WHOO S WHOO? The Great Horned Owl as a Terrestrial Indicator Species in the Ecological Risk Assessment of the Tittabawassee River and Floodplain.

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Transcription:

WHOO S WHOO? The Great Horned Owl as a Terrestrial Indicator Species in the Ecological Risk Assessment of the Tittabawassee River and Floodplain. Chippewa Nature Center, April 27 2006 Sarah Coefield Doctoral Candidate Michigan State University

WHOO S WHOO? Matthew J. Zwiernik, Ph.D Rita M. Seston Timothy B. Fredricks Jeremy N. Moore Dustin L. Tazelaar David W. Hamman Bethany R. Opperman Michael W. Nadeau Emily M. Koppel Lori E. Williams Michael J. Kramer Melissa S. Shotwell Mike M. Fales Patrick W. Bradley John P. Giesy, Ph.D And many more... 2

Special thanks to: Participating landowners Local resources The Dow Chemical Co. 3

Tittabawassee River Ecological Studies This study will examine exposure levels and effects in various wildlife populations. Multiple receptor species Multiple lines of evidence Site-specific study 4

Tittabawassee River Ecological Studies Receptor species Mink Belted kingfisher Great blue heron American robin House wren Tree swallow Eastern blue bird Hooded merganser Wood duck Great horned owl 5

Conceptual Site Model Raptor Heron Passerine birds Invertebrates Small mammals Soil Muskrat Kingfisher Benthic invertebrates Forage fish Mink Sediment 6

Tittabawassee River Ecological Studies Multiple lines of evidence Dietary exposure assessment Tissue-based exposure assessment Population health measurements 7

Tittabawassee River Ecological Studies Food web dietary items Multiple time-points Multiple locations 8

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Food web dietary items 10

Lines of Evidence Productivity and Abundance Great horned owl population health and sustainability Tissue Concentration Owl Swallows/Muskrats Small mammals & Passerines Aquatic emergent insects/aquatic Plants Terrestrial insects and Plants Sediments Soils 11

Why do we need a terrestrial indicator species for an aquatic-based contamination? Dioxin-like chemicals bind to sediment and are deposited in the floodplain during flood events. Terrestrial invertebrates, small mammals, and plants are exposed to this contamination, granting it access to the terrestrial food web. 12

s as Indicator Species There are several factors to consider in choosing an indicator species intensity of exposure relative sensitivity to contaminants ecological function time spent on-site ease or difficulty of conducting field studies with the organisms appropriateness of the surrogate species size and types of the contaminated habitat 13

Physical Characteristics 18-24 inches 2-5 pounds Distinctive ear tufts and large yellow eyes No seasonal, sex, or age difference in plumage Females larger than males 14

North American Distribution The great horned owl has the most extensive range, the widest prey base, and the most variable nesting sites of any American owl. 15

Habitat Open and secondarygrowth temperate woodlands, swamps, orchards, and agricultural areas 16

Nest Selection Do not build or maintain a nest Male selects the territory Nest sites can include hawk nests, crow nests, hollow trees, tussocks of grass, rocky outcrops, caves, abandoned quarries, etc. 17

Reproduction Monogamous Pair remains in territory year-round Sexually mature at 1yr old, but usually not active until at least 2 yrs old 18

Reproduction Early nesters (January- February) Typically lay 1-4 eggs 30 day incubation Female stays on nest while male provides food Altricial Nestlings stay in nest for ~7wks before branching Parents continue to care for offspring until early fall 19

Longevity Known to live up to 28 yrs in the wild Causes of mortality included starvation, predation (typically young owls), leg-hold traps, automobile collisions, shooting 20

Diet Nocturnal predators Prey on mammals and birds Regurgitate pellets 21

Dietary items Voles Bitterns Squirrels Great blue herons Mink Ducks Skunks Swans Raccoons Gulls Opossum Snakes Armadillos Turtles Cats and dogs Lizards Shrews Alligators Moles Fish Muskrats Insects Bats Scorpions Grouse Centipedes Woodpeckers Crayfish Crows Worms Turkeys Spiders Pigeons Road-kill Red-tailed hawks Marmots Kangaroo rats 22

s as Indicator Species Intensity of exposure Secondary consumers = high trophic status Wide variety of prey species integrating several trophic levels Potential for bioaccumulation Relative sensitivity to contaminants Both captive and field studies have shown owls to be highly sensitive to a wide variety of environmental contaminants Ecological function Top of terrestrial food chain 23

s as Indicator Species Time spent on-site Non-migratory (year-round) Ease or difficulty of conducting field studies with the organisms Great horned owls will utilize artificial nesting structures Fledgling offer little resistance Dietary composition can be determined from pellets Size and types of the contaminated habitat The combination of emergent forest, fields, and agricultural properties along the Tittabawassee River and reference areas provide miles of habitat for the owls. 24

s as Indicator Species Appropriateness as Surrogate Species As top predators, GHOs effectively integrate exposures from multiple trophic levels and habitats, and their abundance can be directly related to available prey and ultimately ecosystem health As a result, the owls can be good indicators of effects on all trophic levels. 25

Tissue-based exposure assessment Blood plasma is collected from both juvenile and adult great horned owls 26

Tissue-based exposure assessment: fledglings Nest platforms 27

Tissue-based exposure assessment: fledglings Nest platform installation 28

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Tissue-based exposure assessment: fledglings Nest platform locations 54 nest platforms installed Owls have nested in 10 platforms 30

Tissue-based exposure assessment: fledglings 31

Tissue-based exposure assessment: fledglings 32

Tissue-based exposure assessment: adults 33

Tissue-based exposure assessment 34

Population Health: Abundance and Productivity 35

Population Health: Abundance and Productivity 36

Population Health: Morphological measurements 37

Population Health: Foraging range, dispersal, survival 38

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Dietary Composition Analysis 40

Dietary Exposure Imerman Park GHO Dietary Composition by Frequency Bird Lagomorph Peromyscous Meadow Vole House Mouse Meadow Jumping Mouse 41

Dietary Exposure Imerman Park GHO Dietary Composition by Biomass Meadow Jumping Mouse House Mouse Meadow Vole Bird Peromyscous Lagomorph 42

Dietary Exposure Assessment Representative Reference Small Mammal PCDD/DF Concentrations (Site 2) Avian TEQs (ng/kg) 25 20 15 10 5 Shrew Deer mouse Meadow jumping mouse Meadow vole Northern flying squirrel White footed mouse 0 43

Dietary Exposure Assessment Representative Downstream Small Mammal PCDD/DF Concentrations (Site 3) 6000 Avian TEQs (ng/kg) 5000 4000 3000 2000 1000 0 Shrew Deer mouse Eastern chipmunk House mouse White footed mouse 44

So what is a TEQ, anyway? TEQ = Toxic equivalent TEQs allow toxicologists to speak to each other with a minimum of confusion 45

TEQs: an example for the real world Take a trip around the world 50,000 pesos 25 pounds 72 euros 800 yen 374 marks How much money do you have? 46

Dietary Exposure Assessment Estimated Daily dietary dose (ng/kg/day) based on WHOAvian TEQs for total TCDDs Small Mammals Herbivorous Small Mammals Shrews Total Small Mammal Dietary Exposure ADDpot Reference 0.0004 to 0.0109 ADDpot Target 0.04 to 1.04 0.0003 to 0.0013 0.0565 to 0.283 0.0007 to 0.0123 0.0979 to 1.32 47

Summary Dietary exposure assessment Examination of prey remains Dietary items have been sampled Telemetry is being used to determine foraging area Tissue-based exposure assessment Samples collected Addled eggs Blood plasma Population health Productivity measurements Clutch size Hatching success Fledging success 48

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Questions Sarah J. Coefield Graduate Research Assistant Michigan State University Aquatic Toxicology Laboratory (517) 432-3100 x172 coefield@msu.edu 50