Legacy metals, a result of previous environmentally unsound practices, pose a challenge to the rehabilitation of urban aquatic ecosystems. The current study focuses on a harbor in Vancouver, British Columbia, Canada, where use of antifouling paints for hull cleaning occurred for ca. 30 years. Sediment metal concentrations were mapped by depth and distance from where hulls were cleaned. By relating metal concentrations to the benthic invertebrate community and bivalve metal content, results indicate that cleaning activities severely impacted sediment quality. However, sewer outfalls, which integrate non-point sources of metals to the harbor, also contributed to poor sediment quality and high metal concentrations in bivalves. For the aquatic system to recover, non-point diffuse metal sources must be addressed, regardless of the challenge.
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Ballan-Dufrançais C, Jeantet AY, Geffard A, Amiard JC, Amiard-Triquet C (2001) Cellular and tissue distribution of copper in an inter-sedimentary bivalve, the baltic clam Macoma balthica, originating from a clean or a metal-rich site. Can J Fish Aquat Sci 10:1964–1974
Bendell-Young LI (2006) Contrasting the community structure and select geochemical characteristics of three intertidal regions in relation to shellfish farming. Environ Conserv 1:21–27
BIEAP (2006) Burrard Inlet Environmental Action Program. Application for Coordinated Environmental Review of Proposed Sediment Sampling Works in Coal Harbor. City of Vancouver, BC. BERC CPR#200612B027
Bird DJ, Duquesne S, Hoeksema SD (2011) Title: complexity of spatial and temporal trends in metal concentrations in macroinvertebrate biomonitor species in the Severn Estuary and Bristol Channel. J Mar Biol Assoc UK 1:139–153. doi:10.1017/S0025315410001918
Cain J, Luoma S (1986) Effect of seasonally changing tissue weight on trace metal concentrations in the bivalve Macoma balthica in San Francisco Bay. Mar Ecol Prog Ser 28:209–217
CCME, Canadian Council of Ministers of the Environment (2006) Canadian Environmental Quality Guidelines
Clarke KR (1993) Non-parametric multivariate analyses of changes in community structure. Aust J Ecol 18:117–143
Clarke KR, Gorley RN (2006) PRIMER v6: Users Manual/Tutorial PRIMER-E: Plymouth, 2006, England
Comber SDW, Gardner MJ, Boxall ABA (2002) Survey of four marine antifoulant constituents (copper, zinc, diuron and irgarol 1051) in two UK estuaries. J Environ Monit 3:417–425
Davis AP, Sholouhian M, Ni S (2001) Loading estimates of lead, copper, cadmium and zinc in urban runoff from specific sources. Chemosphere 44:997–1009
Hewitt CN, Rashed MB (1990) An integrated budget for selected pollutants for a major rural highway. Sci Total Environ 1:375–384
Johnsen A, Engøy T (2000) Contamination from Marine Paints—A Norwegian Perspective. Defense Technical Information Center Compilation Part Notice ADPO10602. Part of report: Approaches to the implementation of Environment Pollution Prevention Technologies at Military Bases
Johnson LT, Gonzalez JA (2004) Staying Afloat with Nontoxic Antifouling Paint Strategies for Boats. California Sea Grant College Program Report No. T-054. URL: http://ucanr.org/sites/coast/Nontoxic_Antifouling_Strategies/
Luoma S, Cain D, Ho K, Hutchinson A (1983) Variable tolerance to copper in two species from San Francisco Bay. Mar Environ Res 10:209–222
Meinkoth N (1981) The Audubon Society Fields Guide to North American Seashore Creatures Alfred A Knopf. Inc. New York
Neira C, Delgadillo-Hinojosa F, Zirino A, Mendoza G, Levin LA, Porrachia M, Deheyn D (2009) Spatial distribution of copper in relation to recreational boating in a California shallow water basin. Chem Ecol 6:417–433
Pan K, Wang WX (2009) Biodynamic to explain the difference of copper body concentrations in five marine bivalve species. Environ Sci Technol 43:2137–2143
Phippen B (2001) Assessment of Burrard inlet water and sediment quality (2000) Report prepared for Water Protection Branch Ministry of Water Land, and Air Protection Victoria BC http://www.env.gov.bc.ca/wat/wq/objectives/burrardinlet/index.htmlDecember 2001
Piola RF, Dafforn KA, Johnston EL (2010) The influence of antifouling practices on marine invasions. Biofouling 4:497
Schiff K, Diehl D, Valkirs A (2004) Copper emissions from antifouling paint on recreational vessels. Mar Pollut Bull 3–4:371–377
Turner A (2010) Marine pollution from antifouling paint particles. Mar Pollut Bull 2:159–171
Turner A, Fitzer S, Glegg GA (2008) Impacts of boat paint chips on the distribution and availability of copper in an English River. Environ Pollut 1:176–181
Warnken J, Dunn RJK, Teasdale PR (2004) Investigation of recreational boats as a source of copper at anchorage sites using time-integrated diffusive gradients in thin film and sediment measurements. Mar Pollut Bull 9–10:833–843
We thank Dr. N. Angerilli for initiating this study. Field assistance of C. Santacruz, T. L’Espérance and A. Parsamanesh is gratefully appreciated. We thank T. Soo for editing assistance and N. Duckham for graphic design.
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Duckham, C., Bendell, L.I. Legacy Metals Within Urban Aquatic Environments and the Challenge They Pose to Rehabilitation. Bull Environ Contam Toxicol 91, 396–401 (2013). https://doi.org/10.1007/s00128-013-1082-8
- Anti-fouling paints
- Sewer outfalls