Tested • Four different methods of data collection arc to be tested in the pilot study giving a total of five different data sets for analysis. They are: 1. 2. 3. 4. 5. Self-administered questionnaire Telephone interview Face-to-face interview Telephone interview and medical exaTiination Face-to-face interview and medical examination. The saTie questionnaire will be used for methods 1, 2 and 3. Differing additional instructions, standard probes and explanatory remarks will be issued for the questionnaire for each of methods 2 and 3. The questionnstire is dividad- into two- booklets - ons for the male, the other for his wife. The one questionnaire also serves veterans and controls. The areas of the questionnaire not applicable to controls are clearly designated. The mailing initiating the self-administered questionnaire, telephone interview and face-to-fcce interview will take place on the sense day. A mailing house v/ill be used for the pilot study as this will b'e necessary in any type of family survey. 4.1 1. * ™ ' ~~f-admini.—stored Questionnaire Sel — •--•---•--••-----— - ------ ' — •---"• '-----' " 1 3 The two questionnaires, two postage paid return addressed envelopes and tv.'O questionnaire cor.ifi-.er it slips will be mailed together with an individually addressed covering letter. A reminder letter, together with another set of questionnaires, ccmrnant slips and return envelopes will, be sent ?s-/y_ weeks later to non-responclers. Ten days later, again, continued non-respbnders will be contacted by telephone reminder call and a door-knrck reminder will be made about 12 days after that. There will be no deviation from the self -administered approach. Neither telephonists nor door-knock interviewers may conduct the' interview.. The door knocker may take delivery of the questionnaire. 4.1 2. Te_le3hone i An individually addressed letter will be mailed to each veteran together w:.th two slips (on which fie and his wife will suggest the lest tirr.ss and telephone numbers at v.-hic:i they can be contacted) and two postage paid addressed return envelopes. Telephone interviewing will take place or. t!io re turn slips are receiver] . ton-resporidfjrs v/ill be contacted by r.,«cns of a printout provided by Telecom or by consulting telephone directories. Thone v/itl-iout teleph.o;«?s v/ill be door-knockeci and inter viev.'C-c' f2co-to-i'ace. v . 4.1 3. ^ ^ A .. J: ° I inter views "r.cb£.! Initial contact will be by neans of on iridiv.iiii..all.y yr'drossed Ir.tter t-xplainicg the stu'Jy r.nci ttiat an ir.tcrvir:v;er will cnll ov uclt'plv.'.no to rnnko times. To:: thn inter views. Tlss trap, and wife will bo inl.c^-viev.-c;ci at l.ir:-er. find places convordc.'nt to tier;;. �' ft ' -14- In all three methods an attempt will be made to get non-responders to complete' a mini-questionnaire including brief health entails and the reason for non-response. 4.1 4. TelephonG: interview plus_rcqdical exafnination On completion of the telephone interview, the interviewer will offer, to a prs-se3acted sample, the medical examination. Family preference for location and time will be noted. 4.1 5. race-to-fcicc interview plus medical examination On completion of the face-to-face interview the interviewer v/ill offer to a pre-selected sample the medical examination. Again the family preference for location and time will be noted. Appointments for the examination will be finalised from the Study office. The entire fieldwork period from the mailing date to cut-off is two calendar months. 4.2 The broad objectives of the questionnaire are: • . To collect all data that may be relevant. Areas to he covered are exposure to herbicides, serviceman's medical disorders, familybirth defects, female reproductive histories, possible confounding factors, comparability of veterans and controls: . To collect valid data. ' . Upgrade personal details for continued subject surveillance. . Ease of management and administration.' -. To facilitate easy entry into computer snd the subsequent editing. , To collect relevant data to categorise individuals for each disorder. . To attract and hold the interest of the subject. II. 1has been possible to design or,;- ciuostionnairc, which contains the items c'eivnrtf necessary to achieve these objectives, that cjin successfully be both self- t'.rid interviev-'er-ac^dnistcrcd. The use of the standard GuosUomriJrc-! r.lso ailor/s Tor f-xac.-t statisriceil anofiysis of the; quality of clatti between rr.cthc'Js o.'id rerr.ovos a vc:ri?i/iQ rram the f.swosn'.cnt of resp rates. ]nc.!ivicinal items have t'C-yn disigrjcci to cr-ver one v? more of the ncj (.icLti areas: �^ . . .. . • . . . • . . .. -15' general demographic socioeconomic comparabiJity of veterans arid controls confounding factors 3ong-terrr. surveillance of the veteran exposure to herbicides medical status of veteran reproduction in women birth defects in children. • . / '' . - ; Available literature and experience suggested that the male subjects would not adequately answer questions on reproduction in their wives, birth defects Jn their children nor be able to give the names and addresses of attending doctors or hospitals. It was, therefore, decided to provide one questionnaire for the man and a shorter separate questionnaire for his wife , to provide details of her reproductive history and any birth defects in her • • children (details of the structure of the questionnaire are appended in 10. 1). .1 ' The internal design of the questionnaire has considered: number of questions. On3y those needed to gain necessary data have been included. No areas of interest are omitted. Question design. The qj.-estions are simply worried; easily understood; not open to interpretation; allow for and cover all possibJe answers to each question. Length. The questionnaire is of reasonable length with no unnecessary areas. The order of questions is logical and tactful. "fte subject's task is straightforward, simple and ronains constant for closed questions. .:, The instructions and explanations to the subject or interview&r are adequate and clear, friendly and occur es frequently as necessary. * Coding provisions arc clear and -nccurnte and alJow for spc-edy operation. ton-ceded questions provide well-designed space for writinrj opon--en.cbd answers --.rid the coding plan provides for the ultimate coding . Th'-! skip instructions follow one? system only. As both vritco'c-ris and controls arc using the s?.;*ie questionnaire c.l^ar ciofirsitioM has been provided whore questions aro not relevant for centre] s. Coriipr.jTitij lity . Vihei'O possible r.nd i-pproprJat.e the questionnaire provides for Comparability with othoi relevant studies. �-16- • fS 4.3 Data Jpol lgj2Uon_ f 'or jjuesti onna ire 4.3.1 Interviews Standard explanations, probes and extra question leads will be written into the questionnaires used for both telephone and face-to-face interviews. A questionnaire manual, specific interviewing manual and a coding manual will be issued. 4.3.2 Interviewers . • • . The telephone interviewing, face-to-face interviewing, telephone . reminder and door-knock reminder burden of the pilot study is to be contracted to an interviewing consultancy. Only firms capable of undertaking the family survey will be considered. The consultant will bs required to provide female interviewers of the highest stanoard and experience. Close field supervision will be mandatory to ensure correct interviewing techniques, quality control of data and standard approach. In addition information will be provided by the consultant on fundamental comparability matters such as time taken for interview, number of calls (telephone, in person) to achieve interview, rapport, relative costs. times .of day and week contacts were established, fc'ach respondent, will be eskod to complete the subject's comment sheet, which was mailed with the questionnaire, to gain direct information from each subject about his OY: her feelings about the questionnaire and the study in general. After each telephone and face-to-face interview the respondent will be asked these questions also, further feedback about the pilot study, the questionnaire and the data collection method will be gained in debriefing sessions with interviewers and their supervisors. t\ . /! Coding _s_ncj_ Jjs t a J'n tr y for .Ousst Jcnna .Ire 4./S.1 Coo'i ncj Where the possible range of answsrs to a question can be anticipated, the question is pre-coded. Whore tables of responses occur, the coding scheme is prc-plsnnad. Alphabetical punching will be used where coding :!& impossible and where absolute accuracy of recording is needed e.g. names a open dat of coded answers is required. Tha subject will tick pve-codod boxes or y.-rite answers in full. i-sse cofnpletea1 schso'uics will bs editec1 ard poftcoded by study staff. -._\c';:"'1: o- f ;:cri_ interv.k:v.|s The interviewer will automatically code t'Eicf1. reply except Ir.o^c ing p-jstcudii-g which vail La done in the office. TMe L;;!fir,t;t".-ip.-iiri; layout iu fJcr-ignc-c! so tint thin can bs rvvia �Medical The medical examination is being developed in order to examine 200 families, 100 of whom will be controls and 100 will be veterans. 100 of the families have been interviewed by telephone end 100 face to face. The medical examination is planned to be the sama in essentials in the pilot study as any medical examination that rcay be conducted in the main survey of families. /4.5.I. .Objectives . The objectives of the medical examination in the pilot study are: 1. To compare the methods of data collection i.e. to determine if medical examination contributes to the quality of the data. 2. To help validate information obtained at interview. 3. To screen subjects for • • • (i) Specific conditions - in the past or present, that could be related to herbicides. (ii) Present state of health. (iii) Indications of chronic disease that may or may not be related to herbicide effect. A. To look for observable birth defects in the offspring of subjects. 4.5.2. Ths conditions presently regarded by Veterans as related to herbicide exposuie include: '. ' i Skin dir.ecr.r; » paiticu.lfjr.ly chloraene; Altered Behaviour e.g. violent niaocJ swings; Neurological sy.T.ptor.is su;h as nj^bnviss ana tingling of extremities; 'Various cjastro-int^stinal disturbances. , ! Many of these complaints are subjective and difficult to measure. With this in mind the proposed bodies. 1 t-"xar,iin;-ition v.'ill not be primarily ciir.ea.se oriented but rather sy::iptu."; oriented. It v/ill involve a d:-:t.yi.lcd Medical I Li story in order to determine if the outcomes of interest exist, but in the context of post and present health, PiTsoriyl, fciin?.Jy jsrd cccupational histories as vzll as a pl'iysi examination v/ilh specie. I sifiph-ayis on t^rotet to-c?as will bz jncluded. A series of psyches lo-j.icr. 1 ti'-r.ts j n ccTinion u:;e on.- p3r:nnc:d in an effort to elucidate the particularly difficult area oT bc'Ivjv.i.otJT.T,! change. �4.5.3 Facility ' • _ It ir> proposed that the medical examinations should take place at a centrally located public Hospital or other facility. A team of two physicians, one paediatrician, 2 nurses and a clerk should be able to handle A families in the examination period which is estimated to be 3-4 hours. The location should have laboratory, equipment, waiting room and interviewing room facilities. The Medical history and physical examination will be performed by separate physicians, while psychological tests will be supervised by nurses. . . . �" '-19- •' . tt 5. - 5.1 VALIDATION OF MEDICAL. DATA Overview ^ * "" • .' • N ' ff ' Medical record validation is planned to run concurrently with the checking, editing and coding as well as input cf the data.. It is • important that the validation and input phases are co-ordinated and that an even balance of work is maintained. Medical record validation will be 'performed by the medical record administrator (Ms. Keitha Jones) appointed to the project, with the assistance of a second medical record administrator. 5.2 Methodology Upon receipt of information from 600 Pilot Study survey questionnaires, information will be checked, edited, coded and input by key punch operators. Computer lists of all YES responses to medical questions will be generated, pjovidinr] the subject has completed the section on health care facility treatment/type of facility/address of facility/approximate date of treatment. Listings will be by subject name v/ith groupings by health care facility to be approached. Computer validation checklists will be generated for each subject, containing the following information; SUBJECT'S NAML7ADDRESS/DOB/CUESTION NUMBER (YES RESPONSE) NAME OF HEALTH CARE FACILITY. KsLhodoloyy of validation of Hospital Medical Records will be as follows: ed ValjLcintion Format •. i 1. 2. 3. 4. Condition investigated Condition not investigated Condition investigated but not-validated Condition investigated/condition confinr.ed and accounted for by known disease factors 5. Condition investicjatcci/conciitjon confirmed but not accounted for by known disease factors Lists of medical records to be viewed vill be; sent to esch hospital medic.!!, record Fd:n.unstratcr/|-or>pitfil administration with a photoco-.y of the subject's signed consent to release information. The subject's oricjinal consent forn will be retained v/iLhi.n the Her'jicicie Study offices, Each valiaation checklist v.-iJJ be coded by ths M . R . A . using the Int.c?.national C3assif.1 cation of Discr.fcas Sth. f\evJ£ion V.'.H.O. r.i> each conJition is validated. Viilidator's irdtir-ls nrid clclc of vr«.Ucation wi.ll also to eritcvecj. . �-205.3. £onditjonsjto_bc_ va3.iidatcd \ The following target organs/systems/conditions v.'ill be assigned specific disease codes, using I.C.D.9 for the purpose of validation. Broad 1.C.D.9 groupings will be used for preliminary statistical analysis. TARGET ORG AN/SYSTjFM/CONDI TION ICO GROUPING ICD SPECIFIC COOES Demiatological • Nsoplastic Hepatic Haemopoetic Immunological (Endocrir e/Me tabol i c/Nu tr i t) Cardiovascular Renal Reproductive - Male (Incl. Sexual) - Female Neurological 680 - 709 140 - 239 570 ~ 573 280 - 289 to be decided 240 - 279 390 - 459 580 - 599 • 600-608 (D.S.M. Ill) (ICO 9-300-316)? 630 - 676 610-629 320 - 389 Medical record validation will also include chocking hospital medical records for: Reported deaths of offsprings ) Reported neoplasms of offsprings ) VETERANS & CONTROL Reported Birth defects of offspring) Reported birth defects, reported deaths/reported neoplasms of offspring will be coded using JCC 9 aftc-.r medical record validation. �5 /J - Service M3d.lcal Records (covering the period of Vietnam Conflict) Army health services medical records are storeri in Melbourne (separately from the Central Army Records Office) and vail be viewed in order to determine: 1.1 Type of medical data available Number of mecljcal examinations performed Content of each medical examination Methods of question batteries/scoring used by the Army medical personnel Methods of determining medical status on entry into the army Determine who will retrieve/select 600 index cards and pre-code the information 1.2 It is proposed that the statistician and medical record administrator view and select these records for the Pilot Study 1.3 These records are stored via the last tv/o digits of the Army service number (6 or 7 digit number depending on type of enlistment). 5.5 N'qn-Service Records 5.5.1 Valicjat1on j.isj_ rig rb so ita 1 Records 5.5.1.1 in all subj ects Identification sheet/reported final diagnoses Hospital discharge summary/concurrent final diagnoses - copy retained by M.R.A. Operation charts - Various treatment charts Physician's notes (past/present history of illness to be validated) Nurses notes Consultation charts . . . Laboratory cherts/biochemistry - Abnormal rerults/x-ray/cat scans/nuclear nsdicine/special radiolog.i cal procedures Cancer registration notification and subsequent fornis .Hospital discharge reports (rases where no discharge summary is .available) ., �5.5.1.2. ^Additional sources for birth j nf onMtion nnd_bir_th_ 9^ Obstetrical charts/delivery charts Newborn (reported birth defects) charts 5.5.2 . • ' - Validation v/i. tfy General Practi t ipnsr Records The methodology will be as for hospital medical records, refer 5.2.1 with computer validation checklists, and standard contract letter (comptuer generated) requesting validation of reported yes responses to target organ conditions. The £[U_a.li_ty of_J^ta_obtG.incb_le from G.P. records is at nr_cfinnt;__an facTor._ l_ b_ ~ r r e " . o n V t x i storage iJs "well as 're IrToval we triads _ Ij> .alsojjin i'^ino\sTi_facu.or. The R.A.c.G.F. P.b.M.R. system has been Tritreauced~tC) rJany G.P"" surgeries in N.S.W. and in these cases retrieval of recent medical information should present no problems. 5.5.3. Vaiidation - - ' - - - The methodology will be as for Hospital/G.P. records and presents the sane problems of retrieval systems. Quality of data available is also an unknown factor. 5. 5. i\ ffiljdjatj.on using cithej^fedicajl ^Record Sources "... 1. Death certificates 2. Post mortem reports 3. Coroners Court Medicn.1 Records may be used for reported deaths by ir.ScTis of misadventure. These reports do not appc-;ar to be" sent to hospital medical record departments as a matter of course. /u Health Statistics Bureau 5. Perinatal Statistics Unit Commoriwea.Hh Institute of Health Sydney University - Or. Paul Lancaster. ;/ 6. Maternal and Child Health Division of Health Coniaiicsicm - Dr. . (GratUn-Smith) . • .7. Community Health Centres D. Mco'i'oank for 1975 is an unbiased although limited source of JFifonT.^tion (as a foll--bT'c!< validstion instivr.-.?nt ) . Kocovds are hold hy t!io Cc:.Y.ionwi?ciJih j>pGrt[:,ant of Health, i\\v.i could possibly be i.;s<;Ci as a va.Udat j.on fo? refiorte-c! riiar;nosr;i-> 01 as an i ncopendont source of dc:t? on ouvcer;:2. This is biing ifivcstignlf-a furth.ev. ~lhs major p/o^le-ri Et present appears to be retrieve:], of identifying :.rifonaatio;i. . �6. CONFIDENTIALITY AND PRIVACY ISSULS 6-1 Confidentiality ' \ • ' .. , • Much of the information being sought is sensitive and personal, and some may be relevant should the veteran make a future medical claim. In order to reduce non-compliance, it is essential that in format ion collected from subjects should be used only for the purposes of the investigation, and that this can be absolutely guaranteed. A unique confidential survey number v/ill be assigned to each subject and only this number wiJl be used to identify data. A separate f le vail be kept of names, service number and this confidential survey number. The investigation should be required to refuse access to individual data to any other government department or organisation. A means to ensure this is currently being investigated, one possibility being that members of the study team should have the status of Census Officers. • •• • 6.2 Privacy Medical record administrators constantly face the problem of balancing the desire for personal privacy against the need for public/research information. In many situations a great deal of personal discretion is used, since legal precedent is practically non-existent.. 6.2.1 New Sputl'i V.'n I cs privacy Corr<mij._tce_ The New South Wales Privacy Ccrrmittee was established under the Privacy Act, 1975 (N.S.W.) as a direct result of Professor W.L. Morrison's Report cri the Law of privacy (1973). The 13 robbers of the Privacy Committee have four main functions; namely - Research (to research and develop a general policy towards privacy), Complaints, Public Education, and Law Reform. •^. 6.2.2 Heal th Corr^ission _oj*__ Ngw South Wales The Health Commission of N.S.W. refers any requests for research involving difficult confidentiality issues to the N.S.W. Privacy Committee, and is usually guided by that Commit lee's decision, before allowing the researcher access to Hospital Medical Records. i The Health Cnraiission of New South Wales has also distribute:! a Circular No. 80/106, issued 31 st March 1900, to all Hospitals and Corwunity Health Centres. . . . _ . . J d °f this circular states "No information concern.! no a patient cff'cTicnr'is to be supplied to another person without the written consent of the patient or client. This written consent must be preserved in the case notes". The client must be ]'Nr GRMfD of the purposes of th? lj;-iiy requci'-lincj hir> confidential information, and must be Icyully capable of giving conse:-it. This consent must be fjccly given, arid cover what is required. Section 8.3 fAfites "Information should not b:.: supplied for ror;'X:?::!i v/ithout consc;n'L"o"fThe p'sticnl. or conbultal.icn \;i th the.1 eppropriatt; t'ics;;.ii;aj or rocjicr.n.l r.ut! ;ori ty . Attention is r'j'i'Wii vo lh:; guiciijliivji; for acccrcs vo dav.n p;:oa;ced by tn>? Privacy Commit toe". �,-./, J,^ •. . 6.?..'!>. Action^.bcinn_t_fike_n ": -24- . - Letters explaining the aims, recjirerr.ents and Methodology of the Veterans Herbicide Study will be sent to both the Privacy Convnitteo of N.S.W. and the Health Commission of M.S.W., and if required, discussions v/ill be organised between members of the herbicide Study Group and the Privacy Committee. Prof. L. Davidson v/ill be writing tc the Department of Veterans' Affairs in Canberra to address the question of confidentiality of a national level. At no time will medical records of any kinci be viewed by a member of the Veterans Herbicide Study without the express informed consent of Veterans/Controls/Wives etc. Production of the patient's signed consent will accompany all requests for medical record validation. Confidentiality and privacy of questionnaires will be maintained at all times within the offices of the Herbicide Study Group. �-25- • 7. 7.1 STATISTICAL ANALYSIS OF TIE PILOT STUDY Response Rates . > - Three types of response rates are of interest: (a) overall response i.e. v/hethcr any questions answered (? agreement to participate) * C-*) ^I^IJl^Lj^SSD^L i'G> now many ar>d which questions were answered • • - -1satisfactorily. (This is an aspect of data quality) (c) nj3dic_al_examination response i.e. hov/ many of the respondents agree •. . " to and attend a medical examination Ths rates (a) and (c) will be assessed as follows for each of the three interview modes: 100 -Vietnam veterans (V) and 100 non-Vietnam controls (C) Stratified random sample of 50 from each of V and C groups These are the 'selected individuals' Questionnaire to all 200-> Response rate (a) If 'selected individual, responds to questionnaire ascs/tain willingness to participate in nodical exmsmination On3y fcir T and FT modes,- ascertain av.tfjr.clance rate at medical exa'njnation e.sonso �tt ' • -26- . • ' ••' "' ' Sierniatycki* has found that the three interview modes yielded response rates of (a) SA - 70.3% (b) T - 73.5% (c) » FF - 84.1% Similar results are expected in our study and will be presented as follows: Interview Mode Pecentarje overall response Within respondents % positive response •' to medical SA T -Within respondents % attendance at medical (estimate only) KF The estimate of the % attendance at medical for the SA mode will be calculated on the basis of the observed mean attendance rate among those in the T and TF modes who gave a positive response. Only an estimate is to be calculated for the SA mode because of the time requirements for the pilot survey. Al] response rates will be calculated usinrj appropriately weighted values from each stratum. The rate (b) will be used to identify sensitive areas of the questionnaire whose wording should be reconsidered and to alert the statistician to tests whose power may be seriously affected by the presence of missing values. Power studies will have to be conducted in the light of the (b) response rates. All three response rates will be used as estimates of the figures to b& expected in ths main survey power calculations associated with the various hypotheses to be tested can then be made using these estimates. ". There are two important aspects here: (a) .the problem of non-response.1 on specific questions should bo' addressed. This has two obvious implications (i) can the question bs changed so as to increase response rate? (ii) \vhat is the effect on the power of the tts.ts to lie carried out ), say, estimates of the missing vnlu-is? ( ) 0. Sic;niatycki. A cornporison of n.ail, telephone and home .interview * strategics for household feaHh surveys AJi'H 69: 23B-M5, 1^75. �W ' • -27- ' (b) The problem of bias i.e. false reporting of nodical status. There are several ways in which one can try to detect this and determine hew often it occurs in different typos of individuals: • (i) use of medical records librarian to check on diagnosed illnesses (ii) use Army entrance medical examination data if feasible on some reported illnesses (iii) use incidence of medical disorders thought to be unrelated to herbicide exposure to "flag" over-reporting (iv) look at correlations between the battery scorer, on the questionnaire and on the medical. Low correlation could indicate false reporting and/or an inconsistent form of scoring in these two modes. 7.3 Comparability ' •. The issue of comparability of the V and C groups lias several aspects: (a)tfs'dicalrecords of the; entrancefcxaniwill be available on all 600 individuals. In addition, agu at enlistment, length of service and Regular/National service status are already known for each individual. (b) Additional information will only be available from respondents. It is there fore necessary to determine whether the respondent (R) c-nd non-respondent (fW) sections of the V and C subgroups sampled ore comparable. This will be done via (i) entrance medical exa<n records, age of enlistment, length of service. Rsgu 1 fir/National service status, place of residence (ii) a mini-questionnaire to Ws. This will ask for education, occupation and any chronic radical problems in self or family. • If the R and MR sections of the sample of 600 are comparable on the. basis of (i) &nd (ii) in both th2 V and C groups, no adjustment is necessary. If nnt, the differences should bs ascertained and taken into account when preparing pcv-ver calculations for the main study onci devising .possible statistical, analyses. •' (c) The R sections of tho V and C su!. groups will be compared via additional inf conation on the questionnaire e.g. nationality, income, education, occupation, ru::;.. I/urban r;tatus. (d) Within the: V subgroups of respondents it will also ht> necessary to compare ttiosr-; v;!ic went, into the; fr'.old with those v.'iio stayed on the bases. If it is founri th-:;t groups arc not comparable:, the rli f f crciv.cs should be ascortn\r-.o.n r.nrl thsir known i :i fu.oL-i in ti-.e areas of intriri-;;!: siioi .'Id br: su.'J i.o.'i oj.oscOy. Wl^vrevor povr:.bJo. t-n appj-nf)rJolo adjusl'i^nt sliould be iixjo.-i.o'-it^o in the: CM'irJoir-.. �U - • 8. • -28- . APPENDICES ' ' ' 8-1 Structure of A • - MALr QUEST IpKMIRE (For Pilot Study) 1.. Personnel information. 2. General information 2.1 Nature of study itself 2.2 Subjects participation 2.2.1. Importance 2.2.2. Voluntary • • . '. 2.2.3. Confidential 2.3 Contacts for further information. 3. Instructions. 3.1 How to fill in the questionnaire 3.2 V/hat to do with completed questionnaire 3.2.1. Where; to send it 3.2.2. Date to send it by 3.3 Contacts for help in filling in questionnaire A. Subject identification A.I Todays date A.2 ' Surname A.3 Given names " A.A Address in full A.5 Mono phone number A.6 Work phone number A.7 Confidential survey number , . - ' . . • . ' 5. Demoqraphics 5.1 'Dole of birth • 5.2 Type of place where lived while growing up 5.3 Years of schooling 5.4 Tertiary qualifications 5.5 Kaeiai origins .: ' ^ . • • ..-. 6. Occupational and Exposure History 6.1 Gencial job history • 6.1.3. Prior to go: no defence services 6.1.2 V.'hilo in defence services 6.1.3. After leaving defence services 6.2 Job contact with specific chemicals and substanc-es ' 6.4 Details of defence service 6. <';,.! Da to of enlistr.-.f.int 6.A.2 Ital'e of clisehriiVjt; 6.-'i.3 Status within service f - - t* \ t- i +• ' '• ' :' ' 6.5.1 L'Crto'ls of service 6.5.2 Details of cf;i.::iiicul exposures 6.5.2. .1 Sprayifn;, riie!.rlcMls 6.5.2.2 Mixino, carryinrj or locrJirg chi:mi.CQls 6.5.2.3 Clctrniri:; or rqi.'iin'nci equipmsnt used to carry • �6.5.2. 4 . In area while it was being sprayed by aircraft • 6.5.2.3 In area while it was being sprayed from vehicle, boat or backpack 6.5.2.6 In area where vegetation was dead and dying 6.6 Leisure time exposure to specific chemicals and substances 7. Medical history 7.1 Height ' ' . 7.2 Weight ' 7.3 Self-rating of heal.h 7.3.1 Physical health 7.3.2 Mental health 7.4 Specific medical conditions requiring validation 7.4.1 Derrnatologic 7.4.2 Neoplastic ' 7.4.3 Hepatic 7.4.4 HaeiTiOpoietic 7.4.5 Immunologic : ' • . ' ' 7.4.6 Cardiac 7.4.7 Endocrine conditions • 7.4.8 Urinary/kidney conditions " """ 7.4.9 Reproductive ' . 7.4.10 Neurologic 7.4.11 Psychological 8. History of smoking, alcohol and marijuana use 8.1 Sn-oking tii story 8.1.1 Now/ever 8.1.2 Stopped/started 8.1.3 Quantity 8.2. Alcohol Consumption 8.2.1 Now/ever 8.2.2 Stopped/started '. . 8.2.3 Quantity 8.3. Marijuana use 8.3.1 Lver 8.3.2 Quantity 9. s Marital history ' "' 9J Current, marital status . 9.2 Number of marriages 9.3 Number of relationships lasting more than 6 months .. ' 10. ljj-egrr;incy outcome 10.3 ftecord of all live births 3.0.2 Record of all occasions on which tried for n period of at least a year to conceive n child but were not ab.le lo c.io so 10.3 Record of all prrcjriTiric.ies not ending in a Live birth 10. /: i'.c-cc-icl of oil children horn with birth defects 10.5 Kf^-erd of nil ci'iildren di£;(jnosea as bejiio cancer 11. f't-STcp'Jons of hijsbindr. or ex-hutbcinds health 13.1 Pliysicr.1 health �. •• , - . • 12. Closing statment 12.1 : * -30- . . . Thanks 12.2 Reminder about what to do with questionnaire B. FEMALE QUESTIONNAIRE 1. Personnel information2. 3. General information 2.1 Nature of study itself 2.2 Subjects participation 2.2.1 Importance 2.2.2 Voluntary * 2.2.3 Confidential 2.3 Contacts for further information .' Instructions 3.1 How to fill in the questionnaire 3.2 What to do with completed questionnaire 3.2.1 Where to send it - 3.2.2 Date to send it by 3.3 Contacts for help in filling in questionnaire A. Subject identification 4.1 Todays date A.2 Surname A. 3 Given n&r;:es A.i\ Address in. full A.5 Home phone number A. 6 Work phono number . 5. Demoqraphics 5.1 "Date of birth 5.2 Years of schooling 5.3 Tertiary qualifications 5.A Racial origins 6. Occupations! History 6.1 General job history 7. Medical history 7.1 Height 7.2 height 8. History of smoking and alcohol consumption 8.1 Srr.old.ng KLstory 6.1.1 tow/ever 8.1.2 Stoppod/stnrted 8.1.3 Clientity " . 8.2 Alcohol consumption 8.2.1 Now/ever 8.2.2 Sloppy/started 8.2.3 Qjcntily �& ' -31- 9. Marital history 9.1 Current marital status 10. Pregnancy outcome 10.1 Record of all live births including children who have since died 10.2 Record of all occasions on which tried for a period of at least a year to conceive a child but were r.ut able to do so 10.3 Record of all pregnancies net ending in a live birth 10./i Record of all children born with birth defects 10.5 Record of all children diagnosed as having cancer 11. Perceptions of husbands or ex-husbands health 11.1 Physical health 11.2 Mental health 12. Closing statement' . " .- 12.1 Thanks 12.2 Reminder about what to do with questionnaire �-32•2 ' tniclurc of the M i e r i i a l r l i s ^ o r ^ a P d t e r J i c a l Examination of Adu3 t s It is proposed to examine 200 subjects and their children. The time of the medical examination will be approximately 3 to 4 hours. It is proposed to examine the veterans children at the same time generally in the company of their mother. PROGRAMME The proposed medical examination will be in six parts :Administration, medical history, laboratory data collection, physical examination, psychological tests, examination of offspring. SCOPE AND CONTENT OF THE MEDICAL EXAMINATION • 1. ADMINISTRATION - 10 minutes. During administration identification details and age etc. will be collected 2. MEDICAL HISTORY - A5 minutes. Performed by Physician No. 1. The system review v/i31 be a standard medical history with more or less emphasis on outcomes of interest. 3. LABORATORY DATA - 15 minutes. Vcne puncture to be performed by a nurse. Laboratory data to provit!?. haernato.logy and biochemical information. - Provision to be made for serum storage at -70-' C. The nurse will also record vital statistics e.g. height, weight and supervise spirometry. 4. PHYSICAL. EXAMINATION -• 60 minutes. Performed by Physician No. 2. (i) General examination major systems. (ii) Skin examination with photography if necessary. % " . •(iii) tourological examination. • (iv) [-.'Xcittination of target organs e.g. liver, spleen, 3'yrcph glands and testes. 5. PSYDDLCGICAL TESTS -• 60 minutes. Proposed Psycho] coir;:-:! ttsts are the Corne.l] Index (C.I..) end the M.innesot'i! ;>j]tiplujs;ic Personality Inventory (f..Mpj). Two olhc:i indices tl>:>.t may be suitable are K:inn corisidarrd - tho Onr.t? tv^siJonnaire and the !5ock Octpressic.i :nvc i ritory. A re-run of the Army's pjycholorjical tests prior to ent:y into i'ho servicos is being coroicirred. iics'i tests iiifiy be yr^inisVcrc-'Ci by <; nurse. �-336. OFFSPRING •' - ' • - . ' . - examination to be performed by a Paediatrician. (i)• General physical examination. (ii) Birth defects. . 8.3 Medical Examination of Children '., -. •' ' .. •• As previously stated it is intended that the children of veterans be examined by a Paediatrician at the same time as the subjects are being examined. Resources are being planned on the basis of examining approximately 400 children. .. The medical examination of the children will have as its objectives: 1. An estimate of present state of health. 2. Recording of any observable birth defects 2.. _ _ validation of any reported birth defects or medical conditions. A provisional list of birth defects has been compiled based en tht birth defects to be included in a case-control study of the effect of service in Vietnam to be conducted by the Center for Disease Control, Atlanta, USA. A parent of the children will be asked about the listed birth defects and confirmation will bs sought cither with evidence of surgical correction or at physical examination. Where the terminology is general and a positive response is obtained, specification and confirmation will be obtained via hospital and doctor nodical records. �d . -34- 6.3.1. List of Birth Defects . SPINA BIFIDA AND/OR HYDROCEFKALUS MICROCEPHALUS • NEUROFI6ROMOTOSIS . -' ' ' ' < ' "' ANOPHTHALMOS MICROPHTHALMOS • . ' BUPHTHALMOS CONGENITAL CATARACT . . ' COLOBOMA ANOf/iALY OF TIE EAR - IMPAIRING HEARING KIART CONDITIONS CONGENITAL CYSTIC DISEASE OF ANY ORGAN ANOMALIES OF THE GASTRO INTESTINAL TRACT CLEFT LIP AND/OR PALATE HYPGSPADIUS EPIDSPADIUS . ' . ANOMALIES OF THE URINARY TRACT ' ANOMALIES OF THE FEMALE GENITAL TRACT CLUB FOOT REDUCTION DLTOrWITIES OF THE LIMBS CHONDRODYSTRCHIY OSTEO GttlESIS IMPERFECT A HEREDITARY OEDEMA OF THE'LEGS SPECIFIC ANOMALIES OF HAIR SPECIFIC ANOMALIES OF NAILS ANOI-IALIES OF TH: ENDOCRIK:: SYSTEM ;/ SITUS INVERSUS DOWNS SYNDROME DI AF'HfViG 1ATIC HH^I A CONGENITAL NEOPLASf-! ' - CYOTOMEGALO VIRUS - HERPES SIMPLEX SYPilYLIS ' ' - �SECTION 2 DRfiFT REPORT -:.26/02/81 HERBICIDE EXPOSURE IN VIETNAM CONSIDERATIONS JOHN ROGERS �1. INTRODUCTION - 1 t 2. HERBICIDES USED BY US FORCES 1 3. HERBICIDES USED BY AUSTRALIAN FORCES 4 4. NON HERBICIDE EXPOSURE 5 . 5. SUMMARY OF POSSIBLE CHEMICAL EXPOSURES IN VIETNAM 5 6. MODELLING EXPOSURE 6 7. DATA 8. . . . 6 AERIAL SPRAYING - a) Spray drift ' " 8 i) "Deterministic" model. Conclusions ' 8 10 t ii) "Statistical" model Comments 9. RECOMMENDATIONS 10. REFERENCES APPENDIX I 11 11 -• ' ' .7 13 - - '' -. 14 ' . Comments on Recofiimondations . 19 i. APPENDIX II Additional references required APPENDIX III "Statistical" model 20 - . 23 �Research on 2,4-0, 2,4,5-T and related herbicides began during World War II, and had at that time a clearly military connotation. However, herbicides were not used for military purposes in World War II. The first, small-scale military use of herbicides was in the 1950's in the Malayan "emergency". In tha early 1960's the possibility of tactical use of herbicides was given considerable impetus. A number of herbicictas were evaluated, in various combinations, for their phytoxic effectiveness in South Vietnam. In South Vietnam, the first military herbicide operations were carried out in early 1962, and were phased out in 1971. After a relatively slow buildup from 1962 to 1965, the operations increased rapidly to a peax in 1967, declined, but only slightly, in 1968 and 1969, and dropped sharply in 1970. According to information from US Department of Defence, the last herbicide spraying by fixed-wing aircraft was flown on January 7, 1971. After this, herbicide operations were limited to spraying around perimeters of the fire bases, on enemy cache sites, and along land and water communication routes, and v/ere all carried out by'helicopter or on the ground. The last helicopter operation under U.S. control was flown on Cctooer 31, 1971. Herbicides used by US forces The herbicidal "Agents" used for military purposes in South Vietnam were identified by cods names referring to the color of bands painted on the containers of the chemicals. These of interest to thisstudy are the Agents: Orange, White & Blue. Agent Orange is a 50:50 mixture of the n-butyl esters of 2,4-0 ([2,A-ciichloroprTenoxy]acetic acid) and 2,4,5~T ([2,4,5-trichloropnenoxyjacetic acid). Each gallon of Orange contained t\ ID of 2,4-0 and 4.6 Ib of 2.5,5-T en an acid ectjivalent___ _ basis.3 Orange was tne agent used most extensively in uris Vietnam war" until its use was terminated on April 15, 1970 because of the concerns of its possible teratogsnicity and its concaminati.cn with the highly toxic TCDO (2,J5,7,8-tetrachlorodioerizo-para-dioxin). /\g_cnt Wnite is a mixture containing 2 Ib of 2,4-0 and'6.54 Ib of piclordm"(4-amino-3,5,6-trichloropicolinic acid) per gallon on an acid equivalent basis, (or 4:1 on a molar basis). It is a formulated product containing 2,4-0 and picloram as the triisopropsnolamine salts, with tne addition of surfactants and water. *This introduction is based on material in reference a (17). Acid equivalent is the weight of the acid form of the chemical, this is used oecause the weights of various ester or amine formulations vary. Expression in terms of acid equivalents provides a uniform basis for comparison of different formulations �Avjgnt Bluj3 was formulated as the sodium salt of cacocJylic acid (hydroxycrirp.nlnylarsine oxide). It contained a minimum of'21 percent sodium cacciiylate v/ith additional free cacoclylic .-jcid for a total dimetnylarsinic acid equivalent of not less tran 26 percent on a weight basis, or 3.1 Ib of cacodylic acid and about 1.7 Ib arsenic per gallon, v/ith 5 percent surfactant and 0.5 percent antifoam agent. All agents were intended for use at a rate of 3 gal./acre (28 litres per hectare), except that in the earlier operations and on rare occasions thereafter, only half of this dose was used. The homicides were applied oy US forces fixed-wing aircacft (UC-123), helicopter (UH-1), from trucks, from river boats, and from backpacks. South Vietnamese forces may have also oeen involved disseminating the herbicides Orange, White & Blue by these methods. Both aircraft types were outfitted with special spraying equipment, consisting essentially of a container for the herbicide and a spray boom witn nozzles. The container of tne UC-123 spray system had a nominal capacity of 1000 gal. -and the plans normally flew at 150 ft. (45 m) with a delivery speed of 130 to 140 knots. The "spray-on" time of 3 1/2 to 4 minutes permitted approximately 950 gallons of herbicid-j to be distributed at the rate of 28 litre/hectare over a path of 14 km length. During the peak of activity (1968--1969) approximately 30 C-123/UC-124 aircraft were employed. However, r'nany other squadrons of C-123 aircraft were used routinely throughout South Vietnam in transport operations (4). Tne capacity of the UH-1 spray system container was 2GO gal. but the helicopter could carry only 100 gal. d'js to weight limitations. Spraying by fixed-wing aircraft accounted for the greater majority of the nerbicide used in the Vietnam war, at least into the later part of 1970 from which time on helicopter herbicide operations increased and gradually became predominant, until they became the only aerial means of heroicide delivery. (17) The amount of herbicide used by year is listed in table 1 (17) and the estimates of quantities of herbicide component total usage is given in table 2 (66). Tne region that received the greatest concentration of herbicides was the Rung-Sac Special Region south of Saigon and adjoining Pnouc Tuy province (where tns Australians were posted). This level is reflected in the quantities used in military region III which included the Rung-Sat Special Region (taole 3). Trie correspondence of spray missions in military region III and ins positions of Australian soldiers has yet to be determined - and the numbers involved is suoject only to conjecture. �Tablc 1 Application of^.. War_by Year (17) 1962July 1965 Millions of Aug-fec 1965 1966 1967 ._ 1968 Orange NAa .37 White NAa 0 Blue NAa 0 Total' 1.27 ' .37 1.64 3.17 1969 _ _ 1970 Total 2.22 3.25 .57 .0 0 11.22 .53 1.33 .2.13 1.02 .22 .01 5.24 .02 .38 .28 .26 .13 .00 1.12 4.83 4.63 4.53 .97 .01 18.85 2.19 a Not available TABLE 2. Estimated quantities of herbicicios ijr-.ci TCDD ciiggeminaterj in _ Soutn Vieinc.:,\ frc.~'. January ic^i2^(^ru^ry_I97i_ (6i) Chemical Pounds 2,4-D 55,940,150" 2,4, 5-T 44,232,600 363 F3icloram Cacodylic Acid Total of Herbicides 3,041,800 ,3,543,710 106,763,260 Tne mean TCOD concentration in Herbicide; Orsngn was estimated at 1.93 ppm. v• �TA3L£ !> y.^Jj?LrbJj:lc^^ . ' A : ' '' Herbicide Expenditure (gallons) Orange White Blue Combat Tactical Zones CTZ I 2,250,000 363,000 . 298,000 CTZ II 2,519,000 729,000 473,000 e 5,309,000 3,719,000 294,000 1,227,000 435; ooo J#,p_00 5,2/16,000 1,127,000 * CTZ III (includes Saigon) CTZ IV Subtotals J,227,00 Grand total * Source: HERBS tape (65) Herb,icides strai ion f orces Australian troops may have also ooen exposed to herbicides sprayed for perimeter vegetation control around the Australian camps. The cnemicals used were on the whole obtained commercially from within Australia and included GRAXX3XONE (paraquat) REGLCNE (diquat), TOROON 50D (piclora;n/2,4-D) and HYVAR (oranacil). Tne annual usage in Vietnam -in -the years 1960 to 1971 was of the order of ( ) 6: 9,000 liters of diquat 1,600 liters of TORDON 500 4,000 kg bromacil .• •' Cofn.T.encing November 1967 a field investigation was conducted under scientific supervision to establish the metnodology for disseminating tnese herbicides. Suossquent to toxic effects b:>ing found in operators -breakdown of mucous membranes, nose oleed-5, ulceration of lips and conjunctivitis - the use of DM50* was discontinued and strict procedures for handling were recommended (31). In addition the Department of Defense "accords a fairly high degree of probability" that the Australia Task Force procurrcd and used 1,000 gallons of Agent Blue (cacodylic acid) obtained from local sources ( ) 6. * DM50 is a chemical which accelerates the uptake of herbicide into plants, and unfortunately has tlu same-effect for hu-r.ans. �-5- Non Herbicide Exposures • •• . .• Further to th3 heroicides diss-^rnnunated by the U.S. forces, the Australian troops may have co;na in contact with Ma.lati~i:'.on sprayed from specially prepared C--123 planes or "uug-biras". • The Malathion was selected for malarial mosquito control on advice frcin the World Health Organization. Unlike the hsroicidcs which were sprayed in "remote" areas the Malathion was sprayed "indiscriminately" over populated areas, "even whole to,-;ns" (A.L. Young, private conuiunication). These aircraft routinely sprayed insecticide adjacent to military and civilian installations, as well as in areas where military operations were in progress or about to commence (4) Medical treatments are also of interest, in particular (1) antimalarial drugs including the experimental drug Dapsone which was used oetween 1969 and 1970and withdrawn after adverse side effects and (2) innoculations for Plague which too had adverse side effects but remained in use. Summary of possible^ j^hj^nica 1 exposures in ^i.".tnam. Thus the chemicals which are of interest to the Australian Veterans Herbicide study are: 1. Agents used by U.S. forces (a) Orange '(b) White . . . (c) Blue . (d) Malathion; ;"•"" . .. . . 2. "Agents" used by Australian forces (a) Grammoxone , / (b) Reglone (c) llyvar [(d) Agent Blue] (e) Insecticides; 3. Australian Medical Treatments '"V- (a) Antimalarials (b) Plague innor.ulations. *" " i �• Modjjllincj exposure -6- . The object of the Veterans l-brbici.de Gtuay is to explore the causal effects of hcrbicirJe exposure in Vietnam with regard to possible adverse health outcome in Australian Vietnam Veterans. The hypothesis that a certain herbicide (or even combinations of chemicals) could cause the undesirable health effect can only be demonstrated by being consistent with the current knowledge of the chemical(s) biological action. Secondly to validate the supposition a dose-response relationship must bo shown i.e. TTe health effect should increase with increasing exposure. Any attempt to determine the 'dose1 or exposure of military personnel must be predicted on events that occurred at least ten years ago. Since there was no sampling program associated with the handing or dissemination of the heroicides in South Vietnam, a . quantitative determination of exposure in terms of actual dose can only be suoject to speculation (/'O. • However, it is still possible to determine "relative" exposure levels. For tne "Agents" of greatest concern, namely Orange, White and Blue, it is true to say that exposure did not include all Australian servicemen. Moreover, within the military population at risk, the range in magnitude of exposure must have been great. The range is so great that it is plausible that the possible errors in predicting this "relative" exposure may be less than the range itself. Data To predict exposure levels with certainty it is necessary to have a minimum of verifiable data available. To demonstrate a possiole causal or 'legal' connection requires a higher standard of documented information. Exposure to Malathion is a case which amplifies this point. No documented information regarding the "indiscriminate:" spraying of this substance is available. It may be possible to show relationship between otner highly correlated confounding factors, such as corneat duty or season and presumed Mslathion exposure. .Witnout supplementary documentary evidence it is impossible to separate the effects of the selection criteria from the exposure. A correlation between such "Malathion exposure" and health effects would ue insufficient to prove the causal nature of exposure. There is no way that such an effect could DC ascribed to the exposure to Malatnion alone. To obtain a presumed exposure level for Agents Orange, White and Blue the follo.vjng sources of data are available: 1. The so called "HERBS" computer tapes which document the herbicide sprayinfj missions of United States fixed wing aircraft, [approximately 8CK of total heruioido dissrainated by �-7- Unitcd States and South Vietnam forces is documented on these tapes]. The information on tape includes: Start co-ordinates, finish co-ordinate, gallons of agent and type of agent. The spraying from helicopters is omitted - as is record of aerial spraying before 1965. 2. The Australian army has supplied the locations of approximately 70% of Australian Units [based on commander diary information]. This is the so called "CM)11 data. Vital co-ordinate information is currently incomplete, but should be able to bs obtained. 3. A comprehensive survey of all Army personnel in South Vietnam to be conducted by this study will include questions .to fill in information gaps i.e. Report possible exposure to helicopter spray missions; unit postings (which are not included in "CARD" data); subjective information on exposure to handling herbicides, spraying from backpacks, trucks and boats, to aerial spraying and to.areas that were recently sprayed. Questions allowing the assessment of the internal consistency of the soJrces of information are to be included. 4. Survey questions will include checks for accidental and occupational exposure to phenoxy herbicides, arsenicals, asbestos and other Detrimental environmental agents outside the potential exposure in Vietnam. Aerial Sgrayjnc[ ' • • ' The exposure to the aerial application to these agents may be separated logically into four areas: a. Spj?ay_drift and concentrations in "jungle"* from aerial application. This concerns the fate of spray from the time the spray leaves the plane until spray particles impact on the jungle foliage, tree trunks and ground and to the herbicide distribution within the jungle ecosystem. •b< J^LF.°_nrO°nt£LOLa!LG. in JunQle 3nc' hence likely sources of contamination. Addresses .the following areas: i) volatalisation and revolatalisation ii) pnotodeconiposition and biodegredation of herbicide components • iii) redistribution of herbicide components within the jungle environment e.g. after leaf fall iv) Bioaccumulation "jungle" is used to indicate all possible tynes of vegetation such as forest, savanna, mangrove, swamp and cultivated land. �• -8t ^ • . c. Exposure ^nodes; i.e. exposure via dermal, alimentary and pulmonary routes including relative absorption values and likely sources of contamination via eacli route. d. Exposure categories i.e. use current data in the scientific literature to choose a_ priori meaningful exposure level categorisations. a) Spray drift There are two models which are proposed for spray drift calculation. They are not of necessity mutually exclusive and are as follows: i) J!te_teiininj.stic^ model of spray fate. "The generalised model format is for a mass continuity equation that in principle provides a complete description of the trajectory and properties of an aerosol or heavy particulate cloud, from the time of cloud stabilization to the collection by downwind surfaces. The terms included in the generalised model must therefore specify the direction and rate of downwind cloud travel, the alongwind crosswind snd vertical cloud dimensions of travel time and distance, the distribution of material within the cloud as a function of time and distance., and loss of material through gravitational settling, impaction or deposition on vegetation or other surfaces." (19) Ine model snculd also provide for the. effects of variations in chemical and physical properties of the material contained in the spray cloud e.g. the volatility of components; the mode of release and source emission time; and in meteorological, micro-meteorological, terrain and vegetative factors. Spray "drift" is used interchangab.lv to describe two distinct processes. Trie first type of "drift" refers to the variation of the actual flightpath to the "HERDS" data and the second to the .spreading of the spray cloud due to physical and meteorological conditions. The former could conceivably be tens of kilometres while the latter should be 1 kilometre at most. Although it has been stressed that the pilots were able to lay spray swaths accurately and that drift "just did not occur" (A.L. Young private communication), [Herbicide]" mission commanders stated that drift was a common problem and could extend frcv.i 1 to ?. kilometers. Ons "Rancn Hand" commander said in several cases drift could be up to 10 k:n. (These .instances were mountainous regions usually occupied by enemy forces) (18). r To reliably estimate the spray fate requires the following information. 1) Jl^UyJ__fJ^Y,.:path. The "IERRS" tapes give: the positions of flighupaLn""cn;ipaj"rits. SJncc all trie 1'jxed wiivj mission �preparation included aerial reconrmsanoe it :n<ay bs assumed that the endpoints or at leas'; the startpoint was relinbJy achieved. However it has been stated that the actual flightpath may have deviated markedly from a straight line (A.L. Young private communications) with terrain being a major factor. Furthermore, if a mission involved clearing jungle along a river bank or road, the straight line approximation would be grossly in error*. 2) Sp_L?iy_.-PJ:lliy£.icl sizs,_o'iRt.ribution is a critical factor in determining drift potential "revolatilisat Ion arid particularly fate within the jungle canopy -- drops smaller than ISQuci would .pose a problem. If the spray is volatile, i.e. Orange, the larger droplets can vapouriss to these dimensions, exaggerating the problem. The droplet size is highly dependent on viscosity, nozzle geometry, spray system pressure and aircraft speed. Incomplete data on particle size distribution is included in Table 4. . k TABLE 4 Spray characteristics of C-12'.5 Modular Internal Spray Systern_._TflTTs'pray m'aterlai'uhkriov/n'j" Aircraft speed Aircraft altitude Tank volume Spray time Particle size: (percentage by volume) 100J 1.9% . 100-500U 76.2% 500 130 Knots 150 ft (45 m) 1,000 gal (4,500 1) 3.5-4 min • 21.995 87% impacted within 1 min 13K drifted or volatilized Mean particle volume * • 0.61ul The committee on Effects of Herbicides in Vietnam (17) found several instances where defoliation missions were more than 8km from the nominated path. �The problem of volatility would also affect the water soluble Agents Blue and White which were sprayed in a concentrated form. Experience in agriculture has shown that it is possible for the water to vapouriss from spray particles leaving a dust of the concentrate which impacts with extreme unreliability (70). The effect varies inversely with droplet size. The water solubility of these Agents mean that they have a vastly different environmental fate if it rained within 6 hours of application. Il^rpjnme^ejrolp^Y.. The "deposition and/or drift of a spray cloud is hlgnly dependant on the locajL_ meterological conditions. Such factor as terrain, jungle surface and tiros of day dictate local v/ind direction, thermals and inversions which are impressed upon the larger scale weather patterns. Fortunately jungle provides micrometerological patterns which are stable over large areas so reliable predictions are possible given the factors of terrain, jungle surface, time of day and weather. A factor which interacts considerably with micro-meteorological factors to produce drift is aircraft spray height - it must be stressed that, although highly dedicated, the US pilots were operating undsr combat conditions, in many cases over difficult terrain so that the value of 150ft (45m) must be treated as a nominal altitude only. Conclusions . - The overwhelming problem yet to be faced is that of the validity of this model. Agricultural experience (70) has shown the inadequacies, even disasters, of models of spray behaviour in well controlled situations. The variety of specialised models available and the controversy over their validity (0), (9), (19), (70), (71) illustrates the potential problems. Furthermore the available models concern the application of dilute solutions (of ths order of 1 in 100) applied over an even crop surface by single lignt plane from an altitude of 3 meters •versus the situation in Vietnam where a concentrated solution was applied over a rougn jungle surface by a formation of cargo planes, flying at a nominal 45 meters. The utility of such models to the Vietnam situation could only be classed as fortuitous. In addition volatile esters "were requested [and used] in order to achieve more uniform coverage withj.n_ a forest csnopy"(66). Thus the volatilisation from puri:ic.U>s~~wiv.hin the sp ay cloud and from herbicide on leaf surfaces must, be included in any model of spray fate and/or exposure. It is obvious that there are many problems to be addressed before the deterministic mocisl would be a viable preposition. Validity could only be assessed by a careful re-enactment of the Vietnamese spraying operations under a variety of operational and wea tt if r cone1 i ti ons. �-11ii) Statistical Model The requirements of the "deterministic" rncdsl for hard data may not be fulfilled from the distance of time so it is suggested that a simpler "statistical" model of spray fate be used. It will be assumed that the planes started from the "HERBS" startpoint and headed in the direction of the endpoint. The variance of the probability distribution function of the actual fligntpath is assumed to increase with increasing distance from the startpoint. The "actual" endpoint is distributed at a mean distance of 14 km from the startpoint. The percolation and vertical distribution of spray within the jungle is more complex. The "deterministic" model would be of great benefit in calculating this distribution. The most satisfactory method would be to assign various fractions of the spray cloud to the sections of interest in the jungle ecosystem i.e. soil and lower canopy. 'The spray swath distribution function is derived assuming the flightpath is known. The major factor affecting variance of this distribution function being the number of aircraft and the terrain. The position of the troops will be treated as a two dimensional gaussian distribution centered on the "CARD" data co-ordinate. The variance will include such factors as co-ordinate accuracy and whether the troops were on patrol. The time effect is included in a simple exponential model of herbicide component decay choosing appropriate decay rates from the scientific literature. The effect of vegetation cover protection and exposure modes is included as a multiplicative factor. Considering ths simplifications so far, it is proposed that a simple cumulative model of exposure be used, giving relative exposure days as an output. (For the full mathematical treatment see Appendix III.) Comments The relativity of unrelated modes of exposure poses scientific problems which will take at least 6 man months to treat. References (!>), (22), (26), (40), (41), (42), (50), (_58) and experience in Australia with council workers spraying 2,4,5-T coupled with U.S. Air Force documents (currently requested) concerning calibration and spray simulation will enaole a reasonable connection to be obtained. The latter documents will also provide a more accurate basis for the numerical values proposed in Appendix III. The work of Isensec (35) tins shown that bioaccumulation .(1000-6000 x accumulation) of dioxin contained in contaminated silt is possible by aouatic organisms. Considering the volu.v.s of Agent Orange (the source of dioxin) which was distributed over the Rung Sat �-12fishing region it is dioxir, contamination highly cpcculntjvs. health effects it is significant fraction highly probable that seafood was a source of - the relative amounts and significance is For the purposes of regression analysis on hoped that this background exposure is' no a of the total exposure. �-1J5- ftecojr[fiy ndnt i otis_ 1. Run modified "HOPPS:I program using simple assumptions to estimate size of exposed group. 2. Maintain liason with Australian and U.S. experts in the fields of Pesticides. 3. Continue collecting relevant articles from World literature. . • 4. Develop models for (a) Spray drift (b) Environmental fate of herbicides (c) Exposure modes (d) Exposure categories. 5. That the models of drift and environmental fate be tested using • simulants to assess likely validity of theoretical predictions of drift and foliage penetration under conditions similar to those in South Vietnam. / 6. The proposed models should be subject to extensive scientific peer review �-14- 1. Comments by Dow Cftem j.cal Company on oresqntati.cn JTttr!<2_by_ D,r. _T.D. Sterling Royal COTnissiori~ - Herbieldejs~and PesTicicias 1973 2. Report of ths _ Consul tatlve Council^ onjconqonital abnormalities in j:hs Yarram District Oept. of Primary Industry" Canberra 1978 ~ Principles and Methods for jevaluat Ing the _tox ic i ty_qf_ chsm icals. ! Environmental Health Criteria' 6 TiHO 1978" " " " • Part 4. Criteria for Cstsrmlninn,_E_xpjJsu_re_ Leysjs^M-l.i.H taiQL^_rs5nr}? 1_ to^jjloxin and j-ieraicida drangs during t^e'vTet'nam War TcJra'Yt) USAF " ~ 5. Advisory Committes on Pesticides Further _Rov .lev/ of the Sa.rety For use In ths U.K. of the Herbicide 2,/t,3,-T "- 1980 6. Pcstlcidos used in Vistnafn Host 11 i t i e s and t_hg 1 r u se . in _ Agriculture : Ccnparitivg Study (draff) Environmental Health ' Dept. Health) 1980 7. Anon Report^ qn^ the Asrial uss(_of_ Phenoxy Horb-lcides Department of Food and Agricufuffe California 19"78 6. Bache D . H . , Saye r W . 3 . D . Transport of Aerial Spray, I.__A mode 1 of Aerial Dispersion Agric. Meterol. 15 pp 257-271 1975 » 9. Bache D.H., Uk S. Transport of Aeria 1 Soray , n_.___ Igsnsp^or t jvithin a crop canopy Agric. Meterol. 15 pp"3Vl-377 1975~ 10. Barnes J.M. 11. Bartleson F.D., Harrison D.D., Morgan J.D. Field Studies of wildlife exposed to TCDD contaminated .Soils AFATL-TR-75-49 "1975 . _ Assessing Hazards...Fro_m low doses of toxic subs cancels Br. teci. "Bul." 31 op I95-2CO 1975 * 12. Baur J.R. , Bovey R.W., McCall H.G. Thermal and Ultraviolet loss of Herbicides Arch. Environ. Contam. Toxicol 1 p'p 239 -"302 "1973 '13. Bbhm H.H. , Muller H. Model Studies on the Accumulation^ _p_f ferbicides LJ Microalgae NaturwissensnaYten 63 p296 1976 14. Bovey R.W. , Young A.L. The Science of 2, A, 5, -T and Assqciatsd Phenoxy Herbicides Wiley I960" 15. Byast T.H., Hance R.J. pj^gr^djrti^njpJL^^ Soils _lncupated_ in tjng Ll^oo^s 'cory_ - 197? 16. Cocucci S. e al AbDrotinn_jridjrrr.nsJ.oj;a^i_o_n_jDj^_.t^^ ^ 17. '*'•* PP;*y2"-'tS4 1979 Committee on the Effects of Herbicides in Vietnam The__E_ffects_gif l'!?rJi-iP^.es_-ir] A°'^^_/J ' ^ l . . J ~ Summary and Conclusions "National clL^^l Academy of Sciences �-15Comptroller General L!Lj> i_£rcyn_cj__Trc:qps In _Squch Vlelna'n v/ere_in areas sprayed with Hgrbicide rj'vanrfj' U."5~ iJelTcral /\ccbjntin"g'"orrTce l~979 "" 19. Cramer H.E., Boyle D.G. llj£jiicnLn£^ particle; behavlcijr - - 20. Crosby D.G. Conquering thg Monster — T^e_Phgtpohemicaj[_ Past rue tign^of ^l°J!P.cl-i9£iP_5. 1'^itn MaficnafMeeting oT Arr.erican CheinicaT'SoH'ety 1977 "(See Kcport on Aerial use . . . ) 21. Crosby D.G. , Wong A. S. ^ ~ " " ~ ' 19/7 22. Phar M.M., Tandon J.S. , Sircar K. P. ^sorpUon_ejTd_Dccretionjof 2 > A,.'j-TrJ L chlqroo(ienoxy Ac st. ic_ Acid^in Map "Arch ."frit r'PharTikYcody'n . 210 pp 230-255 "1974" 23. Dodge J.M. 24. Donaldson T.W., Irvine F.N. 2j_A, 5-T Res iducs in Dlackbsrry_Fj.'iji t Asian v/sed Science Society Corif. r979"~ 25. Farwell S.O., Robinson E., Powell W.J. , Adams D.F. Survey of airbourns 2, A-D in South Central Wash i ngton J. Air. Pollut. Con cam. '26 pp 22A~-3"i5 1976 26. Feldman R.J., Haibach H.L. PgLrc^tenpous^onstrabion of ^sornu^Postj.cides and Herbicides in Man Tox. Appl. Pnarm". 28"pp 125-132" 1974 27. Gsbefugi I., Baumann R., Korte F. ^^c^j^^sr^^j^cr^j^jj^^ • jiJCOD) unter simulierten Ur^^^ltbediTp^j'sn Naturiwissehs'ci : ialf"tibn~64 pp 486-487 1977 . 28. Gehring P.J. e_t al_ The Fatc_qf 2.4,5-T Following Oral Ad.T.inistratiofi to Man Tox. Appl. Pnarm. 26 p'p 352-"36l 1973 " """" ~ -- -- Trig Phenoxy Hgrblcidss - A Sum:nary - 1977 7th 29.. Hance R.J. Herbicide pgrsistence and breakdown in soil in the long term Proc. Assoc. Ap"p"r~Biol.~ - 30. Hiles R.A. and Bruce R.D. ZjJiLJbL^A^JlL0^ elimination _in the rat: First Trdgfr"6'f'"zc'r~o_ n'fdpv?" CoVtneuT'l'oxicol. 14 pp 599~ 600 " 1976 31. Holt E.S. (Major) ^Rsoort_of_the spraying oif J tJ rbic_l_des at_ J.st_ ArA.U~.FiVG" RopoiT "2/68 "1963" " " • 32. Hook J.B., Cardona R. Osborn J.L., Bailie M.D. The Renal _Hand.li.na of Cosmst. Toxicol. 14 pp 19-23" "1976" 33. I ARC Monographs Vol. I ARC Lyon 1973 2 34. 1ARC Monographs Vol. 15 Some' inorgcinic f.nd £rnono^J.alic_cp;i:f:ioi.ind_s ...... " ..... " .................... ~~ ..... """ Somq_ Fu^^ntsM-fi^JJ^ �-1635. -I ARC Monographs Vol. 23 Borne Mstals and Metallic Compounds IARC Lyon 1980 " 36. Isensee A.R. Bioaccumulation of 2,3,7,8 (TCDD) in 'Chlorinated Pnenoxy Acids and their D~ioxins'~~Ramel (edT~ 19/8 37. Isensee A.R., Jones G.F.. /V3sprDtioj}^ajid_Tjraj}sj^c_a^gn_o^f Rggt_ and Foliage^Applied ^^-Dichloroohe^nqi^ 2.71 - bTch j qrod i o'^n^p'-pj:dioxln . and 2,3,7,8 TCDD J. AgrTTood" Cnem. 19 pp f2J.O-f2i4 1971 " 38. Kimbrough R.D. (eu) Halogenated Biphenyls,, Kaphthalenes, pj.benzgdioxj.ris and related products Elsevier North" riofland "J980 39. Kirkwood R.D. Plant target areas and methods of attacking them Application of Pesticioes 2 Cranfield i960 40. Aerial Kolmodin-Hedrnan B, Erne K and Akerblcm M. flielo^/\Dp_lic_ation_ of pj-ienoxy • •herbicides in Field Worker Exposure during Pesticide Application ~eo TordoTr 1979 Al. Lavy T.L. Measuroment of 2? A, 5£T exposure of^forest workers Forest Produces" A'ssociaton 1978 National A2. Leng M.L. ReaHstic Evaluat3.on of J-brcan Exposure jTrgni^aopj ^-^^j 2,4,5-1 sprays Dow" CneiiTical Co.Tipa"ny " 1973 43. McNulty W.P. Toxicity 0/2.3,7,8 - Tetrachlorodibsnzo-n-:dioxin for Rr^S'JS Monkeys: Brief Rdporu Bull. Environ. Contain" l"ox~r8~pp""l08""-109 1977 44. " Nash R.G., E3eall M.L. Fatc_of_Si IVRX,,^!^. ,_ip_ _and ?-12i2jQj TCODJn_a ' mlcroagroecosystem chamosr A3S~PAP AM. Cl-EM "socTl"75 p$T"TsT78 " ' 45. Nash R.G., Bsall M.L. Distribution of Silycx, 2,A,-D and TCDi) toplipd •• to Turf in _Chafnbers and Field P'fots J.~Agric. cFicm. 28 pp ~5"i4^623 J'980 46. Office of the President Report_on_ ^Jl^T A report of the panel on Herbicides of the -President 's'Scie'rice Advisory Committee. C.M. McLeod Chairman. Office of Science and Technology 47. Poland A., Glover E. , Kende A,S. SterpqopecJ.fic_,_ . of 2, ^i 7j 8 - 1 e t r ach 1 o roc! i ben ?. o -r^-c'l J c"x ih_ J5£jj(T>a Qc'M:o\Jal "" " ?." IB 6l Cnem 2M "pp 4936~494"6 "1976 48. Poland A., Kende A. ^JJ^.S-leJij'ajphl^orcciibjijn^ cpnt: cmi j r.ant and m J l c u I V P "f'^'J- TTOG" "35 p p ~ 49. Poland A., Kendo A. 50. Ramsey J.C., Lavy T.L. and Bra'jn IV.H. 51. F^pgiyni G. EstJnintion of thc_l_CDD tpxic_ppU5nt,:lnl in " ~ ' ~ C c n i L~" S'c,c'.~ ~ioxjf.:ol "[i''t-"i"iii"i7"" " " ~ " TlTe_Gc>nct}c_Exprorision_of AHM ActivJ.t'y:_ ryidRnc^ _ j n fYaTrpsZibn'sTv'r:''jn]"c"ii ~ "" " T.97'7 "........." E_x_nosurc of For r. s i: " Wo jJke r s_ t.g ' ~ ' " ' " �-17- 52. Rose J.Q. ej: al_ The £ate_ pXJ?^ _ _ following single .ar.J"repeatwT Or'al_"Do5es~"to JtiiVT<at~"~Tox. AppTr"f3harm. ' 36 pp"209-226""T976" 53. Schultz D.P., Harman P.O. Residues of 2./i,-D in Pcr.d Waters, Mud, and Iis!lJ.2Zl Pest- Mon - J - 9 PP 173-179 1974 ~ ~" 54. Simpson G.R. Aerial Spraying - S a f e Use of PesUoidgs on Cotton Crops Health Commission of N.S".-W. 1979 " ." ' ". 55. • 56. Sirons G.J., Frank R.F., Dell R.M. PicLojran^Rsjsid^^ Macdonal^^Cjrtj/jr Freejway Right qf Way^ BGl~i EnVir6rr."c"bn'ta"?Tf.~ Tox. 18 pp 526-533 1977"' Stevens T.S., DiPastiuals L.C., Farmer J.D. Acu^c_IJiha_latJLO^Tcx_i£(y_ooy__ ' .1 Herb icicles, .CscocfylTc "Acid and" . _ _ Disodiuir. Mathanoarsbnic'^cicl Bull. Environ. ContarnrTox. 2Jrpp'"Jo?i-311 ••a— - -• ••HI •• — I • • I* .-».•-.<•••-*—..—J»^. . J.. II I •— i . I I 1979 57. Stewart W. A Retrospective Study of Agnnt_0^ange_jnnjj Vietnam Veterans (Draft)~ US" Veterans7\3sbciation 1979 58. Tordoir W.F., Van Heemstra (ed) T. Field_ Workgr Expos-jre duri Pesticide Application Elsevier Nortn Holland 1930 59. Torstensson N.T.L. Dearedaticn__o_f 2,/t-D nnd MCPA in Soils of low pH Env. Qual. Safe. (SuppT3" pp" 262-5" 1975 60. Walsh I..M. et al Occurrence anci Distrihuti^on _of ^.rcenic in__Soils and Plants EnvirotiT lteaitfrpers.""l? pp 67-71 1977 61. Ward C.T., Matsumura F. Fate of 2,3,78 (TCDD) in a Model Aquatic _Envirpnrnent Arch. Environ. Con cam. Tox. "7 p~p 349-357 1978 62. Wauchope R.D., McWhorter C.G. Arsenic Residues int Sjjyb Simulated MS_M_A_ Spray Drift Bull. EnvTrdni" " Con tan. "fox.' 17 p"p r65"-167 1977" 63. V/eakley B.S. How dangerous is sodium cacodylate? J. Micros. 249-251 1977 64. Woolson L'.A. Rate <^J\rsj?nicn]js_jjiJ}^ Environ. Health Pefs. 19 pp"73~81. 1977 65. Young A. L. Use of Herbicides in South , Vietnam JLggl^gT^ Educational Conference on Heruiciae Ora'nya, Silve'r Springs Maryland 1.900 66. Young A . L . , Calcagni J.A., Thalken C.E., Tremblay J.W. ln;?_J.oxA^ mnn ris< of 67. Young A.I.., Thalken C.E., Arnold E.L., Cupello 3.M. , Cockerharn L.G., S...?j ?.J.i 8"JTCDCO. jLJlJyi\q.J:nxiro[i^cnt j_Sj^™^ ~ ' " ~ " " " 109 pp �-1868. Young A . L . , Wolfs W.M. Cr^r^ia J[o_^_e^ujTj0tinr; ^?P°stjr?_]:c!V(l!-^. 0?> miHtary_persopnol._to Dipx Jri" ~c:7icl_horb Vb Lc!?. JJrsnif :-j JjuHn'q j'^_ Viecr':o:,i tfa: ~ Position ^er'l^nluUxf by USlJOO* to L.6 VACC'i2"Cec"~i979 69. Zepp R.G. , Wolfe N . L . , Baughman fi.L., Gordon J.A. ^hemipnl^ anf[ Riotochsmica 1_ Alts r a t i o _n_f _ 2,A-D Esters in theAc]uatic J Southeast &Tv."~Res7"Lat3. U.S". 1975 70. Casimir M., Watt J.W. Ac'rial Snrny Apnl icat.ion _ Agaihist Insects .Pests AG Bulletin. Department of Agriculture NSW 079" 71. Cran field Institute of Technology College of Aeronautics. Aerial Application of Pesticides. Vol. I-II, Short Course, 1900. �-19- 2. (a) Mr James Watt, Research & Development Officer (Gayer Australia), 666-9041 - field trials/aerial spraying .(mathematical models/literature) (b) Mr Jack Snelson, Pesticides Co-ordinato.v for Commonwealth Department of Primary Industry (062) 72-3933 - most complete source of world literature concerning pesticides available in Australia tc (c) Mr Brad brett, Australian Veterinary Chemical Association (AVCA), Uth Floor, 60 York Street (290-0700) - good source of literature - excellent contacts in private and public sectors (d) Or - "Dick" Albanez statistics theoretical models of spray drift exposure (of Ranch Hand personnel). 3. (a) Jack Snelson is an excellent source (b) C.I.H. library is most helpful in obtaining material once the reference is found (c) Commonwealth Health library, Canberra has access to the Dialog database which includes Chemical Abstracts and Science Citation Tndgx_. Tne latter is line" most" useful source for D-) obtaining complete list of "material published by a given author in given years (ii) obtaining complete list of all books/articles which cite a given work. Relevant authors are: Alan Poland D.G. Crosby G. Rcggiani H.E. Cramer - enzyme induction heroicide degredation Seveso/dioxin long term effects. Spray drift (d) The Medlars/Mcdline database has already been searched and printouts are filed. (This database is limited because it excludes articles without a direct medical context.) (e) Obtain as much in formation as possible concerning American experiences with thsir surveys via Dick Albanez and Bill Wolfe - especially information much Al Young may have, and the report by Steven Mocks dealing with the herbicide spray mission simulations cone in Florida by USAF. �-20- References yet to he obtained .. ^ Anonymous , 197/4 . D JJinoci tion_ o_f _n.ranga_ torJiici dc_oy _ino.inoration . Final Environ^2nlarjvtaIe;nenE'r "OepartmenF'of the Air Fo'rce, Washington, D.C. 737 p. Bethel, J.S., Turnbull, K.J., Briggs, D. and Florcs, J. , 1975. l^iJay^r^o£_yie^nain fore5_ts_. American Forests, : 26-30, 36-61." Brown , • 3 . W . , 1 962 . Vegetation?*.! spray tests in Jpu.tlTj/jjBtna^. U.S. Army Chemical Corps [Biological Laboratories, Fort Oe'trick, Frederick, Maryland. 11? p. Available from the Defense Documentation Center, Defense Logistics Agency, Cameron Station, Alexandria, Virginia, DOC Number PD 476961. Carrier, J.M., 1974. Jh?_J^^yjl'lJ^il^hJcid^_jn^^nG and Mickey's Informants in South Vietnam. The Effects of" Herbicides Ln South Vietnam. Part B. Working Papers. National Academy of Science, Washington, D.C. 15 p. Coates, 3.H. , Sharpe, L.M. and Pollack, H. , 1962. The present sJ^tH %_° L.9.nILr DAc.aJL Jlci?i.E2LL-9.!L.v.L195i.? t L9n__i n__r els tic n 60 _m i 1 it a ry nseds'. Tecnnical Mo'tes 62-68. """Institute ToT Dsfen'ss Analyses', " Departmsnt of Defense, Wasnington, D.C. 30 p. Craig, D.A. , 1975. i-MJLtJJ?JLkApA^ Historical Report. San Antonio Air LcglstTcs Center, Oirectcfate of Energy Management, Kelly AFB, Texas. 58 p. Darrow, R.A., 1973. fpLi.?3G_(^na_ract^r|^ics__ c u ; ^ Sci. Soc. Am. "Aostrf 66, pp. 29-30. Wsed -. Darrow, R.A. , Irish, K.R. and Minarik, C.E., 1969. H?rbicidss_ Used Technical Report SAOQ-TR-69-11078. ^ Directorate of Air Force Aerospace Fuels, Kelly AFB, Texas. 60 p. . •' / Darrow, R.A., Truchclut, G.B. and Bartlett, C.M. , 1966. OCON1JS defoliation test: program. Technical Report 79. Crops DeparLTnenYJ"7~BioIc"gicar"Sciences Laboratory, U.S. Army Biological Center, Fort Patrick, Frederick, Maryland. 216 p. _ Basj3_G3G;ji:own, N:;_w~Brunsw jck,_ Canada. ' TechnicarTi'e.'iiorandum " 141. "D^paftmenT oP"Li>2 ~Ar>,y~, "FortDstrick, Frederick, Maryland. Demaree, K.D. and Creager, R.A., J968. ~ Fee, D.C. , Hughss, B.M., Taylor, M.L., Tiernan, T.O. and Hill, C.E., 1975. Analy,l^C3l__MGJ^hod_ql_ony__fqr .Hj_rj)i£idQ__Ora:Tgo. Vol. I . I DeterrMin'ation of UiTgin o"i"u5AV" 'i'toc'ks ~ locnnical Report ARL-75--0110. Aerospace Research Laboratories, Wright-Patterson AFB, Ohio. 30 p. �-21Grover R.J. Relative Volocj t ies of ester &_arninc t ,2,4-D KccdTSci . "24 f 26-28"" ^ ™ Grover R.3. , Maybank J. and Yoshida K. 1972 Droplet and vapour d r i f t from uu ty 1 e s ce rjr.nd d irne thy_l am incjva 1 tn o f ~2 , 4-0 Weed" Sci 20: 320-324 Harrigan, E.T., 1970. Calibration Test of tha UC-12:5:</A/A63Y-1 Snray_ Sy_s_tenni. Technical Repoi7Lr"ATJTC-lTf-7~u"J6. Arnia'TidhC'Developir.en'if and Test Center, Eglin AFB, Florida. 160 p. Hughes, B.M., Fee, D.C. , Taylor, M . L . , Tiernan, T.O., Hill, C.F. and Wu, R.L.C. , 1975. Analytical Msthodplogy^^ for jj^rplcirJe^ " " Vol. I. Determination oi" Giemical Co.T.positicn". technical" Report A.RL-75--0110. Aerospace Research Laboratories, Wright-Patterson AFB, Ohio. 357 p. Hurt t , W . and Darrow , R . A . , 1968 . Biolpgical_ ef Feet iveness o F_Stul 1 §i£LuAlJDl^.^f!SS.' Technical Kepoft"ArATL-TR"68-l22". "Mr Force" ArfnamdhV Laboratory, Eglin AFB, Florida. 31 p. Irish, K.R. , Darrow, R.A. snd Minarik, C.E., 1969. Inrormation tnanunl - . - ion ontroI in SoutheGs t Asia . Mic I . Pubi ic . 33. Department of the Army, Fort De trick, Frederick, Maryland. 71 p. Kearney, P.C. , V.'oolson, E.A. , Isensee & Hslling, C.S., 1973. JeJ,rGc!^jr£dJjDj2!^^ Dpccn u_am i nn t ion . Environ. Health Perspect. Exp. fssue No. 5, pp". "273-277. Klein, R.E. and Harrigan, E.T., 1969. Comparison/Test of Defoliants. Technical Report ADTC-TR-69-30, Vol. I. " Armament "Development and Test Center, Eglin AFB, Florida. 356 p. McConnell, A.F. , 1970. Mission: RANCH HAND. Air University Review, 21 ( ) 89-94. 2: Newton , , M . , 1 975 . E£i\^oj]^_s£t aj_imoact_ _q f _ " A ^ D . . . reforestation _tests JJ2J!'c-Ll;££r!Jrlrc^O' 'A'eed Sci. Soc. ATI., 'Ao'sTrT' 1 Vi7"52 p. Tschi rley , F . H. , 1 968 . Response __p_f _t.r onicQ_l _,and_ .SMbj: r£p_ij^a l__woody_ £la_nts_J;o crie."Tncal t"reat-;.iqnts. ~ t«searcn Report D^-f3-67. AgricukuFaTTtoseafcn Service's, U.S. Department of Agriculture, Washington, D.C. 197 p. Westing, A.H., 1976. ^3ogi£al_j:cn_s£gjo^ Jtndcjchina War. SlbckhoJiri InterniVtTonai Peace Research InstituceT"""Alrngrist and Wiksel Interr.ation, Stockholm, Sweden. 119 p. �-22- Statistical model To be "tabled at meeting. �SECTION 3 • . Revised Pjjins and Estimates for the Study During January 1931, three sets of plans for the study were prepared in conjunction with Professor MacLennan, Dr. Byth and Ms. Rose. These plans (copies of which are attached) addressed the Investigation Programme at three levels: Overall Strategic Plan 1 Year Plan (1981) Plan for the Pilot Survey (to June 1981) Since these plans were prepared, more detailed ones have been compiled in each of the main disciplinary areas of the study. We are currently monitoring progress agajnst these plans on a weekly basis. We look forward to the opportunity to give a presentation of the current plan and on progress. �IXSTITU-TE: OF HEALTH PROJECT PLAN 193T I Apii! RESEARCH PROGRAMME: ASPECT OF INVESTIGATION 1932 Oc'ob* July January "Ajsr.t Orange* Scientific In J Year Mcsf'cr Plon 1933 j October ! April Jonuory. April July October January Maintain nomot and oddf*ii«« 3a*a «n mortality and iMiotui of v«i«funt oid control* i , . I .I »-.«.n at1f f.nd.^op* U . Swb-iiflkJcn | J I .- J P«inll«d cmolyi 1 * of nior'ulilw „, .„ QPC>m|..> '?rt' P-'olUd Irian fof f i '• onf.*»r«n family turvcltloifi •"-" I I D«1ul'«d ona'yili of blflti <?•'•£•« a'ld reproduction Main l r«.peil F.««n|naiion of vamp'm of •«l*cl»d * i t ] W. 3. T^c .'*n?*S o' *ha o:* iniorvtfwi ' '' ' - - no.'n i^rvey <^np«nc/* on f/i* me * A MAJOR EVENTS CoTplciion i Analysis o? Vcioron Mortality of Pilot Survey I PrtfarrA by! 1.', . .i . Approvrd by: • • Preliminary Findings for Main Survey j Cennmvnti: Main Survey Report J �CC-J.W-JMVEAi.7K INSTITUTE 0? HEAS.TH RESEARCH PROGRAMME: PROJECT PLAN ts:vj =!S:YY or svc^er "Agent Oror-ijc" Scientific lnv«tiso^on ASPECT OF MVESTICATiOSi Master Plan for 1981 1981 Jc-iJory February April McrcS Juno May July- August Sentcrfibor October November December PROJECT I Uc*lon : j / t f * t t S w ^ ' a i ' - ' l / a * Arf^y N«f, a, Lnnir»'» ^ • f O * - . i » ' «v*!i . wi fig '1»i.-i ln..» ^ | ! anj Sla'jl of V.i.rno, m<< Con'iol.l CARO, £!<KI»r«l till, lmi»l;r.ill«i, Wo'or Nullify, »or S.r.lt. Horn.., R«gli-ir of | '! I PI011 V.i.funi ««: C«.»r«li't001 .oc..^..,. ! I j • S." AJ Cnncfue* Publicity *:'*»iiMifi»« ta> •M.,UI|S St,,iU( J • T«'«|>'.on« 1 i i t n f v ' « w f?00', t onrf ivv'op Main Su'fn/ S"u*»ay ii»<*f*f! CO')) L*.. I j j ! 1 i{nrf't« o*i<J R«i'in* CifVffioill'al**, •] PtJtm'orri .1C. ! " a.rtMl, AdJ.tienol P*rio<in«t No..!.J P*«por» S'oi:»'lewl T > « r i for in* Mo'n Surv ' I 0«i» Mor.Q.j«ni«iii r In Ofdri of J" Priority . ; Secruit Core Teem ! • •* Piio: Survey Personnel ' V f ^01". ',.1 Pilot Survey Storied Pilo! Survey Completed F'*sared bv: Recruit Main Su'vey Personnel Apurovso by: 0,.:*. Main Survey Slnrtea Survcillene* A . Long Term . Surveillance Started Comm*p.f«: ?r,lr , . �r . ' „ , . . jjr-^xg- 7*2; S^"*"*;) j fTiiA^iL.'W L'XSVjRSiTY Or SYDNEY 1 ! i ! Jcv.,o,.31 i 2j i 9J ! 16| p si * Lw i r t AM t KJJ r^^ PI iw i ii | 1 23| February 2G i i i ^ e..',.i. I 10 J ' 17 3 27 t |l P.I.I f~* " ! '..l .., * I I " : 1 »'»-»..<,.,!• i 1 ! • ' "Vli.*, •?•. j ; T 1 ;• Sit.,,'o'J 26 j Pi"«0t Surv«r R»p«rl of Flna.nn. and f_> 3 10 24 ! 17| t 31 ' ] 1 *• i<. SRC p.ft..w.l..r *l P,^...r.t ' °l.(in. -..M U ^nr -^ \Pf'r'iduf*"*** * ** Oooc Knot'. T S.A.Q. L ** 1 J;- -•. L^^—= 1 ' LH'*-« j ' " " !•! "':r.-_, |! ."".r.^r.. 'Jf .'.'.eei «i ..' =3 U; ~" A J 1 i . - — j —1 ' 1 Tj M.JI.ol £.„,„„„„„.. V JF^.I... (.00) ^ .- " . I ••;.'..,;,..„. • ,,.-.-. 14' ; • !-*: """• UV = C ! u 3 ^ Inh.nution I . S ', -E.po.^. ' . . ... ^ i £ A i I1 SAP ;. ' , • : • ' • : ' : ! i ; ' : •: • Cw.Ticnc? Pilot Su'vey Visit . i • . . ' | ' ' ' ; ! . ' . i ' • ' . : ^ 19 4 «*r i . ii) ""•", r".,,h,0...-.l*i TP'OCC v..,!v, 12 ••'. j •Oe-.Oi.'d.-.lQf . p ^ " • =J 1 U."., j j C 'H j '•*• A.t.l.nn' 1 J MAJ33 HVCSTS 5 2? jW,ii. »f Pi!.» &*»•» L •; ! • ^:;'V'v^.,V^'n ==r~. ! i 221 i • St! - A<imi«j>!rrcd Cut Jtiennoire L • '°'M S , i 15 July , ' i £;:'';!?'""•"•"* j .';^"."c.'™i j j June Ounilty o r In'ormation , - "—' via '*• Mnltlna —t > i 8 Pilot Survoy j ^ ^ . . 1 - , 1 24 May *• * ' ** > Ctili.'.ici '..Ic.'vUwl Did . . | "i...-,. I ' | .. ' , | —-j rf-.! •>< '•"'"«' . -- • r~ni.«". ' : !:j?,..|_ i !-••- i 20 I !->f»fVi«.v*ft priori* £. " < ~ , ^-.. . ! 13) April - r-| •j'slr"1 v ., i ! 6| "Ajcnt Oranja" Scientific Ir.vfittiga!;^ ASPECT OF INVESTIGATION: - ..-run "™~r°""""-r£rl ^--•"-• I i Telephone interviews — il ~ . i a:.:' ::..... H -n 1 27 RESEARCH PROGRAMME: * Face — to - Face Interviews i A.. *, i ir " 1 A^S i**L.iAs^ 1 , 11. i R.,I.»& . .. . - ^-%^ ri March 20 13j j >MO"f» i 1 ' • P^dby, . A,p, '; , . • ' ' . ' , ; • ; . i . . . • ^ > • Non-v»(»roni, at Con fro) t ' A , Con-.plcte . Pi!ct . Survey ... • • ' i Submission to Scientific Review Ccrr.mitteo ..... • .''.:• • • ' • ' : ; . . • 1 ' i i \ 1 C 1J ' . • � Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 070 Folder The folder containing the original item. 1885 Series The series number of the original item. Series III Subseries IV Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Date A point or period of time associated with an event in the lifecycle of the resource February 26 1981 Title A name given to the resource Submission to the Scientific Advisory Committee, Australian Veterans Herbicide Studies, 3rd Meeting to be held in Sydney 3 & 4th March 1981. Subject The topic of the resource AVHS study protocol ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 070 Folder The folder containing the original item. 1888 Series The series number of the original item. Series III Subseries IV Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Kameron, A. J. Description An account of the resource Corporate Author: W. D. Scott and Company Date A point or period of time associated with an event in the lifecycle of the resource 1981-04-01 Title A name given to the resource Australian Veterans Herbicide Studies: Overview of the Proposed Studies on the Effects of Exposure to Herbicides on the Health of Australian Vietnam War Veterans Subject The topic of the resource AVHS study protocol congenital birth defects veteran psychological health ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 070 Folder The folder containing the original item. 1899 Series The series number of the original item. Series III Subseries IV Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Jessop Description An account of the resource Corporate Author: Commonwealth of Australia, Senate, Standing Committee on Science and the Environment Date A point or period of time associated with an event in the lifecycle of the resource December 8 1981 Title A name given to the resource Reference: Pesticides Inquiry (Official Hansard Report), Tuesday, 8 December, 1981. Subject The topic of the resource Australian Parliamentary hearings health effects pesticide regulation AVHS ao_seriesIII Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Title A name given to the resource Alvin L. Young Collection on Agent Orange Description An account of the resource The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young. For more about this collection, <a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a">view the Agent Orange Exhibit.</a> Text A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text. Box The box containing the original item. 071 Folder The folder containing the original item. 1903 Series The series number of the original item. Series III Subseries IV Dublin Core The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/. Creator An entity primarily responsible for making the resource Jessop Description An account of the resource Corporate Author: Commonwealth of Australia, Senate, Standing Committee on Science and the Environment Date A point or period of time associated with an event in the lifecycle of the resource February 4 1982 Title A name given to the resource Reference: Pesticides Inquiry (Official Hansard Report), Melbourne, Thursday, 4 February 1982. Subject The topic of the resource Australian Parliamentary hearings health effects dioxin AVHS ao_seriesIII