From Epidemiology to Risk Factors aka DDREF: Light and Shadows

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From Epidemiology to Risk Factors aka DDREF: Light and Shadows MELODI 2011, Rome November 2, 2011 Dale L. Preston Hirosoft International Eureka, CA

Outline DDREF Origins and Background DDREF in Practice Defining the DDREF LSS low dose extrapolation factors (DDREF) BEIR VII Bayesian analysis Pooling epi studies Whither (wither) DDREF - personal views and random thoughts 2

Radiation Protection Define limits for occupational and public radiation exposures to protect against unnecessary and unjustifiable risks Primary focus on lifetime cancer risks Some concern with hereditary and fetal risks Relatively low doses (e.g. 1 100 mgy) Fractionated or chronic low dose rate exposures ( e.g. < 5 mgy per hour) are most common Low LET exposures (e.g. x-rays, gamma rays) most likely 3

State of Knowledge Circa 1980 Atomic bomb survivor data indicated increased cancer rates Acute exposures Information largely from higher doses (0.2 to 4 Gy) Little information on dose response shape or low dose effects Dose response estimates not included in early LSS reports Chromosome aberration data suggest non-linear dose response for acute exposures Upward curvature over low dose range Other experimental data suggested non-linear dose response and reduced effects at low dose rates 4

Dose and Dose-Rate Effects View from 1980 NCRP Report 64 1980 5

(Original) DDREF Justification Because Linear extrapolation of survivor risks to low doses believed to over-estimate response True dose response in survivors likely to be concave upward Chromosome aberration data from human and experimental data concave upward at lower doses Experimental data suggested risk per unit dose decreased with decreasing dose rate Therefore A Dose / Dose Rate Effectiveness Factor (DDREF) should be used to reduce A-bomb survivor based risk estimates used to develop radiation protection standards 6

DDREF in Practice ICRP 1990 and 2007 Consensus value of 2 for solid cancers Leukemia risk estimates based on LQ model with no adjustments BEIR V DDREF not applied BEIR VII Developed a posterior distribution based on A-bomb survivor incidence data and some animal data Mean of 1.5 and a 95% credible interval of about 1 to 3 Used 1.5 for computation of solid cancer risks 7

DDREF in Practice Interactive Radio-Epidemiological Program (IREP) risk projections 0,4 0,35 0,3 Breast & Thyroid Other solid cancer Probability 0,25 0,2 0,15 0,1 0,05 0 0.5 0.7 1 1.5 2 3 4 5 DDREF 8

Characterizing the DDREF Today More LSS data Risk estimates are described with more detail and precision More knowledge of effect modification Other epi studies provide relevant risk estimates Mayak and Techa River UK nuclear workers (NRRW), IARC 15-country worker study, Chernobyl liquidators Evolving efforts to more fully characterize uncertainty in risk estimates Dose errors, model uncertainty, New radiobiology Adaptive response, bystander effects, genomic instability, 9

Estimating a DDREF (LDEF) from acute exposure data Assess as a function of curvature in LQ dose response model 2 α + β d β LDEF( d) = = 1+ d = 1+ θ d α d α For the A-bomb survivor Life Span Study (LSS) data Fit linear dose response model Fit linear quadratic model with curvature θ : Define LSS LDEF (θ) as α α α L d α d + θ d 2 LQ For LSS with data doses up to 1.5 or even 2 Gy LQ L ( ) LSS ( θ ) 1+ θ LDEF 10

LSS Solid Cancer Mortality Dose Response Linear ERR/Gy 0 2 Gy 0.45 Suggestion of non-linearity (LQ model on 0 2 Gy) P = 0.03 Curvature 0.77 LSS-LDEF 1.97 LSS often described as a high dose study, but has as more information on risk at relatively low doses (<100 mgy) than many low dose studies relative risk excess 1.5 1.5 0 Solid Cancer Mortality Dose Response 0 1 2 3 weighted colon dose (Gy) Using RERF public dataset DS02can.csv (www.rerf.or.jp) Proximal zero dose baseline (adjusted for distal and NIC) 11

LSS Solid Cancer Mortality Dose Response 0 0.5 Gy Linear ERR/Gy 0 2 Gy 0.45 0 0.1 Gy 0.76 0 0.15 Gy 0.71 Test for trend 0 0.1 Gy P = 0.04 0 0.15 Gy P = 0.006 excess relative risk.25.2.15.1.05 Solid Cancer Mortality Dose Response 0 0.1.2.3.4.5 weighted colon dose (Gy) Using RERF public dataset DS02can.csv (www.rerf.or.jp) Proximal zero dose baseline (adjusted for distal and NIC) 12

LSS Solid Cancer Incidence Dose Response Linear ERR/Gy 0 2 Gy 0.49 No evidence of non-linearity (LQ model on 0 2 Gy) P > 0.5 Curvature 0.12 LSS-LDEF 1.14 excess relative risk 1.5 1.5 Solid Cancer Incidence Dose Response 0 0 1 2 3 weighted colon dose (Gy) Using RERF public dataset DS02can.csv (www.rerf.or.jp) Proximal zero dose baseline (adjusted for distal and NIC) 13

LSS Solid Cancer Mortality Dose Response 0 0.5 Gy Linear ERR/Gy 0 2 Gy 0.49 0 0.1 Gy 0.51 0 0.15 Gy 0.51 Test for trend 0 0.1 Gy P = 0.08 0 0.15 Gy P = 0.01 excess relative risk.25.2.15.1.05 Solid Cancer Incidence Dose Response 0 0.1.2.3.4.5 weighted colon dose (Gy) Using RERF public dataset DS02can.csv (www.rerf.or.jp) Proximal zero dose baseline (adjusted for distal and NIC) 14

BEIR VII Bayesian Analysis Data Sources LSS cancer incidence data (Preston et al 2007) Selected mouse studies of radiation and cancer Doses < 2 Gy Adjusted for competing risks 11 ORNL experiments in RFM or Balb-C mice (also used by NCRP In 1980) (Edwards, 1992 / Storer 1979) Cancer risks Lung (3); Hardrerian gland (2); Mammary (2); Uterine (1); Pituitary (1); Myeloid leukemia (2) Life-Shortening Acute and Chronic exposure experiments 15

BEIR VII Bayesian Analyses Animal Cancer Data Data from 11 cancer experiments with unconstrained (black) and constrained (orange) LQ fits Common curvature assumed for constrained fits Data taken from experiments described by Edwards (1992) 16

BEIR VII Bayesian Analyses Life Shortening Data Life Shortening in female RFM female following acute and chronic exposures to different total doses with dose response curve fitted to 0 1.5 Gy range Mean life leng gth (days) 400 500 A A BEIR 7 Life Shortening Analysis RFM female mice A A A C A A C 600 A A A C C 0 1 2 3 4 Dose (Gy) Data taken from Storer et al (1992) 17

LSS BEIR VII Bayesian Analysis Risk models Estimate curvature in LQ model fit to all solid cancer Mouse cancer data Cancer dose response modeled assuming LQ models with common curvature across experiments Life Shortening data Model dose response for inverse life expectancy with 1 = α d + β d L( d) 1 =α d L( d) Estimate curvature as 2 for acute exposures and for chronic exposures β α 18

LSS BEIR VII Bayesian Analysis Posterior Densities Define posterior density as normalized profile likelihood for curvature ( θ ) Animal data Define posterior densities for cancer and life shortening data using normalized profile likelihoods for the curvature Average these densities and renormalize to obtain radiobiological posterior Combined data Define posterior density as the (normalized) product of the LSS and radiobiological posterior densities 19

BEIR VII Bayesian Analysis Results Probability density 0.5 1 1.5 Radiobiology LSS Combined 0 (1) 1 (2) 2 (3) 3 (4) Curvature (LSS-LDEF) MLE Mean Median 90% Cred. Int. Radiobiology 1.4 2.3 2.0 (1.1 to 4.5) LSS 1.2 1.6 1.4 (0.9 to 3.2) Combined 1.2 1.5 1.4 (1.0 to 2.4) 20

BEIR VII Bayesian analysis Criticisms Are the experiments used appropriate Might certain tumor types distort the results (Harderian glands) 8 of the experiments involved female mice whose ovaries are very sensitive to radiation which might distort hormonal balance and risks Why include studies with leukemia as an outcome Why not use other animal studies e.g. fractionation study discussed in BEIR VII Why not consider other epi studies What about other non-animal radio-biology experiments 21

DDREF Estimation From Epi Studies (Jacob et al 2009) Identified 12 analyses of 8 low-dose-rate moderate dose studies with solid cancer or all-cancer risk estimates Techa River, Chernobyl Clean-up E workers Rocketdyne. ORNL, and Hanford workers UK nuclear workers, French nuclear workers IARC 15-country nuclear work study Significant dose response in 7 of 12 analyses Compared published ERR/Gy estimates with analogous linear LSS risk estimate Comparable LSS subset and dose (e.g. LSS skin dose : film badge dose) 22

DDREF Estimation From Epi Studies s Computed ERR ratios q = with a monte-carlo based variance estimate ( ) V s Computed pooled risk ratio as Q = s ERR ERR q s V s s 1 V s s LSS ( s) DREF = 1/Q 23

DDREF Estimation From Epi Studies Results and Conclusions Individual mortality studies DREF = 0.8 (90% CI 0.5 to 2.0) Rocketdyne, Chernobyl clean-up workers, Techa River, UK radiation workers, ORNL workers, French workers, Hanford workers Alternate grouping of mortality studies Q = 0.5 (90% CI 0.3 to 0.8) Rocketdyne, 15-country worker study, Chernobyl clean-up workers, Techa River Incidence studies Q = 1.0 (90% CI 0.65 to 2.4) Conclusions Low dose rate studies do not seem to have lower risks per unit dose than the LSS Use of a DDREF of 2 may be inappropriate 24

Contrary Views Is the Current DDREF Too Small? EPRI 2009 there is a need to re-evaluate the magnitude of the dose and dose-rate effectiveness factors (DDREF) including significant radiobiology data suggesting non-linear effects at low and very low doses, implying that health effects may be significantly less at low dose-rates than risk factors currently used. [Emphasis added] Animal and experimental data Recently discovered cellular processes (e.g. adaptive response, bystander effects, genomic instability, ) High background radiation and other neglected epi studies 25

Contrary Views Is the Current DDREF Too Small? From Program on Technology Innovation: Evaluation of updated research on health effects and Risks Associated with low-dose ionizing radiation. (EPRI 2009) 26

Whither DDREF Personal Views DDREF concept developed around 1980 to allow for perceived inadequacies in low dose/.low dose-rate risk estimates based on the atomic bomb survivor data Reflected a view that with more data dose response would be concave upward at low doses (cf the battle of BEIR III) Shorthand for real issues What is shape of the radiation dose response in the low dose region How does the dose response change with dose rate Cancer (and possible non-cancer) dose response is highly uncertain at low doses and low-dose rates Likely to differ for different outcomes (cf solid cancer and leukemia in the LSS) Epi studies are extremely unlikely to resolve issue at doses / doserates of primary interest to radiation protection ( e.g. < 10 mgy) Relevance of experimental radiobiology unclear (and will remain so) 27

Whither DDREF Personal Views There is no compelling evidence against the LNT as a description of radiation effects on cancer risks Despite limitations the Epi data are the most relevant to radiation protection Little reason to use DDREF for radiation protection at this time Develop resources to facilitate better definition and estimation of DDREF Database of relevant studies (with as much detailed data as possible) More thought about how to combine these data to estimate the quantity (quantities) of interest 28

Whither DDREF Challenges Develop better/ more complete methods to characterize uncertainty in the risk estimates from specific studies Take these uncertainties into account in developing the risk estimates that underlie standards and risk projections 29

Acknowledgments The opinions I have expressed are strictly my own, but I am grateful to many people with whom I have discussed these issues over the years including: Michael Fry, Owen Hoffman, Albrecht Kellerer, Peter Jacob, Don Pierce, Elaine Ron, Warren Sinclair, Dan Stram I particularly want to thank Owen Hoffman and his SENES colleagues (John Trabalka, Julian Apostoaei, David Kocher, and Brian Thomas) for letting me look at their very useful draft report on the development of DDREFs for use in the next version of IREP. 30