Pesticides in the Chesapeake Bay Watershed

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Presentation transcript:

Pesticides in the Chesapeake Bay Watershed Vicki Blazer, Kelly Smalling, Michelle Hladick and Patrick Phillips U. S. Geological Survey

Adult Fish Kills in the Potomac Multiple bacterial pathogens, but no consistent findings Aeromonas hydrophila and other motile Aeromonads Aeromonas salmonicida Flavobacterium columnare Multiple, often heavy parasite infestations Leeches, trematodes, myxozoans, cestodes Opportunistic fungal infections Skin papillomas Largemouth Bass Virus High prevalence of intersex, vitellogenin in male fishes Impaired Ecosystem Immunosuppression

Mortalities of YOY Smallmouth Bass Susquehanna Occurring since 2005, late spring/early summer Also coinfections Aeromonas hydrophila and other motile Aeromonads Flavobacterium columnare Largemouth Bass Virus Trematodes Cestodes Myxozoan parasites

Correlations with Landuse and Chemicals PA Drainages Study done in late summer Discrete water samples at time of fish sampling 11 sites in the Susquehanna, 5 out of basin Chemical Contaminants or Landuse Intersex Prevalence rho p Intersex Severity rho p Agricultural landuse 0.6843 0.0170 0.7044 0.0129 WWTP/sewage facilities -0.5298 0.0794 -0.8441 0.0936

Spawning Study Potomac Intersex and Land-use Conducted in the spring, 5 sites in the Potomac, 1 out of basin Landuse Characteristics Intersex Prevalence Intersex Severity r2 p Human population 0.39 0.10 0.42 0.08 # WWTP 0.22 0.24 0.34 0.13 WWTP flow 0.32 0.15 0.63 0.02 Percent agriculture 0.63 0.02 0.50 0.05 # Animal feeding operations 0.28 0.17 0.56 0.03 Total animal numbers 0.27 0.18 0.48 0.06 Animal density 0.49 0.05 0.58 Poultry Houses

Intersex and Chemical Correlations Discrete water samples collected in spring at Potomac sites No estrogens were present at levels above the detection limit Chemical Contaminants Intersex Prevalence Intersex Severity rho p Atrazine 0.93 0.003 0.88 0.009 Deethylatrazine 0.78 0.039 0.68 0.090 Acetochlor 0.65 0.116 0.79 0.036 Metolachlor 0.87 0.011 0.81 0.028

Chesapeake Bay Endocrine Disruption Study Agricultural Integrator Sites 4 - 6 sites where monthly to biweekly water samples, plus storm events, are collected and analyzed for hormones, pesticides, phytoestrogens and total estrogenicity from Nov. 2014 to present Sediment samples in spring and fall Tissue samples for contaminant analyses Adult fish are collected in the spring prespawn (2013- 2017) and at some sites in the summer and fall YOY (1-3 months of age) are collected in early summer (2013-2017)

Location of Integrator Sites Pine Creek Chillisquaque Creek West Branch Mahantango Location of Integrator Sites Antietam Creek South Branch Potomac

Integrator Site Water Samples Analyzed for 130 pesticides or degradates (GC) 13 including neonics (LC) – not included Detected 30 at least once Most only occasionally detected Atrazine, simazine, metolachlor – most common; fipronil, metalaxyl next most common

Pesticides Detected Herbicides Insecticide Fungicide Atrazine Simazine Metolachlor Fipronil Metalaxyl Pine (43a) 19b (1c) 1 (0) 12 (1) 0 (0) WB Mahantango (47) 41 (17) 34 (9) 2 (0) 2 (0) Chillisquaque (36) 14 (3) 32 (9) 7 (0) Antietam (42) 36 (3) 39 (5) 11 (0) 0 (0) SB Potomac (41) 18 (0) 3 (0) 10 (1) aTotal number of water samples from 11/2014 through 7/2017 bTotal detects cDetects above the 100 ng/L assessment threshold

Chillisquaque Atrazine Concentrations (ng/L) 37,971 Jan Feb March April May June July Aug Sept Oct Nov Dec

Adults - recrudescence Key Exposure Periods Nest/eggs – sediment/water Water food, sediment Water, maternal, sediment Final maturation, sperm quality YOY – sexual differentiation and organ development Adults - recrudescence April – May June – July August – Dec - March

Water Versus YOY Tissue Bifenthrin (4) and pendamethalin (6) only occasionally detected Bifenthrin detected only once on 10/29/15 at Chilli Pendamethalin not detected at all in water samples in 2015

YOY Whole Body Pesticides (ng/g; ppb) Chillisquaque Date 8/14/14 Bifenthrin Metolachlor p,p’DDD p,p’-DDE Pendimethalin 1 6.3 7.3 2 0.7 1.0 3.4 11.6 3 0.3 0.5 2.4 4.4 4 0.6 1.1 5.2 5 0.9 3.7 9.4 6 20.1 7 3.5 7.6 8 14.5 9 1.6 1.4 1.5 14.1

Recent USGS Study Midwestern Streams Citation – Complex mixtures of dissolved pesticides show potential aquatic toxicity in a synoptic study of Midwestern U.S. streams by Lisa Nowell and 10 coauthors in Science of the Total Environment: In press 100 streams weekly water samples during May-August 2013 Compared streams in agricultural and urban settings 94 pesticides and 89 degradates were detected Median of 25 compounds detected per sample and 54 detected per site

Midwest Stream Study Used aquatic life benchmarks and the Pesticide Toxicity Index as a screening level assessment for potential effects on fish, benthic invertebrates and aquatic plants Pesticide toxicity index utilizes these benchmarks to assess potential toxicity of pesticide mixtures – calculating toxic units and concentration additions for pesticides with the same modes of action Aquatic life benchmarks (fish) based on a few species exposed in the laboratory to individual pesticides Life cycle/partial life cycle/early life stage assessments – assess survival, growth of adult and young, maturation, eggs spawned, hatchability, embryo survival and visible abnormalities

Conclusions Few compounds were predicted to be major contributors to toxicity Atrazine, metolachlor, fipronil, acetochlor, imidacloprid, carbendazim, organophosphate insecticides Aquatic invertebrates = 53% of the streams predicted to have chronic toxicity, 12% acutely toxic Aquatic plants 75% had acute but reversible effects with 9% having chronic longterm effects on plant communities Potential effects on fish were unlikely

Adverse Effects Monitoring Myxozoan Trematode metacercariae Flavobacterium columnare Fish Immune System Adverse Effects Monitoring Snail host Benthic Worm host Actinopsore Fish infective stage Cestode pleurocercoid Intermediate host Amphipod, copepod

Underlying Infections a a a a a a

Trematode Example Atrazine Bifenthrin – immunomodulation Increase algal/periphyton Increased snail populations Atrazine Immunomodulation Increased trematode cercariae Bifenthrin – immunomodulation Reduces aquatic insect larvae which consume cercariae Estrogens (estrone) - immunomodulation, increase snail populations Increased Trematode Infections

Acknowledgements USGS – Chesapeake Bay Environments and Environmental Health programs WV Division of Natural Resources MD Department of Natural Resources PA Fish and Boat Commission PA Department of Environmental Protection West Virginia University Penn State University