Addressing Pressured Treated Wood
CCA-treated wood does leach arsenic into the environment. EPA has not at this time concluded that CCA-treated wood posses unreasonable risks or should be removed or replaced. Several studies have shown that arsenic in CCA does in fact leach out of CCA-treated wood, both, when the wood is new and when the wood ages. Also arsenic is easily transferable to the hands of anyone coming into contact with the wood according to several swipe tests. However, the jury is still out to the exact risk of this type of pressured treated wood since EPA is making several risk assessment of CCA-treated wood. One EPA study is evaluating children’s exposure at residential and recreational sites. The service life of CCA-treated wood products is 25-40 years.
Until the proposed phase-out of the chemical by the
It is forecasted that the quantity of CCA-treated wood disposed within the next 20 to 30 years (which corresponds to the typical service life of treated wood products) will be on the order of 14 million cubic meters per year, which is the approximate quantity that is currently purchased today. This quantity of arsenic is significant and can impact the environment to a considerable extent if the wood is not properly disposed.
There is debate as to the exact CCA-treated wood impact upon public health. CCA wood used in playground equipment has some activities calling it “Poisoned Playgrounds.” While those in the wood preservative industry contend that highest amount of arsenic found in dirt under CCA decks would still provide less than one-twelfth the average exposure of arsenic that a child receives merely in drinking water. The state appointed Florida Physicians Workgroup concluded last year that, “the available data have not demonstrated any clinical disease associated with arsenic exposure from playground equipment of the CCA-treated wood.[2]
EPA recommends that children who play outside around CCA structures should wash their hands prior to eating. Also people working with CCA- treated wood should reduce exposure by wearing dust mask, goggles, gloves and other protective clothing.
Since 1995 a research team from the
In Florida, arsenic observed in soils was greater than background concentrations (28.5 mg/kg)3. Also below deck arsencis concentrations exceeded Florida's soil clean-up target levels, potentially threatening human health and the environment. The data further indicates that metals do migrate through soil released by runoff impacting groundwater.
The potential use of alternative wood preservatives must be promoted to subsitute CCA and minimize CCA waste. These alternatives are less harmful since they do not contain arsenic.
Improved disposal-end management play a key role in lessening the environmental impacts of CCA waste. Such new disposal methods can sort CCA wood from untreated wood and support full-scale technological methods to lessen arsenic exposure to the public and environment. Untreated wood can be recoverd as a fuel, mulch and other uses once reasonable assurances are provided that this wood is free of CCA.
There are three primary disposal pathways for CCA-treated wood: within construction and demolition (C&D) landfills, recycled as wood fuel, or recycled as mulch. In 1996, an evaluation of wood waste at three C&D facilities found that the wood waste piles were composed of 9 to 30% CCA-treated wood (Solo-Gabriele et al. 2000).
There are two types of waste leaching guidelines, the Synthetic Precipitation Leaching Procedure (SPLP) and the Toxicity Characteristics Leaching Procedure (TCLP). These tests involve the addition of a waste material to a leaching fluid and contacting the waste with the fluid for a period of 18 hours. The metal concentrations in the leachate are then measured at the end of the test. If the concentration of a given metal exceeds a set level, then the waste fails that particular test. In general, SPLP is used to evaluate whether a waste can be land applied or disposed in an unlined landfill. The TCLP test is used to evaluate whether the waste can be disposed in a lined landfill. Results have shown that CCA-treated wood consistently fails guidelines based on the SPLP test and will on occasion fail guidelines based on the TCLP results.
CCA-treated wood within wood fuel is of concern due to potential toxic air emissions, such as the incineration arsenic and chromium and the resulting metals found in the ash. Subsequent studies to characterize CCA-treated wood ash indicate that all ash samples made entirely from CCA-treated wood failed TCLP regulatory levels and would thus be considered a hazardous waste. It was also found that a mixture of 95% untreated wood with 5% CCA-treated wood would cause the ash to fail on some occasions. The proportion of CCA-treated wood within the wood fuel mix should be less than 5%.
There has been a recent increase in the use of C&D wood waste for the production of colored mulch. Since much of this may be contaminated with CCA, recycled C&D CCA-treated wood becomes land applied increasing the potential for contaminating the environment with arsenic, chromium, and copper.
CCA-treated wood best management practice must be developed to lessen CCA chemicals into the environment. Numerous alternative wood preservatives are being developed and used by the American Wood Preservers’ Association. However, there needs to be a CCA-treated wood management plan to minimize risks when CCA-treated wood is used, recycled, burned or disposed of. How we can best manage CCA-treated wood so it harm our health our environment?
*Much of the information in this paper was borrowed from Helena M. Solo-Gabriele1, Timothy G. Townsend, John Schert, “Environmental Impacts of CCA-Treated Wood: A Summary from Seven Years of Study Focusing on the U.S. Florida Environment.”
[1] Cole and Clausen, 1996; Micklewright, 1994
[2] Michael Fumento, “Protecting Kids Right off the Playground.” Scripps Howard News Service,
[3] Helena M. Solo-Gabriele1, Timothy G. Townsend2, John Schert, “Environmental Impacts of CCA-Treated Wood: A Summary from Seven Years of Study Focusing on the
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