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EVALUATING THE UNITED STATES
ENVIRONMENTAL PROTECTION AGENCY’S
SAFE DRINKING WATER ACT:
AN ASSESSMENT ON
DI(2-ETHYLHEXYL)PHTHALATE
IN DRINKING WATER
A Q U I E R A H A L S E Y, M P H C A N D I D AT E
J E F F E R S O N S C H O O L O F
P O P U L AT I O N H E A LT H
M P H C A P S T O N E P R O J E C T
P R E S E N T AT I O N
A P R I L 1 , 2 0 1 5
KEYWORDS
ATSDR – Agency of Toxic Substances and Disease Registry
DEHP – Di(2-ethylhexyl)phthalate
EDC - Endocrine-Disrupting Compound
EPA – Environmental Protection Agency
EU – European Union
IARC - International Agency for Research on Cancer
MCL(G) – Maximum Contaminant Level (Goal)
MGD – Million Gallons per Day
NPDWR – National Primary Drinking Water Regulation
NPL - National Priorities List
PPB – Parts per Billion
PVC – Polyvinyl Chloride
REACH – Registration, Evaluation and Authorization of Chemicals
SDWA – Safe Drinking Water Act
TSCA – Toxic Substances Control Act
PROJECT GOAL
To evaluate the U.S. EPA’s SDWA in order to determine if the current MCL of
6ppb for DEHP in drinking water needs to be reassessed and lowered.
RESEARCH QUESTIONS
1. Does DEHP pose a significant human health risk that warrants additional
regulations under the current mandates of the SDWA?
2. Are adequate safeguards in place to limit safe exposure of DEHP in public
drinking water supplies or does the current MCL/MCLG standard need to
revised to further reduce risks?
3. Can more stringent regulation of DEHP be justified under the cost/benefit
guidelines required by the SDWA?
BACKGROUND
 Endocrine Disruptor
 Exogenous substance or mixture that alters the function(s) of the endocrine
system and consequently causes adverse health effects in an intact
organism, or its progeny, or (sub)populations (Snedeker, 2002)
 Found in plastics, personal care items, pharmaceuticals, and industrial
chemicals
 Exposure: ingestion, inhalation, and skin contact
POTENTIAL REPRODUCTIVE EFFECTS OF EDCS
Transgenerational and multigenerational effects
Cryptorchidism
 90% of boys will have normal fertility if only 1 testis is undescended at birth
Hypospadias
 Urethra forms abnormally during weeks 8–14 of pregnancy
 Opening of the urethra is on the underside of the penis, instead of at the tip
 Effects 5 boys out of every 1,000 born in the U.S. (CDC, 2014)
EDC: POTENTIAL BREAST CANCER RISK
(Snedeker, 2002)
 EDC exposure increases the growth of breast cancer (BCERC, 2007)
EDC: PHTHALATE ESTERS
 Phthalates or plasticizers – compounds made from alcohols and phthalic
anhydride (BCERC, 2007)
 Industrial chemicals added to plastics to increase pliability
 Exposures: air, soil, water, food, milk, medications and medical devices
 Bioaccumulation can occur in humans and wildlife
BIOACCUMULATION
Saeidnia and Abdollahi, 2013
DI(2-ETHYLHEXYL)PHTHALATE (DEHP)
 Introduced in 1939
 Production increased from 194 million pounds in 1975 to 397 million pounds in
2005 (NTP, 2014)
 1994, DEHP was added to EPA’s SDWA NPDWR
 Finished drinking water goal of 6ppb for MCL (enforceable limit) and 0 for
MCLG
 Exposure is based upon dose, duration and pathway
DEHP CHEMICAL STRUCTURE
 Formula: C24H38O4
 Diester of phthalatic acid and branded-chain 2-ethylhexanol
DEHP CLASSIFICATION
 In 2000, the IARC changed its classification for DEHP from “possibly
carcinogenic to humans” to “cannot be classified as a carcinogen to
humans”, because of the difference in how the livers of humans and primates
respond to DEHP as compared with the livers of rats and mice (ATSDR, 2002)
 U.S. and EU considers it a “probable human carcinogen”
 In 2011, IARC changed classification to “potentially carcinogenic”
DEHP IN CONSUMER GOODS
 PVC, food packing, medical devices, and surgical gloves
 Severely affects kidneys, liver, and reproductive system
 40% for medical devices, 30% for consumer goods, and 30% for
construction related applications (NTP, 2014)
DEHP IN THE ENVIRONMENT
Air
 Less than 3% of total U.S. domestic supply of DEHP is released to air
(ATSDR, 2002)
 Dust particles are carried back to earth through gravity, rain or snow (ATSDR,
2002)
Soil
 Sinks to sediments at bottom of water
 Found at 248 of 737 NPL sites (ATSDR, 2011)
 92% of U.S. domestic supplies are released in landfills (ATSDR, 2002)
DEHP IN THE ENVIRONMENT
Water
 DEHP has been found in wastewater, surface water and treatment plant
discharges
 Concentrations have been measured at 0.6 – 2,400 ppb in surface waters,
and at 0.04 – 420 ppb in ground water obtained from private wells, offsite
from landfills and facilities that use DEHP in manufacturing (ATSDR, 2002)
 Leaches when bottled water is above 75°F
DEHP METABOLITES
 Three DEHP metabolites: Mono-2-ethylhexyl phthalate (MEHP), Mono-(2-ethyl-
5-oxohexyl)phthalate (MEOHP) and Mono-(2-ethyl-5-hydroxyhexyl)phthalate
(MEHHP)
 65% of DEHP metabolites are excreted in urine
 2007-2009 Canadian Health Measures Survey
 5,600 Canadians ages 6-79
 2009-2011 Canadian Health Measures Survey
 6,400 Canadians ages 6-79
IARC 2011 STUDY
IARC, 2012
POPULATION AT RISK
 Pregnant and lactating mothers and patients undergoing medical procedures
 Male fetus’, male neonates, and peripubertal male children
 In 2005 EU banned the use of DEHP in children’s toys
DRINKING WATER REGULATIONS
 Safe Drinking Water Act (1974)
 Federal law that ensures drinking water quality
 National Primary Drinking Water Regulation
 Sets enforceable MCL for drinking water contaminants
 MCL – health based goal
 MCLG – non-enforceable goal
SAMPLE INTERVIEW QUESTIONS
 Is DEHP a persistent problem in drinking water?
 Which approach to the removal of DEHP yields the greatest drinking water
benefit?
 Are the three DEHP metabolites: MEHP, MEHHP, and MEOHP tested in
drinking water?
 Is DEHP significant enough to continue warranting national regulation?
 Does TSCA and REACH achieve adequate public health safeguards in applying
risk reduction strategies?
INTERVIEWS
Agency of Toxic Substances and Disease Registry
 Dimock site in Susquehanna, PA
Aqua America
 Consistent non-detects and GAC costs
Environmental Protection Agency
 Second Six-Year Review
 Third Six-Year Review Process for Phase V chemicals underway
AQUA AMERICA DEHP DETECTIONS
GRANULAR ACTIVATED CARBON COSTS
 1 million gallons of water can serve approximately 4,000 people daily
 Carbon is replaced every 24 months
 Philadelphia water system maximum capacity is 683 MGD (CoP, n.d.)
 4.2x larger than the 162 MGD system
Million Gallons
per Day
Process Cost System Cost
Operation &
Maintenance
Cost
0.500 MGD $127,693 $205,218 $38,037
1.000 MGD $424,944 $755,924 $103,013
10.000 MGD $1,946,151 $2,989,935 $634,150
75.072 MGD $11,347,113 $16,700,567 $4,432,122
108.104 MGD $15,793,110 $23,130,659 $6,299,662
162.000 MGD $23,130,878 $33,735,768 $8,783,318
POLICY ANALYSIS: TSCA (1976)
 Different approaches for handling new and existing chemicals
 Presumption of innocence
 EPA is responsible for burden of truth
 Least burdensome approach
 TSCA is ineffective in removing existing chemicals of risk from market
POLICY ANALYSIS: REACH (2006)
 Precautionary Principle – If effects are scientifically unknown then the product
or action should not be taken
 Data requirements are same for new and existing chemicals
 15 year DEHP risk assessment completed in 2008
 Environmental Quality Standards
 2014 - Substance of Very High Concern (European Chemicals Agency, 2014)
 Separate from industry and government decisions
LIMITATIONS
 Few epidemiological studies on humans due to exposure uncertainty
 Outdated risk assessments
 (ATSDR, 2002)
 Interviews with government officials
CONCLUSIONS
 DEHP is ubiquitous in the environment
 People are routinely exposed to DEHP from multiple sources
 Health risks associated with exposure are uncertain
 Interviewees stated DEHP is rarely detected in drinking water
 Third Six-Year Review screening in process for phthalates
 Current MCL of 6ppb is appropriate based upon Second Six-Year Review
 DEHP’s MCL for drinking water does not need to be revised
ACKNOWLEDGEMENTS
 Committee Chair: Richard Pepino, MSS
 Committee Preceptor: Lee Blum, PhD
 Capstone Coordinator: Nancy Chernett, MPH
 Interviewees: Lora Werner, MPH, Charles Hertz, PhD, Michael Pickle, ME,
Crystal Rodgers-Jenkins, MS and Rajiv Khera, P.E.
 Lauren Williams, M.Ed
 Family and Friends
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Halsey Capstone Presentation

  • 1. EVALUATING THE UNITED STATES ENVIRONMENTAL PROTECTION AGENCY’S SAFE DRINKING WATER ACT: AN ASSESSMENT ON DI(2-ETHYLHEXYL)PHTHALATE IN DRINKING WATER A Q U I E R A H A L S E Y, M P H C A N D I D AT E J E F F E R S O N S C H O O L O F P O P U L AT I O N H E A LT H M P H C A P S T O N E P R O J E C T P R E S E N T AT I O N A P R I L 1 , 2 0 1 5
  • 2. KEYWORDS ATSDR – Agency of Toxic Substances and Disease Registry DEHP – Di(2-ethylhexyl)phthalate EDC - Endocrine-Disrupting Compound EPA – Environmental Protection Agency EU – European Union IARC - International Agency for Research on Cancer MCL(G) – Maximum Contaminant Level (Goal) MGD – Million Gallons per Day NPDWR – National Primary Drinking Water Regulation NPL - National Priorities List PPB – Parts per Billion PVC – Polyvinyl Chloride REACH – Registration, Evaluation and Authorization of Chemicals SDWA – Safe Drinking Water Act TSCA – Toxic Substances Control Act
  • 3. PROJECT GOAL To evaluate the U.S. EPA’s SDWA in order to determine if the current MCL of 6ppb for DEHP in drinking water needs to be reassessed and lowered.
  • 4. RESEARCH QUESTIONS 1. Does DEHP pose a significant human health risk that warrants additional regulations under the current mandates of the SDWA? 2. Are adequate safeguards in place to limit safe exposure of DEHP in public drinking water supplies or does the current MCL/MCLG standard need to revised to further reduce risks? 3. Can more stringent regulation of DEHP be justified under the cost/benefit guidelines required by the SDWA?
  • 5. BACKGROUND  Endocrine Disruptor  Exogenous substance or mixture that alters the function(s) of the endocrine system and consequently causes adverse health effects in an intact organism, or its progeny, or (sub)populations (Snedeker, 2002)  Found in plastics, personal care items, pharmaceuticals, and industrial chemicals  Exposure: ingestion, inhalation, and skin contact
  • 6. POTENTIAL REPRODUCTIVE EFFECTS OF EDCS Transgenerational and multigenerational effects Cryptorchidism  90% of boys will have normal fertility if only 1 testis is undescended at birth Hypospadias  Urethra forms abnormally during weeks 8–14 of pregnancy  Opening of the urethra is on the underside of the penis, instead of at the tip  Effects 5 boys out of every 1,000 born in the U.S. (CDC, 2014)
  • 7. EDC: POTENTIAL BREAST CANCER RISK (Snedeker, 2002)  EDC exposure increases the growth of breast cancer (BCERC, 2007)
  • 8. EDC: PHTHALATE ESTERS  Phthalates or plasticizers – compounds made from alcohols and phthalic anhydride (BCERC, 2007)  Industrial chemicals added to plastics to increase pliability  Exposures: air, soil, water, food, milk, medications and medical devices  Bioaccumulation can occur in humans and wildlife
  • 10. DI(2-ETHYLHEXYL)PHTHALATE (DEHP)  Introduced in 1939  Production increased from 194 million pounds in 1975 to 397 million pounds in 2005 (NTP, 2014)  1994, DEHP was added to EPA’s SDWA NPDWR  Finished drinking water goal of 6ppb for MCL (enforceable limit) and 0 for MCLG  Exposure is based upon dose, duration and pathway
  • 11. DEHP CHEMICAL STRUCTURE  Formula: C24H38O4  Diester of phthalatic acid and branded-chain 2-ethylhexanol
  • 12. DEHP CLASSIFICATION  In 2000, the IARC changed its classification for DEHP from “possibly carcinogenic to humans” to “cannot be classified as a carcinogen to humans”, because of the difference in how the livers of humans and primates respond to DEHP as compared with the livers of rats and mice (ATSDR, 2002)  U.S. and EU considers it a “probable human carcinogen”  In 2011, IARC changed classification to “potentially carcinogenic”
  • 13. DEHP IN CONSUMER GOODS  PVC, food packing, medical devices, and surgical gloves  Severely affects kidneys, liver, and reproductive system  40% for medical devices, 30% for consumer goods, and 30% for construction related applications (NTP, 2014)
  • 14. DEHP IN THE ENVIRONMENT Air  Less than 3% of total U.S. domestic supply of DEHP is released to air (ATSDR, 2002)  Dust particles are carried back to earth through gravity, rain or snow (ATSDR, 2002) Soil  Sinks to sediments at bottom of water  Found at 248 of 737 NPL sites (ATSDR, 2011)  92% of U.S. domestic supplies are released in landfills (ATSDR, 2002)
  • 15. DEHP IN THE ENVIRONMENT Water  DEHP has been found in wastewater, surface water and treatment plant discharges  Concentrations have been measured at 0.6 – 2,400 ppb in surface waters, and at 0.04 – 420 ppb in ground water obtained from private wells, offsite from landfills and facilities that use DEHP in manufacturing (ATSDR, 2002)  Leaches when bottled water is above 75°F
  • 16. DEHP METABOLITES  Three DEHP metabolites: Mono-2-ethylhexyl phthalate (MEHP), Mono-(2-ethyl- 5-oxohexyl)phthalate (MEOHP) and Mono-(2-ethyl-5-hydroxyhexyl)phthalate (MEHHP)  65% of DEHP metabolites are excreted in urine  2007-2009 Canadian Health Measures Survey  5,600 Canadians ages 6-79  2009-2011 Canadian Health Measures Survey  6,400 Canadians ages 6-79
  • 18. POPULATION AT RISK  Pregnant and lactating mothers and patients undergoing medical procedures  Male fetus’, male neonates, and peripubertal male children  In 2005 EU banned the use of DEHP in children’s toys
  • 19. DRINKING WATER REGULATIONS  Safe Drinking Water Act (1974)  Federal law that ensures drinking water quality  National Primary Drinking Water Regulation  Sets enforceable MCL for drinking water contaminants  MCL – health based goal  MCLG – non-enforceable goal
  • 20. SAMPLE INTERVIEW QUESTIONS  Is DEHP a persistent problem in drinking water?  Which approach to the removal of DEHP yields the greatest drinking water benefit?  Are the three DEHP metabolites: MEHP, MEHHP, and MEOHP tested in drinking water?  Is DEHP significant enough to continue warranting national regulation?  Does TSCA and REACH achieve adequate public health safeguards in applying risk reduction strategies?
  • 21. INTERVIEWS Agency of Toxic Substances and Disease Registry  Dimock site in Susquehanna, PA Aqua America  Consistent non-detects and GAC costs Environmental Protection Agency  Second Six-Year Review  Third Six-Year Review Process for Phase V chemicals underway
  • 22. AQUA AMERICA DEHP DETECTIONS
  • 23. GRANULAR ACTIVATED CARBON COSTS  1 million gallons of water can serve approximately 4,000 people daily  Carbon is replaced every 24 months  Philadelphia water system maximum capacity is 683 MGD (CoP, n.d.)  4.2x larger than the 162 MGD system Million Gallons per Day Process Cost System Cost Operation & Maintenance Cost 0.500 MGD $127,693 $205,218 $38,037 1.000 MGD $424,944 $755,924 $103,013 10.000 MGD $1,946,151 $2,989,935 $634,150 75.072 MGD $11,347,113 $16,700,567 $4,432,122 108.104 MGD $15,793,110 $23,130,659 $6,299,662 162.000 MGD $23,130,878 $33,735,768 $8,783,318
  • 24. POLICY ANALYSIS: TSCA (1976)  Different approaches for handling new and existing chemicals  Presumption of innocence  EPA is responsible for burden of truth  Least burdensome approach  TSCA is ineffective in removing existing chemicals of risk from market
  • 25. POLICY ANALYSIS: REACH (2006)  Precautionary Principle – If effects are scientifically unknown then the product or action should not be taken  Data requirements are same for new and existing chemicals  15 year DEHP risk assessment completed in 2008  Environmental Quality Standards  2014 - Substance of Very High Concern (European Chemicals Agency, 2014)  Separate from industry and government decisions
  • 26. LIMITATIONS  Few epidemiological studies on humans due to exposure uncertainty  Outdated risk assessments  (ATSDR, 2002)  Interviews with government officials
  • 27. CONCLUSIONS  DEHP is ubiquitous in the environment  People are routinely exposed to DEHP from multiple sources  Health risks associated with exposure are uncertain  Interviewees stated DEHP is rarely detected in drinking water  Third Six-Year Review screening in process for phthalates  Current MCL of 6ppb is appropriate based upon Second Six-Year Review  DEHP’s MCL for drinking water does not need to be revised
  • 28. ACKNOWLEDGEMENTS  Committee Chair: Richard Pepino, MSS  Committee Preceptor: Lee Blum, PhD  Capstone Coordinator: Nancy Chernett, MPH  Interviewees: Lora Werner, MPH, Charles Hertz, PhD, Michael Pickle, ME, Crystal Rodgers-Jenkins, MS and Rajiv Khera, P.E.  Lauren Williams, M.Ed  Family and Friends
  • 29. REFERENCES: Anawalt, Bradley D., MD. (2013). An Introduction to the Endocrine System. Retrieved from: http://www.hormone.org/hormones-and-health/the-endocrine-system Agency of Toxic Substances and Disease Registry (ATSDR). (2002). Toxicological Profile for Di(2- ethylhexyl)phthalate. Retrieved from: http://www.atsdr.cdc.gov/toxprofiles/tp9.pdf Aqua America. (2015). Overview. Retrieved from: https://www.aquaamerica.com/about- aqua/overview.aspx ATSDR (2011). ATSDR Record of Activity/Technical Assist. Retrieved from: http://www2.epa.gov/sites/production/files/documents/dimock-atsdr.pdf ATSDR. (2014a). Public Health Statement for Di(2-ethylhexyl) phthalate (DEHP). Retrieved from: http://www.atsdr.cdc.gov/PHS/PHS.asp?id=376&tid=65 ATSDR. (2014b). Priority List of Hazardous Substances. Retrieved from: http://www.atsdr.cdc.gov/SPL/ Awwa Research Foundation (AwwaRF). 2008. State of Knowledge of Endocrine Disruptors and Pharmaceuticals in Drinking Water. Retrieved from: http://environmentalhealthcollaborative.org/images/91228_State_of_Knowledge.pdf
  • 30. REFERENCES: Breast Cancer & The Environment Research Centers (BCERC). (2007). Early Life Exposure to Phthalates and Breast Cancer Risk in Later Years. Retrieved from: http://www.bcerc.org/COTCpubs/BCERC.FactSheet_Phthalates.pdf Centers for Disease Control and Prevention (CDC). (2013). National Biomonitoring Program. Biomonitoring Summary. Phthalate Overview. Retrieved from: http://www.cdc.gov/biomonitoring/DEHP_BiomonitoringSummary.html CDC. (2014). Facts about Hypospadias. Retrieved from: http://www.cdc.gov/ncbddd/birthdefects/hypospadias.html City of Philadelphia (CoP). (n.d.). About Philadelphia Water. Retrieved from: http://www.phila.gov/water/aboutus/Pages/AboutPhiladelphiaWater.aspx Denison, R. A. (2009). Ten Essential Elements in TSCA Reform. Retrieved from: http://www.edf.org/sites/default/files/9279_Denison_10_Elements_TSCA_Reform_0.pdf Diamanti-Kandarakis, E., Bourguignon, J., Giudice, L. C., Hauser, R., Prins, G. S., Soto, A. M., Zoeller, R. T., & Gore, A. C. (2009). Endocrine-disrupting chemicals: An endocrine society scientific statement. Endocrine Review, 30(4), 293-342. doi: 10.1210/er.2009-0002 Dictionary.com. (2015). Precautionary Principle. Retrieved from: http://dictionary.reference.com/browse/precautionary%20principle%20?s=t Environmental Protection Agency (EPA). (1992, July 17). Federal Register. National Primary Drinking Water Regulations; Synthetic Organic and Inorganic Chemicals; Final Rule. Retrieved from: http://water.epa.gov/lawsregs/rulesregs/sdwa/chemicalcontaminantrules/upload/FR7-17-923_GS.pdf
  • 31. REFERENCES: EPA. (1995). National Primary Drinking Water Regulations. Di(2-ethylhexyl) Phthalate. Retrieved from: http://nepis.epa.gov/Exe/ZyPDF.cgi/9100PO48.PDF?Dockey=9100PO48.PDF EPA. (2001). Removal of Endocrine Disruptor Chemicals Using Drinking Water Treatment Processes. Retrieved from: http://nepis.epa.gov/Adobe/PDF/30004HGG.pdf EPA. (2004). Understanding the Safe Drinking Water Act. Retrieved from: http://www.epa.gov/safewater/sdwa/pdfs/fs_30ann_sdwa_web.pdf EPA. (2006). 2006 Inventory Update Reporting: Data Summary. Retrieved from: http://www.epa.gov/oppt/cdr/pubs/2006_data_summary.pdf EPA. (2010, March 29). Federal Register. National Primary Drinking Water Regulations; Announcement of the Results of EPA’S Review of Existing Drinking Water Standards and Request for Public Comment and/or Information on Related Issues; Notice. Retrieved from: http://www.gpo.gov/fdsys/pkg/FR-2010-03-29/pdf/2010-6624.pdf EPA. (2012a). Human Health Risk Assessment. Retrieved from: http://www.epa.gov/risk_assessment/health-risk.htm
  • 32. REFERENCES: EPA. (2012b). The Safe Drinking Water Act Amendments of 1996. Strengthening Protection for America’s Drinking Water. Retrieved from: http://water.epa.gov/lawsregs/guidance/sdwa/theme.cfm EPA. (2012c). Phthalates Action Plan. Retrieved from: http://www.epa.gov/oppt/existingchemicals/pubs/actionplans/phthalates_actionplan_revised_20 12-03-14.pdf EPA. (2012d). Water: Public Water Systems. Public Drinking Water Systems: Facts and Figures. Retrieved from: http://water.epa.gov/infrastructure/drinkingwater/pws/factoids.cfm EPA. (2013). Water: Drinking Water Contaminants. National Primary Drinking Water Regulations. Retrieved from: http://water.epa.gov/drink/contaminants/index.cfm Erythropel, H.C, Maric, M., Nicell, J. A., Leask, R. L. and Yargeau, V. (2014). Leaching of the plasticizer di(2-ethylhexyl)phthalate (DEHP) from plastic containers and the question of human exposure. Appl Microbiol Biotechnol. (2014). 98:9967-9981. Doi 10.1007/s00253-014-6183-8 European Chemicals Bureau. (2008). European Union Risk Assessment Report. DEHP. Retrieved from: http://www.dehp- facts.com/upload/documents/webpage/DEHP%20RA%20report%20full.pdf
  • 33. REFERENCES: European Commission. (2013, September 17). Enterprise and Industry. REACH - Registration, Evaluation, Authorisation and Restriction of Chemicals. Retrieved from: http://ec.europa.eu/enterprise/sectors/chemicals/reach/index_en.htm European Council for Plasticizers and Intermediates. (2015). EU Risk Assessment confirms no general risk to human health from DEHP. Retrieved from: http://www.dehp-facts.com/ra Falconer, I. R. (2005). International Journal Environmental Research. Public Health. 2006(3(2)), 180- 184. Retrieved from: http://www.ncbi.nlm.nih.gov/pmc/articles/PMC3807508/pdf/ijerph-03- 00180.pdf Fleisch, Abby F., Wright, Robert O., and Baccarelli, Andrea A. (2012). Environmental epigenetics: a role in endocrine disease. Journal of molecular Endocrinology (2012) 49 R61-R67. doi:10.1530/JME-12-0066 Food and Drug Administration. (2002). FDA Public Health Notification: PVC Devices Containing the Plasticizer DEHP. Retrieved from: http://www.fda.gov/MedicalDevices/Safety/AlertsandNotices/PublicHealthNotifications/ucm0621 82.htm Gapany, C., Frey, P., Cachat, F., Gudinchet, F., Fichlinski, P., Meyrat, B-J., Ramseyer, P., Theintz, G., and Burnand, B. (2008). Swiss Medical Weekly 2008;138(33–34):492–498. Retrieved from: http://www.smw.ch/docs/pdf200x/2008/33/smw-12192.pdf
  • 34. REFERENCES: Genuis, Stephen J., Beesoon, Sanjay., Lobo, Rebacca A., and Birkholz, Detlef. (2012). Clinical Study Human Elimination of Phthalate Compounds: Blood, Urine, and Sweat (BUS) study. The Scientific World Journal Volume 2012, Article ID 615068. doi: 1.1100/2012/615068. Retrieved from: http://www.ncbi.nlm.nih.gov/pmc/articles/PMC3504417/pdf/TSWJ2012-615068.pdf Hertz, C., Medora, F., Hudson, C., Arnold, M., and Pickel, M. (2014). Enough is enough. How many SOC non-detects does it take to be meaningful? Marie, Joanne. Cryptorchidism & Infertility. Retrieved from: http://livehealthy.chron.com/cryptorchidism-infertility-1080.html Ministry of Health. (2013). Second Report on Human Biomonitoring of Environmental Chemicals in Canada. Results of the Canadian Health Measures Survey Cycle 2 (2009-2011). Retrieved from: http://www.healthyenvironmentforkids.ca/sites/healthyenvironmentforkids.ca/files/HumanBiomo nitoringReport__EN.pdf National Institutes of Health (NIH). (2010). Endocrine Disruptors. Retrieved from: https://www.niehs.nih.gov/health/materials/endocrine_disruptors_508.pdf National Toxicology Program. (NTP). (2014). Report on Carcinogens, Thirteenth Edition. Di(2- ethylhexyl) Phthalate. Retrieved from: http://ntp.niehs.nih.gov/ntp/roc/content/profiles/diethylhexylphthalate.pdf#search=DEHP
  • 35. REFERENCES: NTP. (2014). Report on Carcinogens, Thirteenth Edition. Di(2-ethylhexyl) Phthalate. Retrieved from: http://ntp.niehs.nih.gov/ntp/roc/content/profiles/diethylhexylphthalate.pdf#search= DEHP Rank, J. (2005). Classification and Risk Assessment of Chemicals: The Case of DEHP in the Light of REACH. The Journal of Transdisciplinary Environmental Studies, 4(3). Retrieved from: http://www.journal-tes.dk/vol_4_no_3/no2_hoj.pdf Santana J, Giraudi C, Marengo E, Robotti E, Pires S, Nunes I, and Gaspar EM. Preliminary toxicological assessment of phthalate esters from drinking water consumed in Portugal. Environmental Science and Pollution Research 2014 Jan;21(2):1380-90. doi: 10.1007/s11356-013-2020-3. Epub 2013 Jul 31. Saravanabhavan, G., Guay , M., Langlois, E., Giroux, S., Murray, J., & Haines , D. (2013). Biomonitoring of phthalate metabolites in the Canadian population through the Canadian health measures survey (2007-2009). International Journal of Hygiene and Environmental Health, 216(6), 652-61. doi: 10.1016/j.ijheh.2012.12.009 Schierow, Linda-Jo. (2009, July 28). The Toxic Substances Control Act (TSCA): Implementation and New Challenges. Retrieved from: https://www.acs.org/content/dam/acsorg/policy/acsonthehill/briefings/tscareform/c rs-tsca-implementation-2008.pdf
  • 36. REFERENCES: Schierow, Linda-Jo. (2013, April 1). The Toxic Substances Control Act (TSCA): A Summary of the Act and Its Major Requirements. Retrieved from: http://fas.org/sgp/crs/misc/RL31905.pdf Schmidt, Charles W. (2013). Uncertain Inheritance: Transgenerational Effects of Environmental Exposure. Environmental Health Perspectives; doi:10.1289/ehp.121-A298Retrieved from: http://ehp.niehs.nih.gov/wp-content/uploads/121/10/ehp.121-a298.pdf Searles, James. Steptoe & Johnson LLP. (2011). Chemical Regulation: A comparison of US and European Approaches. Retrieved from: http://www.steptoe.com/assets/htmldocuments/China%20TSCA%20v%20REACH_Jim%20Searles_April% 202011.pdf Snedeker, S. (7 Dec. 2002). Breast Cancer. Is there a link to Endocrine Disrupting Chemicals. U.S. National Library of Medicine. (2015). Lipoprotein-a. Retrieved from: http://www.nlm.nih.gov/medlineplus/ency/article/007262.htm Wagner, Charlotte. (2013). Transgenerational effects and EDCs. Retrieved from: http://www.foodpackagingforum.org/news/transgenerational-effects-and-edcs World Health Organization. (1996). Di(2-ethylhexyl)phthalate in Drinking-water. Background document for development of WHO Guidelines for Drinking-water Quality. Retrieved from: http://www.who.int/water_sanitation_health/dwq/chemicals/di2ethylhexyphthalate.pdf World Health Organization. (2015). Children’s Environmental Health. Environmental Risk. Retrieved from: http://www.who.int/ceh/risks/en/