Biocide leaching from CBA treated wood — A mechanistic interpretation
Highlights
► A pH dependent leaching mechanism for CBA treated wood is described. ► The fixation and mobilisation of inorganic and organic biocides was investigated. ► Extractives' quantity and nature depend on pH. ► Competition of ligands for protonation and complexation explains Cu behaviour. ► Tebuconazole seems to interact with OH groups on wood.
Introduction
Pollutant release from construction products in contact with water is currently a research subject receiving attention from the European regulation and standardisation authorities (EC, 2005). Being an economical, durable and aesthetically pleasing building material, treated wood is a frequent choice for construction projects. However, we need to ensure that biocides used for the treatment do not pose a threat to people or environment. Previous studies generally report high leaching rates from treated wood, depending on the type of preservative, exposure conditions and wood specimen (Lebow, 1996, Ahn et al., 2010, van Zomeren et al., 2005, Schiopu et al., 2012).
Understanding the leaching process is crucial for the management of wood products over their whole life cycle, especially during their use stage and end of life (wastes), but also for developing new treatment methods and products. So far, leaching from wood has been investigated for inorganic and a few selected organic preservatives, and factors that influence their release have already been summarised by several authors (Schoknecht et al., 2004, Schoknecht et al., 2005). However, most of these studies only report on results of experimental leaching tests, but do not investigate the chemical mechanisms involved.
As discussed in a recent paper (Tiruta–Barna and Schiopu, 2011), a leaching process implies complex chemical and physical phenomena: biocide interactions with the solid wood structure (fixation), distribution between the solid and liquid phase (mobilisation), and transport processes (mainly diffusion inside the wood porous system). The fixation mechanism of copper on the wood structure has been intensively studied (Jiang, 2000, Lee, 2011, Mettlemary, 2011). This is not the case for other compounds, especially organic biocides, for which the fixation mechanisms have not been elucidated so far. Irrespective of the biocides, very few reaction constants exist in literature allowing a quantitative estimation of the fixation level. Also the mobilisation mechanisms are hardly investigated. What is the role of the wood/water chemistry in terms of pH and extractives on the biocide leaching? No studies have been reported on the composition of the organic matrix in eluates, and no leaching mechanism that includes the role of these extractives has been proposed so far.
The intention of this study was to investigate the leaching behaviour of treated wood and to propose leaching mechanisms for inorganic and organic compounds. The product studied here is sapwood of Pinus sylvestris treated with copper–boron–azole (further called CBA), containing tebuconazole as organic biocide, and monoethanolamine as major constituent. Copper is an essential micronutrient for most living cells, but in larger doses it acts as an algicide, bactericide, fungicide, insecticide, and moldicide (Freeman and McIntyre, 2008); boron is used as insecticide and fungicide (Lebow, 1996); tebuconazole is a fungicide that is added to copper containing wood preservatives to act against copper-tolerant fungi (Grundlinger and Exner, 1990). These properties are hazardous when the biocides are controlees released in surrounding environment.
Experiments based on the leaching procedure of the European standard XP CEN/TS 14429 (‘pH dependence leaching test’ or ‘Acid Neutralisation Capacity test’ — further called ‘ANC’) (CEN, 2006) were performed to determine the acid/base properties of samples from untreated and treated wood and investigate the pH influence on the release of elements, ions and organic compounds. The ANC test is in line with the Construction Products Regulation (EC, 2011). In order to comply with the Basic Requirement BR 3 ‘Hygiene, health and the environment’ of the CPR, the European Commission mandated CEN/TC 351 to develop methods for the assessment of the leaching behaviour of various construction products (based on wood, concrete, etc.) with the same methods, i.e. horizontal approach (CEN, 2012). Other leaching procedures were developed specifically for wood products (e.g. CEN/TS 15119 (CEN, 2007)). Nevertheless, these specific methods are suitable for some regulatory purposes but not for chemical modelling. The method applied in our research was chosen because it is more suitable for a mechanistic model development (equilibrium conditions are reached at different pH values and therefore chemical mechanisms can be identified).
Section snippets
Properties of biocides in treated wood — a review
Wood is a heterogeneous, hygroscopic, cellular and anisotropic material. It is composed of cells, and the cell walls are composed of micro-fibrils of cellulose, hemicellulose, lignin, other minor polysaccharides and a small fraction of extractives (Rowell, 2005). Treatment of wood causes a series of reactions between wood components and constituents of the wood preservative, e.g. complexation, ion exchange, adsorption, hydrolysis.
Wood samples and treatment
Two types of P. sylvestris samples were used in the leaching tests: wood that was cut off 9 years ago (later called ‘conditioned’) and shavings collected from different trees in carpentry (‘fresh’). A description of the samples is given in Table 1.
A wood preservative consisting of copper carbonate (22.5%, i.e. 12.9% Cu), boric acid (4.9%, i.e. 0.65% B) and tebuconazole (0.53%) was used to treat both types of wood (‘conditioned’ and ‘fresh’). In addition, the preservative contained a mixture of
Results
ANC tests deliver two types of results: (i) amount of H+ moles added per L solution, as a function of final pH of the eluate and (ii) variation with pH of the concentration of target substances in the eluates. Such curves were obtained for both untreated and treated wood, ‘conditioned’ and ‘fresh’, as seen in Fig. 2. Concentrations obtained in mg/L were converted to mol/L.
The graph at top-left of Fig. 2 is a titration-like curve; it represents the pH of the system as a function of the acid or
Discussion
During the ANC test, samples from ‘conditioned’ wood respond more sensitively to the addition of NaOH than the ‘fresh’ shavings (Fig. 2), i.e. the buffering capacity is higher for ‘fresh’ than for ‘conditioned’ samples of P. sylvestris. The difference of about 3 pH units between the native pH of untreated and treated wood can be explained by modification of the reactivity of wood due to the preservative treatment. The pKa values of carboxyl groups of hemicellulose and lignin in wood range
Conclusions
Leaching from CBA treated wood was investigated with the aim to identify chemical mechanisms of fixation and mobilisation of biocides based on a pH dependency leaching test (ANC test) that has been already widely applied for waste and concrete construction materials. Despite the fact that it is an aggressive test (test conditions are unlikely to occur under service conditions), ANC results, in combination with a suitable set of analytical methods, provide manifold information about the studied
Acknowledgements
This study was partially carried out at the BAM Federal Institute for Materials Research and Testing in Berlin (Germany), with the financial support of Deutscher Akademischer Austausch Dienst (DAAD). Special acknowledgments to the members of the Divisions 4.1, 4.3 and 1.3 at BAM.
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