Title: Update on Pro Bono Emerging Contaminant Analyses
1Update on Pro Bono Emerging Contaminant Analyses
- RMP Emerging Contaminants Workgroup
- October 17th, 2008
2Updates on EC Analyses
- Triclosan
- Chlorinated paraffins
- Potential Work for 2009, 2010
3Triclosan
- Antimicrobial registered for use as fungicide,
antibacterial, bactericide, disinfectant - Hand soaps, toothpastes, detergents, deodorants,
pesticides, imbedded in plastics and clothing - Use regulated by FDA EPA
- log KOW 4.76
4Why is Triclosan a Concern?
- Antimicrobial resistance
- Dioxin production from photolysis in fresh
seawater (Aranami and Readman, 2007) - Photolysis products include (Latch et al., 2005)
- 2,8-dichlorodibenzo-p-dioxin (2,8-DCDD)
- 2,4-dichlorophenol (2,4-DCP)
- Weakly estrogenic (Ishibashi, 2004)
5RMP Sediment Analysis
- 10 surface sediment samples, 2008 ST
- Mark Cantwell, Rob Burgess EPA
NHEERL, Narragansett, RI - GC/MS, 13C labeled IS
6Triclosan in SF Bay Sediments
- 2008 ST Monitoring
- MDL 5 ng/g dry
Draft data- do not cite or quote
7Comparison to Other Locations
(RMP)
(Miller 2008)
(Miller 2008)
(Wilson 2008)
(Aquera 2003)
(Singer 2002)
8Triclosan Toxicity
- No sediment toxicity studies
- Estimated SF Bay porewater concentration max 0.4
µg L-1 - Daphnia magna (Orvos et al., 2002)
- reproductive NOEC 40 µg L-1 LOEC 200 µg L-1
- Rainbow trout (Oncorhynchus mykiss) 71.3 µg L-1
(Orvos et al., 2002) - Decreased post-hatch survival, behaviorial
effects - Tadpoles (Rana pipens) (Fraker and Smith, 2004)
- Reduced activity 0.23 230.0 µg L-1
- Algae (Wilson et al., 2003)
- Reduce the biomass of algal communities 0.12 µg
L-1 - Change community structure and reduce genus
richness of algal communities at 0.012 µg L-1
- Microbial, algal, fish toxicity testing ongoing
(EPA NHEERL)
9Additional Concerns
- Conversion to 2,7 2,8 dichlorodibenzodioxin?
- Methyl triclosan?
- Effluents and sanitary sewer overflows (SSOs)
10Chlorinated Paraffins/Chlorinated n-Alkanes
- C10 to C30 technical mixtures
- 30 to 70 Cl- by mass
- Primary uses high temperature lubricants in
metal working machinery, flame retardants in
plastics - Minor uses additives in sealants, adhesives,
paints, rubber - Largest group of high molecular weight Cl
hydrocarbons in commercial use - Used since 1930s, declined after 1980s
- Bioaccumulative (log Kow 5.9-8.1)
- Ubiquitous
- Persistent, toxic, long-range transport
- Environmental fate, transport unknown
11Chlorinated Paraffins/Chlorinated n-Alkanes
- Commercial formulations
- short (C10-C13), medium (C14-C17), long (C20-C30)
- Short-chain chlorinated paraffins
- Most extensive use
- Highest potential for env. release because of
open use - Highest toxicity
- Listings
- EPA Toxic Release Inventory
- Priority toxic substances (Canadian Env.
Protection Act) - Priority hazardous substance (EU)
- HPV chemicals in late 1990s
Concern for SF Bay?
12Short-chain chlorinated paraffins
- Gregg Tomy (Canadian Dept of Fisheries and
Oceans) - White croaker from Oakland (1), South Bay (2) in
2006 - Cormorant eggs from 3 sites (1 comp/site) in 2006
- Harbor seal blubber (3 sites) in 2007
13Chlorinated Paraffins in SF Bay Wildlife Compared
to Other Locations
lt0.9
5
SF Bay samples Surrogate standard quantifiable
in fish only (148, 65 and 119)
14C11
C12
C10
White croaker
C13
Cormorant eggs
Harbor seal blubber
15Other POPs in SF Bay Cormorant Eggs
16Are Concentrations in SF Bay Wildlife a Concern?
- Limited toxicity information available, most
based on exposure to technical mixtures - Sub-lethal effects, most short-term exposures
- Chronic toxicity studies sparse
- Narcosis is mode of action
- Dietary uptake in juvenile rainbow trout (Cooley
et al 2001) - Narcosis effects, liver lesions at 220-5500 ng/g
body burden (SF Bay biota concentrations at least
1-2 orders of magnitude lower) - Low acute toxicity
17Future/Potential Work
- Single-walled carbon nanotubes (L. Ferguson)
- Siloxanes? (M. Alaee, Environment Canada)
- Quaternary ammonium compounds?
- (400/sample, B. Brownawell, Stonybrook Univ.)