Chromated copper arsenate (CCA)-treated wood has been used worldwide since 1933. In properly fixed wood, the chromium, copper, and arsenic are tightly bound to the wood fibers. However, it has long been known that small amounts of these metals do leach from properly treated wood products. These metals, particularly the cupric ion (Cu2+), are known to be highly toxic to aquatic organisms at concentrations as low as 6 μg Cu l−1. The United States Environmental Protection Agency has established a marine water quality standard of 2.9 μg Cu l−1 total copper. Washington State has established a marine water quality standard of 2.5 μg Cu l−1 and a marine sediment standard of 390 mg Cu g−1 (dry sediment). Comparison of these standards with the results of bioassays suggests that these levels are sufficiently low to protect even the most sensitive organisms. Metal losses are an inverse function of time and decline to background levels within 60–90 d of treated wood immersion. Increasing use of CCA-treated wood to construct residential bulkheads in estuarine environments on the east coast of the United States has raised concerns regarding the near-term environmental risks associated with these uses. This paper reports the development of a spreadsheet-based computer model to predict water column and sediment concentrations of copper leached from bulkheads and piling. Model output is compared with data in Weis et al. (1991, 1993) and Weis and Weis (1992). The model predicts environmental levels of copper that are highly dependent on input parameters but below regulatory levels for most projects constructed in reasonably well-circulated bodies of water. The model does demonstrate the possibility of exceeding regulatory standards for up to 3 wk when bulkheads are installed in very poorly flushed aquatic environments or where the surface area of the CCA-treated wood structure is a significant proportion of the water body surface area.
[1]
F. H. Tainter,et al.
Effect of rapid redrying shortly after treatment on leachability of CCA-treated southern pine
,
1993
.
[2]
Keith R. Solomon,et al.
Acidity as a factor in leaching of copper, chromium and arsenic from CCA-treated dimension lumber
,
1990
.
[3]
J. Weis,et al.
Transfer of contaminants from CCA-treated lumber to aquatic biota
,
1992
.
[4]
J S Weis,et al.
Toxicity to estuarine organisms of leachates from chromated copper arsenate treated wood
,
1991,
Archives of environmental contamination and toxicology.
[5]
J. Irvine,et al.
The Mechanism of Leaching of Copper-Chrome-Arsenic Preservatives from Treated Timber in Saline Waters
,
1976
.
[6]
J. Dorigan,et al.
Physiological responses of marine organisms to environmental stresses
,
1987
.
[7]
R. Eisler.
Mercury Hazards to Fish, Wildlife, and Invertebrates: A Synoptic Review
,
1987
.
[8]
Kenneth Y. Chen,et al.
Migration of trace metals in interfaces of sea water and polluted surficial sediments
,
1977
.
[9]
Jerome O. Nriagu,et al.
Arsenic in the Environment Part I: Cycling and Characterization
,
1994
.
[10]
P. Cooper.
Leaching of CCA from treated wood: pH effects
,
1991
.
[11]
S. Dahlgren.
Kinetics and Mechanism of Fixation of Cu-Cr-As Wood Preservatives. Part V. Effect of Wood Species and Preservative Composition on the Leaching during Storage
,
1975
.
[12]
J. Weis,et al.
Copper, Chromium, and Arsenic in Estuarine Sediments Adjacent to Wood Treated with Chromated-Copper-Arsenate (CCA)
,
1993
.