Systema(c*Reviews,*Riskof*Bias andEvidenceEvaluaon ...

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Tracey J. Woodruff, PhD, MPH Professor and Director UCSF Program on ReproducBve Health and the Environment Risk Assessment Specialty Sec1on (RASS) January 14, 2015 Systema(c Reviews, Risk of Bias and Evidence Evalua(on for Characteriza(on of Environmental Chemicals

Transcript of Systema(c*Reviews,*Riskof*Bias andEvidenceEvaluaon ...

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Tracey  J.  Woodruff,  PhD,  MPH  Professor  and  Director  

UCSF  Program  on  ReproducBve  Health  and  the  Environment  

 Risk  Assessment  Specialty  Sec1on  (RASS)    

   January  14,  2015  

 

Systema(c  Reviews,  Risk  of  Bias  and  Evidence  Evalua(on    for  Characteriza(on  of  

Environmental  Chemicals  

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(CUE  workshop  has  a  good  cartoon)  

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Environmental  health  literature  is    vast,  diverse,  and  of  variable  quality  

How  do  we  evaluate  scien0fic  evidence  to  

make  decisions?  And  shorten  the  0me  between  science  and  

decision?  

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Clinical sciences have faced and addressed these same challenges

Thank you Lisa Bero

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     What  is  Evidence  Based  Medicine?  

• Defined as, the “conscientious, explicit, and judicious use of the current best evidence in making decisions about the care of

individual patients” ���

• In general, systems of EBM combine:

(1) existing scientific evidence;

(2) clinical expertise; and

(3) patient values and preferences

to make diagnosis, prognosis and treatment decisions.

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Grades of Recommendation Assessment, Development

and Evaluation

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But  Evidence  Based  Medicine  

Methodologies  Are  Not  Directly  

Transferable    to  Environmental  Science!  

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Naviga1on  Guide  Methodology  

A  systemaBc  and  transparent  method  to  evaluate  the  quality  of  evidence  and  to  support  evidence-­‐based  decision  making,  bridging  the  gap  between  clinical  

and  environmental  health  

BRIDGING  CLINICAL  &  ENVIRONMENTAL  HEALTH  

 Developed  by  UCSF’s  Program  on  ReproducBve  Health  and  the  Environment  in  collaboraBon  with  the  NavigaBon  Guide  Working  Group  in  2009  

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Naviga1on  Guide  Work  Group  

The  Cochrane  Collabora1on  

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Overview  of  the  Methodology  

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 “    …systema1c-­‐review  standards                        provide  an  approach  that  would                        substanBally  strengthen  the  IRIS                      process…”      NAS  2014  

“EPA  should  consistently  use  a  more  systema1c  approach  to  evaluaBng  the  literature  ……….”  NAS  2014  

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Weight  of  Evidence  

“too  vague  and  is  of  lidle  scienBfic  use”  

NaBonal  Academy  of  Sciences  2014  

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Evaluate  each  evidence  stream  separately  using  systemaBc  and  transparent  approaches  

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Systema1c  Review  Approach  for  Each  Evidence  Stream  

“PECO”  Statement  

SystemaBc  search  

Select  Studies  

Extract  Data  &  Data  

Analysis  

Rate  Quality  of  Evidence  

Rate  Strength  of  Evidence  Non  Human  

Data  

“PECO”  Statement  

SystemaBc  search  

Select  Studies  

Extract  Data  &  Data  

Analysis  

Rate  Quality  of  Evidence  

Rate  the  Strength  of  Evidence  

Human    Data  

Overall  Co

nclusio

n  

A  pre-­‐specific  analy1c  plan  (protocol)  is  developed  and  applied  consistently  to  the  evidence.        

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Systema1c  Review  Approach  for  Each  Evidence  Stream  

“PECO”  Statement  

SystemaBc  search  

Select  Studies  

Extract  Data  &  Data  

Analysis  

Rate  Quality  of  Evidence  

Rate  the  Strength  of  Evidence  

Overall  Co

nclusio

n  

A  pre-­‐specific  analy1c  plan  (protocol)  is  developed  and  applied  consistently  to  the  evidence.        

    opula1on     xposure     omparator     utcome  

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“PECO”  Statement  

SystemaBc  search  

Select  Studies  

Extract  Data  &  Data  Analysis  

Rate  Quality  of  Evidence  

Rate  the  Strength  of  Evidence  

Rate  Quality  of  Evidence  

Rate  Strength  of  Evidence  

Rate  the  Quality  and  Strength  of  the  Evidence    

High  Moderate  

Low  

Sufficient  evidence  of  toxicity  

Limited  evidence  of  toxicity  

Inadequate  evidence  of  toxicity  

Evidence  of  lack  of  toxicity  

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•  Risk  of  Bias  

•  RaBng  quality  of  evidence  

Rate  Quality  of  Evidence  

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Lam  et  al.  EHP  2014  

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True  Effect  0  

True  Effect  0  

Risk  of  Bias  vs  Random  Error  1.  Bias   2.  Random  Error  

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“The  commidee  notes  that  assessing  the  quality  of  the  study  is  not  equivalent  to  assessing  the  risk  of  bias  in  the  study.  An  assessment  of  study  quality  evaluates  the  extent  to  which  the  researchers  conducted  their  research  to  the  highest  possible  standards  and  how  a  study  is  reported.  Risk  of  bias  is  related  to  the  internal  validity  of  a  study  and  reflects  study-­‐design  characterisBcs  that  can  introduce  a  systemaBc  error  (or  deviaBon  from  the  true  effect)  that  might  affect  the  magnitude  and  even  the  direcBon  of  the  apparent  effect.  An  assessment  of  risk  of  bias  is  a  key  element  in  systemaBc-­‐review  standards;  potenBal  biases  must  be  assessed  to  determine  how  confidently  conclusions  can  be  drawn  from  the  data.”    The  commidee  emphasizes  the  importance  of  assessing  risk  of  bias  for  all  study  types.  

“the  commidee  emphasizes  the  need  for  EPA  to  assess  the  “risk  of  bias”  in  individual  studies.”  [for  all  study  types]  

NaBonal  Academy  of  Sciences  2014  

Risk  of  Bias  &  NAS  

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Low risk

Probably low risk

Probably high risk

High risk

Sequence generation Allocation concealment Blinding Incomplete outcome data Selective reporting

Other bias Conflict of interest

0% 20% 40% 60% 80% 100%

Recruitment strategy Blinding Confounding Exposure assessment Incomplete outcome data Selective reporting Conflict of interest Other bias

Evaluate  Risk  of  Bias  

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Factors  for  downgrading/upgrading  evidence  were  derived  directly  from  factors  used  in  GRADE  and  Cochrane  

High  

Moderate  

Low  

     Animal  evidence  •  Level  of  study  control  •  RandomizaBon  key  factor  in  default  of  “high”  in  GRADE  

•  Studies  find  humans  more  suscepBble  to  chemical  exposures  than  animals    

       Human  evidence  

•  Non-­‐randomized,  but  variable  quality.    Cochrane  review  finds  similar  results  between  RCTs  and  ObservaBonal  studies  

 

Rate  the  Quality  of  the  Evidence    

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Factors  that  DECREASE  quality  level  

1.    Risk  of  bias  (study  limita1ons)  

Possible  raBngs:  0=no  change;  -­‐1  or  -­‐2  downgrade  1  or  2  levels  For  Human  and  Animal  evidence      

2.  Indirectness  

3.  Inconsistency  

4.  Imprecision  

5.  Publica1on  bias  

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Factors  that  INCREASE  quality  level      

1.    Large  magnitude  of  effect    

2.    Dose  response    

3.    Confounding  minimizes  effect              

Possible  raBngs:  0=no  change;  -­‐1  or  -­‐2  downgrade  1  or  2  levels  For  Human  evidence  only      

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NaBonal  Academy  of  Sciences  2014  

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Evidence  Stream  

Human   Non-­‐human  mammalian  

StarBng  raBng   Moderate   High  

Downgrade

  Risk  of  Bias   0   -­‐1  Indirectness   0   0  Inconsistency   0   0  Imprecision   0   0  PublicaBon  bias   0   0  

Upgrade

  Large  magnitude  effect   0   N/A  Dose  response   0   N/A  All  possible  confounding  would  confirm  negaBve  result  

0   N/A  

    Grade   0   -­‐1  

Final  ra1ng   Moderate   Moderate  

Summary  of  Quality  of  Evidence  for  PFOA  

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QUALITY  OF  EVIDENCE  

Moderate  

High  

Low  

STRENGTH  OF  EVIDENCE  (LEVEL  OF  CERTAINTY  REGARDING  TOXICITY)  

Sufficient  evidence  of  toxicity  

Limited  evidence  of  toxicity  

Inadequate  evidence  of  toxicity  

Evidence  of  lack  of  toxicity  

 CRITERIA:  1.   Quality  of  evidence:  2.   What  is  the  direc1on  of  effect?    3.   What  is  the  confidence  in  the  

effect?    4.   Are  there  other  compelling  

adributes  of  the  data  that  influence  certainty?    

Rate  the  Strength  of  Evidence    

 

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Methodological  Needs  •  Criteria  for  moving  from  quality  to  strength  of  evidence  

•  Methods  to  include  all  potenBal  types  of  evidence,  i.e.,  assessing  chickens,  flies  and  in  vitro  data  

•  Improved  methods  of  animal  toxicity  tesBng  –  high  ROB  may  be  prevalent  for  key  domains  

•  MechanisBc  data  is  considered  under  other  consideraBons….  Further  development  needed  

•  Consider  the  nature  and  extent  of  consensus  that  is  needed  for  a  decision  

 

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Conclusion  

•  Doable  •  Rigorous,  systema1c,  transparent  and  doable  •  Capacity  to  evolve  with  changes  in  evidence  stream  

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Acknowledgements  PFOA  Case  Study  Authors  

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Acknowledgements Navigation Guide Funders (since 2009)

–  USEPA –  US Environmental Protection Agency STAR (RD83467801) –  National Institute for Environmental Health Sciences (ES018135) –  Cal-EPA –  Fred Gellert Foundation –  Clarence Heller Foundation –  New York Community Trust –  Forsythia Foundation –  Passport Foundation –  Johnson Family Foundation –  Heinz Endowments –  Rose Foundation –  Kaiser Permanente –  Planned Parenthood Federation of America –  UCSF Phillip R Lee Institute for Health Policy Studies

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Program  on  ReproducBve  Health  and  the  Environment  

Thank  you  

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Sir  AusBn  Bradford  Hill    -­‐    incompleteness  of  science    …  “does  not  confer  upon  us  a  freedom  to  ignore  the  knowledge  we  already  have,  or  to  postpone  the  ac0on  that  it  appears  to  demand  at  a  given  0me”  (Hill  1965).