Metal Birds

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    Oksana Lane1, Oscar Brenes2, Peter Doherty3 , Pablo Elizondo4, and Robert Taylor5, Bruce Rinker1*1 Biodiversity Research Institute, Gorham, Maine, USA; 2 Reserva Playa Tortuga, Ojochal, Costa Rica; 3 Virginia, USA; 4 INBioparque, San Jose, Costa Rica; 5 Trace Element Research Laboratory,

    Texas A&M, College Station, Texas, USA

    *Presenter

    Heavy metals screening in feathers of resident birds and neotropical migrants at

    selected sites in Costa Rica and Panama

    Metales pesados en las plumas de aves residentes y migratorias neotropicales, en

    sitios selectos de Costa Rica y Panam

    ABSTRACT: We non-lethally collected feather samples from resident and migrant birds from

    several sites representing different habitats in Costa Rica and Panama to assess if exposure to

    mercury (Hg) and/or other heavy metals are of concern at these sites. Of 43 species sampled

    in Costa Rica and nine in Panama, mercury exposure was in generally low at all sites. The

    American pygmy kingfisher (Chloroceryle aenea) had the highest mercury levels of all birds

    sampled, ranging from 2.8 to 5.7 ppm (parts per million) in Panama to 11 ppm at Cao Palma

    Research Station in Barra del Colorado Wildlife Refuge, Costa Rica. Feather mercury

    concentrations over 4.6 ppm are considered elevated in songbirds (Jackson et al. 2011) and

    over 40 ppm in fish-eating birds (Evers et al. 2008). Invertivorous neotropical migrantssuch

    as the northern waterthrush (Seiurus noveboracencis), spotted sandpiper (Actitis macularius)

    and piscivorous species such as resident kingfishers foraging in aquatic habitats (ie. streams

    and mangroves) tended to have higher feather mercury concentrations than other species.

    A subset of feather samples (n = 39) were analyzed for other metals including several

    essential elements. Here we focus on selected metals that were elevated in sampled birds:

    aluminum (Al), barium (Ba), copper (Cu), iron (Fe), manganese (Mn), strontium (Sr), tin (Sn)

    and zinc (Zn).

    ACKNOWLEDGEMENTS

    We are grateful to Alejandra Martinez and the staff from CATIE, Todd Lewis fromCao Palma Biostation, Costa Rica, biologists Jon Van Dort and Evelyn Paola

    Thibodeau, and the staff of the Center for Caribbean Conservation and Reserva

    Playa Tortuga all helped with bird capture and banding. We thank Kevin Regan at

    BRI for Hg analysis.

    American Pygmy Kingfisher (Chloroceryle aenea), resident in Costa Rica and Panama

    Figure 1. Study sites in Costa Rica and Panama

    INTRODUCTIONHeavy metals are among the most toxic poisons known with the nervous system often being the principal

    target. We are unaware of any published studies that address heavy metal exposure to the resident birds

    and neotropical migrants of Mesoamerica. Most of the toxicity information available focus on aquatic

    organisms, particularly fish, but little has been published on metal toxicity in other vertebrates including

    birds.Elevated exposure to Al can be toxic to fish and cause pulmonary and developmental problems. Barium

    does not bioaccumulate but at high exposures can induce gastrointestinal distress, muscular paralysis, and

    cardiovascular problems at concentrations exceeding 10 ppm (Moore 1991). Toxic effects to birds from

    exposure to Cu include reduced growth rates, lowered egg production, and developmental abnormalities

    (US EPA 2008). Elevated concentrations of Mn in birds have been known to cause decreased hemoglobin,

    anemia, and reduced growth (ATSDR 1991). Elevated levels of Zn can cause mortality, pancreatic

    degradation, reduced growth, and decreased weight gain in birds (Eisler 1993, NAS 1980). And mercury, in

    its methylated form, is a well known neurotoxin and has been shown to affect reproductive success in birds

    (Evers et al. 2008, Jackson et al. in press).

    Many studies have surveyed for heavy metals in pelagic sea birds, but fewif anyhave assessed heavy

    metal exposure to the resident and migrant birds of Mesoamerica. This study provides an initial survey of

    heavy metal concentrations for the region.

    METHODSAND STUDY AREAOuter tail feathers (R6) were pulled from birds

    captured using mistnets. Birds were released

    following sampling at the site of capture. Sampling

    was completed between November 15, 2010 and

    April 19, 2011. Mercury analysis in feathers wasdone using a Direct Mercury Analyzer (DMA-80) by

    Millestone Inc. at Biodiversity Research Institute

    Wildlife Mercury Research Lab in Maine, USA.

    Trace metal scan was done using ICP-MS at the

    Trace Element Research Lab at Texas A&M

    University, Texas, USA.

    In Costa Rica we sampled 2 sites in the lowlands

    on the Caribbean Coast near Tortuguero (Cao

    Palma and Tortuguero), one site in a cacao

    plantation near Volcan Turrialbo (CATIE), one site in

    San Jose (INBio Parque) and one site on the Pacific

    Coast in the wetlands of Ojochal (Reserva Playa

    Tortuga). In Panama three mangrove sites were

    sampled on the Atlantic coast (Playa Bonita,

    Panama Vieja and Juan Diaz; Figure 1).

    RESULTSSee table 1 for metal concentrations by site

    and individuals, and figures 2 and 3 for

    summary of selected heavy metals by site

    and species. Due to lack of funding only a

    few samples were screened for heavy

    metals. This study serves as a pilot

    screening to determine if further sampling is

    necessary to assess contaminant exposure to

    birds and other wildlife in Central America

    and to locate sources of contamination.

    Table 1. Concentrations of heavy metals in bird feathers (ppm or mg/kg) from Costa Rica and Panama (numbers in re

    we consider high or elevated; species in bold are considered residents).

    LITERATURECITED

    Evers, D. C., L. Savoy, C. DeSorbo, D. Yates, W. Hanson, K. Taylor, L. Siegel,J. Cooley, M. Bank, A. Major, K. Munney, B. Mower, H. Vogel, N.

    Schoch, M. Pokras, M. Goodale, and J. Fair. 2008. Adverse effects

    from environmental mercury loads on breeding common loons.

    Ecotoxicology 17:69-81.

    Jackson, A. K., D. C. Evers, M. A. Etterson, A. M. Condon, S. B. Folsom, J.

    Detweiler, J. Schmerfeld, D. A. Cristol. 2011. Mercury exposure

    affects the reproductive success of a free-living terrestrial songbird,

    the Carolina wren (Thryothorus l udovicianus). The Auk. In press.

    DISCUSSIONCertain species, such as the spotted

    sandpiper, appear to have elevated levels of

    several toxic elements including copper (Cu),

    manganese (Mn), Tin (Sn) and mercury (Hg).

    In addition to exposure through diet,

    shorebirds may ingest a portion of the

    metals by consuming contaminated

    sediment while foraging. Many heavy metals

    are also used in pesticides and

    manufacturing and birds may occupy

    agricultural habitats or areas downstream

    from polluted areas allowing for exposure to

    many contaminants.

    It appears that further investigation into

    contaminant exposure to birds in Central

    America is warranted based on these

    preliminary data.

    Figure 2. Concentrations of trace elements in tail feathers of

    individual spotted sandpipers in Costa Rica and Panama.

    Figure 3. Mercury concentrations in feathers of kingfishers from Costa

    Rica and Panama.

    RESUMEN: no letales recogieron muestras de plumas de aves residentes y migratorias de varios sitios que

    representan los diferentes hbitats en Costa Rica y Panam para evaluar si la exposicin al mercurio (Hg) y

    / u otros metales pesados son motivo de preocupacin en estos sitios. De 43 especies muestreadas en

    Costa Rica y nueve en Panam, la exposicin al mercurio fue en general baja en todos los sitios. El martn

    pescador estadounidense enano (Chloroceryle aenea) tenan los niveles ms altos de mercurio de todas

    lasaves objeto de muestreo, que van desde 2,8 hasta 5,7 ppm (partes por milln)en Panam a 11 ppm en

    Cao Palma Estacin de Investigacin en Barra del Colorado Wildlife Refuge, Costa Rica. Concentraciones

    de mercurio en plumas de ms de 4,6 ppm se consideran elevadas en aves cantoras (Jackson et al. 2011) y

    ms de 40 ppm en aves piscvoras (Evers et al. 2008). Invertivorous migrantes neotropicales, tales como

    el waterthrush norte (Seiurus noveboracencis), playero manchado (Actitis macularius) y las especies se

    alimentan de peces como el martn pescador residente de alimentacin en los hbitats acuticos (ros y

    manglares es decir), tendan a tener mayores concentraciones de mercurio que otras especies de

    plumas. Un subconjunto de muestras de plumas (n = 39) fueron analizadas por otros metales incluyendo

    varios elementos esenciales. Aqu nos centramos en los metales seleccionados que fueron elevados

    en aves objeto de muestreo: de aluminio (Al), bario (Ba), cobre (Cu), hierro (Fe), manganeso (Mn),

    estroncio (Sr), estao (Sn) y zinc (Zn).

    0

    2

    4

    6

    8

    10

    12

    American Pygmy Kingfisher

    (Chloroceryle aenea)

    Green and Rufous

    Kingfisher (Chloroceryle

    inda)

    Green Kingfisher

    (Chloroceryle americana)

    Juan Diaz, Panama (3; 1)

    Cao Palma, Costa Rica (1)

    Rio Balso, Ojochal, Costa Rica (1)

    Feather

    Mercury(ppmf

    w)

    Site Species Al Ba Cu Hg Mn Sn Sr Zn

    Cao Palma, CR American Pygmy kingfisher 9.5 0.81 9.87 11.29 2.98 3.62 2.29 141

    Northern waterthrush 10.7 1.96 5.62 2.20 14.9 1.29 1.43 119

    Red-capped manakin 90.6 3.39 7.9 0.50 24.2 3.91 2.73 106

    S ummer t an ager 3 1. 7 4. 41 5.9 7 0. 09 13. 5 3.6 5 1 .31 1 04

    Swainson's thrush 13.1 2.09 6.57 0.50 8.86 3.85 1.25 97.7

    Swainson's thrush 52.2 2.35 6.68 0.19 12.8 2.28 1.57 93.7

    White-collared manakin 50.2 4.83 6.36 0.35 8.67 3.3 2.76 109

    Wood thrush 260 7.86 7.92 1.89 47.8 2.22 4.62 96.1

    Wood thrush 342 9.01 6.53 1.67 37.9 2.15 4.1 95.2Tortuguero, CR Swainson's thrush 36.3 3.9 9.58 1.02 9.98 3.36 1.51 102

    Yellow bell ied flycatcher 10.6 3.83 6.2 1.26 40 3.31 2.02 96.6

    CATIE, CR Baltimore oriole 288 6.34 8.34 0.27 15.3 2.06 4.61 61.2

    Chesnut-sided warbler 21.8 2.83 6.66 12.4 4.18 1.23 110

    Passarin's tanager 458 25.5 7.33 0.08 52.9 2.1 5 1 1 10 3

    Yellow-throated euphonia 61 31.9 5.3 0.06 8.87 4.24 8.63 100

    In Bi o, S an Jose, CR N ort hern wa tert hru sh 3 1. 8 2. 03 1 9. 6 1. 24 1 7. 5 2.5 7 2.58 9 6. 8

    Philadelphia v ireo 56.3 1.56 6.59 0.21 1.43 4.32 1.12 90.2

    Reserva Play Tortuga, Ojochal, CR Black-hooded antshrike 20.1 4.25 7.43 0.03 19.6 5.13 5.28 154

    Blue-grey tanager 34.2 7.19 7.14