Skip to main content
Log in

Chronic Toxicity of Unweathered and Weathered Macondo Oils to Mysid Shrimp (Americamysis bahia) and Inland Silversides (Menidia beryllina)

  • Published:
Archives of Environmental Contamination and Toxicology Aims and scope Submit manuscript

Abstract

Chronic, 21–28-day toxicity tests of Macondo source (Massachusetts, or MASS) and weathered Slick A (CTC) and Slick B (Juniper) oils field collected during the 2010 Deepwater Horizon (DWH) Incident in the Gulf of Mexico (GOM) were conducted using standardized procedures. Standard species, Americamysis bahia and Menidia beryllina, were evaluated for changes in survival and growth during daily static-renewal tests. Both species demonstrated an increased sensitivity to low-energy water accommodated fractions (WAFs) of un-weathered MASS oil, with growth and survival decreasing as oil loading rate increased from 0.01 to 1.0 g/L. Survival and growth of mysid shrimp exposed to weathered oil (Slick A and Slick B) did not differ from that of test controls. In contrast, survival and growth of inland silversides declined relative to that of test controls at loading rates of 1 g/L for both weathered oils. Based on the concentration of total polycyclic aromatic hydrocarbons (TPAH42), no observed effect concentrations were lower for inland silverside survival (5.00–7.61 µg/L) and growth (<2.02 to <7.61 µg/L) in chronic exposures to Slick B and Slick A weathered oils compared with mysids (4.75–17.9 µg/L). Average TPAH concentrations in full strength WAFs followed the weathering trend, with 165 ± 17.2, 17.9 ± 0.480, and 4.75 ± 0.521 µg/L for MASS, Slick A, and Slick B oils, respectively. The effect (LOEC, IC25) and no-effect exposure concentrations (in TPAHs) from the standardized laboratory toxicity studies with un-weathered and weathered oils are discussed relative to the actual exposure concentrations in the GOM in 2010. The exposures evaluated in the laboratory toxicity tests represent the highest concentrations of total PAHs that were rarely observed in water column samples collected in the GOM during the release and post release periods of the DWH incident.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Fig. 1
Fig. 2
Fig. 3
Fig. 4

Similar content being viewed by others

References

  • Almeda R, Wambaugh Z, Wang Z, Hyatt C, Liu Z, Buskey EJ (2013) Interactions between zooplankton and crude oil: toxic effects and bioaccumulation of polycyclic aromatic hydrocarbons. PLoS ONE 8:e67212

    Article  CAS  Google Scholar 

  • Anderson JW, Neff JM, Cox BA, Tatem HE, Hightower GM (1974) Characteristics of dispersions and water-soluble extracts of crude and refined oils and their toxicity to estuarine crustaceans and fish. Mar Biol 27:75–88

    Article  CAS  Google Scholar 

  • ASTM E1191-03a (2008) Standard guide for conducting life-cycle toxicity tests with saltwater mysids. ASTM International, West Conshohocken

  • Barron MG (2012) Ecological impacts of the Deepwater Horizon oil spill: implications for immunotoxicity. Toxicol Pathol 40(2):315–320

    Article  CAS  Google Scholar 

  • Barron MG, Ka’aihue L (2003) Critical evaluation of CROSERF test methods for oil dispersant toxicity testing under subarctic conditions. Mar Pollut Bull 46:1191–1199

    Article  CAS  Google Scholar 

  • Barron MG, Hemmer MJ, Jackson CR (2013) Developments of aquatic toxicity benchmarks for oil products using species sensitivity distributions. Integr Environ Assess Manag 99:1–6

    Google Scholar 

  • Biomonitoring Science Advisory Board (BSAB) (1994) Criteria for acceptable variability of marine chronic toxicity test methods. Washington Department of Ecology BSAB Report #1

  • Boehm PD, Murray KJ, Cook LL (2016) Distribution and attenuation of polycyclic aromatic hydrocarbons in Gulf of Mexico seawater from the Deepwater Horizon Oil Accident. Env Sci Tech 50:584–592

    Article  CAS  Google Scholar 

  • Brette F, Machado B, Cros C, Incardona JP, Scholz NL, Block BA (2014) Crude oil impairs cardiac: excitation-contraction coupling in fish. Science 343:772–776

    Article  CAS  Google Scholar 

  • Carls MG, Rice SD, Hose JE (1999) Sensitivity of fish embryos to weathered crude oil: Part I. Low level exposure during incubation causes malformations, genetic damage, and mortality in larval Pacific herring (Clupea pallasi). Environ Toxicol Chem 18:481–493

    Article  CAS  Google Scholar 

  • Clark JR, Bragin GE, Febbo EJ, Letinski DJ (2001) Toxicity of physically and chemically dispersed oils under continuous and environmentally realistic exposure conditions: applicability to dispersant use decisions in spill response planning. In: Proceedings of the 2001 international oil spill conference, pp 1249–1255

  • Crane M, Newman MC (2000) What level of effect is a no observed effect? Environ Toxicol Chem 19:516–519

    Article  CAS  Google Scholar 

  • Dubansky B, Whitehead A, Miller J, Rice CD, Galvez F (2013) Multi-tissue molecular, genomic, and developmental effects of the Deepwater Horizon oil spill on resident Gulf killifish (Fundulus grandis). Environ Sci Technol 47(10):5074–5082

    Article  CAS  Google Scholar 

  • Echols BS, Smith A, Gardinali P, Rand G (2016a) An evaluation of select test variables potentially affecting acute oil toxicity. Arch Env Contam Tox 70:392–405

    Article  CAS  Google Scholar 

  • Echols BS, Smith AJ, Gardinali PR, Rand GM (2016b) The use of ephyrae of a scyphozoan jellyfish, Aurelia aurita, in the aquatic toxicological assessment of Macondo oils from the Deepwater Horizon incident. Chemosphere 144:1893–1900

    Article  CAS  Google Scholar 

  • Faksness LG, Altin D, Nordtug T, Daling PS, Hansen BH (2015) Chemical comparison and acute toxicity of water accommodated fraction (WAF) of source and field collected Macondo oils from the Deepwater Horizon spill. Mar Poll Bull 91:222–229

    Article  CAS  Google Scholar 

  • Fingas M (2011) Oil spill science and technology: prevention, response, and cleanup (Gulf Professional Publishing, Burlington MA, 2011), 1192 pp

  • Giddings JM, Hall LW, Anderson TA, Hosmer AJ, Kendall RJ (2005) Atrazine in North American surface waters: a probabilistic aquatic ecological risk assessment. Society of Environmental Toxicology and Chemistry, Pensacola Gulf Science Data http://gulfsciencedata.bp.com

  • Heintz R, Short J, Rice S (1999) Sensitivity of fish embryos to weathered crude oil: Part II. Increased mortality of pink salmon (Oncorhynchus gorbuscha) embryos incubating downstream from weathered Exxon Valdez crude oil. Environ Toxicol Chem 18:494–503

    Article  CAS  Google Scholar 

  • Incardona JP, Swarts TL, Edmunds RC, Linbo TL, Aquilina-Beck A, Sloan CA, Scholz NL (2013) Exxon Valdez to Deepwater Horizon: comparable toxicity of both crude oils to fish early life stages. Aqua Toxicol 142:303–316

    Article  Google Scholar 

  • Incardona JP, Gardner LD, Linbo TL, Brown TL, Esbaugh AJ, Mager EM, Scholz NL (2014) Deepwater Horizon crude oil impacts the developing hearts of large predatory pelagic fish. Proc Nat Acad Sci 111:E1510–E1518

    Article  CAS  Google Scholar 

  • Lee K, Boufadel M, Chen B, Foght J, Hodson P, Swanson S, Venosa A (2015) Expert panel report on the behaviour and environmental impacts of crude oil released into aqueous environments. R Soc Can, Ottawa, ON. ISBN 978-1-928140-02-3

    Google Scholar 

  • Lehr BP et al. (2010) Oil Budget Calculator: Deepwater Horizon. Technical Document: A Report to the National Incident Command, November 2010. 217 pp

  • NAS (2013) An ecosystem services approach to assess the impacts of the Deepwater Horizon oil spill in the Gulf of Mexico. Chapter 4, Oil Spill Response Technologies. Committee on the effects of the Deepwater Horizon Mississippi Canyon 252 oil spill on ecosystem services in the Gulf of Mexico, Ocean Science Board, NRC. National Academy Press, Washington, DC

  • Neff JM (1999) Toxicity effects. Element 8. In: Robertson SB (ed) Guidelines for the scientific study of oil spill effects. Robertson Environmental Services Publishers, Langley, pp 1–31

    Google Scholar 

  • NOAA (2010) Analytical quality assurance plan. Mississippi Canyon 252 (Deepwater Horizon) Natural Resource Damage Assessment. Version 2.2

  • OSAT (2010) Summary report for sub-sea and sub-surface oil and dispersant detection: sampling and monitoring. Operational Science Advisory Team, Unified Area Command, Deepwater Horizon MC252, 17 December 2010, pp 35

  • Pastorak RA, Anderson JW, Butcher MK, Sexton JE (1994) West coast marine species chronic protocol variability study. Columbia Aquatic Sciences (PTI Contract No. C333-03-01)

  • Paul JH, Hollander D, Coble P, Daly KL, Murasko S, English D, Basso J, Delaney J, McDaniel L, Kovach CW (2013) Toxicity and mutagenicity of Gulf of Mexico waters during and after the Deepwater Horizon oil spill. Environ Sci Technol 47:9651–9659

    Article  CAS  Google Scholar 

  • Prince RC, Elmendorg DL, Lute LR, Hsu CS, Haith CE, Senius JD et al (1994) 17.Alpha. (H)-21.beta. (H)-hopane as a conserved internal marker for estimating the biodegradation of crude oil. Environ Sci Technol 28:142–145

    Article  CAS  Google Scholar 

  • Rand GM (1995) Fundamentals of aquatic toxicology-effects. Environmental fate and risk assessment. Taylor & Francis, Boca Raton, FL

    Google Scholar 

  • Rhoton SL, Perkins RA, Braddock JF, Behr-Andres C (2001) A cold-weather species’ response to chemically dispersed fresh and weathered Alaska North Slope crude oil. In: Proceedings, 2001 international oil spill conference, American Petroleum Institute, Washington, DC, pp 1231-1236

  • Schuett K (2010) Source oil sample provenance (Updated Oct7 2010)

  • Singer MM, Jacobson S (2001a) Acute effects of fresh versus weathered oil to marine organisms: California findings. In: Proceedings of the 2001 international oil spill conference, API, Washington, DC, pp 1263–1268

  • Singer MM, Aurand D, Bragin GE, Clark JR, Coelho GM, Sowby ML, Tjeerdema RS (2000) Standardization of the preparation and quantitation of water-accommodated fractions of petroleum for toxicity testing. Mar Pollut Bull 40:1007–1016

    Article  CAS  Google Scholar 

  • Singer MM, Aurand D, Coelho GM, Bragin GE, Clark JR, Sowby ML, Tjeerdema RS (2001b) Making, measuring, and using water accommodated fractions of petroleum for toxicity testing. Proceedings, 2001 international oil spill conference. API, Washington, DC

  • Solomon KR, Baker DB, Richards P, Dixon KR, Klaine SJ, La Point TW, Kendall RJ, Giddings JM, Giesy JP, Hall LW Jr, Weisskopf C, Williams M (1996) Ecological risk assessment of atrazine in North American surface waters. Environ Toxicol Chem 15:31–76

    Article  CAS  Google Scholar 

  • U.S. Environmental Protection Agency (USEPA) (1991) Technical support document for water quality-based toxics control. U.S. Environmental Protection Agency, Washington, D.C. EPA-505-2-90-001. 335 pp

  • U.S. Environmental Protection Agency (USEPA) (2002) Short-term methods for estimating the chronic toxicity of effluents and receiving waters to marine and estuarine organisms, 3rd edn. U.S. Environmental Protection Agency, Washington, D.C. EPA-821-R-02-014. 464 pp

  • Wu D et al (2012) Comparative toxicity of four chemically dispersed and undispersed crude oils to rainbow trout embryos. Environ Toxicol Chem 31:754–765

    Article  CAS  Google Scholar 

Download references

Acknowledgments

This work was supported by BP Exploration & Production Inc. and the BP Gulf Coast Restoration Organization. These studies were conducted at Environmental Enterprises USA (Slidell, LA). This is contribution number 786 from the Southeast Environmental Research Center at Florida International University.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to B. Echols.

Rights and permissions

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Echols, B., Smith, A., Gardinali, P.R. et al. Chronic Toxicity of Unweathered and Weathered Macondo Oils to Mysid Shrimp (Americamysis bahia) and Inland Silversides (Menidia beryllina). Arch Environ Contam Toxicol 71, 78–86 (2016). https://doi.org/10.1007/s00244-016-0280-x

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s00244-016-0280-x

Keywords

Navigation