U'S' EPA Emerging Pollutants Workshop Nonylphenol and Nonylphenol Ethoxylates: Aquatic Toxicity, Est - PowerPoint PPT Presentation

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U'S' EPA Emerging Pollutants Workshop Nonylphenol and Nonylphenol Ethoxylates: Aquatic Toxicity, Est

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... and Nonylphenol Ethoxylates: Aquatic Toxicity, Estrogenicity and Treatability ... Chronic aquatic toxicity of NP... All studies were subject to a quality review ... – PowerPoint PPT presentation

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Title: U'S' EPA Emerging Pollutants Workshop Nonylphenol and Nonylphenol Ethoxylates: Aquatic Toxicity, Est


1
U.S. EPA Emerging Pollutants WorkshopNonylphenol
and Nonylphenol Ethoxylates Aquatic Toxicity,
Estrogenicity and Treatability in Wastewater
Effluent
  • Charles A. Staples
  • Ellen M. Mihaich
  • Barbara S. Losey
  • Chicago, IL
  • August 11-14, 200.

2
Background...
  • Nonylphenol ethoxylate (NPE) surfactants are
    widely used in applications that are sent to
    sewage treatment plants when spent
  • While NPEs are generally easily treatable in well
    run treatment plants, residues from
    biodegradation are often detectable in effluents
  • It is of interest to examine the potential risks
    to the environment from these residues
  • Risk assessment is the preferred means of
    addressing these compounds

3
Background...
  • Risk assessment requires
  • Exposure data
  • Ecotoxicity data
  • The results of risk assessment are used by risk
    managers to control and manage potential unwanted
    risks
  • Purpose
  • Examine the ecotoxicity database, including
    endocrine-modulating effects, for the NPEs, NPEC,
    NP that are most common in effluents as shown in
    treatability studies

4
Treatability studies of NPE surfactants...
  • Example Canadian STPs (receive municipal and
    industrial wastes)
  • STP-A
  • activated sludge (2), nitrification, tertiary
    (3) treatment and UV disinfection
  • removal efficiency of 97 for all species
  • STP-B
  • non-nitrifying activated sludge (2), chlorine
    disinfection
  • removal efficiency of 86 for all species

5
Treatability studies of NPE surfactants...
  • Ahel and Giger (1994a,b), Lee and Peart (1998)
  • main products in raw sewage are commercial NPE
  • main components in final effluents were NPEC with
    some NPE1,2, and traces of NP
  • Monitoring studies
  • 30 Rivers Study
  • NP NPE1,2 0.1 µg/L, NPE3-16 2 µg/L
  • USGS National Reconnaissance Survey
  • NP, NPE1,2 medians 0.8 to 1.0 µg/L
  • Risk assessments of NPE residues from STPs in
    surface water should encompass
  • NPEs, NPEC, NP

6
Chronic aquatic toxicity of NP...
  • Critical review of chronic aquatic toxicity data
    for NP and NPE
  • Dozens of studies, endpoints, LOEC, NOEC
  • Survival, growth, reproduction
  • Manuscript to be submitted to International
    Journal of Human and Ecological Risk Assessment
  • SSD analysis shows that the data support the
    draft USEPA WQC for NP (5.9 ?g/L)

7
Chronic aquatic toxicity of NP...
  • All studies were subject to a quality review
  • 1. Thorough description of the experimental
    design, including test material identification
    and description, exposure regime and
    replication
  • 2. Analytical confirmation of test
    concentrations
  • 3. Description of all ecologically relevant
    endpoints and all supplemental secondary
    biochemical and morphological information
    collected, including a full description of how
    they are measured

8
Chronic aquatic toxicity of NP...
  • All studies were subject to a quality review
  • 4. Use of test procedures that are based, at
    least generally, on internationally accepted
    procedures and practices, including both draft
    and final methods
  • 5. Clear linkage of reported findings with the
    exact experimental design, and,
  • 6. Sufficient reporting of results, including
    system performance, adequacy of control
    performance, toxicity results, and statistical
    methods employed to ascertain how the data
    support the conclusions.

9
Survival ChV x Growth ChV ? Reproductive ChV
Figure 1. Chronic values (ChV) for survival (),
growth (x) and reproduction (?) for fish (F),
aquatic invertebrates (INV), and algae (ALG) by
NPEx.
10
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11
Determination of in vivo endocrine effects in
fish from NPE and biodegradation metabolites
  • Gordon Balch and Chris Metcalfe (Trent
    University, Peterborough, ON, Canada), February
    2003
  • Exposed medaka fish to NP, NPE1, NPE4, NPE9,
    NPEC1 from 1 to 100 days post-hatch
  • Endpoints
  • sex ratio
  • secondary sex characteristics
  • liver VTG
  • testis-ova

12
Results...
13
Study Results...
14
Conclusions from medaka study...
  • NP induced gonadal intersex and mixed secondary
    characteristics in male medaka at 30 and 100 ?g/L
  • Mixed secondary sex characteristics were induced
    in males at 300 ?g/L NPE1
  • No evidence of estrogenicity with NPE4, NPE9 or
    NPEC up to 1000 or 3000 ?g/L
  • No effect on sex ratio for any compound

15
Summary and Conclusions...
  • Ecotoxicity studies show increasing toxicity with
    decreasing ethoxylation
  • Ecotoxicity studies of NPECs show them to be
    relatively non-toxic
  • Only NP showed estrogenic potential in a
    long-term developmental study with medaka
  • Thus, the available database of conventional
    chronic studies should be adequate to address the
    ecotoxicity of the various biodegradation
    intermediates of NPE surfactants

16
Summary and Conclusions...
  • Treatability studies show that well run STPs are
    effective at removing NPE surfactants, but
    residues do enter receiving waters
  • Risk assessments of surface waters receiving STP
    effluents should address all biodegradation
    intermediates
  • Risk management to reduce risk from natural
    hormones in human waste simultaneously addresses
    NPE, NP, NPEC
  • Risk management to reduce risk from industrial
    sources should include Best Management Practices
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