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Contaminants of Emerging Concern in the Tidal Delaware River A Pilot Monitoring Survey y Science and Environmental Summit Delaware Estuary January 13, 2009 Ron MacGillivray, Ph.D.

• Goal Goal:: collect ambient water data on contaminants of •

emerging concern Participants:: DRBC, Axys Analytical Laboratories, Participants American Aquatic Testing Laboratory

Delaware River Basin

Sampling Locations

2007 Parameters

# of analytes

PBDE - polybrominated

46

diphenyl ethers

PFC - perfluorinated

compounds

PPCP - pharmaceuticals and

personal care products

Hormones and sterols

HR GC/MS EPA Method 1614

13 LC/MSMS

54 LC/MSMS

24 GC/LRMS

C b Carbamate t pesticides ti id

21 LC/MSMS

NP and NPE – nonylphenol l h l and NP ethoxylates

3 GC/MS

PPCP in Tidal Delaware River

Caffeine Triclocarban

400

Diphenhydramine Naproxen

350

OTC

Ibuprofen Fluoxitine

300

Codeine Carbamazapine

ng/L

250

prescription

Dilti Diltiazem Dehydronifedipine

200

Gemfibrozil

codeine

Trimethoprim p

150

Sulfanilamide Sulfamethoxazole

100

Sulfadimethoxine Sulfadiazine

50

Ofloxacin Norfloxacin

0 50 mouth of bay

68

80

90 RM

105

131

Erythromycin-H2O Clarithromycin

head of tide

Azithromycin

antibiotics

• Aquatic ecotoxicity data, primarily based on individual compounds d and d single i l species i tests, t t are readily dil available for only 16 out of the 21 PPCP analytes detected limiting assessment of risk to aquatic life. life

• Risk Index = PEC/PNEC – Risk Index > 1.0 (clarithromycin effect on algal growth) – Risk Index > 0.1 ((carbamazapine p effect on Ceriodaphnia p dubia, ibuprofen effect on Hydra, erythromycin and fluoxitine effect on Pseudokirchneriella subcapitata, sulfamethoxazole effect on cyanobacteria) – First Tier screening for prioritization of future assessment and characterization

• Concurrent, short short--term chronic toxicity tests in the ambient water samples p with endpoints p of survival,, growth g and reproduction did not indicate toxicity.

• In salinities from 0 to 10 ppt using six species: – – – – – –

fathead minnow, Pimephales promelas in a 77-day test mysid, Americamysis bahia in a 77-day test i l d silverside, inland il id Menidia M idi beryllina b lli in i a 77-day d test t t water flea, Ceriodaphnia dubia maximum of 88-days duration green alga, Pseudokirchneriella subcapitata in a 9696-hour test amphipod, h d Hyalella l ll azteca in a 1010 0-day d waterwater-only l test

• Assessment of ecotoxicity from PPCP in the tidal Delaware

River would be further informed by estrogenicity screening, biomarker measurements and population (sex ratio) surveys.

Hormones and Sterols In Ambient Waters Of The Tidal Delaware River 250

200

n ng/L

150

100

50

50

0 80 90

River Miles

105

head of tide

ne tro Es

131

N

mouth of bay

l ro te os m es ol D an st le ol ho an C st ro op ic Ep ol an st ro op ne C ro nd hi et or

68

PFC In Ambient Waters Of TheTidal Delaware River

1,000 900 800

ng/L

700 600 500 400 300 200 100 0

50

68

80

River Miles

90 105 131

PFOSA PFOS PFHxS PFBS PFDoA PFUnA PFDA PFNA PFOA PFHpA PFHxA PFPeA PFBA

PFOA In Ambient Water Of TheTidal Delaware River

80

@ S. Del. Mem. Br.

70 @ Liston Point

60

Minnesota Pollution Control Agency (MPCA) - fish consumption criteria (fcc) = 1,620 ng/L g water and fcc = 610 ng/L g - drinking

PFOA ng/L

50

40 @ Marcus Hook

30

20 @ Schuylkill R. @ Pennsauken R.

10

@ Biles Channel

0 50 0

68

80

90

River Miles

10 105

131

PFOS In Ambient Waters Of TheTidal Delaware River 9 @ Schuylkill R. @ Pennsauken R.

8

@ S. Del. Mem. Br. @ Marcus a cus Hook oo C Creek ee

PFOS ng P g/L

7

MPCA human health based surface water criteria 6 ng/L Mississippi River

@ Liston Point

6 5 4 @ Biles Channel

3 2 1 0 50

68

80

90

River Miles

105

131

PBDE In Ambient Waters Of TheTidal Delaware River

8000 7000 6000

4000 3000 2000 1000 0 D E

BD

BD

N

xB

E

E

BD

D pB

H

E

D

E

E

D

E

E

D

D iB Tr

iB

131

D E

head of tide

105

BD Te

90

River Miles

B Pe

80

H

68

O

50 mouth of bay

pg/L

5000

Summary PPCP

– Detected 21 compounds out of 54 compounds – Concentrations in the ng/L range – Availability of ecotoxicity data limiting assessment of risk to aquatic life

Hormones

– Primarily detected fecal sterols – New analytical method with few surrogates available and numerous QA/QC notes

PBDE

– DBDE and other homologs detected at pg/L levels – PBDE monitoring continuing in fish tissue

PFC – PFNA highest PFC concentrations at ng/L levels – PFOS levels exceed some safety benchmarks – Additional information needed for assessment especially on longer p chain and sulfonated compounds

Next Steps – Survey: 2008 sampled; 2009 planned – Information I f ti exchange h – Investigate additional assessment methodologies

• e.g., Species sensitive distribution – Characterize effects • e.g., estrogenicity bioassays, aquatic life Contact Information: [email protected] http://www.state.nj.us/drbc/emc.htm