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New and Emerging Contaminants/Endocrine Disrupting Compounds

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New and Emerging ContaminantsEndocrine Disrupting Compounds – PowerPoint PPT presentation

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Title: New and Emerging Contaminants/Endocrine Disrupting Compounds


1
New and Emerging Contaminants/Endocrine
Disrupting Compounds
2
EPA Definitions
  • Contaminant Any physical, chemical, or
    biological, that does, or may occur in water.
  • Contaminant Candidate List The primary source of
    priority contaminants for which EPA conducts
    research to make decisions about whether
    regulations are needed. These contaminants are
    currently unregulated by existing national
    primary drinking water regulations.

3
  • Known Contaminants Those that have been
    identified in the technical literature and
    adequately characterized to enable a judgment
    regarding their inclusion in the CCL universe.
  • Emerging Contaminants A subset of agents
    previously evaluated as not requiring inclusion
    in the CCL, for which new information becomes
    available which heightens concern and triggers
    re-evaluation.
  • New Contaminants Agents that are or may be
    newly-discovered or synthesized, for which little
    is known about their potential occurrence or
    adverse health effects.

4
How About
  • Any contaminant of anthropogenic origin, that is
    known or proven to cause harm, either acutely or
    chronically, to the biological component of an
    aquatic ecosystem, including humans.

5
Targeted Contaminants
  • Veterinary and Human Antibiotics
  • Tetracyclines, fluoroquinolones, macrolides, and
    sulfonomides.
  • Human drugs
  • Prescription (antihypertensives, antidepressants,
    anticoagulant, etc)
  • Non-prescription (analgesics, anti-inflammatorys,
    stimulants, etc.)

6
  • Industrial and Household Wastewater Products.
  • Insecticides
  • Plasticizers
  • Detergent metabolites
  • Fire retardants
  • PAHs (naphthalene, anthracene, fluoranthrene,
    etc.)
  • Anti-oxidants
  • Personal care products (fragrances, deodorants,
    etc.)

7
  • Sex and Steroidal Hormones
  • Biogenics (17ß- estradiol, estrone, progestrone,
    testosterone, etc)
  • Pharmaceuticals (ovulation inhibitors, hormone
    replacement, etc.)
  • Sterols (cholesterol, 3b-Coprostanol, etc.)

8
  • As population centers expand and grow, emerging
    contaminants will become increasingly emergent.

9
Endocrine Disrupting Compounds
  • Several of these contaminants can interact with
    endocrine systems and cause a disruption to
    normal functions in several ways.
  • They can act like a natural hormone and bind to a
    receptor. This causes a similar response by the
    cell, known as an agonist response.
  • They can bind to a receptor and prevent a normal
    response, known as an antagonistic response.
  • A substance can interfere with the way natural
    hormones and receptors are synthesized or
    controlled.

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11
Consequences of Endocrine Disrupting Compounds
(EDCs)
  • Chemicals affected by the endocrine system
    determine behavioral responses.
  • These, in turn, determine what works and what
    doesnt re. life history strategies for
    survival and reproduction.

12
  • Behavioral responses are what drive evolutionary
    history and speciation.
  • A disruption in the ability to make correct
    choices regarding survivability and reproduction
    has the ability to disrupt evolutionary
    processes.

13
Wildlife as Indicators of EDC Exposure
  • All vertebrates share remarkably similar
    endocrine systems.
  • Several studies have attempted to determine
    physiologic effects in wildlife, especially
    wholly aquatic species like fish.

14
Difficulties
  • Synergism and additive effects of several
    compounds.
  • Compound-specific body targets.
  • Poor information re. life history and behavioral
    patterns of even the most common fish species.
  • Isolation of endocrine disruption as a stressor.
  • Lack of adequate controls and replicates due to
    cost of analyses.

15
Quantifying Potential Endocrine Disruption in
Effluent-Dependent Waters in Arizona Fish as
Habitat Assessment Biomarkers
  • Large support from USGS
  • Gail Cordy (hydrology/water quality)
  • Dr. Timothy Gross (endocrinology, histopatholgoy)
  • Larry Barber (pharmaceutical and sex hormone
    analysis)
  • Ed Furlong (wastewater compounds)
  • Dana Kolpin (logistics)
  • Nick Paretti (graduate student)

16
Research Design
  • Bonytail chub (gila elegans) kept in large,
    recirculating aquaria at ERL.
  • Four tanks, 2 treatment and 2 control.
  • Control tanks filled with water treated by
    charcoal filtration and reverse osmosis.
  • Treatment tanks filled with varying
    concentrations of effluent (1/3, 2/3, and full
    strength)

17
  • Effluent collected from the Santa Cruz River
    below Roger Road WWTP.
  • Water samples collected and analyzed for EDCs.
  • Blood collected from fish at the end of each
    dose, in a non-destructive manner, and analyzed
    for 17ß-estradiol, 11-ketotestosterone, and the
    egg protein vitellogenin.
  • Histopathology done after each dose to determine
    stage of gonadal development.

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22
Results to Date
  • End of 1/3 dose, March 2005.
  • End of 2/3 dose, July 2005.
  • All doses will last approximately 4 months with
    sampling of fish and water occurring after 3
    months.
  • Fish currently exposed to full strength effluent.

23
Preliminary EDC Analyses
  • Source Effluent
  • 32 compounds including the EDCs 17ß-estradiol,
    estrone, nonylphenol ethoxylates, and bisphenol A
    at concentrations from 0.03 to 9 µg/L.

24
1/3 Dose EDCs
  • Control Tanks
  • 6 compounds including DEET and 4 tert octylphenol
    (No known EDCs).
  • Treatment Tanks
  • 22 compounds including nonylphenol ethoxylates
    and bisphenol A.
  • No difference in sex hormone levels or
    histopathology at 1/3 dose.

25
2/3 Dose EDCs
  • Control Tanks
  • 6 compounds including DEET, cholesterol, phenol,
    and oil/gas combustion by-products (no known
    EDCs).
  • Treatment Tanks
  • 35 compounds including nonylphenol ethoxylates
    and bisphenol A .

26
  • As population centers increase, a likely increase
    in the amount and concentration of EDCs.
  • Awaiting results from fish serum and
    histopathology from 2/3 dose.
  • Awaiting results from estrogen(s) and
    pharmaceuticals from USGS.

27
  • Aquatic species can, by longevity of exposure, be
    excellent indicators of exposure to low-dose
    EDCs.
  • EDWs may provide beneficial habitat for native
    species but care must be taken to avoid
    ecological traps.

28
Questions?
Bisphenol-A
Ortho-N-Nonylphenol
Ethinyl Estradiol
Methoxychlor
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