AN ABSTRACT OF THE THESIS OF Cheney L. Vidrine for the degree of Master of Science in Wood Science presented on June 19, 2008. Title: Copper Compounds for Durable Composites: Effects on Material Properties. Abstract approved: _____________________________________________________________________ Jeffery J. Morrell Frederick A. Kamke The effects of incorporation of selected biocides on physical and mechanical properties of aspen strandboard were assessed using five copper-based preservatives or zinc borate at three retention levels. Tebuconazole or 4,5-dichloro-2-N-octyl-4isothiazolin-3-one (DCOI) were added as co-biocides to selective copper-based treatments. Mold box tests showed that only panels treated with DCOI provided significant protection against mold growth, and DCOI with a copper-based preservative provided the best protection. Exposure to brown or white rot fungi in a laboratory soil block test showed that all preservatives except micronized copper hydroxide or DCOI alone reduced weight losses below 10 %. The other three copperbased preservatives performed well independently. The addition of DCOI or tebuconazole markedly improved mold resistance. No reductions in bending strength or stiffness were associated with biocide addition. Internal bond strengths in panels treated with the liquid copper-based preservative were significantly lower than the untreated controls. Preservative addition was associated with increased thickness swelling compared to the untreated controls, but this effect was slight. Some treated panels also experienced slight increases in the rate of linear expansion, but the values all were well below the maximum accepted thickness swelling value. Some preservatives were slightly prone to chemical leaching, but two copper-based biocides were highly resistant. The results indicate that the three copper-based preservative systems increased resistance to decay fungi without adversely affecting mechanical or physical properties. Further field studies to assess resistance to fungal and insect attack are underway. © Copyright by Cheney L. Vidrine June 19, 2008 All Rights Reserved Copper Compounds for Durable Composites: Effects on Material Properties by Cheney L. Vidrine A THESIS submitted to Oregon State University in partial fulfillment of the requirements for the degree of Master of Science Presented June 19, 2008 Commencement June 2009 Master of Science thesis of Cheney L. Vidrine presented on June 19, 2008. APPROVED: _____________________________________________________________________ Co-Major Professor, representing Wood Science _____________________________________________________________________ Co-Major Professor, representing Wood Science _____________________________________________________________________ Head of the Department of Wood Science and Engineering _____________________________________________________________________ Dean of the Graduate School I understand that my thesis will become part of the permanent collection of Oregon State University libraries. My signature below authorizes release of my thesis to any reader upon request. _____________________________________________________________________ Cheney L. Vidrine, Author ACKNOWLEDGEMENTS The author expresses sincere appreciation to the following people and organizations for their assistance towards the completion of this thesis. This work would never have been completed without the undying support of Dr. Jeffery J. Morrell throughout the entirety of the thesis process. Dr. Fredrick A. Kamke endowed the author with knowledge and training in the manufacturing of strand-composite panels. Camille Freitag provided time, patience and a wealth of knowledge for the author to complete the biological testing. Mental and mechanical support was kindly bestowed by Milo Clausen. Dr. Alan Preston, Dr. Lehong Jin and Christoph Schauwecker of Viance LLC (Charlotte, NC) provided materials, expertise and limitless support for the project. Connie Love provided expertise and assistance with a variety of tasks during the experimental phase of the work. In all stages of the project, Amanda J. Benton provided endless assistance, perspective and support. Louisiana-Pacific’s Newberry, MI siding plant kindly donated all of the aspen strands used in the study. Resin was provided by Georgia Pacific Chemicals LLC (Albany, OR). Wax was supplied by Hexion Specialty Chemicals Inc (Springfield, OR). Zinc borate was graciously donated by Rio Tinto Minerals (Edgewood, CO). The support of these organizations was vital to the completion of this work. The author would also like to thank Dr. Jeffery Stone and Dr. Claire Montgomery for their willingness to serve on my graduate committee. TABLE OF CONTENTS Page Chapter 1 -- Introduction................................................................................................ 1 Background ............................................................................................................ 1 Objectives............................................................................................................... 2 Chapter 2 – Literature Review ....................................................................................... 3 Use of Composites ................................................................................................. 3 Oriented Strandboard ............................................................................................. 4 Composite Durability ............................................................................................. 4 Mold of Composites............................................................................................... 5 Mold Growth .................................................................................................. 5 Health Issues .................................................................................................. 7 Fungal Decay of Composites ................................................................................. 8 Brown Rot Fungi ............................................................................................ 9 White Rot Fungi ............................................................................................. 9 Soft Rot Fungi .............................................................................................. 10 Building Practices That Encourage Decay........................................................... 10 Treatment Methods of Wood Composites ........................................................... 12 Naturally Durable Wood Substrates............................................................. 13 Recycled Treated Wood Substrates.............................................................. 14 Pre-Treatment of Wood Substrates .............................................................. 15 Post-Treatment of Wood Substrates............................................................. 16 In-Process Treating of Wood Substrates...................................................... 17 Preservatives for Treatment of Strand-Composite Panels ................................... 18 TABLE OF CONTENTS (continued) Page Copper-Based Preservatives......................................................................... 19 Chlorothalonil............................................................................................... 20 Didecyl Dimethyl Ammonium Chloride (DDAC)....................................... 21 Bifenthrin ..................................................................................................... 21 Isothiazolone ................................................................................................ 22 Triazoles ....................................................................................................... 22 Borates.......................................................................................................... 23 Acetylation ................................................................................................... 24 Isocyanates ................................................................................................... 25 Chapter 3 – The effects of novel copper-based preservative technologies on the resistance of aspen strandboards to biological degradation. ............................ 26 Abstract ................................................................................................................ 26 Introduction .......................................................................................................... 27 Materials and Methods ......................................................................................... 30 Panel Fabrication.......................................................................................... 30 Retention Analysis ....................................................................................... 33 Soil Block Test ............................................................................................. 34 Mold Box Test.............................................................................................. 35 Statistical Analysis ....................................................................................... 36 Results and Discussion......................................................................................... 36 Retention Analysis ....................................................................................... 36 Soil Block Test ............................................................................................. 38 Mold Box Test.............................................................................................. 43 TABLE OF CONTENTS (continued) Page Additional Research ............................................................................................. 47 Conclusions .......................................................................................................... 48 References ............................................................................................................ 49 Chapter 4 – The effects of novel copper-based preservative technologies on the mechanical and physical properties of aspen strandboard. .............................. 53 Abstract ................................................................................................................ 53 Introduction .......................................................................................................... 53 Materials and Methods ......................................................................................... 56 Panel Fabrication.......................................................................................... 56 Static Bending .............................................................................................. 59 Internal Bond Strength ................................................................................. 59 Permanent Thickness Swell ......................................................................... 60 Hygroscopicity ............................................................................................. 60 Resistance to Leaching................................................................................. 61 Statistical Analysis ....................................................................................... 62 Results and Discussion......................................................................................... 62 Static Bending .............................................................................................. 62 Internal Bond Strength ................................................................................. 65 Permanent Thickness Swelling .................................................................... 67 Hygroscopicity ............................................................................................. 75 Resistance to Leaching................................................................................. 79 Conclusions .......................................................................................................... 80 References ............................................................................................................ 81 TABLE OF CONTENTS (continued) Page Chapter 5 – General Conclusions................................................................................. 84 Bibliography................................................................................................................. 86 Appendices................................................................................................................... 96 Appendix A – Statistical Output .......................................................................... 96 LIST OF FIGURES Figure Page 1. Cutting pattern used to produce test specimens ....................................................... 33 2. Weight losses of strandboard blocks subjected to various treatments and exposed to Gloeophyllum trabeum in a soil block test................................................................... 40 3. Weight losses of strandboard blocks subjected to various treatments and exposed to Postia placenta in a soil block test............................................................................... 41 4. Weight losses of strandboard blocks subjected to various treatments and exposed to Trametes versicolor in a soil block test ....................................................................... 42 5. Surface mold growth on CC1 or CC2 and tebuconazole treated strandboard in an AWPA E24 mold box test............................................................................................ 45 6. Surface mold growth on strandboards treated with DCOI alone or as a co-biocide with two copper complexes.......................................................................................... 46 7. Cutting pattern used to produce test specimens ....................................................... 58 8. Determination of specific gravity............................................................................. 59 9. Modulus of elasticity of treated and untreated strandboards ................................... 65 10. Internal bond strength of treated and untreated strandboards ................................ 66 11. Thickness swelling of treated and untreated strandboards after 2 hours of water submersion ................................................................................................................... 69 12. Thickness swelling of treated and untreated strandboards after 24 hours of water submersion ................................................................................................................... 70 13. Moisture contents of untreated and treated strandboards after 2 hours submersion ...................................................................................................................................... 73 14. Moisture contents of untreated and treated strandboards after 24 hours submersion ...................................................................................................................................... 74 15. Moisture contents of treated and untreated strandboards conditioned at 30°C and 30% RH conditioning room environments .................................................................. 77 16. Moisture contents of treated and untreated strandboards conditioned at 30°C and 90% RH conditioning room environments .................................................................. 78 LIST OF FIGURES (Continued) Figure Page 17. Linear expansion with change in moisture content of treated and untreated strandboards conditioned at 30°C and 30% RH, then 30°C and 90% RH................... 79 LIST OF TABLES Table Page 1. Preservative treatments assessed.............................................................................. 31 2. Visual scale to rate the extent of mold growth......................................................... 35 3. Chemical retentions of aspen strandboards treated with various preservatives...... 37 4. Wood weight losses of aspen strandboard blocks subjected to various treatments and exposed to decay fungi in a soil block test............................................................ 39 5. Effects of various treatments on mold resistance of strandboards in an AWPA E24 mold box test. ............................................................................................................... 44 6. Preservative treatments assessed.............................................................................. 57 7. Effects of the addition of preservatives on mechanical properties of strandboards. 63 8. Thickness swelling of treated and untreated strandboards after 2 or 24 hours of submersion ................................................................................................................... 68 9. Moisture contents of treated and untreated strandboards submerged in water for 0, 2 or 24 hours ................................................................................................................... 72 10. Moisture contents and linear changes in treated and untreated strandboards conditioned under two different temperature/relative humidity regimes..................... 76 11. Resistance of treated strandboards to chemical leaching after 14 days in an AWPA E10 leaching test .......................................................................................................... 80 CHAPTER 1 -- INTRODUCTION Background Wood is the primary building material used in North America. Concerns regarding excessive harvesting of old- and second-growth forests have led to an increased use of wood-based composites that utilize small diameter logs and processing waste that would otherwise be discarded. Oriented strandboard (OSB) is composed of various sized strands that have been oriented in a specific direction and pressed to a desired thickness and density. The small size of the strands allows the use of small, inexpensive logs that reduce panel cost compared to plywood. Although OSB can tolerate brief periods of wetting during construction, it is designed to be a dry-use product. Wood products are susceptible to mold, decay or insect attack when exposed to high moisture environments for prolonged periods. Due to the geometry of the product and the species composition, OSB is generally considered to be more susceptible to decay than softwood plywood. In response to rising energy costs, a number of building practices have been implemented to seal homes in order to limit the escape of warm or cold air. These practices reduce the interior/exterior air exchange and can trap moisture from both interior and exterior sources. The accumulation of moisture within wall cavities can lead to mold and decay. The continued use of wood-based composites in moisture-prone applications is adding to the growing perception that wood is a non-durable material. Increasing the ability of wood-based building materials to tolerate short term wetting would yield 1 2 more durable buildings, and the production of decay-resistant wood composite panels is one possible solution. Objectives The objectives of this project were: • • • Determine the effectiveness of various copper-based preservative technologies incorporated into the furnish of strandboard Evaluate the efficacy of two organic biocides in combination with these copper-based preservatives Determine the effects of incorporating various copper-based preservatives on physical and mechanical properties of strandboard panels 3 CHAPTER 2 – LITERATURE REVIEW Use of Composites Merriam-Webster (1993) defines a composite as “a solid material which is composed of two or more substrates having different physical characteristics and in which each substrate retains its identity while contributing desirable properties to the whole.” A wood-composite is a manufactured solid material in which solid wood, strands, veneers or fibers are permanently connected to each other or another material by means of mechanical fasteners and/or adhesives. The goal is to combine desirable characteristics of each component to create a new material with characteristics that are superior to the original substrates in terms of mechanical properties, homogeneity, dimensions, durability, price or aesthetic values. Many composites also distribute defects inherent to the material, such as knots, more evenly, thereby producing materials with much better performance predictability. This homogeneity can also have the added benefit of reducing the tendency to shrink, warp and bow (Laks & Palardy, 1990a). Composites can also be used to optimize material utilization. For example, higher quality material can be used where higher stress concentrations are likely to occur, while lower quality material can be used in neutral axes. Wood-based composites are also able to use small substrates, eliminating the requirement for large timbers. This allows for the utilization of small diameter logs and processing waste (i.e. trimmings, chips and fines), which helps to increase the efficiency of material use and reduces the need for tree harvesting. There is a multitude of commercially available composite materials, each with its own attributes. 4 Oriented Strandboard Composite panels are used in both structural and non-structural applications, and are composed of veneers, strands, fiber or particles. Plywood and oriented strandboard (OSB) are currently the two most widely used materials for structural applications. Plywood consists of laminated veneers, while OSB is composed of various sized strands that have been oriented in a specific direction, combined with resin and pressed to a desired thickness and density. Plywood was the only structural wood panel available until the advent of OSB in the late 1970’s. OSB products surpassed North American plywood production in 2000 (SBA, 2008). The main advantage of OSB over softwood plywood is cost. Because of the small size of the strands that make up OSB, expensive “peeler” logs used to manufacture plywood are unnecessary, and smaller, lower quality species of wood, such as aspen (Populus tremuloides), can be employed. The lower cost of the material in OSB greatly reduces the final cost per panel compared to plywood. The resource impact of OSB is also lower than that of plywood because it alleviates pressure to use large logs from slow-growing species, such as Douglas-fir (Pseudotsuga menziesii) (Laks & Palardy, 1990a). Composite Durability Although wood and wood-based composite sheathing panels can tolerate brief periods of wetting during construction, they are designed to remain dry while in service. Exposing these products to high relative humidities or liquid water for 5 prolonged periods sharply increases the chances of mold, stain or decay (Fogel & Lloyd, 2002; Morris et al., 1999). Softwood plywood panels tend to be more resistant to decay and mold attack than OSB (Laks, 1999; Laks et al., 2002). Even though OSB and strand-composite products are made from decay susceptible species, they are increasingly being used in applications that subject them to conditions suitable for insect and fungal attack (Jeihooni et al., 1993; Morrell, 2002; Morris, 1995; Morris et al., 1999). The higher susceptibility of OSB to decay reflects both the geometry of the product and the species composition. OSB is composed of small strands that have been pressed together. This process results in numerous void spaces that act as pathways for moisture and organisms to enter the panel. The increased water accessibility results in more rapid swelling of individual strands, which opens gaps that allow better access for the fungi (Anderson, 1972; Chung et al., 1999). The higher nitrogen content of aspen also favors stain and mold fungi, and these organisms can increase wood permeability and lead to a tendency for OSB to sorb even more water (Morris et al., 1999). The lower intrinsic decay resistance of poplar compared to softwood species also reflects the lower lignin content (Laks, 2002). Mold of Composites Mold Growth Mold and decay fungi require an ample supply of oxygen, adequate temperature range, liquid water and the availability of nutrients for growth. Because 6 these conditions are almost exactly the same as those necessary for human existence, it is not surprising that fungi are common in wood framed housing. Molds are fungi whose visible damage is largely confined to the surface of a substrate, although they grow more deeply into the material. Mold occurs primarily in the sapwood, where low molecular weight carbohydrates, proteins, lipids and other compounds stored in xylem parenchyma cells are readily available (Laks, 2002). Discoloration of the wood is due to the development of pigmented spores on the surface, although shallow discoloration may also occur within the wood (Scheffer & Cowling, 1966). The hyphae of mold fungi grow though the pits in the wood cells and this damage renders the wood more permeable. The more permeable wood wets faster and may therefore be more susceptible to fungal decay. Of the approximately 250,000 species of fungi, only a small percentage are classified as mold fungi, and all molds are members of the Ascomycota. Unfinished aspen OSB often develops a dark discoloration due to the fungus Alternaria when used in exterior applications, athough other common molds such as Epicoccum, Aureobasidium, Penicillium, Paecilomyces, Trichoderma, and Diplodia are often isolated from moldy panels (Schmidt, 1993). Although humid air does not have enough water vapor to wet wood adequately to support the growth of decay fungi, some researchers have found it to be adequate for mold growth (Clausen & Yang, 2007). Others suggest that condensation of water onto wood surfaces, not high relative humidity (RH), is necessary for mold growth (Morrell, 2002). The amount of available water, which is usually expressed as water activity or as RH, is the most important factor for growth (Nielsen et al., 2004). Wang 7 (1993) found that RH also plays an important role in the rate of mold growth. Growth is most rapid at temperatures between 15-25ºC when RH exceeds 90%. Health Issues A major concern regarding the growth of mold in homes and office buildings is the fear that spores produced by these fungi induce sinus and respiratory problems. A number of molds commonly found in buildings produce mycotoxins that may lead to adverse health effects in some individuals (Nielsen et al., 2004). The majority of the molds found in buildings are species of Cladosporium, Penicillium, Alternaria, Fusarium, Trichoderma,and Stachybotrys. All of these genera contain species capable of producing of mycotoxins (Clausen & Yang, 2004). Members of the genera Cladosporium, Penicillium, and Alternaria can cause chronic sinus infections, respiratory infections and induce asthma attacks (Fogel & Lloyd, 2002). Aspergillus, another common mold genus, contains two species considered to be pathogenic to humans (Clausen & Yang, 2004). In the 1990’s, outbreaks of pulmonary humosiderosis (bleeding lung disease) killed approximately 70 children. The outbreaks were, at first, linked to the toxic mold Stachybotrys atra, and were attributed to have resulted from inadequate home ventilation and humidity controls (Jacobs et al., 1999). The initial concerns regarding the exposure to mycotoxins such as those produced by Stachybotrys have not held up to scientific scrutiny, although some sensitive individuals may be prone to asthmatic attacks due to mold exposure (CDC, 2000; IOM, 2004). Despite these findings, mold is no longer an acceptable blemish on 8 most consumer-related wood products and there is a continuing need for methods to produce mold resistant materials. Fungal Decay of Composites Wood decay fungi are specialized heterotrophic fungi, usually basidiomycetes along with some ascomycetes, which obtain most of their nutrients from the decomposition of wood holocellulose. Some of these fungi also have the ability to utilize lignin. The requirements for growth of decay fungi are the same as those for molds. Most decay fungi prefer temperatures between 15 and 45ºC. Although atmospheric oxygen is required for growth, most wood-inhabiting fungi will prosper at relatively low oxygen levels. Energy and metabolites are obtained from wood cell wall components. An ample amount of water is also required for the decay process. Water acts as a reactant for cell wall hydrolysis, a diffusion medium for degradative enzymes and solublized wood components, a medium for important life systems and as a swelling agent of the wood substrate (Zabel & Morrell, 1992). Most fungi that degrade wood require a wood moisture content (MC) above the fiber saturation point (FSP). The FSP is the level at which no more water can be bound to the cell wall, and any additional water accumulates as liquid and vapor within the lumen. The FSP for most wood species is between 27 and 30% MC. Although MCs above the FSP are required for initial growth, fungi can continue to grow at MCs as low as 20% once the wood substrate has been colonized (Morrell, 2002). Decay fungi can be separated into three distinct decay types based upon their mechanisms of decay and the different cell wall constituents they degrade. Brown and 9 soft rot fungi tend to preferentially degrade the carbohydrate fraction, while white rot fungi can degrade all three components. Although brown rots and whites rots can be found concurrently on all wood species, brown rots preferentially decay softwoods while white rots prefer hardwoods (Schmidt, 1993). Brown Rot Fungi Brown rot fungi preferentially attack the carbohydrate portion of the cell wall. The brown residue left after degradation, hence the name “brown rot,” consists of partially demethylated lignin. These fungi rapidly and severely depolymerize the crystalline cellulose in the early stages of attack at relatively low weight losses. Brown-rot degradation of cellulose appears to involve two mechanisms, oxidation and hydrolysis, that might be either sequential or concurrent. These reactions appear to be intertwined, with oxidation most likely accomplished by a non-enzymatic mechanism, and hydrolysis catalyzed by a complex of enzymes (Highley et al., 1994). White Rot Fungi White rots degrade all components of the cell wall. The whitened appearance of white-rotted wood is due to the removal of the brown colored lignin and oxidative bleaching reactions that occur during the decay process. Initially, some white rot fungi preferentially degrade the lignin portion of the cell wall. Because these fungi require carbohydrates as an energy source, which lignin cannot provide, the cellulose and hemicellulose portions of the cell wall are simultaneously degraded, but at a slower rate. The breakdown of lignin primarily occurs through a series of exzymatic 10 oxidative reactions. As with brown rot fungi, hemicellulose and cellulose are first disrupted by oxidative reactions that make the substrates more accessible to enzymatic degradation. Hydrolysis is accomplished by enzymes that break cellulose and hemicellulose into glucose and other simple sugars that can be absorbed and metabolized by the fungi (Eaton & Hale, 1993; Zabel & Morrell, 1992). Soft Rot Fungi The term soft rot is used to describe ascomycetes that attack the outer surface of wood in relatively wet environments. There are two distinct methods by which soft rot fungi attack wood cell walls. Cavity formation, or Type I, is characterized by the degradation of the S2 layer within the cell wall. Cellulases and phenol oxidase enzymes degrade cellulose and lignin, respectively, and are secreted from fine microhyphae growing parallel to the wood cell microfibrils. This decay mechanism creates diamond-shaped cavities that continue in stepwise start-stop chains that are unique to soft-rotted wood. Type II soft rot is described as a general erosion of wood cell walls, beginning from the S3-lumen interface and attacking outward. Type I and Type II soft rot can occur independently, within the same piece of wood or by the same fungus within the same piece of wood (Goodell et al., 2008). Because soft rot fungi are usually found to degrade wood products in wet environments, like telephone poles or fence posts, they are generally not considered a threat to wood composite panels. Building Practices That Encourage Decay 11 Rising energy costs in North America have encouraged an array of building practices designed to conserve energy by sealing homes to limit the escape of warm or cold air. Unfortunately, reducing the interior/exterior air exchange can also trap moisture from many interior sources within the building. (Anderson, 1972; Barnes & Amburgey, 1993; Cassens, 1978; Laks, 1999; Laks et al., 2002; Merrill & TenWolde, 1989; Morrell, 2002; Schmidt, 1993). One of the most common and problematic of these practices is to wrap buildings with a weather-resistant barrier. These plastic-like membranes are wrapped over the sheathing and under the exterior siding to prevent the intrusion of air and moisture. Although building wraps accomplish this task, they also prevent the escape of moisture generated from within the building. The accumulation of moisture within wall cavities can lead to mold and decay (Barnes & Amburgey, 1993; Schmidt, 1993; Yang et al., 2007). The more efficiently new buildings reduce heat transfer, the greater the potential for moisture condensation to occur (Anderson, 1972; Merrill & TenWolde, 1989). In cold climates, condensation occurs when the colder outside wall surface cools the warm, moist indoor air as it contacts the inside wall surface. Excess condensation within wall cavities, though not clearly linked to wood decay (Burch et al., 1979; Burch & Treado, 1978; Sherwood, 1983; Tsongas, 1980, 1986), can provide in ideal environment for mold growth (Fogel & Lloyd, 2002; Morrell, 2002). The opposite effect occurs in air-conditioned houses in warm climates when moist air on the outside condenses on colder, air-conditioned interior surfaces. 12 Concerns about the cost of building materials also led to architectural design changes in many wood structures that inadvertently promoted the possibility of exterior moisture intrusion. Decreases in the size of roof overhangs reduced material costs, but also increased the probability that wetting of siding will occur (Scheffer & Moses, 1993). Inadequate site drainage, water leaks, poor insulation, relatively flat roof pitches, improper ventilation, and indoor pluming all contribute to increased indoor moisture accumulation (Barnes & Amburgey, 1993; Clausen & Yang, 2004; Morrell, 2002; Morris, 1997). Poor execution of building features compounds the issues associated with new design features and energy efficient sealed homes (Laks, 1999; Morrell, 2002). All of these factors, coupled with the increased use of less durable sheathing and an increasingly litigious society, have resulted in a substantial rise in moisture-related building issues. Treatment Methods of Wood Composites The continued use of wood-based composites in moisture-prone applications is adding to the growing perception that wood is a non-durable material. Increasing the ability of wood building materials to tolerate short term wetting would yield more durable buildings, and the use of decay resistant wood composite panels is one possible solution (Yang et al., 2007). Contemporary composites must be both effective and environmentally acceptable. Murphy et al. (1993) summarized the criteria for an acceptable preservative treatment process for wood composites: 13 • • • • • • • Efficacy – The preservative should be effective against decay fungi and wood degrading insects. Environment – The treatment operation and product should have acceptable environmental characteristics. Mechanical properties – The treatment should have no negative impacts on mechanical properties. Physical properties – Interference with physical properties, such as EMC and dimensional stability, should be minimal. Appearance – Unless it is desired for identification purposes, the treatment should not change the appearance of the wood. Speed and Flexibility – The treatment process should be as rapid as possible and be able to produce as much product to meet orders in short notice. Verification and compliance with standards – The treated material should be easily analyzed for quality control. Other considerations when designing a preservative treatment are the product life cycle, compatibility and adaptability with current processes, resin and additive systems, stability and consistency of the preservative, and product durability and characteristics (Ross et al., 2003; Wu, 2004). Theoretically, achieving uniform biocide distribution in wood-based composites should be easier to attain than in solid wood products (Barnes & Amburgey, 1993). Durable wood composites can be produced through the use of wood species with high natural durability, incorporating recycled treated wood, pre-process preservative treatments of the wood, post-process preservative treatments and in-process preservative treatments (Gardner et al., 2003). Treatment methods are dependent upon the final product. Naturally Durable Wood Substrates The use of naturally durable wood species as the primary strand type produces a synthetic chemical-free, decay resistant wood composite panel, and this approach 14 has been commercialized to a limited extent (Gardner et al., 2003). The heartwood of certain tree species contains fungal and insect resistant extractives (Hawley et al., 1924). The heartwood of naturally durable species like western redcedar could be used as furnish for particleboard, OSB and other composite panels (Yang et al., 2007). Important issues, such as availability of raw materials, effects of extractives on bonding, variable heartwood decay resistance and possible effects of heat on durability must be addressed (Gardner et al., 2003). Recycled Treated Wood Substrates One other method for fabricating durable strand composite panels is to use recycled treated wood as the raw material. Chromated copper arsenate (CCA) was the most widely used preservative treatment of wood for residential applications from the 1970’s until 2004. Large volumes of CCA treated lumber will continue to come out of service over the next few decades. Instead of disposing of this material in landfills, where it may take decades or more to degrade, it may be possible to turn this wood into strands that can be used as OSB furnish (Gardner et al., 2003; Laks & Palardy, 1993; Li et al., 2004; Mengeloglu & Gardner, 2000; Zhang et al., 1997). There are a number of issues that must be addressed before commercialization of this process. Bonding problems can arise due to the presence of insoluble metal deposits that inhibit adhesion between the wood and the resin (Gardner et al., 2003; Vick et al., 1996). Worker safety and environmental problems may also arise due to the potential for arsenic releases during processing of composite panels made from treated wood (Smith & Shiau, 1998). Furthermore, a large portion of CCA treated members only 15 contain a shell of protection surrounding an untreated core. As a result, furnish prepared from such material would contain mixtures of heavily treated, lightly treated and untreated particles. This variability makes it difficult to ensure that a targeted amount of preservative is present in the resulting composite panel (Laks & Palardy, 1993). Pre-Treatment of Wood Substrates It is also possible to produce wood composite products using wood substrates that have been treated prior to pressing (Gardner et al., 2003; Morrell, 2002). Strands, veneers or solid wood members can be treated by dipping, soaking or spraying chemical onto the materials. The wood is then dried and processed into a finished panel. This approach can be used with any type of wood composite, although it has some issues. As with recycled treated wood for wood composites, bonding of treated wood can pose a challenge. Pre-treating the substrate also requires an extra drying step, which is energy intensive and less efficient. Finally, any chemicals used must be safe to handle, create no hazardous waste and not negatively affect final panel properties. An alternative to chemical treatments is the pre-treatment of strands using various heating processes that alter the wood chemistry to reduce moisture uptake and, potentially, fungal attack. The effects of heat treatment on solid wood properties are well understood (Seborg et al., 1953; Stamm, 1956; Tjeerdsma et al., 1998), and the process can reduce fungal decay in low moisture environments. Heat pre-treatment of strands does not appear to be effective against mold or brown-rot fungi (Kartal, 2007). 16 Heat treatment of strands also dramatically reduces the mechanical properties of the resulting OSB (Paul et al., 2006). For these reasons, heat treatment appears to be unacceptable for protecting wood-based composite panels from decay. Post-Treatment of Wood Substrates Some wood composites can be treated after production using conventional treatment methods (Gardner et al., 2003; Laks & Palardy, 1990a; Morrell, 2002; Wu, 2004) such as spraying, immersion or pressure treatment. The envelope of protection created by the spray and immersion treatments are designed to provide short term resistance to decay, mold and water intrusion during transportation and building construction (Ross et al., 2003; Wu, 2004). The advantages of these treatments include low cost and relative ease of application. Pressure treatment of wood composites is generally limited to glued laminated wood (glue-lams), laminated veneer lumber (LVL) and plywood. Pressure treatment of glue-lams often only provides an envelope of protection which can be breached if the post-treated product is cut, notched or drilled (Gardner et al., 2003). Other wood composites, including strand or fiber composites, often experience unacceptable, permanent deformation during pressure treatment with water-based preservatives (Laks, 1999; Morrell, 2002). Deformation results in permanent thickness swelling, strength reduction and an increase in surface roughness of the panel (Wu, 2004). As a result, pressure treating is not considered to be a suitable method for protecting many of these wood-based composites. The vapor boron process, whereby trimethylborate diffuses into pressed panels under a vacuum and reacts with water to produce boronic acid and methanol, could be 17 a non-swelling method of post-process treating durable panels (Morrell, 2002). Methanol can be recovered at the end of the process and used to produce new trimethylborate. The treatment does not interfere with the adhesive when used in composite panels, and has only slight negative effects on mechanical properties. Because the treatment is applied to the final product, there are no issues related to the disposal of treated off-cuts (Murphy & Dickinson, 1997; Murphy et al., 1993; Murphy & Turner, 1989). The limiting factors with this process are the treatment cost, the difficulty recovering the methanol within the wood and the inability of boric acid to fix to wood. As a result, vapor boron is only suitable to environments not subjected to wetting and would not be ideal for most durable wood composite panels. Supercritical fluids may also be used as carriers for impregnating biocides into composites (Morrell, 2002). Supercritical fluids are solvents that diffuse through wood like gasses but can have solvating properties like liquids (Gardner et al., 2003). Supercritical fluids have been found to have no negative impacts on mechanical properties of various wood-based composites, and the process results in excellent preservative distribution (Acda et al., 1996). The biggest disadvantage of commercializing supercritical fluid treatment is the high capital cost of the highpressure treatment facility. In-Process Treating of Wood Substrates One of the more effective methods for treating strand and fiber composites is to incorporate the biocide into the furnish prior to pressing. Uniform distribution of the preservative within the product can provide much better protection than “shell” 18 treatment (Laks & Palardy, 1992). Finished products can also can be machined at any point without losing resistance to biological attack because the entire panel is uniformly treated (Gardner et al., 2003; Laks & Palardy, 1993). Factors that affect the suitability of a preservative for in process treatments include preservative thermal stability, the diffusivity of the chemical during consolidation, the presence of emulsifiers in the preservative formulation, preservative availability in powder or liquid form, adhesive interactions and wood species (Laks & Palardy, 1992). Five attributes of an ideal in-process treatment system include (Laks & Palardy, 1993): • • • • • Preservative remains stable during pressing No interference of the preservative with adhesive bond formation Biocide relatively immobile within the product during service Strength properties of the panel not negatively affected by the preservative Limited volatility of the biocide, especially during processing There are a number of methods for applying preservative to OSB. An additional sprayhead or blender system may be used to treat the strands before or after drying. Chemical can also be mixed with the adhesive or wax before application to strands in the blender, liquid preservative can be sprayed onto the strands, or a powdered chemical can be mixed into the blender. Powdered preservatives can also be metered onto dried strands just before they are placed in the blender, where the powder would be mixed with the strands (Laks & Palardy, 1990b). Of all these methods, preservative addition to the adhesive or wax is probably the most convenient for the manufacturer (Laks & Palardy, 1992). Preservatives for Treatment of Strand-Composite Panels 19 There are a number of preservatives that may be suitable for composite panels. Each has advantages and disadvantages in terms of cost, safety, ease of handling and efficacy. Copper-Based Preservatives Waterborne copper-based preservatives, such as chromated copper arsenate (CCA) have long dominated the treated sawn dimensional lumber and plywood markets. Since the 2004 withdrawal of CCA from residential building applications, new generation, arsenic free, copper-based preservatives have been used to treat both lumber and plywood. These preservatives have been shown to protect waferboards against fugal attack, but the added steps of dip-treating and drying the strands prior to blending make manufacturing uneconomical (Boggio & Gertjejansen, 1982). These chemicals also affect bonding and reduce mechanical properties of the panels (Goroyias & Hale, 2000; Hall et al., 1982). Other copper preservatives, such as copper naphthenate, ammoniacal copper complexes or copper carbonate in powdered forms have shown good efficacy when included in wood composite panels (Kirkpatrick & Barnes, 2006b). Kirkpatrick and Barnes (2006a) continued research by Schmidt (1991) and found that powdered copper naphthenate could be added to the furnish of aspen strandboards without significant negative effects on mechanical and physical properties. Copper ammonium carbonate (CAC) was found to be effective and was used as an pre-process preservative for OSB produced by Potlatch Corporation (Preston et al., 2003). The added steps during strand pre-treatment before blending made the CAC treatment 20 uneconomical. Goroyias and Hale (2000) added a copper carbonate hydroxidebased preservative, with boric acid, tebuconazole, and an aliphatic amine derivative as co-biocides, at various points during the manufacturing of strandboard. They found that the preservative reduced mechanical properties when sprayed in-line with resin application and pressed at 210°C. Copper based biocides appear to have a strong potential as wood composite panel preservatives if formulation and application methods can be optimized. Preferably, a powdered copper complex would be added to the strands prior to resin application and pressed using a standard press schedule. Chlorothalonil Chlorothalonil has been used as a mildewcide in paint and as a fungicide and termiticide in agricultural and industrial applications. Chlorothalonil is often combined with methylene bis-thiocyanate in the anti-sapstain market (Freeman, 2008). The chemical is also an effective preservative in solid wood (Woods & Klaver, 1992; Woods et al., 1995). However, Laks et al. (1992) found that chlorothalonil produced very little reduction in weight losses of solid wood by brown or white rot, even at high loadings. Micales-Glaeser (2004) found only moderate effectiveness against mold on pine and aspen blocks, while Laks et al. (1992) determined that high loading levels or in combination with other biocides gave effective protection to lumber products. This molecule is exceptionally difficult to solubilize, and some of the poor performance observed in previous tests may reflect formulation issues. 21 Didecyl Dimethyl Ammonium Chloride (DDAC) Didecyl dimethyl ammonium chloride (DDAC) is a quaternary ammonium compound that is broadly effective against fungi, colorless, has low toxicity to nontarget organisms, has limited volatility and dissolves easily in organic and aqueous solvents. DDAC has been found to effectively prevent decay in laboratory tests, but has produced variable protection in above ground field tests (Yu & Ruddick, 1995). It is the most common quaternary ammonium compound used as a co-biocide in ammoniacal copper quat (ACQ), and is also commonly used with 3-iodo-2-propynyl butyl carbamate (IPBC) as an anti-sapstain preservative. Solid wood treated with DDAC alone provides very little protection against mold fungi, but greatly reduces mold growth when combined with chlorothalonil (Micales-Glaeser et al., 2004). Although DDAC does not interfere with bonding properties when used with phenol formaldehyde adhesives (Vick et al., 1990), the chemical has a tendency to leach inservice (Nicholas et al., 1991; Ruddick & Sam, 1982), which is probably reflected in the poor decay resistance results. The low efficacy against mold fungi and the tendency to leach in-service makes DDAC a poor candidate for a composite panel preservative. Bifenthrin Bifenthrin is a low-toxicity insecticide that has proven to be very effective against termites at low loadings. It is chemically stable, compatible with fungicides, has a high vapor pressure and is soluble in a range of solvents (Rustenburg, 1995; Shires et al., 1996). Norton and Stephens (2007) showed that this insecticide could be 22 successfully added into multiple adhesive systems for use in composite panels. Although widely used in Australia as an effective preservative when combined with a supplemental fungicide, this chemical is not currently used for wood treatment in the US. Bifenthrin has the potential to be a co-biocide for insect protection of wood-based composite panels. Isothiazolone Isothiazolone (DCOI) is a broad-spectrum fungicidal preservative that is effective at low levels against decay fungi in both laboratory and field tests (Leightley & Nicholas, 1990; Nicholas et al., 1984). Williams and Lewis (1989) found that DCOI reduced mold growth on Scots pine (Pinus sylvestris) lumber. Wood pressuretreated with isothiazolone produced no harmful combustion products when burned, which indicates that isothiazolone treated wood can be safely incinerated for disposal (Yu, 1997). Isothiazolone is a water insoluble preservative that is delivered into wood using an oil-in-water micro-emulsion that results in a uniform distribution of nanometer-sized droplets that provide consistent treatment throughout the wood product (Yu & Leightley, 1992). These formulations exhibit minimum leaching losses while providing good anti-fungal efficacy (Hegarty et al., 1997). These favorable attributes make isothiazolone a potential candidate for composite panel protection. Triazoles Triazoles are a class of compounds that contain a five-membered ring of two carbon atoms and three nitrogen atoms. Azole-based fungicides are widely used in a 23 range of agricultural and pharmaceutical applications. These biocides inhibit fungal ergosterol biosynthesis, and their highly specific mechanism of action gives them low mammalian toxicity. Azaconazole provided good protection against fungal decay, was leach resistant and did not affect mechanical properties of waferboard when added as a dry powder to the furnish with PF resin (Schmidt & Gertjejansen, 1988). Jeihooni et al (1994) found that azaconazole did not affect panel properties and still provided protection against a brown rot fungus. Aspen OSB treated with tebuconazole using supercritical carbon dioxide was less resistant to decay in an above ground field test than similarly treated plywood (Morrell et al., 2005). While there is little data on the efficacy of triazoles in composites, there is a wealth of data on solid wood. Clausen and Yang (2003; 2005; 2007) found that thiabendazole and voriconazole completely inhibited mold growth of dip-treated southern pine. Tolley et al. (1998) found that tebuconazole and propiconazole provided moderate protection against mold, but protection was improved when the chemicals were combined. In other tests, tebuconazole treated wood experienced weight losses below 10% when exposed to brown or white rot fungi (Laks & Palardy, 1992). The combination of very low mammalian toxicity, little effect on wood composite properties and excellent decay resistance makes tebuconazole a candidate for further research in composite panels. Borates Borates have a number of appealing benefits as wood preservatives, including good efficacy against fungi and insects, fire retardancy, ease of application into the board furnish, low cost, low mammalian toxicity and low environmental impact. 24 Borates do not have a significant vapor pressure and will not degrade under press conditions (Laks & Palardy, 1990b). However, borates have a few disadvantages that limit them as an ideal wood composite panel preservative. Biologically-effective treatment levels of sodium borate and boric acid react with phenol formaldehyde (PF) resin to prevent good adhesion between wood substrates, resulting in boards with unacceptably low mechanical properties. It is believed that the resin cures prior to strand consolidation due to the reaction of boron ions with the functional methylol groups on the resin molecules (Lee et al., 2001). The interference problem can be reduced by using pMDI resin instead of PF resin, but this has other negative effects including higher panel production costs (Laks et al., 1988; Laks & Palardy, 1993). A number of borate treatments, including disodium octaborate tetrahydrate (DOT) and anyhydrous borax, are extremely water-soluble and their propensity to leach in-service makes them unsuited to exterior exposures (Gardner et al., 2003). As an alternative, zinc borate (ZB) is a relatively waterinsoluble alternative that is currently used in exterior applications with low to moderate leaching hazards (Laks, 1999; Manning & Laks, 1996). This chemical has sufficient solubility to produce protective boron levels in water within the wood cell, but is not so soluble that it will completely migrate from the wood. In addition, ZB has less interaction with resin and does not adversely affect bonding like other borates. Acetylation Chemicals such as acetic anhydride can react with hydroxyls in the wood to limit moisture uptake and thereby increase the dimensional stability of wood and limit 25 wood decay (Rowell et al., 1997). Phenolic or isocyanates resins can be used to acetylate OSB strands prior to blending. Gardner et al. (2003) and Okino et al. (2004) found a reduction in mechanical properties due to reduced penetration of the adhesive into the modified cell wall. Kumar and Morrell (1993), on the other hand, found that the use of thioacetic acid instead of the more common acetic anhydride produced increases in internal bond strength, maximum bending load and tensile strength. Weight gains of the acetylating agent must be upwards of 17% to provide sufficient biological protection. This unavoidably high weight gain, coupled with bonding issues due to reduced adhesive penetration, make acetylation a poor candidate for a treatment of price-sensitive commodity composite panels like OSB. Isocyanates Chemical modification of strands using an isocyanate polymer system prior to blending can improve resistance to biological attack and the dimensional properties of OSB. The modifying agent reacts with cell wall hydroxyl groups to form crosslinkages that reduce hygroscopicity. Wood modification is attractive because there are no residual toxic materials in the wood. The major drawbacks that eliminate isocyanates as an acceptable preservative for wood composite panels are associated with the large uptakes required to produce protection and the cost of treatment (Wu, 2004). 26 CHAPTER 3 – THE EFFECTS OF NOVEL COPPER-BASED PRESERVATIVE TECHNOLOGIES ON THE RESISTANCE OF ASPEN STRANDBOARDS TO BIOLOGICAL DEGRADATION. Abstract Mold and decay resistance of aspen strandboards treated with various copperbased preservative systems were evaluated in laboratory tests. Five copper-based chemicals or zinc borate were blended into the furnish at three retention levels. Tebuconazole or 4,5-dichloro-2-N-octyl-4-isothiazolin-3-one (DCOI) were added as co-biocides to selective copper-based treatments. All retention levels were well below targets. Panels were inoculated with four common molds and subjected to high temperature and humidity for eight weeks, according to AWPA Standard E24. Most panels experienced extensive mold growth, but panels treated with DCOI had marked resistance to attack. The two combinations of copper-based preservatives and DCOI also performed well. Panels were also assessed for decay resistance in a laboratory soil block test against the brown rot fungi Gloeophyllum trabeum or Postia placenta, or the white rot fungus, Trametes versicolor, according to AWPA Standard E10. All preservatives reduced weight losses caused by G. trabeum or T. versicolor below 10 %, except for micronized copper hydroxide or DCOI alone. The four other copperbased preservatives performed well independently and with the addition of DCOI or tebuconazole. The results suggest that incorporating combinations of copper-based preservative systems with organic co-biocides improved decay and mold resistance of aspen oriented strandboard. 27 Introduction Oriented strandboard (OSB) is a composite sheathing panel product composed of various sized strands that have been mixed with resin, oriented in a specific direction and pressed to a desired thickness and density. OSB is a high quality product that effectively utilizes lower quality species of wood. The inexpensive raw material costs are passed on to the consumer as a low cost product. The resource impact of OSB is also lower than that of plywood, the traditional sheathing panel product, due to the tree species used (Laks & Palardy, 1990a). Although wood and wood-based composite sheathing panels can tolerate brief periods of wetting during construction, they are designed to remain dry while in service. Exposing these products to high relative humidities or liquid water for prolonged periods sharply increases the chances of mold, stain or decay (Fogel & Lloyd, 2002; Morris et al., 1999). Softwood plywood panels tend to be more resistant to decay and mold than OSB (Laks, 1999; Laks et al., 2002). Even though OSB and strand-composite products are made from decay susceptible species, they are increasingly being used in applications that subject them to conditions suitable for insect and fungal attack (Jeihooni et al., 1993; Morrell, 2002; Morris, 1995; Morris et al., 1999). In response to rising energy costs, a number of building practices have been implemented to seal homes to limit the escape of warm or cold air. These practices reduce the interior/exterior air exchange, which can trap moisture from both interior and exterior sources (Anderson, 1972; Barnes & Amburgey, 1993; Cassens, 1978; Laks, 1999; Laks et al., 2002; Merrill & TenWolde, 1989; Morrell, 2002; 28 Schmidt, 1993). Accumulation of moisture within wall cavities can lead to mold and decay (Barnes & Amburgey, 1993; Schmidt, 1993; Yang et al., 2007). A variety of methods can be used to protect composite panels from biological attack (Gardner et al., 2003). In-process treatments appear to be among the best treatment methods. Uniform preservative distribution within the product produces much better protection than “shell” treatments provided by post-treatment processes, while pre-treating the substrate requires an extra drying step that is energy intensive and costly (Laks & Palardy, 1992). There are a number of preservatives that may be suitable for composite panels. Each has advantages and disadvantages in terms of cost, safety, ease of handling and efficacy. Organic biocides are increasingly used as wood preservatives because of their low toxicity to non-target organisms and rising consumer concerns about the use of heavy metals. Triazoles are a class of organic fungicides that are widely used in agriculture, and are increasingly employed as co-biocides in wood preservatives. These systems provide adequate protection against decay fungi, moderate protection against surface mold, and little interference with mechanical or physical properties of OSB (Schmidt & Gertjejansen, 1988; Tolley et al., 1998). Isothiazolone is a broad spectrum fungicide that has been found to reduce mold growth (Williams & Lewis, 1989) and to be effective against decay fungi in both laboratory and field tests (Leightley & Nicholas, 1990). Borates have a number of appealing benefits as wood preservatives, including good efficacy against fungi and insects, fire retardancy, ease of application into the 29 board furnish, low cost, low mammalian toxicity and low environmental impact (Laks & Palardy, 1990b). However, borates have a few disadvantages that limit them as composite panel preservatives. Biologically-effective treatment levels of sodium borate and boric acid react with phenol formaldehyde (PF) resin to prevent good adhesion between wood substrates, resulting in boards with unacceptably low mechanical properties. A number of borate treatments, including disodium octaborate tetrahydrate (DOT) and anyhydrous borax, are extremely water-soluble and therefore have a propensity to leach in-service (Gardner et al., 2003). As a result, these products are not recommended for ground-contact. As an alternative, zinc borate (ZnB) is a relatively water-insoluble alternative that is currently used in coated exterior applications with low to moderate leaching hazards (Laks, 1999; Manning & Laks, 1996). Various physical or chemical modifications have also been assessed for OSB protection, including acetylation, isocyanates, supercritical fluids and heat treatment (Acda et al., 1996; Kumar & Morrell, 1993; Murphy & Turner, 1989; Paul et al., 2006). None of these treatments are currently practical due to unacceptable weight gains, efficiency issues and/or cost. The use of copper preservatives, such as copper naphthenate, ammoniacal copper complexes or copper carbonate in powdered forms have shown good efficacy when included in wood-based composites (Kirkpatrick & Barnes, 2006b). Kirkpatrick and Barnes (2006a) continued research by Schmidt (1991) and found that powdered copper naphthenate could be added to the furnish of aspen strandboards without any significant effects on mechanical and physical properties. Copper ammonium 30 carbonate (CAC) was found to be effective and was used as a pre-process preservative for OSB produced by Potlatch Corporation (Preston et al., 2003). The added pre-treatment steps of the strands before blending make CAC treatment economically infeasible. Goroyias and Hale (2000) added a copper carbonate hydroxide-based preservative, with boric acid, tebuconazole, and an aliphatic amine derivative as co-biocides, at various points during the manufacturing of strandboards. They found that the preservative reduced mechanical properties when sprayed in-line with the resin and pressed at 210°C. Copper based biocides appear to have a strong potential as a composite panel preservative if formulation and application methods can be optimized. Preferably, a powdered copper complex would be added to the strands prior to resin application and pressed in a standard press schedule. The objective of this research was to evaluate the effects of incorporating various copper-based preservatives into the furnish, with or without organic cobiocides, on the resistance to mold and decay of aspen strandboards. Materials and Methods Panel Fabrication Commercially manufactured aspen strands obtained from Louisiana-Pacific (Newberry, MN) were dried in a commercial laundry dryer to approximately 3% moisture content (MC) and stored in plastic bags until use. Preservatives were acquired from Viance, Inc (Charlotte, NC) and Rio Tinto Minerals, Inc (Edgewood, CO). Seven chemicals were incorporated individually or in combination into board furnishes at various target concentrations (Table 1) and 31 compared to untreated negative controls and zinc borate treated positive controls. Each treatment group was replicated on six panels. Table 1. Preservative treatments assessed for their ability to improve strandboard panel durability Treatment Untreated control Zinc Borate Copper Ammonium Acetate Complex (liquid) Copper Diammine Acetate Copper Diammine Carbonate Micronized Copper Basic Copper Carbonate Copper Diammine Acetate / Tebuconazole Isothiazolone Isothiazolone / Cu Diammine Acetate Isothiazolone / Cu Ammonium Acetate (liquid) Untreated control Abbreviation Control Loading (wt/wt %) Matt MC (%) Manufacturer 0 7.4 0.585 7.4 Rio Tinto ZB 0.878 7.4 Minerals 1.17 7.3 0.25 10.2 CC 1 0.50 13.1 Viance 0.75 16.0 0.25 7.4 CC 2 0.50 7.3 Viance 0.75 7.3 0.25 7.4 CC 3 0.50 7.3 Viance 0.75 7.3 0.25 7.4 MCOH 0.50 7.3 Viance 0.75 7.3 0.25 7.4 BCC 0.50 7.4 Viance 0.75 7.3 0.5 / 0.01 7.3 CC 2 / azole 0.5 / 0.02 7.3 Viance 0.5 / 0.04 7.3 0.05 6.7 DCOI 0.05 / 0.5 6.6 Viance DCOI / CC 2 0.05 / 0.5 12.4 DCOI / CC 1 0 5.7 Control (400 seconds) Due to the size of the blender (6 ft diameter, 3 ft depth), each furnish batch was capable of producing three panels (strands, preservative, wax and resin). The strands were added first, and then dry salts of treatment chemical were sprinkled over the mixture. The preservative and the strands were then blended for five minutes at 16 revolutions per minute. A touch-up paint spray gun attached to the inside of the blender was used to spray the liquid copper complex onto the tumbling strands. DCOI (4,5-dichloro-2-N-octyl-4-isothiazolin-3-one) was added to the wax emulsion. 32 A wax emulsion with 58% solids content (Hexion Specialty Chemicals; Springfield, OR) was sprayed onto the tumbling strands at a loading of 1.0% wt/wt using the touch-up paint spray gun. OSB face-resin with 48% solids content (GeorgiaPacific; Albany, OR) was then applied to the strands at a loading of 3.5% wt/wt through a spinning disk atomizer at 6000 rpm during blending. A 560mm square forming box was placed on top of a steel caul plate and blended strands were distributed in the box. No attempt was made to orient the strands. The forming box was removed and a second caul plate was placed atop the formed mat. The mat and caul plates were then placed in the hot press. The hot press, with upper and lower platens set at 200º C, pressed the mat to a target thickness of 11 mm for 200 seconds. Because of the difficulties in producing acceptable boards using DCOI, press time was increased to 400 seconds. A second untreated control group was also pressed for the extended time. The press was then vented by opening at a rate of 0.002 cm/second for 60 seconds to produce finished boards that were approximately 12.7 mm thick and had a density of approximately 577 kg/m³. Approximately 90 mm was trimmed from each edge of the board using a table saw. Specimens were then cut from the panels for biological and mechanical tests (Figure 1). 33 Figure 1. Cutting pattern used to produce test specimens from treated and untreated strandboard panels Retention Analysis The six leached blocks from each treatment were ground to pass a 30 mesh screen and combined for preservative analysis. The level of each preservative component in the wood was determined using the appropriate analytical method: Copper was determined by X-ray spectroscopy according to AWPA Standard A9 (AWPA, 2006e). ZB treated wood was extracted by nitric acid digestion (AWPA, 2006f), and analyzed by Inductively Coupled Plasma Emission Spectrometry (ICP) following AWPA Standard A21 (AWPA, 2006g). DCOI and tebuconazole were extracted in methanol; the resulting extracts were analyzed by High Performance 34 Liquid Chromatography (HPLC) with UV detection, according to AWPA Standard A30 or Standard A28, respectively (AWPA, 2006h, 2006i). Soil Block Test The American Wood Protection Association (AWPA) Standard E10-06 soil block test is a relatively rapid laboratory method for determining the decay resistance of preservative treated wood-based material (AWPA, 2006a). Three 19 mm by 19 mm blocks were cut from each panel, labeled, oven-dried at 103º C and weighed. Ponderosa pine sapwood cubes (19mm) were included as comparator controls. The blocks were submerged in deionized water for 15 minutes to increase MC, and sterilized by exposure to 2.5 mrad of ionizing radiation from a cobalt 60 source. Decay chambers were prepared by filling 480 ml glass jars halfway with potting soil, adding 20 ml of water, and placing western hemlock (for brown rot fungi) or alder (for white rot fungi) feeder strips on top of the soil. Caps were loosely screwed on and the jars were autoclaved for 45 minutes at 125º C. After cooling, the feeder strips were inoculated with 2 to 3 mm diameter malt agar disks cut from the actively growing edges of cultures of the test fungus. Two brown rot fungi, Gloeophyllum trabeum (Pers.ex. Fr.) Murr. (Isolate # Madison 617) and Postia placenta (Fr.) M. Larsen et Lombard (Isolate Madison 698), and one white rot fungus, Trametes versicolor (L. ex Fr.) Pilát (Isolate # FP-101664-Sp) were evaluated. The jars were loosely capped to allow air exchange, and incubated until the feeder strips were thoroughly covered by the mycelium. Two sterilized blocks from a given treatment were then placed on the feeder strip within the jars. The jars were 35 incubated at 28º C for 12 or 16 weeks for the brown or white rot fungi, respectively. Each treatment variable was evaluated on six blocks per test fungus. After incubation, the jars were removed from the chamber, brushed free of mycelium, weighed, oven dried at 103º C and weighed again. Percent weight loss of the blocks was used as a measure of decay resistance. Mold Box Test The AWPA Standard E24-06 mold box test is a relatively rapid method for determining the resistance of wood-based material surfaces to mold fungi (AWPA, 2006b). Samples (75 mm by 100 mm) were cut from each board. A small hole was drilled in one corner to allow for the attachment of a wire hanger. The samples were sprayed with an inoculum solution containing the following common molds: Aureobasidium pullulans (d. By.) Arnaud, Aspergillus niger v. Tiegh., Penicillium citrinum Thom and Alternaria alternata (Fr.) Keissl. The samples were suspended above moist soil, which was in a tray above water, in the sealed mold box. The interior of the mold box was maintained at 25º C and the room was maintained at 20º C, thus resulting in an elevated relative humidity and the potential for condensation. Table 2. Visual scale to rate the extent of mold growth on treated and untreated strandboard panels. Rating 0 1 2 3 4 5 Description No mold growth Mold covering up to 10% of surfaces Mold covering between 10% and 30% of surfaces Mold covering between 30% and 70% of surfaces Mold on greater than 70% of surfaces Mold on 100% of surfaces 36 The samples were incubated for 8 weeks, and were inspected every two weeks by individually removing samples and visually assessing each for degree of discoloration on a scale (Table 2). Statistical Analysis Differences between treatments and the control groups were assessed using a Completely Randomized Design analysis of variance using SAS 9.1 (SAS Institute, α = 0.05). Tukey’s Honestly Significant Difference multiple comparison test was used to determine differences between treatment means to minimize Type I errors, that is to conclude something was different when it was actually the same. Duncan’s Multiple Range Test was used prior to the Tukey’s Studentized Range Test for multiple comparisons to harmonize the mean cell size when there were unequal replications. Results and Discussion Retention Analysis Target retentions were not met for any preservative treatments (Table 3). Panels treated with CC 1 alone had the best retention because it was sprayed onto the strands during blending, but retention levels were still 27 to 35% below target levels. CC 2, CC 3 and BCC treated panels were 53 to 71% below target retentions. Insufficient preservative adherence to the strands, even after the addition of wax and resin, was one cause for the low retentions because they were added to the blender as solid copper-compounds. MCOH were up to 89% retention below the target level, indicating a major incompatibility of the preservative formulation with this application 37 method. DCOI was added to the wax, and was assumed to have good distribution onto the strands with minimal loss. The lower retentions may have been due to degradation of the biocide due to exposure to high temperatures in the press. Table 3. Chemical retentions of aspen strandboards treated with various preservatives Treatment Strandboard Control Abbreviation Control Zinc Borate ZB Copper Ammonium Acetate Complex (liquid) CC 1 Copper Diammine Acetate Complex CC 2 Copper Diammine Carbonate Complex CC 3 Micronized Copper MCOH Basic Copper Carbonate BCC Cu Diamine Acetate / Tebuconazole CC 2 / azole Target Retention Actual Retention a (wt/wt %) (wt/wt %) 0.585 0.878 1.17 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.5 / 0.01 0.5 / 0.02 0.5 / 0.04 0.05 0.05 / 0.5 0.05 / 0.5 0.861 1.218 1.881 0.183 0.332 0.486 0.088 0.146 0.292 0.095 0.226 0.353 0.039 0.055 0.115 0.095 0.168 0.238 0.189 / 0.006 0.217 / 0.012 0.235 / 0.024 0.024 0.025 / 0.164 0.027 / 0.375 Isothiazolone DCOI Isothiazolone / Cu Diammine Acetate DCOI / CC 2 Isothiazolone / Cu Ammonium Acetate (liquid) DCOI / CC 1 Strandboard Control (400 seconds) Control (400 seconds) a Values represent the combination of six treatment blocks analyzed by appropriate method. 38 Soil Block Test Weight losses for both sets of untreated strandboards exposed to G. trabeum were greater than 50%, indicating that conditions were suitable for aggressive fungal attack, and that the extra press time alone had no effect on decay resistance (Table 4). All chemical treatments reduced weight losses to below 10%, except panels treated with DCOI alone, micronized copper hydroxide (MCOH), and the lowest treatment levels of copper diammine acetate (CC 2) and basic copper carbonate (BCC) (Figure 2). The DCOI levels employed were extremely low and were not intended to provide protection against fungal decay. The poor performance of the particulate copper was surprising, although it may be due to extremely low copper retentions. This system was an experimental formulation and is not directly comparable to the micronized copper systems currently in commercial use. Panels treated with combinations of DCOI and the liquid copper ammonium acetate complex (CC 1) performed the best against G. trabeum, with average weight losses below 1%. Panels treated with CC 1 alone experienced similar weight losses, suggesting that DCOI was not needed for decay resistance. Table 4. Wood weight losses of aspen strandboard blocks subjected to various treatments and exposed to decay fungi in a soil block test Retention (wt/wt %) a Wood Weight Loss (%) G. trabeum P. placenta T. versicolor Treatment 55.6 (4.4) a,b 18.6 (27.5) b 52.8 (12.0) b,c Control 0.585 6.2 (9.6) e,f 1.0 (0.1) b 2.6 (2.1) e ZB 0.878 1.9 (0.6) e,f 1.2 (0.1) b 1.5 (0.2) e 1.17 1.4 (0.1) f 1.2 (0.2) b 1.4 (0.1) e 0.25 4.4 (0.7) e,f 1.1 (0.2) b 3.3 (0.3) e CC 1 0.50 3.2 (1.0) e,f 1.3 (0.1) b 2.2 (0.4) e 0.75 2.4 (0.7) e,f 16.4 (23.1) b 2.2 (0.3) e 0.25 12.2 (5.6) e,f 0.8 (0.2) b 13.3 (2.7) e CC 2 0.50 3.8 (1.3) e,f 25.3 (23.9) a,b 6.0 (2.2) e 0.75 2.7 (1.0) e,f 1.0 (0.1) b 2.6 (0.7) e 0.25 9.4 (2.3) e,f 16.9 (24.7) b 7.9 (1.7) e CC 3 0.50 2.8 (0.7) e,f 15.4 (22.8) b 3.7 (1.3) e 0.75 1.9 (0.4) e,f 0.9 (0.1) b 3.4 (0.8) e 0.25 46.0 (16.9) b 21.2 (31.4) b 29.4 (12.8) d MCOH 0.50 29.6 (14.2) c,d 0.8 (0.1) b 33.0 (12.7) d 0.75 41.8 (23.1) b,c 34.6 (27.1) a,b 41.2 (23.3) c,d 0.25 17.4 (3.7) d,e 0.8 (0.1) b 8.6 (1.7) e BCC 0.50 3.3 (1.3) e,f 15.7 (23.2) b 3.7 (0.9) e 0.75 2.0 (0.8) e,f 0.8 (0.1) b 2.9 (0.6) e 0.5 / 0.01 2.7 (0.6) e,f 0.8 (0.1) b 4.7 (1.2) e CC 2 / azole 0.5 / 0.02 2.0 (0.3) e,f 1.1 (0.1) b 3.2 (0.4) e 0.5 / 0.04 1.6 (0.3) e,f 12.1 (5.7) b 3.6 (1.6) e 0.05 62.4 (7.0) a 25.1 (33.7) a,b 58.6 (5.3) a,b DCOI 0.05 / 0.5 2.3 (0.7) e,f 35.4 (27.4) a,b 4.4 (1.8) e DCOI / CC 2 0.05 / 0.5 0.8 (0.2) f 17.9 (26.7) b 1.2 (0.4) e DCOI / CC 1 53.5 (12.3) a,b 27.4 (31.9) a,b 67.8 (11.7) a Control (400 seconds) 68.4 (2.1) a 63.0 (1.0) a 28.4 (5.1) d Pine Control a Values represent means of 6 blocks per treatment, while figures in parentheses represent one standard deviation. Isothiazolone, Waferboard Controls at 400 seconds and Pine Controls represent means of 5, 5, and 6 blocks, respectively. Values followed by a common letter are not signifantly different using Tukey's Studentized Range test that was harmonized using Duncan's Multiple Range Test. 39 40 Weight Loss - G. trabeum 70 60 Weight loss (%) 50 40 30 20 10 O I CO CC I/ 2 C on C C tr o 1 l pi (40 ne 0) co nt ro l O D C D C C 2 I/ /a D C le zo C BC M C O H 3 C C C C 2 1 C C ZB C on tr o l 0 Figure 2. Weight losses of strandboard blocks subjected to various treatments and exposed to Gloeophyllum trabeum in a soil block test. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. Weight losses from panels treated with tebuconazole and CC 2 were less than 3%. This was a slight improvement over CC 2 alone at the medium target retention, but the differences were not statistically significant. Increased tebuconazole retentions appeared to be associated with reduced weight losses, but these differences were not statistically significant. It is likely that the added fungicide had only a minimal effect because of the protection already afforded by the copper compound. Zinc borate (ZB) performed as well as the copper compounds with a maximum weight loss of 6.2% for the lowest target retention, illustrating the excellent performance of this system. 41 Weight losses of untreated and treated OSB blocks exposed to P. placenta were extremely variable, and there were no statistically significant differences between any treatment groups (Table 4). Pine control blocks experienced 63% weight loss, which validated the test and reflected the preference of brown rot fungi for softwoods. Weight Loss - P. Placenta 70 60 Weight loss (%) 50 40 30 20 10 O I CO CC I/ 2 C on C C tr o 1 l pi (40 ne 0) co nt ro l O D C D C C 2 I/ /a D C le zo C BC M C O H 3 C C C C 2 1 C C ZB C on tr o l 0 Figure 3. Weight losses of strandboard blocks subjected to various treatments and exposed to Postia placenta in a soil block test. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. All copper-based treatments experienced mean weight losses above 10% in at least one of the three treatment levels, and there appeared to be no dose response for any treatment chemical (Figure 3). The decay of panels treated with copper-based preservatives by P. placenta probably reflects the well-known tolerance of this fungus to copper biocides. 42 Treated and untreated blocks exposed to T. versicolor experienced weight losses similar to those exposed to G. trabeum, indicating that conditions were suitable for aggressive fungal attack (Table 4, Figure 4). Weight losses exceeding 50% were found on both untreated strandboard control groups. Pine controls had a mean weight loss of 38%, reflecting the preference of white rot fungi for hardwoods. ZB performed exceptionally well against T. versicolor at all three levels tested. Weight Loss - T. versicolor 70 60 Weight loss (%) 50 40 30 20 10 O I CO CC I/ 2 C on C C tr o 1 l pi (40 ne 0) co nt ro l O D C D C C 2 I/ /a D C le zo C BC C O H 3 C C C C 2 1 ZB C C M C on tr o l 0 Figure 4. Weight losses of strandboard blocks subjected to various treatments and exposed to Trametes versicolor in a soil block test. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. All three copper complexes performed well against T. versicolor. Panels treated with CC 1 had the best efficacy overall, with the lowest treatment level resulting in only 3.3% weight loss. This may be a reflection of the increased retention of the liquid preservative compared to the other treatments. The medium target 43 retention of CC 2 had a mean weight loss of 6%, and performance was slightly improved by the addition of tebuconazole. As with the brown rot fungi, MCOH performed poorly against the white rot fungus with no evidence of a dose response effect. In this case, the highest target retention experienced the greatest amount of weight loss, although the differences were not statistically significant. Low retention levels, as noted earlier, probably played a role in the poor performance of this system. Panels treated with combinations of DCOI and CC1 or CC 2 performed as well as panels treated only with these copper complexes at the same target retention levels. DCOI was added at extremely low levels as a mold inhibitor and its failure to improve performance of copper compounds at this level is not surprising. Mold Box Test Very few treatments had any effect on mold resistance of strandboards (Table 5). ZB, CC 2, CC 3, MCOH and basic copper carbonate at all treatment levels received ratings of at least 3, representing between 30 and 70% surface coverage, after 2 weeks in the mold box. These treatments all received ratings of at least 4, or greater than 70% coverage, by week 3. CC 1 appeared to reduce mold growth after 2 weeks, especially at the highest retention level (Figure 5), possibly because the liquid preservative was more evenly distributed over the strand surfaces. The highest retention level of CC 1 had a rating of 4.2 after 4 weeks, indicating that this compound no longer protected against mold growth. While copper compounds are widely used Table 5. Effects of various treatments on mold resistance of strandboards in an AWPA E24 mold box test a Mold Rating b Week 8 Treatment Week 2 Week 3 Week 4 Week 6 3.7 (0.6) a,b,c,d 3.7 (1.0) a,b,c 4.3 (0.8) a,b,c 4.7 (0.5) a Strandboard Control 0.585 3.3 (0.6) a,b,c,d,e 4.0 (0.0) a,b 4.3 (0.5) a,b,c 5.0 (0.0) a ZB 0.878 3.7 (0.6) a,b,c,d 4.2 (0.4) a,b 4.2 (0.4) a,b,c 4.8 (0.4) a 1.17 3.7 (0.6) a,b,c,d 4.0 (0.0) a,b 4.5 (0.5) a,b 4.8 (0.4) a 0.25 3.0 (1.0) a,b,c,d,e 4.3 (0.5) a 4.5 (0.5) a,b 4.8 (0.4) a CC 1 0.50 3.0 (1.7) a,b,c,d,e 4.5 (0.5) a 4.8 (0.4) a 5.0 (0.0) a 0.75 1.7 (1.2) d,e 3.8 (0.8) a,b 4.2 (0.4) a,b,c 5.0 (0.0) a 0.25 4.3 (0.6) a,b 4.8 (0.4) a 4.7 (0.5) a,b 5.0 (0.0) a CC 2 0.50 4.3 (0.6) a,b 4.7 (0.5) a 4.8 (0.4) a 5.0 (0.0) a 0.75 5.0 (0.0) a 4.5 (0.5) a 4.8 (0.4) a 4.8 (0.4) a 0.25 4.3 (0.6) a,b 4.5 (0.5) a 4.7 (0.5) a,b 5.0 (0.0) a CC 3 0.50 3.7 (0.6) a,b,c,d 4.2 (0.4) a,b 4.8 (0.4) a 5.0 (0.0) a 0.75 4.3 (0.6) a,b 4.5 (0.5) a 4.8 (0.4) a 5.0 (0.0) a 0.25 3.7 (0.6) a,b,c,d 4.2 (0.4) a,b 4.3 (0.5) a,b,c 4.5 (0.5) a,b MCOH 0.50 4.3 (0.6) a,b 4.5 (0.5) a 4.5 (0.5) a,b 4.7 (0.5) a 0.75 4.3 (0.6) a,b 4.5 (0.5) a 4.5 (0.5) a,b 4.8 (0.4) a 0.25 4.0 (0.0) a,b,c 4.2 (0.4) a,b 4.2 (0.4) a,b,c 4.7 (0.5) a BCC 0.50 4.0 (0.0) a,b,c 4.3 (0.5) a 4.5 (0.5) a,b 4.7 (0.5) a 0.75 4.0 (0.0) a,b,c 4.5 (0.5) a 4.3 (0.5) a,b,c 5.0 (0.0) a 0.5 / 0.01 4.3 (0.6) a,b 4.5 (0.5) a 4.5 (0.5) a,b 5.0 (0.0) a CC 2 / azole 0.5 / 0.02 3.0 (1.0) a,b,c,d,e 4.2 (0.4) a,b 4.5 (0.5) a,b 4.8 (0.4) a 0.5 / 0.04 2.0 (0.0) c,d,e 4.0 (0.0) a,b 4.0 (0.0) a,b,c 4.8 (0.4) a 0.05 2.5 (0.8) b,c,d,e 3.0 (1.1) b,c 3.7 (0.5) b,c,d 4.3 (0.5) a,b 4.7 (0.5) a,b DCOI 0.05 / 0.5 1.5 (0.5) e 2.5 (0.5) c,d 3.3 (0.5) c,d 3.8 (0.4) b,c 4.2 (0.4) b,c DCOI / CC 2 0.05 / 0.5 1.3 (0.8) e 1.7 (0.8) d 2.8 (0.8) d 3.3 (0.5) c 3.7 (0.5) c DCOI / CC 1 3.8 (0.4) a,b,c 4.2 (0.4) a,b 4.7 (0.5) a,b 4.8 (0.4) a 5.0 (0.0) a Strandboard Control (400 seconds) a Mold was visually assessed for the degree of discoloration on a scale from 0 to 5, where 0 denoted no discoloration. Values represent means of 6 blocks per treatment, while figures in parentheses represent one standard deviation. Values followed by a common letter are not signifantly different using a Tukey's Studentized Range test that was harmonized using Duncan's Multiple Range Test. Retention (wt/wt %) b The first test was discontinued after 6 weeks because all treatments had failed. The second test was evalutated for the full 8 weeks. 44 45 in heavy duty wood treatments, they are prone to surface mold growth on prolonged wet storage. This performance attribute appears to extend to copper in panel products. Boards treated with CC 2 and supplemented with tebuconazole appeared to experience reduced mold growth at 2 weeks, but all had experienced substantial mold growth by week 3 (Figure 5). These data showed that tebuconazole performed poorly as a moldicide, but this might be due to insufficient target loading levels or actual retentions less than half the target levels. Clausen and Yang (2005) found that the 0.043 wt/wt % of voriconazole, which shows more efficacy against mold than tebuconazole, was needed to inhibit mold growth on unseasoned southern pine. This suggests that 0.024 wt/wt % tebuconazole was inadequate in this application (Table 3). Mold Resistance 5 Rating (0-5) 4 3 2 Control CC 1 (7500ppm Cu) 1 CC 2 (5000ppm Cu) / azole (400ppm) 0 0 1 2 3 4 5 6 Week Figure 5. Surface mold growth on CC1 or CC2 and tebuconazole treated strandboard in an AWPA E24 mold box test. Values represent means of 6 replicates. 46 Mold growth was much lower on panels containing DCOI alone or with copper compounds throughout the 8 week test (Figure 6). Boards treated with DCOI alone had a rating of 2.5 after two weeks, although this was not significantly different from the controls (400 seconds). DCOI also showed good efficacy against mold growth as a co-biocide. Addition of DCOI to panels with CC 1 and CC 2 resulted in ratings below 4, even after 6 weeks of exposure. Actual DCOI retentions were half of the target levels (Table 3), suggesting that resistance to mold growth would have been improved had target levels been met. DCOI is subject to degradation at high pHs (Morrell, 2004), but the two copper complexes did not appear to completely diminish moldicidal efficacy. Mold Resistance 5 Rating (0-5) 4 3 2 Control DCOI DCOI / CC 2 DCOI / CC 1 Control (400) 1 0 0 1 2 3 4 5 6 7 8 Week Figure 6. Surface mold growth on strandboards treated with DCOI alone or as a cobiocide with two copper complexes. Values represent means of 6 replicates. 47 Additional Research The ability of a preservative system to adequately protect a wood product is dependent upon the system’s efficacy against attack by multiple biological organisms in a specified intended use. The laboratory soil block test is a relatively rapid method for evaluating decay resistance, but it uses unrealistic conditions for degradation of most wood products. In the worst case scenario, OSB would be exposed in an exterior above-ground environment. To test the efficacy of the treated and untreated strandboard panels in exterior above-ground application, samples were exposed using AWPA Standard E18-06 ground proximity field test (AWPA, 2006c). Two 50 mm by 125 mm samples were cut from each board and labeled with metal identification tags. The samples were shipped to Hilo, HI where they were exposed in a ground proximity test. Squares of 100 mm thick concrete masonry blocks were placed directly in contact with the ground. The cinder blocks allowed moisture to wick from the soil to the samples, but did not allow direct soil/wood contact. The sample blocks were placed on top of the concrete blocks and the assembly was covered with a shade cloth that allowed rain to pass through, but prevented exposure to direct sunlight. The assembly resulted in a high moisture regime that created an extreme above ground decay environment. The samples will be visually evaluated on an annual basis for soundness on a scale from 0 to 10, where 0 denotes failure and 10 denotes no sign of degradation. There is also a need to evaluate the resistance of the treated panels to termite damage. A termite field test was initiated using an adaptation of AWPA Standard E9- 48 06 field test for the evaluation of wood preservatives used in non-soil contact (AWPA, 2006d). Two 50 mm by 125 mm samples were cut from each board and labeled with plastic identification tags. The samples were sent to Hilo, HI, where they were placed horizontally on 100 mm high concrete masonry blocks, which are placed directly in contact with the ground above a known Formosan termite (Coptotermes formosanus) colony. Wood stakes were driven into the ground within the array to provide an upward pathway for foraging termite workers. Untreated pine sapwood sticks (19 mm by 19 mm at various lengths) were placed between rows of samples so that termites could attack untreated wood to reach the test samples. The assembly was covered with a plywood box that prevented overhead wetting. The samples will be visually evaluated at six month intervals for soundness on a subjective scale from 0 to 10, where 0 denotes failure due to termite attack and 10 denotes no attack. Conclusions Retentions levels for all treatments were significantly below targets. Nearly all preservative treatment systems except MCOH or DCOI alone were effective against brown or white rot fungi. Panels treated with CC 2, CC 3 or BCC experienced unacceptable weight losses at the lowest target retentions. Panels treated with CC 2 and tebuconazole did not perform differently from those with the copper complex alone. Panels treated with CC 1 and DCOI appeared to provide the most protection, but this could not be confirmed due the low replication. Very few of the preservative systems had any effect on surface mold growth on the panels. Panels treated with CC 1 or CC 2 with the highest retention of tebuconazole initially limited mold growth, but 49 were nearly completely covered after three weeks. DCOI significantly improved resistance to mold growth compared to untreated panels. The combination of DCOI with CC 1 or CC 2 provided the best protection against mold. Copper-based preservatives in conjunction with DCOI appeared to provide the best protection for aspen OSB. References Acda, M.N., Morrell, J.J., & Levien, K.L. (1996). Decay resistance of composites following supercritical fluid impregnation with tebuconazole. Material und Organismen, 30(4), 293-300. Anderson, L.O. (1972). Condensation problems: Their prevention and solution. In U.S. Forest Products Laboratory. U.S.D.A Forest Service Research Paper (Vol. FPL 132, pp. 36 ): Madison, WI AWPA. (2006a). E10-06. Standard method of testing wood preservatives by laboratory soil-block cultures. In AWPA Book of Standards. Granbury, TX. AWPA. (2006b). E24-06. Standard method of evaluating the resistance of wood product surfaces to mold growth. In AWPA Book of Standards. Granbury, TX. AWPA. (2006c). E18-06. Standard field test for evalutaion of wood preservatives intended for use category 3B applications exposed, out of ground contact, uncoated ground proximity decay method. In AWPA Book of Standards. Granbury, TX. AWPA. (2006d). E9-06. Standard field test for the evaluation of wood preservatives to be used in non-soil contact. In AWPA Book of Standards. Granbury, TX. AWPA. (2006e). A9-01. Standard method for analyzsis of treated wood and treating solutions by X-ray spectroscopy. In AWPA Book of Standards. Granbury, TX. AWPA. (2006f). A7-04. Standard for wet ashing procedures for preparing wood for chemical analysis. In AWPA Book of Standards. Granbury, TX. AWPA. (2006g). A21-00. Standard Method for the analysis of wood and wood treating solutions by inductively coupled plasma emission spectrometry. In AWPA Book of Standards. Granbury, TX. 50 AWPA. (2006h). A30-00. Standard method for the determination of 4,5 Dichloro-2N-octyl-4-isothiazolin-3-one (RH-287) in wood by high performance liquid chromatography (HPLC). In AWPA Book of Standards. Grandbury, TX. AWPA. (2006i). A28-05. Standard method for determinination of propiconazole and tebuconazole in wood, in waterborne formulations and in treating solutions by HPLC. In AWPA Book of Standards: Grandbury, TX. Barnes, H.M., & Amburgey, T.L. (1993). Technologies for the protection of wood composites. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products, Forest Products Society, Madison, WI. pp. 7-11. Cassens, D.L. (1978). Importance of Wood Deterioration in Single-Family Residences for East Baton Rouge Parish, Louisiana. Forest Products Journal, 28(8), 19-24. Clausen, C.A., & Yang, V.W. (2005). Azole-based antimycotic agents inhibit mold on unseasoned pine. International Biodeterioration & Biodegradation, 55, 99-102. Fogel, J.L., & Lloyd, J.D. (2002). Mold performance of some construction products with and without borates. Forest Products Journal, 52(2), 38-43. Gardner, D.J., Tascioglu, C., & Wålinder, M.E.P. (2003). Wood composite protection. Washington, DC: American Chemical Society: Distributed by Oxford University Press. Goroyias, G.J., & Hale, M.D. (2000). Effect of point of preservative addition on the mechanical and physical properties of strandboard treated with Tanalith 3485. Document No IRG/WP 00-40152. In The International Research Group on Wood Preservation, Stockholm Sweden. Jeihooni, A., Krahmer, R.L., & Morrell, J.J. (1993). Microdistribution of Chromated Copper Arsenate in Douglas-fir Flakeboard. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 93-99. Kirkpatrick, J.W., & Barnes, H.M. (2006a). Copper naphthenate treatments for engineered wood composite panels. Bioresource Technology, 97(15), 19591963. Kirkpatrick, J.W., & Barnes, H.M. (2006b). Biocide Treatments for Wood Composites―A Review. Document No IRG/WP 06-40323. In The International Research Group on Wood Preservation, Stockholm Sweden. Kumar, S., & Morrell, J.J. (1993). Improved composites from chemically modified particles. In Proceedings: International Union of Forestry Research 51 Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 33-37. Laks, P.E. (1999). The past, present, and future of preservative-containing composites. In Proceedings: The International Particleboard/Composite Materials Symposium pp. 151-158. Laks, P.E., & Palardy, R.D. (1990a). Bonding and process considerations for preservative-containing waferboard. In Wood adhesives 1990 : Proceedings of a symposium sponsored by USDA Forest Service, Forest Products Laboratory and the Forest Products Research Society Madison, WI. pp. 150-154. Laks, P.E., & Palardy, R.D. (1990b). The development of borate-containing flakeboard. In Proceedings: The International Conference on Wood Protection with Diffusable Preservatives, Forest Products Society, Madison, WI pp. 7679. Laks, P.E., & Palardy, R.D. (1992). Factors that affect the performance of preservative-containing wafer-based composites. In Proceedings: Pacific Rim Bio-Based Composite Symposium pp. 163-171. Laks, P.E., Richter, D.L., & Larkin, G.M. (2002). Fungal susceptibility of interior commercial building panels. Forest Products Journal, 52(5), 41-44. Leightley, L.E., & Nicholas, D.D. (1990). In ground performance of wood treated with a substituted isothiazolone. Document No IRG/WP 3612. In The International Research Group on Wood Preservation, Stockholm Sweden. Manning, M.J., & Laks, P.E. (1996). Zinc borate - a preservative treatment for composites. In Proceedings: Seventeenth Annual Meeting of the Canadian Wood Preservation Association pp. 123-133. Merrill, J.L., & TenWolde, A. (1989). Overview of moisture-related damage in one group of Wisconsin manufactured homes. Ashrae Transactions, 95, 405-414. Morrell, J.J. (2002). Wood-based building components: what have we learned? International Biodeterioration & Biodegradation, 49(4), 253-258. Morrell, J.J. (2004). Mold on Treated Wood. In American Wood-Preservers' Association, Vancouver, B.C. pp. 84-87. Morris, P.I. (1995). Processes to improve the durability of OBS. Edmonton, Alberta: Alberta Land and Forest Service. 52 Morris, P.I., Clark, J.E., Minchin, D., & Wellwood, R. (1999). Upgrading the fungal resistance of OSB. Document No IRG/WP 99-40138. In The International Research Group on Wood Preservation, Stockholm Sweden. Murphy, R.J., & Turner, P. (1989). A vapour phase preservative treatment of manufactured wood based board materials. Wood Science and Technology, 23(3), 273-279. Paul, W., Ohlmeyer, M., Leithoff, H., Boonstra, M.J., & Pizzi, A. (2006). Optimising the properties of OSB by a one-step heat pre-treatment process. Holz als Rohund Werkstoff, 64(3), 227-234. Preston, A.F., Fowlie, D.A., & Archer, K.J. (2003). Dimensionally stable wood composites and methods for making them. United States Patent, United States of America., 6569540(09/550027). Schmidt, E.L. (1991). A resin-compatible copper naphthenate to preserve aspen composites. Forest Products Journal, 41(5), 31-32. Schmidt, E.L. (1993). A review of biological agents on aspen composites and needs for future research. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 23-25. Schmidt, E.L., & Gertjejansen, R. (1988). Trials of two powdered preservatives for phenol-formaldehyde-bonded and polymeric-isocyanate-bonded aspen structural composite board. Forest Products Journal, 38(3), 19-21. Tolley, M.P., Laks, P.E., & Fears, R. (1998). Evaluation of chlorpyrifos and fungicides alone and in combination for control of insects and fungi in wood and wood composites. Document No IRG/WP 98-30187. In The International Research Group on Wood Preservation, Stockholm Sweden. Williams, G.R., & Lewis, D.A. (1989). Observations on the colonization of freshlyfelled timber treated with prophylactic chemicals by mould and sapstain fungi. Document No IRG/WP 1394. In The International Research Group on Wood Preservation, Stockholm Sweden. Yang, D.Q., Wang, X.M., & Wan, H. (2007). Biological protection of composite panel from moulds and decay. Document No IRG/WP 07-10612. In The International Research Group on Wood Preservation, Stockholm Sweden. 53 CHAPTER 4 – THE EFFECTS OF NOVEL COPPER-BASED PRESERVATIVE TECHNOLOGIES ON THE MECHANICAL AND PHYSICAL PROPERTIES OF ASPEN STRANDBOARD. Abstract The effects of biocide addition on mechanical and physical properties of aspen strandboards was investigated. Five copper-based chemicals or zinc borate were examined alone or with tebuconazole or 4,5-dichloro-2-N-octyl-4-isothiazolin-3-one (DCOI) as co-biocides. Bending properties, internal bond strength, thickness swelling and hygroscopic properties were determined according to ASTM Standard D-1037. Resistance to chemical leaching was assessed using AWPA Standard E10. Biocide addition produced no reductions in bending strength or stiffness. Internal bond strength was lower in panels treated with the liquid copper-based preservative. Slight increases in thickness swelling and hygroscopic linear change were associated with the addition of nearly all preservatives. Two copper-based preservatives were highly resistant to leaching. The results suggest that biocide addition had no significant negative effects on the properties of aspen strandboards. Introduction The use of oriented strandboard (OSB) in the North American structural panel market has continually risen since its advent in the 1970’s (SBA, 2008). OSB is composed of various sized strands that are oriented in a specific direction and pressed to a desired thickness and density. The relatively small strand dimensions permits the 54 utilization of low quality, low cost raw material that results in a high quality, low cost product. The geometry of the strands within OSB also makes the material more likely to sorb water. These sorption characteristics, coupled with the low durability of the wood species used produces a panel that is more susceptible to decay and mold attack than softwood plywood (Laks, 1999, 2002). OSB is designed as a dry-use product, although it can tolerate brief periods of wetting during construction (Morris et al., 1999). OSB is increasingly used in applications that subject it to conditions conductive to insect and fungal attack (Morrell, 2002; Morris, 1995). A number of building practices implemented in response to rising energy costs attempt to seal homes in order to limit the escape of warm or cold air. These practices reduce air exchange and can trap moisture from both interior and exterior sources (Anderson, 1972; Barnes & Amburgey, 1993; Cassens, 1978; Merrill & TenWolde, 1989). The prolonged accrual of moisture within wall cavities creates conditions conducive to mold, decay and insect attack (Barnes & Amburgey, 1993; Schmidt, 1993; Yang et al., 2007). Preservation technologies can be employed to protect wood from biological attack. Durable wood composites can be produced through the use of wood species with high natural durability, incorporating recycled treated wood, pre-process preservative treatments of the wood, post-process preservative treatments and inprocess preservative treatments (Gardner et al., 2003). The particular treatment methods employed are dependent upon the final product. In-process treatments appear to be the best treatment method for OSB. The equal distribution of the preservative 55 within the product can offer much better protection than “shell” treatments provided by post-treatments (Laks & Palardy, 1992). Pre-treating the substrate also requires an extra drying step that is energy intensive and less efficient. According to Murphy et al. (1993), the criteria for an acceptable preservative treatment process for wood composites are: • • • • • • • Efficacy – The preservative should be effective against decay fungi and wood degrading insects. Environment - The treatment operation and product should have acceptable environmental characteristics. Mechanical properties – The treatment should have no negative impacts on mechanical properties. Physical properties – Interference with physical properties, such as EMC and dimensional stability, should be minimal. Appearance – Unless it is desired for identification purposes, the treatment should not change the appearance of the wood. Speed and Flexibility – The treatment process should be as rapid as possible and be able to produce as much product to meet orders in short notice. Verification and compliance with standards – The treated material should be easily analyzed for quality control. Two of the main limiting factors for the use of some preservative systems in strand-composite panels are their effects on mechanical and physical characteristics. Vick et al. (1990) found that various waterborne systems were incompatible with phenol-formaldehyde adhesives, including ammoniacal zinc arsenate, copper naphthenate, copper octoate, zinc naphthenate, and all borate preservatives tested. Borates have a number of appealing benefits as wood preservatives, and are currently the only biocides used to produce durable OSB panels. However, borates have a few disadvantages that limit their use in composite panels. Biologically-effective treatment levels of sodium borate and boric acid react with phenol formaldehyde (PF) 56 resin to prevent sufficient adhesion between wood substrates, resulting in boards with unacceptably low mechanical and physical properties (Laks et al., 1988; Laks & Palardy, 1993). Copper-based biocides may be useful for incorporation into OSB furnish, but there is little data on the effects of these materials on panel properties. The objective of this research was to determine the effects of incorporating various copper-based preservatives into the furnish on mechanical and physical properties of aspen strandboard. Materials and Methods Panel Fabrication Commercially manufactured aspen strands obtained from Louisiana-Pacific (Newberry, MN) were dried in a commercial laundry dryer to approximately 3% moisture content (MC) and stored in plastic bags until use. Preservatives were acquired from Viance, Inc (Charlotte, NC) and Rio Tinto Minerals, Inc (Edgewood, CO). Seven chemicals were incorporated individually or in combination into board furnishes at various concentrations (Table 6) and their performance was compared to untreated negative controls and zinc borate treated positive controls. Each treatment group was replicated on six panels. Due to the size of the blender, the furnish was prepared in quantities sufficient to produce three panels per batch (strands, preservative, wax and resin). The strands were added first, and then dry salts of the treatment chemical were sprinkled over the mixture. The preservative and the strands were then blended for five minutes at 16 revolutions per minute. A touch-up paint spray gun attached to the inside of the 57 blender was used to spray the liquid copper complex onto the tumbling strands. 4,5-dichloro-2-N-octyl-4-isothiazolin-3-one (DCOI) was added to the wax emulsion. Table 6. Preservative treatments assessed for their ability to improve OSB panel durability Treatment Untreated control Zinc Borate Copper Ammonium Acetate Complex (liquid) Copper Diammine Acetate Copper Diammine Carbonate Micronized Copper Basic Copper Carbonate Copper Diammine Acetate / Tebuconazole Isothiazolone Isothiazolone / Cu Diammine Acetate Isothiazolone / Cu Ammonium Acetate (liquid) Untreated control Abbreviation Control Loading (wt/wt %) Matt MC (%) Manufacturer 0 7.4 0.585 7.4 Rio Tinto ZB 0.878 7.4 Minerals 1.17 7.3 0.25 10.2 CC 1 0.50 13.1 Viance 0.75 16.0 0.25 7.4 CC 2 0.50 7.3 Viance 0.75 7.3 0.25 7.4 CC 3 0.50 7.3 Viance 0.75 7.3 0.25 7.4 MCOH 0.50 7.3 Viance 0.75 7.3 0.25 7.4 BCC 0.50 7.4 Viance 0.75 7.3 0.5 / 0.01 7.3 CC 2 / azole 0.5 / 0.02 7.3 Viance 0.5 / 0.04 7.3 0.05 6.7 DCOI 0.05 / 0.5 6.6 Viance DCOI / CC 2 0.05 / 0.5 12.4 DCOI / CC 1 0 5.7 Control (400 seconds) A wax emulsion with 58% solids content (Hexion Specialty Chemicals; Springfield, OR) was sprayed onto the tumbling strands using the touch-up paint spray gun at a loading of 1.0% wt/wt. OSB face-resin with 48% solid content (GeorgiaPacific; Albany, OR) was then applied to the strands at a loading of 3.5% wt/wt through a spinning disk atomizer at 6000 rpm during blending. A 560mm square forming box was placed on top of a steel caul plate and blended strands were distributed in the box. No attempt was made to orient the 58 strands. The forming box was removed and a second caul plate was placed atop the formed mat. The mat and caul plates were then placed in the hot press. The hot press, with upper and lower platens set at 200º C, pressed the mat to a target thickness of 11 mm for 200 seconds. Because of the difficulties in producing acceptable boards using DCOI, press time was increased to 400 seconds for panels containing this chemical. A second untreated control group was also pressed for the extended time. The press was then vented by opening at a rate of 0.002 cm/second for 60 seconds to produce finished boards that were approximately 12.7 mm thick and had a density of approximately 577 kg/m³. Approximately 90 mm were trimmed from each edge of the board using a table saw. Biological and mechanical test specimens were cut from the panels (Figure 7). Figure 7. Cutting pattern used to produce test specimens from treated and untreated OSB panels 59 Static Bending Static bending was assessed using American Society for Testing Materials (ASTM) Standard D-1037 (ASTM, 1999). A 76 mm by 362 mm sample was cut from each panel and conditioned to constant weight at 20º C and 65% relative humidity. The samples were placed in a universal testing machine that applied a constant centerloaded force to samples at a speed of 6.24 mm/minute to failure. The resulting loaddeflection data were collected and used to calculate modulus of rupture (MOR) and modulus of elasticity (MOE). The samples were weighed after testing, oven-dried and reweighed to determine the MC at the time of the test. Twenty-five mm squares cut from one end of the sample were used to determine specific gravity (Figure 8) by measuring volume and then oven-drying and weighing the blocks. specific gravity, Gm = (W d / Vm) pw Where: W d = Oven-dry weight of wood Vm = volume at moisture content M pw = density of water Figure 8. Determination of specific gravity Internal Bond Strength Internal bond strength was determined according to ASTM Standard D-1037 (ASTM, 1999). A 50 mm square sample was cut from each board, conditioned to constant weight at 20º C and 65% relative humidity and weighed. Both surfaces were glued to aluminum alloy loading blocks designed to hold the blocks securely in the testing apparatus as a tensile force was applied at a speed of 1 mm/minute until failure. 60 After testing, the blocks were oven dried and weighed to determine moisture content. The peak stress at failure and the peak force in kPa were used to assess the effects of treatment on internal bond strength. Permanent Thickness Swell ASTM Standard D-1037 for water absorption and thickness swelling, Method A (ASTM, 1999) was used to determine the water absorption characteristics of the boards. Samples (152 mm by 152 mm) were cut from each board and conditioned to constant weight at 20º C and 65% relative humidity prior to testing. The weight, thickness and volume of each sample were measured, and then each sample was submerged horizontally in water for 2 hours. The samples were removed, allowed to dry for 10 minutes, and wiped free of excess water. The weight, thickness and volume were again measured before re-submerging the samples for another 22 hours. Weight, thickness and volume measurements were made after 24 hours of immersion, and the samples were oven dried at 103° C to determine MC at the various stages of testing. The amount of water absorbed, expressed as moisture content at each time interval, and thickness swelling, expressed as the percent of original thickness, were used to assess the effects of each treatment on panel stability. Hygroscopicity Panel hygroscopicity was determined using a modification of ASTM Standard D-1037 for linear variation with change in moisture content (ASTM, 1999). A 76 mm by 280 mm sample was cut from each board and conditioned to constant weight at 30º 61 C and 30% relative humidity. Each sample was weighed and the length was measured. The boards were conditioned to constant weight at 32º C and 90% relative humidity and then re-measured. The samples were then oven-dried at 103º C, weighed and re-measured. Moisture content and linear change following exposure to each environmental condition were used to assess the effects of treatment on hygroscopicity. Resistance to Leaching AWPA Standard E10 was used to assess the resistance of each chemical to leaching (ASTM, 1999). Test blocks (19 mm by 19 mm) were cut from each board, oven-dried and weighed in collective treatment groups prior to testing. Six samples from each treatment group were placed into a 500 ml beaker, held down by weights in 300 ml of water and placed into a desiccator. A vacuum was applied to the desiccator (13.3 kPa or less) for 30 minutes. The vacuum was then broken and the weights were removed. Leachate water was removed after 6, 24, 48 and then at 24-hour intervals thereafter for a total of 14 days and replaced with an equal amount of fresh deionized water. The blocks were then oven-dried and weighed. The six leached blocks from each treatment were ground to pass a 30 mesh screen and combined for preservative analysis. The level of each preservative component in the wood was determined using the appropriate analytical method: Copper was determined by X-ray spectroscopy according to AWPA Standard A9 (AWPA, 2006e). ZB treated wood was extracted by nitric acid digestion (AWPA, 2006f), and analyzed by Inductively Coupled Plasma Emission Spectrometry (ICP) 62 following AWPA Standard A21 (AWPA, 2006g). DCOI and tebuconazole were extracted in methanol; the resulting extracts were analyzed by High Performance Liquid Chromatography (HPLC) with UV detection, according to AWPA Standard A30 or Standard A28, respectively (AWPA, 2006h, 2006i). Statistical Analysis Differences between treatments and the control groups were assessed using a Completely Randomized Design analysis of variance using SAS 9.1 (SAS Institute, α = 0.05). Because it was important that the comparison minimize Type I errors, (i.e. to conclude something is different when it is actually the same), a Tukey’s Honestly Significant Difference multiple comparison test was used to determine differences between treatment means. Duncan’s Multiple Range Test was used prior to the Tukey’s Studentized Range Test for multiple comparisons to harmonize the mean cell size when there were unequal replications. Results and Discussion Static Bending While there were slight differences between the bending properties of preservative treated strandboard and untreated controls, the differences were not statistically significant (Table 7). The inability to delineate treatment differences was Table 7. Effects of the addition of preservatives on mechanical properties of strandboards a Internal Bond Strength Flexural Property (%) a Specific gravity MOE (Gpa) Treatment MOR (MPa) (kPa) 0.57 (0.02) a,b,c,d,e,f 4.26 (0.5) a,b,c 24.2 (4.2) a 247 (81.0) a,b,c,d,e Strandboard Control 0.585 0.56 (0.02) c,d,e,f 3.87 (0.3) c 22.2 (4.0) a 189 (47.3) a,b,c,d,e,f ZB 0.878 0.58 (0.02) a,b,c,d,e,f 4.28 (0.4) a,b,c 27.0 (4.3) a 199 (46.1) a,b,c,d,e,f 1.17 0.57 (0.03) a,b,c,d,e,f 3.73 (0.5) c 22.7 (5.4) a 254 (64.7) a,b,c,d,e 0.25 0.59 (0.02) a,b,c,d,e,f 4.60 (0.3) a,b,c 23.2 (4.2) a 95 (35.1) e,f CC 1 0.50 0.61 (0.03) a,b 4.95 (0.4) a,b,c 29.1 (2.3) a 67 (59.6) f 0.75 0.62 (0.02) a 5.18 (0.4) a,b 22.2 (9.1) a 139 (79.1) b,c,d,e,f 0.25 0.60 (0.02) a,b,c,d,e 4.79 (0.3) a,b,c 26.5 (4.0) a 225 (151.2) a,b,c,d,e,f CC 2 0.50 0.56 (0.02) b,c,d,e,f 4.11 (0.4) a,b,c 23.2 (5.5) a 244 (61.8) a,b,c,d,e,f 0.75 0.60 (0.04) a,b,c,d,e 4.29 (1.3) a,b,c 25.4 (10.3) a 143 (46.8) b,c,d,e,f 0.25 0.60 (0.02) a,b,c,d,e,f 4.57 (0.3) a,b,c 29.8 (1.7) a 271 (104.4) a,b,c,d,e CC 3 0.50 0.58 (0.02) a,b,c,d,e,f 4.30 (0.5) a,b,c 26.9 (4.2) a 257 (90.5) a,b,c,d,e 0.75 0.59 (0.03) a,b,c,d,e,f 4.51 (0.5) a,b,c 27.0 (4.1) a 301 (33.9) a,b,c 0.25 0.61 (0.03) a,b,c,d 4.90 (1.0) a,b,c 30.2 (5.4) a 299 (35.7) a,b,c MCOH 0.50 0.59 (0.03) a,b,c,d,e,f 4.66 (0.4) a,b,c 30.8 (4.8) a 342 (135.8) a 0.75 0.59 (0.02) a,b,c,d,e,f 4.76 (0.6) a,b,c 27.9 (6.5) a 310 (63.9) a,b 0.25 0.61 (0.02) a,b,c 4.90 (0.4) a,b,c 31.8 (3.0) a 287 (13.9) a,b,c,d BCC 0.50 0.58 (0.03) a,b,c,d,e,f 4.22 (0.9) a,b,c 26.4 (8.4) a 212 (108.1) a,b,c,d,e,f 0.75 0.62 (0.03) a 5.15 (0.6) a,b 31.8 (4.3) a 254 (50.4) a,b,c,d,e 0.5 / 0.01 0.61 (0.02) a,b 4.79 (0.4) a,b,c 27.3 (4.8) a 230 (84.2) a,b,c,d,e,f CC 2 / azole 0.5 / 0.02 0.56 (0.02) c,d,e,f 4.09 (0.5) a,b,c 22.6 (3.6) a 117 (28.7) d,e,f 0.5 / 0.04 0.55 (0.02) e,f 3.96 (0.5) b,c 22.7 (3.5) a 123 (33.1) c,d,e,f 0.05 0.55 (0.02) e,f 4.14 (0.6) a,b,c 25.7 (7.1) a 242 (137.5) a,b,c,d,e,f DCOI 0.05 / 0.5 0.56 (0.03) d,e,f 4.58 (0.4) a 27.7 (3.6) a 281 (45.2) a,b,c,d DCOI / CC 2 0.05 / 0.5 0.60 (0.01) a,b,c,d,e,f 5.24 (0.7) a,b,c 28.7 (5.6) a 290 (164.0) a,b,c,d DCOI / CC 1 0.55 (0.03) f 4.44 (0.8) a,b,c 28.0 (6.1) a 300 (95.4) a,b,c Strandboard Control (400 seconds) a Values represent means of 6 replicates per treatment, while figures in parentheses represent one standard deviation. Means with a common letter are not significantly different using Tukey's Studentized Range Test (α=0.05). Retention (wt/wt %) a 63 64 due to high variability within treatment groups and the use of a conservative multiple comparison tool such as Tukey’s. Strandboards treated with the liquid copper ammonium complex (CC 1) had a tendency to fail in shear, as opposed to tension, during testing. This type of failure reflects poor resin curing or low density in the center of the board where the highest shear stress concentration occurs. Insufficient resin curing was probably due to the high moisture content of the panels produced by the liquid characteristic of the preservative. The high moisture content of the strands increased heat transfer from the outer strands to the internal core, but sufficient temperatures required to cure resin might not have been reached because the water within the core prevented the temperature from exceeding 100°C. Another explanation for poor core bonding may be due to “wash out”, when the excessive moisture within the panel induces resin migration away from the board center (Geimer & Christiansen, 1996). High outer strand moisture content increased the heat exposure for resin in the outer strands, enhancing curing in the tension layers of the panels. This effect was reflected in a slightly higher MOE for panels treated with CC 1 alone or with DCOI (Figure 9). 65 Bending - Modulus of Elasticity 6.0 5.0 MOE (GPa) 4.0 3.0 2.0 1.0 2 C C D C DC O O D I/C I C O C C I/ 2 on C tro C l( 1 40 0) /a zo le C BC O H M C 3 C C 2 C C 1 C C C on tro l ZB 0.0 Figure 9. Modulus of elasticity of treated and untreated strandboards. Values represent means of 6 replicates while error bars represent one standard deviation about the mean. Zinc borate (ZB) had no significant effect on MOR or MOE. While water soluble borates, such as disodium octaborate tetrahydrate, decrease bending properties due to reductions in glue-line strength (Laks et al., 1988; Lee et al., 2001), the low water solubility of ZB limits interaction with water-containing phenolic resins, and minimizes effects on bending properties. Internal Bond Strength CC 1 was the only preservative that significantly affected internal bond strength (Table 7). Panels containing low, medium and high target retentions of CC 1 experienced 61, 73 and 44% reductions in internal bond strength, respectively. While 66 the effect was only statistically significant at the medium retention, the effects were strikingly evident (Figure 10). Reduced internal bond strength probably reflects reduced resin curing in the interior of the panels. Panels treated with DCOI and CC 1 did not experience reduced internal bond strength because these panels were pressed for 400 seconds, allowing for additional resin curing. Internal Bond Strength 500 Maximum Stress (kPa) * 400 300 200 100 2 C C D C DC O O D I/C I C O C C I/ 2 on C tro C l( 1 40 0) /a zo le C BC O H M C 3 C C 2 C C 1 C C C on tro l ZB 0 Figure 10. Internal bond strength of treated and untreated strandboards. Values represent means of 6 replicates while error bars represent one standard deviation about the mean. Previous research showed that ZB reduced internal bond strength of waferboard (Laks & Manning, 1995), while our results showed no significant differences between ZB treated and untreated panels. Lee et al (2001) found that the addition of 0.9 % ZB to phenol formaldehyde (PF) resin reduced the gel time by only 1%, but gel time was greatly reduced as the addition of ZB increased. Reduced gel 67 resin gel time results in pre-curing of the resin prior to pressing, producing poor bonding between strands. Permanent Thickness Swelling Most treatments failed to induce significant negative effects on thickness swelling following a 2 hour submersion. The addition of CC 1 at the medium target retention appeared to significantly increase swelling after 2 hours; however, the data were extremely variable (Table 8). One batch of three panels had high swelling values, while the other had low values (21 to 24% vs. 4.8 and 5.3%). The results suggest that blending may have been a problem with this treatment. The most likely cause was poor blending of the wax. The absence of effect at the lower and higher treatment levels with this system suggests that the chemical was not the cause for increased swelling. Table 8. Thickness swelling of treated and untreated strandboards after 2 or 24 hours of submersion. Thickness Swelling (%)a 2 hour submersion 24 hour submersion Treatment 5.7 (1.2) b 15.0 (1.6) c,d,e,f Strandboard Control 0.585 6.0 (1.1) b 17.2 (0.8) a,b,c,d,e ZB 0.878 6.6 (0.6) b 16.7 (1.6) a,b,c,d,e,f 1.17 6.0 (1.0) b 16.7 (2.6) a,b,c,d,e,f 0.25 6.1 (0.4) b 15.2 (0.8) b,c,d,e,f CC 1 0.50 13.9 (9.6) a 20.8 (8.3) a 0.75 6.2 (0.9) b 14.1 (1.2) c,d,e,f 0.25 8.2 (0.9) b 18.5 (1.7) a,b,c,d CC 2 0.50 7.7 (1.2) b 17.8 (1.7) a,b,c,d 0.75 7.7 (0.9) b 17.3 (1.0) a,b,c,d,e 0.25 7.4 (0.8) b 18.4 (1.0) a,b,c,d CC 3 0.50 7.3 (1.1) b 17.0 (1.8) a,b,c,d,e,f 0.75 7.6 (0.6) b 18.3 (0.8) a,b,c,d 0.25 8.2 (0.8) b 18.7 (1.0) a,b,c MCOH 0.50 8.0 (0.5) b 20.2 (2.1) a,b 0.75 9.0 (2.1) b 21.3 (3.5) a 0.25 7.4 (0.9) b 18.5 (1.9) a,b,c,d BCC 0.50 7.0 (0.5) b 17.7 (0.9) a,b,c,d 0.75 7.3 (0.7) b 19.1 (1.0) a,b,c 0.5 / 0.01 7.0 (0.9) b 17.3 (1.2) a,b,c,d,e CC 2 / azole 0.5 / 0.02 7.0 (0.4) b 17.0 (2.8) a,b,c,d,e,f 0.5 / 0.04 7.4 (0.7) b 17.8 (1.4) a,b,c,d 0.05 6.5 (0.7) b 14.8 (2.2) c,d,e,f DCOI 0.05 / 0.5 5.7 (0.7) b 12.6 (1.3) e,f DCOI / CC 2 0.05 / 0.5 5.2 (0.9) b 13.6 (1.0) d,e,f DCOI / CC 1 4.9 (0.5) b 12.0 (1.3) f Strandboard Control (400 seconds) a Values expressed as a percentage of original thickness. Values represent means of 6 blocks per treatment except micronized copper at 0.50 wt/wt% retention, which had 5. Figures in parentheses represent one standard deviation. Means with a common letter are not significantly different using Tukey's Studentized Range Test that has been harmonized by Duncans Multiple Range Test (α=0.05). Retention (wt/wt %) 68 69 Immersion for 24 hours nearly tripled the degree of swelling of the 200 second control and more than doubled the swelling for most other treatments. In general, biocide addition did not significantly affect swelling (Table 8), although swelling was significantly higher for panels with the medium target retention of CC 1, as well as medium and high target retentions of micronized copper hydroxide (MCOH). The results indicate that addition of biocides to the furnish had a tendency to increase swelling, but the increases were generally not statistically significant. Thickness Swelling - 2 hours 30% Percent Thickness Increase * 25% 20% 15% 10% 5% D O CO DC I / C I O C C I/C 2 on tro C 1 l( 40 0) /a 2 C C D C zo le C BC H M C O 3 CC C C 2 1 CC Co nt ro l ZB 0% Figure 11. Thickness swelling of treated and untreated strandboards after 2 hours of water submersion. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. 70 Thickness Swelling - 24 hours Percent Thickness Increase * * * 30% 25% 20% 15% 10% 5% D O CO DC I / C I O C C I/C 2 on tro C 1 l( 40 0) /a 2 C C D C zo le C BC H M C O 3 CC C C 2 1 CC Co nt ro l ZB 0% Figure 12. Thickness swelling of treated and untreated strandboards after 24 hours of water submersion. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. Voluntary Product Standard PS 2-04 (NIST, 2004) has no specified maximum amount of thickness swelling for OSB, but the Canadian Standard Association Standard 0437 Standards on OSB and Waferboard (CSA, 1993) stipulates a maximum swelling of 15 % for random and oriented strandboards. Except for panels treated with the high or low retentions of CC 1, all treated panels experienced swelling above the standard after 24 hours of submersion. The untreated controls pressed for 200 seconds had a swelling of exactly 15 %, which left no room for any excess swelling due to the presence of preservative. This suggests that panel variables, other than the biocidal additive, were the source for a large amount of swelling. The results indicate 71 that thickness swelling would not be a limitation to the future use of these preservatives. As expected, panel MCs after 2 and 24 hours submersion in water were similar to the thickness swelling results (Table 9). Panels treated with the medium target retention of CC 1 had much higher MCs than any other treatment. Panels with the highest target retention of MCOH had a MC of 25.1 % after 2 hours submersion, an increase of 22 % compared to the untreated control (Figure 13). The same treatment group had an MC of 60.7 % after 24 hours, 34 % higher than the untreated control (Figure 14). This increase may be due to void spaces in the panels created by the aggregation of preservative particles. Table 9. Moisture contents of treated and untreated strandboards submerged in water for 0, 2 or 24 hours Moisture Content (%)a 0 hour submersion 2 hour submersion 24 hour submersion Treatment 9.2 (0.3) a,b 20.5 (1.5) b 45.2 (5.1) b,c,d,e Strandboard Control 0.585 9.3 (0.2) a,b 21.5 (1.9) b 49.9 (2.8) a,b,c,d,e ZB 0.878 9.1 (0.3) a,b 20.4 (1.5) b 46.7 (4.2) b,c,d,e 1.17 9.0 (0.1) b 19.6 (1.3) b 44.6 (4.1) b,c,d,e 0.25 9.2 (0.2) a,b 18.4 (1.2) b 37.4 (3.0) d,e CC 1 0.50 9.4 (0.4) a,b 51.7 (38.3) a 69.3 (39.2) a 0.75 9.5 (0.2) a,b 17.5 (0.7) b 34.6 (2.2) e 0.25 9.4 (0.3) a,b 20.6 (1.5) b 48.7 (5.9) a,b,c,d,e CC 2 0.50 9.1 (0.2) b 18.4 (0.6) b 39.4 (2.0) c,d,e 0.75 9.1 (0.4) a,b 18.6 (0.7) b 38.9 (4.7) d,e 0.25 9.3 (0.1) a,b 20.6 (0.6) b 48.8 (1.3) a,b,c,d,e CC 3 0.50 9.4 (0.2) a,b 20.5 (1.4) b 45.9 (4.5) b,c,d,e 0.75 9.3 (0.1) a,b 19.6 (0.6) b 43.6 (0.9) b,c,d,e 0.25 9.3 (0.3) a,b 21.6 (1.5) b 52.6 (4.4) a,b,c,d,e MCOH 0.50 9.2 (0.3) a,b 22.1 (2.0) b 59.9 (12.6) a,b,c 0.75 9.3 (0.2) a,b 25.1 (8.4) b 60.7 (15.3) a,b 0.25 9.3 (0.2) a,b 19.8 (0.9) b 47.1 (3.2) b,c,d,e BCC 0.50 9.3 (0.1) a,b 20.8 (0.9) b 51.1 (3.6) a,b,c,d,e 0.75 9.2 (0.3) a,b 19.5 (1.2) b 46.7 (5.1) b,c,d,e 0.5 / 0.01 9.2 (0.2) a,b 19.0 (0.7) b 41.0 (1.7) b,c,d,e CC 2 / azole 0.5 / 0.02 9.4 (0.1) a,b 19.2 (0.6) b 41.3 (2.5) b,c,d,e 0.5 / 0.04 9.7 (0.1) a 19.6 (0.6) b 43.0 (2.2) b,c,d,e 0.05 8.0 (0.4) c 21.7 (1.8) b 55.8 (9.0) a,b,c,d DCOI 0.05 / 0.5 8.2 (0.3) c 18.3 (1.0) b 39.3 (2.7) c,d,e DCOI / CC 2 0.05 / 0.5 8.1 (0.6) c 17.5 (1.3) b 38.1 (3.5) d,e DCOI / CC 1 8.2 (0.2) c 19.1 (1.6) b Strandboard Control (400 seconds) a Values expressed on an oven-dry weight basis. Values represent means of 6 blocks per treatment, while figures in parentheses represent one standard deviation. Means with a common letter are not significantly different using Tukey's Studentized Range Test (α=0.05). Retention (wt/wt %) 72 73 Moisture Content - 2 hours * 80 Moisture Content (%) 70 60 50 40 30 20 10 2 C CC D D CO CO I I/ on D C tr o C O C 2 l( I 40 / C 0 C se 1 co nd s) le /a zo BC C M C O H 3 C C 2 C C 1 C C l tr o on C ZB 0 Figure 13. Moisture contents of untreated and treated strandboards after 2 hours submersion. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. 74 Moisture Content - 24 hours * 80 Moisture Content (%) 70 60 50 40 30 20 10 2 C CC D D CO CO I I/ on D C tr o C O C 2 l( I 40 / C 0 C se 1 co nd s) le /a zo BC C M C O H 3 C C 2 C C 1 C C l tr o on C ZB 0 Figure 14. Moisture contents of untreated and treated strandboards after 24 hours submersion. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. A number of the treatment groups had MCs that were lower than the untreated controls after 2 and 24 hours, despite having greater thickness swelling values. For panels treated with CC 1, this effect may have been due to the gradient of resin curing through the thickness profile. Increased curing in the outer layers limited water absorption in these strands and lowered the overall MC, while poor curing in the board center allowed strands to absorb large amounts of water that greatly increased thickness swelling. Moisture behavior in Copper Diammine Acetate Complex (CC 2) amended strandboards may have been due to the alkalinity of the preservative. Mildly alkaline treatments can alter hemicelluloses in hardwoods, causing significant increases in cell wall swelling (Zanuttini & Marzocchi, 2003; Zanuttini et al., 1999). 75 Hygroscopicity Preservatives incorporated into panels had little practical effect on the MC of panels conditioned at 30°C and 30 % relative humidity (RH) (Table 10, Figure 15), while slight MC reductions were noted when panels were conditioned at 30°C and 90 % RH (Figure 16). DCOI treated boards had the highest reductions, but these were still only 0.8 to 1.1 % MC less than the untreated control (400 seconds) at 14.0 % MC. None of the differences were statistically significant in comparison with the controls, indicating that the presence of the preservative did not affect hygroscopicity. Table 10. Moisture contents and linear changes in treated and untreated strandboards conditioned under two different temperature/relative humidity regimes. Retention (wt/wt %) a Panel Moisture Content (%) a 30°C / 30%RH 30°C / 90%RH Linear Change (%) Treatment 5.2 (0.15) b,c,d,e 14.0 (0.19) b,c,d,e,f 0.12 (0.03) b,c Strandboard Control 0.585 5.3 (0.15) b,c,d,e 13.9 (0.08) d,e,f,g,h,i,j,k 0.12 (0.06) b,c ZB 0.878 5.2 (0.08) b,c,d,e 14.2 (0.08) b,c 0.12 (0.02) b,c 1.17 5.1 (0.08) d,e 14.1 (0.10) b,c,d,e 0.10 (0.05) b,c 0.25 5.3 (0.10) b,c,d,e 13.6 (0.10) I,j,k,l 0.09 (0.06) c CC 1 0.50 5.4 (0.08) a,b,c 13.7 (0.16) f,g,h,I,j,k,l 0.13 (0.04) a,b,c 0.75 5.6 (0.08) a 13.9 (0.08) c,d,e,f,g,h,I,j 0.19 (0.09) a,b,c 0.25 5.3 (0.16) b,c,d,e 13.8 (0.23) e,f,g,h,I,j,k,l 0.22 (0.13) a,b CC 2 0.50 5.4 (0.10) a,b,c 13.8 (0.13) e,f,g,h,I,j,k 0.15 (0.03) a,b,c 0.75 5.4 (0.08) a,b 13.9 (0.12) d,e,f,g,h,i,j,k 0.16 (0.03) a,b,c 0.25 5.1 (0.10) e 13.9 (0.17) b,c,d,e,f,g,h 0.15 (0.05) a,b,c CC 3 0.50 5.2 (0.17) b,c,d,e 13.7 (0.15) h,I,j,k,l 0.19 (0.05) a,b,c 0.75 5.3 (0.19) b,c,d,e 13.7 (0.06) g,h,I,j,k,l 0.16 (0.04) a,b,c 0.25 5.2 (0.15) b,c,d,e 13.5 (0.08) l 0.19 (0.10) a,b,c MCOH 0.50 5.2 (0.08) c,d,e 13.8 (0.15) e,f,g,h,I,j,k 0.14 (0.03) a,b,c 0.75 5.2 (0.15) b,c,d,e 13.6 (0.12) j,k,l 0.13 (0.04) a,b,c 0.25 5.2 (0.05) c,d,e 14.1 (0.10) b,c,d 0.13 (0.05) a,b,c BCC 0.50 5.2 (0.06) b,c,d,e 14.2 (0.13) b 0.09 (0.06) c 0.75 5.2 (0.05) c,d,e 14.0 (0.13) b,c,d,e,f,g,h 0.25 (0.06) a 0.5 / 0.01 5.1 (0.08) d,e 14.0 (0.19) b,c,d,e,f 0.14 (0.04) a,b,c CC 2 / azole 0.5 / 0.02 5.3 (0.08) b,c,d,e 13.9 (0.15) b,c,d,e,f,g,h,i 0.14 (0.02) a,b,c 0.5 / 0.04 5.4 (0.10) b,c,d 14.0 (0.14) b,c,d,e,f,g 0.10 (0.02) b,c 0.05 4.6 (0.08) f 13.6 (0.06) I,j,k,l 0.16 (0.02) a,b,c DCOI 0.05 / 0.5 4.6 (0.08) f 13.6 (0.14) k,l 0.09 (0.03) c DCOI / CC 2 0.05 / 0.5 4.6 (0.08) f 14.0 (0.21) b,c,d,e,f,g,h 0.11 (0.04) b,c DCOI / CC 1 4.5 (0.06) f 14.8 (0.18) a 0.11 (0.07) b,c Strandboard Control (400 seconds) a Values represent means of 6 blocks per treatment, except Copper Diammine Carbonate Complex at 0.25 wt/wt% retention, which had 4. Figures in parentheses represent one standard deviation. Means with a common letter are not significantly different using Tukey's Studentized Range Test that has been harmonized by Duncans Multiple Range Test (α=0.05). 76 77 Moisture Content at 30°C & 30% RH 16 14 12 MC (%) 10 8 * 6 4 2 2 C C D C DC O O D I/C I C C O C I/ 2 on C tro C l( 1 40 0) /a zo le C BC O H M C 3 C C 2 C C 1 C C C on tro l ZB 0 Figure 15. Moisture contents of treated and untreated strandboards conditioned at 30°C and 30% RH conditioning room environments. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. 78 Moisture Content at 30°C & 90% RH 16 * * * * * * * * 14 12 MC (%) 10 8 6 4 2 2 C C D C DC O O D I/C I C C O C I/ 2 on C tro C l( 1 40 0) /a zo le C BC O H M C 3 C C 2 C C 1 C C C on tro l ZB 0 Figure 16. Moisture contents of treated and untreated strandboards conditioned at 30°C and 90% RH conditioning room environments. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. Linear change represented the difference in panel length after a sample was transferred from the 30°C and 30% RH environment to an environment at 30°C and 90% RH (Table 10). Linear changes in many treatment groups were greater than the controls, but the differences were only significant in panels treated with the highest retention of BCC (Figure 17). The voluntary product standard PS 2-04 Performance Standard for Wood-Based Structural Use Panels states that “The free panel linear expansion shall be no more than 0.30% along the panel strength axis and 0.35% across the panel strength axis” (NIST, 2004). While it was difficult to compare our nonoriented strandboards to standard OSB, the results suggest that treatment did not have a significant negative effect on linear expansion. 79 Linear Change due to Changes in MC Percent Increase in Length (%) 0.40 * 0.35 0.30 0.25 0.20 0.15 0.10 0.05 D O CO DC I / C I O C C I/C 2 on tro C 1 l( 40 0) /a 2 CC D C zo le C BC H M CO 3 C C 2 CC 1 CC ZB C on tro l 0.00 Figure 17. Linear expansion with change in moisture content of treated and untreated strandboards conditioned at 30°C and 30% RH, then 30°C and 90% RH. Values represent means of 6 replicates, while error bars represent one standard deviation about the mean. Resistance to Leaching CC 1 or CC 2 provided strong resistance to chemical leaching (Table 11). All treatments levels of CC 1 or CC 2 alone experienced 5% or less loss of copper solids. Chemical analysis showed an increase in copper solids due to leaching of panels treated with CC 3 or MCOH. This increase was likely due the sampling of panels with high variations in preservative concentration. The organic preservatives had a tendency to leach from panels, regardless of the presence of a co-biocide. Panels treated with tebuconazole lost between 18 and 29% of active chemical while those 80 treated with DCOI lost between 21 and 28% isothiazolone. These results differ from previous research that found tebuconazole to be leach resistant from small solid wood blocks treated with copper azole (Fox et al., 1994). Resistance to leaching is a desirable preservative attribute, and is beneficial for future development of CC 1 and CC 2 for wood-composite panel treatements. Table 11. Resistance of treated strandboards to chemical leaching after 14 days in an AWPA E10 leaching test. Actual Retention (wt/wt %) Treatment Strandboard Control ZB CC 1 CC 2 CC 3 MCOH BCC CC 2 / azole a Target Retention (wt/wt %) Non-leached Leached Chemical Leached (%) 0.585 0.878 1.17 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.25 0.50 0.75 0.5 / 0.01 0.5 / 0.02 0.5 / 0.04 0.05 0.05 / 0.5 0.05 / 0.5 0.86 1.22 1.88 0.183 0.332 0.486 0.088 0.146 0.292 0.095 0.226 0.353 0.039 0.055 0.115 0.095 0.168 0.238 0.189 / 0.006 0.217 / 0.012 0.235 / 0.024 0.024 0.025 / 0.164 0.027 / 0.375 0.57 0.90 1.30 0.174 0.331 0.472 0.090 0.142 0.287 0.122 0.239 0.382 0.053 0.131 0.243 0.078 0.153 0.266 0.171 / 0.005 0.209 / 0.010 0.185 / 0.019 0.019 0.018 / 0.150 0.020 / 0.354 34 26 31 5 0 3 -2 3 2 -29 -6 -8 -36 -138 -111 18 9 -12 10 / 28 4 / 18 21 / 22 21 28 / 9 25 / 6 DCOI DCOI / CC 2 DCOI / CC 1 Strandboard Control (400 seconds) a Values represent the combination of six treatment blocks analyzed by appropriate method. Conclusions The addition of preservatives had negligible effects on the mechanical and physical properties of aspen strandboards. The results suggest that incorporation of 81 alkaline copper based biocides to the furnish prior to pressing represents a simple, effective method for enhancing panel durability without adversely affecting properties. References Anderson, L.O. (1972). Condensation problems: Their prevention and solution. In U.S. Forest Products Laboratory. U.S.D.A Forest Service Research Paper (Vol. FPL 132, pp. 36 ): Madison, WI ASTM. (1999). D1037-99 - Wood Standard test methods for evaluating properties of wood-based fiber and particle panel materials. In Annual Book of ASTM Standards (Vol. 4.10). West Conshocken,PA. AWPA. (2006e). A9-01. Standard method for analyzsis of treated wood and treating solutions by X-ray spectroscopy. In AWPA Book of Standards. Granbury, TX. AWPA. (2006f). A7-04. Standard for wet ashing procedures for preparing wood for chemical analysis. In AWPA Book of Standards. Granbury, TX. AWPA. (2006g). A21-00. Standard Method for the analysis of wood and wood treating solutions by inductively coupled plasma emission spectrometry. In AWPA Book of Standards. Granbury, TX. AWPA. (2006h). A30-00. Standard method for the determination of 4,5 Dichloro-2-Noctyl-4-isothiazolin-3-one (RH-287) in wood by high performance liquid chromatography (HPLC). In AWPA Book of Standards. Grandbury, TX. AWPA. (2006i). A28-05. Standard method for determinination of propiconazole and tebuconazole in wood, in waterborne formulations and in treating solutions by HPLC. In AWPA Book of Standards: Grandbury, TX. Barnes, H.M., & Amburgey, T.L. (1993). Technologies for the protection of wood composites. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products, Forest Products Society, Madison, WI. pp. 7-11. Cassens, D.L. (1978). Importance of Wood Deterioration in Single-Family Residences for East Baton Rouge Parish, Louisiana. Forest Products Journal, 28(8), 19-24. CSA. (1993). 0437 Series-93 - Standards on OSB and Waferboard. Rexdale (Toronto), Ontario, Canada: Canadian Standards Association. 82 Fox, R.F., Pasek, E.A., & Deshan, P.N. (1994). Copper azole wood preservatives. In Proposal to the American Wood Preservers’ Association Committees to include Copper Azole Type A in AWPA Standard P-5., Conley, GA. Gardner, D.J., Tascioglu, C., & Wålinder, M.E.P. (2003). Wood composite protection. Washington, DC: American Chemical Society: Distributed by Oxford University Press. Geimer, R.L., & Christiansen, A.W. (1996). Critical variables in the rapid cure and bonding of phenolic resins. Forest Products Journal, 46(11/12), 67-72. Laks, P.E. (1999). The past, present, and future of preservative-containing composites. In Proceedings: The International Particleboard/Composite Materials Symposium pp. 151-158. Laks, P.E. (2002). Biodegradation susceptibility of untreated engineered wood products. In Proceedings: Enhancing the durability of lumber and engineered wood products pp. 125-130. Laks, P.E., Haataja, B.A., Palardy, R.D., & Bianchini, R.J. (1988). Evaluation of adhesives for bonding borate-treated flakeboards. Forest Products Journal, 38(11/12), 23-24. Laks, P.E., & Manning, M.J. (1995). Preservation of wood composites with zinc borate. Document No IRG/WP 95-30074. In The International Research Group on Wood Preservation, Stockholm Sweden. Laks, P.E., & Palardy, R.D. (1992). Factors that affect the performance of preservative-containing wafer-based composites. In Proceedings: Pacific Rim Bio-Based Composite Symposium pp. 163-171. Laks, P.E., & Palardy, R.D. (1993). Properties and process considerations for preservative-containing waferboard. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 12-17. Lee, S., Wu, Q.L., & Strickland, B. (2001). The Influence of Flake Chemical Properties and Zinc Borate on Gel Time of Phenolic Resin for Oriented Strandboard. Wood and Fiber Science, 33(3), 425-436. Merrill, J.L., & TenWolde, A. (1989). Overview of moisture-related damage in one group of Wisconsin manufactured homes. Ashrae Transactions, 95, 405-414. Morrell, J.J. (2002). Wood-based building components: what have we learned? International Biodeterioration & Biodegradation, 49(4), 253-258. 83 Morris, P.I. (1995). Processes to improve the durability of OBS. Edmonton, Alberta: Alberta Land and Forest Service. Morris, P.I., Clark, J.E., Minchin, D., & Wellwood, R. (1999). Upgrading the fungal resistance of OSB. Document No IRG/WP 99-40138. In The International Research Group on Wood Preservation, Stockholm Sweden. Murphy, R.J., Dickinson, D.J., Turner, P., Wickens, P.J., & Hashim, R. (1993). Vapor Boron Treatment of Wood Composites. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 49-56. NIST. (2004). Voluntary Product Standard PS 2-04 - Performance Standard for WoodBased Structural-Use Panels. Washington, DC: National Institute of Standards and Technology. SBA, S.B.A. (2007, September 4, 2007). OSB Guide, from http://www.osbguide.com/index.html Schmidt, E.L. (1993). A review of biological agents on aspen composites and needs for future research. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 23-25. Vick, C.B., De Groot, R.C., & Youngquist, J.A. (1990). Compatibility of nonacidic waterborne preservatives with phenol-formaldehyde adhesive. Forest Products Journal, 40(2), 16-22. Yang, D.Q., Wang, X.M., & Wan, H. (2007). Biological protection of composite panel from moulds and decay. Document No IRG/WP 07-10612. In The International Research Group on Wood Preservation, Stockholm Sweden. Zanuttini, M., & Marzocchi, V. (2003). Alkaline Chemi-Mechanical Pulp from Poplar. Relationship between Chemical State, Swelling and Papermaking Properties. Holzforschung(57), 489-495. Zanuttini, M., Marzocchi, V., & Citroni, M. (1999). Alkaline treatment of poplar wood. Holz als Roh- und Werkstoff(57), 185-190. 84 CHAPTER 5 – GENERAL CONCLUSIONS Nearly all preservative treatment systems were effective against brown or white rot decay fungi except all treatment levels of MCOH or DCOI alone. Unacceptable weight losses were incurred for panels treated to the lowest retention levels of CC 2, CC 3 and BCC. Panels treated with tebuconazole and CC 2 provided excellent protection, but the effect of the tebuconazole on panel durability could not be established. The best protection appeared to be achieved through the use of CC 1 combined with DCOI, although the results were not statistically better than other effective treatments. Most preservative treatments failed to reduce the amount of surface mold growth, except DCOI. CC 1 and DCOI provided the best mold protection. Preservative addition had no significant negative effects on the mechanical and physical properties of most aspen strandboards tested. Slight increases in MOE and substantial decreases in internal bond strength were observed for panels treated with CC 1. Increasing panel press time may alleviate this problem. Treated panels tended to swell more than untreated controls, but the effect did not appear to be due to of the biocidal additive. Preservative treated panels were less hygroscopic than untreated controls when conditioned to high and low humidity environments. Linear expansion of some treated panels increased slightly, but all were well below the maximum acceptable thickness swelling value. Incorporation of biocides into panels should not appreciably affect mechanical or physical properties. All three copper complex systems were effective against decay fungi, while panels treated with CC 1 and isothiazolone offered the best protection against mold and decay fungi. Ground 85 proximity and termite field tests, are underway to more fully assess the resistance of these materials to biological attack. 86 BIBLIOGRAPHY Acda, M.N., Morrell, J.J., & Levien, K.L. (1996). Decay resistance of composites following supercritical fluid impregnation with tebuconazole. Material und Organismen, 30(4), 293-300. Anderson, L.O. (1972). Condensation problems: Their prevention and solution. In U.S. Forest Products Laboratory. U.S.D.A Forest Service Research Paper (Vol. FPL 132, pp. 36 ): Madison, WI ASTM. (1999). D1037-99 - Wood Standard test methods for evaluating properties of wood-based fiber and particle panel materials. In Annual Book of ASTM Standards (Vol. 4.10). West Conshocken,PA. AWPA. (2006a). E10-06. Standard method of testing wood preservatives by laboratory soil-block cultures. In AWPA Book of Standards. Granbury, TX. AWPA. (2006b). E24-06. Standard method of evaluating the resistance of wood product surfaces to mold growth. In AWPA Book of Standards. Granbury, TX. AWPA. (2006c). E18-06. Standard field test for evalutaion of wood preservatives intended for use category 3B applications exposed, out of ground contact, uncoated ground proximity decay method. In AWPA Book of Standards. Granbury, TX. AWPA. (2006d). E9-06. Standard field test for the evaluation of wood preservatives to be used in non-soil contact. In AWPA Book of Standards. Granbury, TX. AWPA. (2006e). A9-01. Standard method for analyzsis of treated wood and treating solutions by X-ray spectroscopy. In AWPA Book of Standards. Granbury, TX. AWPA. (2006f). A7-04. Standard for wet ashing procedures for preparing wood for chemical analysis. In AWPA Book of Standards. Granbury, TX. AWPA. (2006g). A21-00. Standard Method for the analysis of wood and wood treating solutions by inductively coupled plasma emission spectrometry. In AWPA Book of Standards. Granbury, TX. AWPA. (2006h). A30-00. Standard method for the determination of 4,5 Dichloro-2-Noctyl-4-isothiazolin-3-one (RH-287) in wood by high performance liquid chromatography (HPLC). In AWPA Book of Standards. Grandbury, TX. AWPA. (2006i). A28-05. Standard method for determinination of propiconazole and tebuconazole in wood, in waterborne formulations and in treating solutions by HPLC. In AWPA Book of Standards: Grandbury, TX. 87 Barnes, H.M., & Amburgey, T.L. (1993). Technologies for the protection of wood composites. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products, Forest Products Society, Madison, WI. pp. 7-11. Boggio, K., & Gertjejansen, R. (1982). Influence of ACA and CCA waterborne preservatives on the properties of aspen waferboard. Forest Products Journal, 32(3), 22-26. Burch, D.M., Contreras, A.G., & Treado, S.J. (1979). The use of low-moisturepermeability insulation as an exterior retrofit system - a condensation study. Ashrae Transactions, 85(2), 547-562. Burch, D.M., & Treado, S.J. (1978). A technique for protection retrofitted wood frame walls from condensation damage. Ashrae Transactions, 84(1), 197-206. Cassens, D.L. (1978). Importance of Wood Deterioration in Single-Family Residences for East Baton Rouge Parish, Louisiana. Forest Products Journal, 28(8), 19-24. CDC. (2000). Update: Pulmonary hemorrhage / hemosiderosis among infants— Cleveland, Ohio, 1993-1996. Morbidity and Mortality Weekly Report, 49(09), 180-184. Chung, W., Wi, S., Bae, H., & Park, B. (1999). Microscopic observation of woodbased composites exposed to fungal deterioration. Journal of Wood Science, 45(1), 64-68. Clausen, C.A., & Yang, V.W. (2003). Mold inhibition on unseasoned southern pine. Document No IRG/WP 03-10465. In The International Research Group on Wood Preservation, Stockholm Sweden. Clausen, C.A., & Yang, V.W. (2004). Multicomponent biocide systems protect wood from decay fungi, mold fungi, and termites for interior applications. Document No IRG/WP 04-30333. In The International Research Group on Wood Preservation, Stockholm Sweden. Clausen, C.A., & Yang, V.W. (2005). Azole-based antimycotic agents inhibit mold on unseasoned pine. International Biodeterioration & Biodegradation, 55, 99-102. Clausen, C.A., & Yang, V.W. (2007). Protecting wood from mould, decay, and termites with multi-component biocide systems. International Biodeterioration & Biodegradation, 59, 20-24. CSA. (1993). 0437 Series-93 - Standards on OSB and Waferboard. Rexdale (Toronto), Ontario, Canada: Canadian Standards Association. 88 Eaton, R.A., & Hale, M.D. (1993). Wood: Decay, Pests and Prevention. London, New York: Chapman & Hall. Fogel, J.L., & Lloyd, J.D. (2002). Mold performance of some construction products with and without borates. Forest Products Journal, 52(2), 38-43. Fox, R.F., Pasek, E.A., & Deshan, P.N. (1994). Copper azole wood preservatives. In Proposal to the American Wood Preservers’ Association Committees to include Copper Azole Type A in AWPA Standard P-5., Conley, GA. Freeman, M.H. (2008). Wood Preservative Formulation Developement and Systems: Organic- and Inorganic-Based Systems In T.P. Schultz, H. Militz, M.H. Freeman, B. Goodell, & D.D. Nicholas (Eds.), Developement of Commercial Wood Preservatives: Efficacy, Environmental, and Health Issues. Washington, DC: American Chemical Society. Gardner, D.J., Tascioglu, C., & Wålinder, M.E.P. (2003). Wood composite protection. Washington, DC: American Chemical Society: Distributed by Oxford University Press. Geimer, R.L., & Christiansen, A.W. (1996). Critical variables in the rapid cure and bonding of phenolic resins. Forest Products Journal, 46(11/12), 67-72. Goodell, B., Qian, Y., & Jellison, J. (2008). Fungal Decay of Wood: Soft Rot - Brown Rot - White Rot. In T.P. Schultz, H. Militz, M.H. Freeman, B. Goodell, & D.D. Nicholas (Eds.), Development of Commercial Wood Preservatives: Efficacy, Environmental, and Health Issues (pp. 9-31). Washington, DC: American Chemical Society. Goroyias, G.J., & Hale, M.D. (2000). Effect of point of preservative addition on the mechanical and physical properties of strandboard treated with Tanalith 3485. Document No IRG/WP 00-40152. In The International Research Group on Wood Preservation, Stockholm Sweden. Hall, H.J., Gertjejansen, R., Schmidt, E.L., Carll, C.G., & De Groot, R.C. (1982). Preservative treatment effects on mechanical and thickness swell properties of aspen waferboard. Forest Products Journal, 32(11/12), 19-26. Hawley, L.F., Fleck, L.C., & Richards, C.A. (1924). The relation between durability and chemical composition in wood. Industrial and Engineering Chemistry(16), 699-706. Hegarty, B.M., Yu, B., & Leightley, L.E. (1997). The suitability of isothiazolone microemulsions as long term wood preservatives. Document No IRG/WP 97- 89 30150. In The International Research Group on Wood Preservation, Stockholm Sweden. Highley, T.L., Clausen, C.A., Croan, S.C., Green, F., III, Illman, B.L., & Micales, J.A. (1994). Research on biodeterioration of wood, 1987-1992. I. Decay mechanisms and biocontrol. Research Paper - Forest Products Laboratory, USDA Forest Service, Madison WI, No. FPL-RP-529, 20. IOM. (2004). Damp Indoor Spaces and Health. Committee on Damp Indoor Spaces and Health, Board of Health Promotion and Disease Prevention, Institute of Medicine. National Academies Press. Washington, DC. Jacobs, D.E., Friedman, W., Ashley, P., & McNairy, M. (1999). The healthy homes initiative: A preliminary plan. U.S. Dept. of Housing and Urban Development, Washington, D.C., 1-82. Jeihooni, A., Krahmer, R.L., & Morrell, J.J. (1993). Microdistribution of Chromated Copper Arsenate in Douglas-fir Flakeboard. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 93-99. Jeihooni, A., Krahmer, R.L., & Morrell, J.J. (1994). Properties and decay resistance of preservative-treated Douglas-fir flakeboard. Wood and Fiber Science, 26(2), 178-184. Kartal, N. (2007). Mold resistance of heat-treated wood. Document No IRG/WP 0740358. In The International Research Group on Wood Preservation, Stockholm Sweden. Kirkpatrick, J.W., & Barnes, H.M. (2006a). Copper naphthenate treatments for engineered wood composite panels. Bioresource Technology, 97(15), 19591963. Kirkpatrick, J.W., & Barnes, H.M. (2006b). Biocide Treatments for Wood Composites―A Review. Document No IRG/WP 06-40323. In The International Research Group on Wood Preservation, Stockholm Sweden. Kumar, S., & Morrell, J.J. (1993). Improved composites from chemically modified particles. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 33-37. Laks, P.E. (1999). The past, present, and future of preservative-containing composites. In Proceedings: The International Particleboard/Composite Materials Symposium pp. 151-158. 90 Laks, P.E. (2002). Biodegradation susceptibility of untreated engineered wood products. In Proceedings: Enhancing the durability of lumber and engineered wood products pp. 125-130. Laks, P.E., Haataja, B.A., Palardy, R.D., & Bianchini, R.J. (1988). Evaluation of adhesives for bonding borate-treated flakeboards. Forest Products Journal, 38(11/12), 23-24. Laks, P.E., & Manning, M.J. (1995). Preservation of wood composites with zinc borate. Document No IRG/WP 95-30074. In The International Research Group on Wood Preservation, Stockholm Sweden. Laks, P.E., & Palardy, R.D. (1990a). Bonding and process considerations for preservative-containing waferboard. In Wood adhesives 1990 : Proceedings of a symposium sponsored by USDA Forest Service, Forest Products Laboratory and the Forest Products Research Society Madison, WI. pp. 150-154. Laks, P.E., & Palardy, R.D. (1990b). The development of borate-containing flakeboard. In Proceedings: The International Conference on Wood Protection with Diffusable Preservatives, Forest Products Society, Madison, WI pp. 7679. Laks, P.E., & Palardy, R.D. (1992). Factors that affect the performance of preservative-containing wafer-based composites. In Proceedings: Pacific Rim Bio-Based Composite Symposium pp. 163-171. Laks, P.E., & Palardy, R.D. (1993). Properties and process considerations for preservative-containing waferboard. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 12-17. Laks, P.E., Pruner, M.S., Pickens, J.B., & Woods, T.L. (1992). Efficacy of chlorothalonil against 15 wood decay fungi. Forest Products Journal, 42(9), 3338. Laks, P.E., Richter, D.L., & Larkin, G.M. (2002). Fungal susceptibility of interior commercial building panels. Forest Products Journal, 52(5), 41-44. Laks, P.E., Woods, T.L., & Richter, D.L. (1992). Evaluation of chlorothalonil for stain and mould control on lumber. Document No IRG/WP 92-3713. In The International Research Group on Wood Preservation, Stockholm Sweden. Lee, S., Wu, Q.L., & Strickland, B. (2001). The Influence of Flake Chemical Properties and Zinc Borate on Gel Time of Phenolic Resin for Oriented Strandboard. Wood and Fiber Science, 33(3), 425-436. 91 Leightley, L.E., & Nicholas, D.D. (1990). In ground performance of wood treated with a substituted isothiazolone. Document No IRG/WP 3612. In The International Research Group on Wood Preservation, Stockholm Sweden. Li, W., Shupe, T.F., & Hse, C.Y. (2004). Physical and mechanical properties of flakeboard produced from recycled CCA-treated wood. Forest Products Journal, 54(2), 89-94. Manning, M.J., & Laks, P.E. (1996). Zinc borate - a preservative treatment for composites. In Proceedings: Seventeenth Annual Meeting of the Canadian Wood Preservation Association pp. 123-133. Mengeloglu, F., & Gardner, D.J. (2000). Recycled CCA-treated lumber in flakeboards: evaluation of adhesives and flakes. Forest Products Journal, 50(2), 41-45. Merriam-Webster's. (1993). Collegiate Dictionary (10th ed.). Springfield, Mass., U.S.A: Merriam-Webster. Merrill, J.L., & TenWolde, A. (1989). Overview of moisture-related damage in one group of Wisconsin manufactured homes. Ashrae Transactions, 95, 405-414. Micales-Glaeser, J.A., Lloyd, J.D., & Woods, T.L. (2004). Efficacy of Didecyl Dimethyl Ammonium Chloride (DDAC), Disodium Octaborate Tetrahydrate (DOT), and Chlorothalonil (CTL) against Common Mold Fungi. Document No IRG/WP 04-30338. In The International Research Group on Wood Preservation, Stockholm Sweden. Morrell, J.J. (2002). Wood-based building components: what have we learned? International Biodeterioration & Biodegradation, 49(4), 253-258. Morrell, J.J. (2004). Mold on Treated Wood. In American Wood-Preservers' Association, Vancouver, B.C. pp. 84-87. Morrell, J.J., Acda, M.N., & Zahora, A.R. (2005). Performance of Oriented Strandboard, Medium Density Fiberboard, Plywood, and Particleboard Treated with Tebuconazole in Supercritical Carbon Dioxide. Document No IRG/WP 05-30364. In The International Research Group on Wood Preservation, Stockholm Sweden. Morris, P.I. (1995). Processes to improve the durability of OBS. Edmonton, Alberta: Alberta Land and Forest Service. Morris, P.I. (1997). Moisture Problems in Vancouver Condominiums. In Proceedings: The Structural Board Association Annual Meeting pp. 1-14. 92 Morris, P.I., Clark, J.E., Minchin, D., & Wellwood, R. (1999). Upgrading the fungal resistance of OSB. Document No IRG/WP 99-40138. In The International Research Group on Wood Preservation, Stockholm Sweden. Murphy, R.J., & Dickinson, D.J. (1997). Wood preservation research - what have we learnt and where are we going? Journal of the Institute of Wood Science, 14(3), 147-153. Murphy, R.J., Dickinson, D.J., Turner, P., Wickens, P.J., & Hashim, R. (1993). Vapor Boron Treatment of Wood Composites. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 49-56. Murphy, R.J., & Turner, P. (1989). A vapour phase preservative treatment of manufactured wood based board materials. Wood Science and Technology, 23(3), 273-279. Nicholas, D.D., Preston, A.F., Greenley, D.E., & Parikh, S.V. (1984). Evaluation of substituted isothiazolone as a potential new wood preservative. Document No IRG/WP 3306. In The International Research Group on Wood Preservation, Ronneby Brunn, Sweden. Nicholas, D.D., Williams, A.D., Preston, A.F., & Zhang, S. (1991). Distribution and permanency of DDAC in southern pine sapwood treated by the full-cell process. Forest Products Journal, 41(1), 41-45. Nielsen, K.F., Holm, G., Uttrup, L.P., & Nielsen, P.A. (2004). Mould growth on building materials under low water activities. Infuence of humidity and temperature on fungal growth and secondary metabolism. International Biodeterioration & Biodegradation, 54, 325-336. NIST. (2004). Voluntary Product Standard PS 2-04 - Performance Standard for WoodBased Structural-Use Panels. Washington, DC: National Institute of Standards and Technology. Norton, J., & Stephens, L. (2007). Bifenthrin recovery from glue-line-treated plywood. Document No IRG/WP 07-20355. In The International Research Group on Wood Preservation, Stockholm Sweden. Okino, E.Y.A., Souza, M.R.d., Santana, M.A.E., Alves, M.V.d.S., Sousa, M.E.d., & Teixeira, D.E. (2004). Evaluation of the physical and biological properties of particleboard and flakeboard made from Cupressus spp. International Biodeterioration & Biodegradation, 53(1), 1-5. 93 Paul, W., Ohlmeyer, M., Leithoff, H., Boonstra, M.J., & Pizzi, A. (2006). Optimising the properties of OSB by a one-step heat pre-treatment process. Holz als Roh- und Werkstoff, 64(3), 227-234. Preston, A.F., Fowlie, D.A., & Archer, K.J. (2003). Dimensionally stable wood composites and methods for making them. United States Patent, United States of America., 6569540(09/550027). Ross, A.S., Ward, H., & Smith, W.R. (2003). New generation of preservation treatments for wood-based panels and other engineered wood products. In European Panel Products Conference, Wales, UK. pp. 8. Rowell, R.M., Dawson, B.S., Hadi, Y.S., Nicholas, D.D., Nilsson, T., Plackett, D.V., et al. (1997). Worldwide in-ground stake test of acetylated composite boards. Document No IRG/WP 97-40088. In The International Research Group on Wood Preservation, Stockholm Sweden. Ruddick, J.N.R., & Sam, A.R.H. (1982). Leachability of didecyl dimethyl ammonium chloride (a quaternary ammonium compound) from four wood species. Document No IRG/WP 3204. In The International Research Group on Wood Preservation, Stockholm Sweden. Rustenburg. (1995). Bifenthrin, a new insecticide for the control of termites and woodboring insects. Document No IRG/WP 95-30076. In The International Research Group on Wood Preservation, Stockholm Sweden. SBA. (2008, May 27, 2008). OSB Guide. The Structural Board Association, from http://www.osbguide.com/index.html Scheffer, T.C., & Cowling, E.B. (1966). Natural resistance of wood to microbial deterioration. Ann. Rev. Phytopath., 4, 147-170. Scheffer, T.C., & Moses, C.S. (1993). Survey of moisture content in houses for evidence of decay susceptibility. Forest Products Journal, 43(11/12), 45-51. Schmidt, E.L. (1991). A resin-compatible copper naphthenate to preserve aspen composites. Forest Products Journal, 41(5), 31-32. Schmidt, E.L. (1993). A review of biological agents on aspen composites and needs for future research. In Proceedings: International Union of Forestry Research Organization (IUFRO) Symposium on the Protection of Wood-Based Composite Products pp. 23-25. Schmidt, E.L., & Gertjejansen, R. (1988). Trials of two powdered preservatives for phenol-formaldehyde-bonded and polymeric-isocyanate-bonded aspen structural composite board. Forest Products Journal, 38(3), 19-21. 94 Seborg, R.M., Tarkow, H., & Stamm, A.J. (1953). Effect of heat upon the dimensional stabilization of wood. Forest Products Journal(3), 59-67. Sherwood, G.E. (1983). Condensation potential in high thermal performance walls cold winter climate. In Research paper FPL 433 - United States Department of Agriculture, Forest Service, Forest Products Laboratory pp. 20. Shires, S., Héloir, P., Chen, B., & Rustenburg, G. (1996). New research data confirming the suitability of bifenthrin as a wood preservative. Document No IRG/WP 96-30116. In The International Research Group on Wood Preservation, Stockholm Sweden. Smith, R.L., & Shiau, R.-J. (1998). An industry evaluation of the reuse, recycling, and reduction of spent CCA wood products. Forest Products Journal, 48(2), 44-48. Stamm, A.J. (1956). Thermal degradation of wood and cellulose. Ind. Eng. Chem(48), 413-417. Tjeerdsma, B.F., Boonstra, M., Pizzi, A., Tekely, P., & Militz, H. (1998). Characterization of thermally modified wood: molecular reasons for wood performance improvement. Holz als Roh- und Werkstoff(56), 149-153. Tolley, M.P., Laks, P.E., & Fears, R. (1998). Evaluation of chlorpyrifos and fungicides alone and in combination for control of insects and fungi in wood and wood composites. Document No IRG/WP 98-30187. In The International Research Group on Wood Preservation, Stockholm Sweden. Tsongas, G.A. (1980). A field study of moisture damage in walls insulated without a vapor barrier. Oak Ridge, TN: Oak Ridge National Laboratory. Tsongas, G.A. (1986). The Spokane wall insulation project - a field study of moisture damage in walls insulated without a vapor barrier. Atlanta, GA: ASHRAE. Vick, C.B., De Groot, R.C., & Youngquist, J.A. (1990). Compatibility of nonacidic waterborne preservatives with phenol-formaldehyde adhesive. Forest Products Journal, 40(2), 16-22. Vick, C.B., Geimer, R.L., & Wood Jr., J.E. (1996). Surface tension, adhesive wettability, and bondability of artificially weathered CCA-treated southern pine. Forest Products Journal, 46(11/12), 89-91. Wang, Q. (1993). Growth of mould and stain fungi on wood-based boards in relation to temperature and relative humidity. Material und Organismen, 28(2), 81-103. Williams, G.R., & Lewis, D.A. (1989). Observations on the colonization of freshlyfelled timber treated with prophylactic chemicals by mould and sapstain fungi. 95 Document No IRG/WP 1394. In The International Research Group on Wood Preservation, Stockholm Sweden. Woods, T.L., & Klaver, C.J. (1992). Evaluation of the effectiveness of Tuff Brite C in the control of sapstain in laboratory and field tests. Document No IRG/WP 923718. In The International Research Group on Wood Preservation, Stockholm Sweden. Woods, T.L., Laks, P.E., Blewett, T.C., & Fears, R. (1995). A combination of chlorothalonil and chlorpyrifos for more effective wood preservation. In Proceedings: American Wood-Preservers' Association pp. 22-43. Wu, Q. (2004). Preservative-treated Structural Wood Composites For Durable Home Construction. In NSF and HUD Housing Research Workshop, Orlando, Florida. Yang, D.Q., Wang, X.M., & Wan, H. (2007). Biological protection of composite panel from moulds and decay. Document No IRG/WP 07-10612. In The International Research Group on Wood Preservation, Stockholm Sweden. Yu, B. (1997). Determination of thermal degradation of isothiazolone treated wood. Document No IRG/WP 97-30154. In The International Research Group on Wood Preservation, Stockholm Sweden. Yu, B., & Leightley, L.E. (1992). Microemulsion formations for wood preservation. Document No IRG/WP 93-30030. In The International Research Group on Wood Preservation, Stockholm Sweden. Yu, Z., & Ruddick, J.N.R. (1995). The effect of didecyldimethylammonium chloride on growth of different strains of mould fungus Gliocladium roseum. Document No IRG/WP 95-10105. In The International Research Group on Wood Preservation, Stockholm Sweden. Zabel, R.A., & Morrell, J.J. (1992). Wood Microbiology: Decay and Its Prevention. San Diego, CA: Academic Press, Inc. Zanuttini, M., & Marzocchi, V. (2003). Alkaline Chemi-Mechanical Pulp from Poplar. Relationship between Chemical State, Swelling and Papermaking Properties. Holzforschung(57), 489-495. Zanuttini, M., Marzocchi, V., & Citroni, M. (1999). Alkaline treatment of poplar wood. Holz als Roh- und Werkstoff(57), 185-190. Zhang, H.J., Gardner, D.J., Wang, J.Z., & Shi, Q. (1997). Surface tension, adhesive wettability, and bondability of artificially weathered CCA-treated southern pine. Forest Products Journal, 47(10), 69-72. 96 APPENDICES Appendix A – Statistical Output Decay Resistance of OSB to G. trabeum 10 11:31 Monday, April 28, 2008 The GLM Procedure Class Level Information Class Levels treatment 25 26 27 27 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 Number of Observations Read Number of Observations Used 160 158 Decay Resistance of OSB to G. trabeum 11 11:31 Monday, April 28, 2008 The GLM Procedure Dependent Variable: weight_loss DF Sum of Squares Mean Square F Value Model <.0001 26 67268.31494 2587.24288 50.01 Error 131 6776.90867 51.73213 Corrected Total 157 74045.22361 > F > F Source Source treatment <.0001 > F Source treatment <.0001 14 R-Square Coeff Var Root MSE weight_loss Mean 0.908476 47.40003 7.192505 15.17405 DF Type I SS Mean Square F Value 26 67268.31494 2587.24288 50.01 DF Type III SS Mean Square F Value 26 67268.31494 2587.24288 50.01 Decay Resistance of OSB to G. trabeum 11:31 Monday, April 28, 2008 The GLM Procedure Duncan's Multiple Range Test for weight_loss NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha Error Degrees of Freedom Error Mean Square 0.05 131 51.73213 Pr Pr Pr 97 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Number of Means 13 14 Critical Range 10.08 10.13 2 3 4 5 6 7 8 9 10 8.35 8.79 9.08 9.29 9.46 9.60 9.71 9.80 9.89 11 12 9.96 10.02 Number of Means 15 16 17 18 19 20 21 22 23 24 25 26 27 Critical Range 10.17 10.21 10.25 10.29 10.32 10.35 10.37 10.40 10.42 10.44 10.46 10.48 10.50 Means with the same letter are not significantly different. Duncan Grouping B B B D D D H H H H H H H H H H H H H H H H H H H H H H H 16 A A A Mean N treatment 68.400 4 27 62.440 5 23 C C C 55.633 6 1 53.500 5 26 E E E 45.967 6 14 41.833 6 16 F 29.617 6 15 G G G G G 17.417 6 17 12.200 6 8 9.350 6 11 6.167 6 2 4.383 6 5 3.817 6 9 3.267 6 18 3.200 6 6 2.833 6 12 I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I 2.683 6 20 2.683 6 10 2.433 6 7 2.333 6 24 1.983 6 19 1.967 6 21 1.933 6 13 1.867 6 3 1.633 6 22 1.350 6 4 0.817 6 25 Decay Resistance of OSB to G. trabeum 11:31 Monday, April 28, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for weight_loss NOTE: This test controls the Type I experimentwise error rate, but it generally has a 98 higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 131 Error Mean Square 51.73213 Critical Value of Studentized Range 5.34438 Minimum Significant Difference 15.952 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A A A A A A A 68.400 4 27 62.440 5 23 55.633 6 1 53.500 5 26 45.967 6 14 41.833 6 16 29.617 6 15 B B B B B B B D D D F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F C C C E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E 17.417 6 17 12.200 6 8 9.350 6 11 6.167 6 2 4.383 6 5 3.817 6 9 3.267 6 18 3.200 6 6 2.833 6 12 2.683 6 20 2.683 6 10 2.433 6 7 2.333 6 24 1.983 6 19 1.967 6 21 1.933 6 13 1.867 6 3 1.633 6 22 1.350 6 4 0.817 6 25 Decay Resistance of OSB to P. placenta 10 11:48 Monday, April 28, 2008 The GLM Procedure Class Level Information Class Levels Values 99 treatment 25 26 27 27 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 Number of Observations Read Number of Observations Used 160 158 Decay Resistance of OSB to P. placenta 11 11:48 Monday, April 28, 2008 The GLM Procedure Dependent Variable: weight_loss DF Sum of Squares Mean Square F Value Model <.0001 26 30690.65305 1180.40973 3.65 Error 131 42396.85967 323.64015 Corrected Total 157 73087.51272 > F > F Source Source treatment <.0001 > F Source treatment <.0001 14 R-Square Coeff Var Root MSE weight_loss Mean 0.419917 144.5421 17.99000 12.44620 DF Type I SS Mean Square F Value 26 30690.65305 1180.40973 3.65 DF Type III SS Mean Square F Value 26 30690.65305 1180.40973 3.65 Decay Resistance of OSB to P. placenta 11:48 Monday, April 28, 2008 The GLM Procedure Duncan's Multiple Range Test for weight_loss NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 131 Error Mean Square 323.6402 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range 20.89 21.98 22.71 23.25 23.67 24.00 24.28 24.52 24.73 24.90 25.06 25.20 25.33 Number of Means 15 16 17 18 19 20 21 22 23 24 25 26 27 Critical Range 25.44 25.55 25.64 25.73 25.81 25.88 25.95 26.01 26.07 26.12 26.17 26.22 26.26 Means with the same letter are not significantly different. Duncan Grouping Mean N treatment Pr Pr Pr 100 C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C 16 A 63.05 4 27 B B B B B B B B B B B B B B B B B B B B B B B B B 35.40 6 24 34.55 6 16 27.38 5 26 25.25 6 9 25.10 5 23 21.15 6 14 18.58 6 1 17.87 6 25 16.90 6 11 16.42 6 7 15.67 6 18 15.42 6 12 12.13 6 22 1.25 6 6 1.18 6 3 1.15 6 4 1.13 6 5 1.08 6 21 1.00 6 2 0.97 6 10 0.90 6 13 0.82 6 15 0.82 6 8 0.80 6 17 0.78 6 20 0.77 6 19 Decay Resistance of OSB to P. placenta 11:48 Monday, April 28, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for weight_loss NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 131 Error Mean Square 323.6402 Critical Value of Studentized Range 5.34438 Minimum Significant Difference 39.9 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A 63.05 4 27 101 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B A A A A A A A A A A 35.40 6 24 34.55 6 16 27.38 5 26 25.25 6 9 25.10 5 23 21.15 6 14 18.58 6 1 17.87 6 25 16.90 6 11 16.42 6 7 15.67 6 18 15.42 6 12 12.13 6 22 1.25 6 6 1.18 6 3 1.15 6 4 1.13 6 5 1.08 6 21 1.00 6 2 0.97 6 10 0.90 6 13 0.82 6 15 0.82 6 8 0.80 6 17 0.78 6 20 0.77 6 19 Decay Resistance of OSB to T. versicolor 1 12:53 Friday, May 23, 2008 The GLM Procedure Class Level Information Class Levels treatment 25 26 27 27 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 Number of Observations Read Number of Observations Used 160 158 Decay Resistance of OSB to T. versicolor 2 12:53 Friday, May 23, 2008 The GLM Procedure Dependent Variable: weight_loss > F Source DF Sum of Squares Mean Square F Value Pr 102 Model <.0001 26 54994.76263 2115.18318 Error 131 5978.44117 45.63696 Corrected Total 157 60973.20380 > F R-Square Coeff Var Root MSE weight_loss Mean 0.901950 48.98894 6.755513 13.78987 Source treatment <.0001 > F Source treatment <.0001 5 46.35 DF Type I SS Mean Square F Value 26 54994.76263 2115.18318 46.35 DF Type III SS Mean Square F Value 26 54994.76263 2115.18318 46.35 Pr Pr Decay Resistance of OSB to T. versicolor 12:53 Friday, May 23, 2008 The GLM Procedure Duncan's Multiple Range Test for weight_loss NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 131 Error Mean Square 45.63696 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range 7.843 8.255 8.529 8.730 8.887 9.013 9.119 9.208 9.285 9.352 9.411 9.464 9.512 Number of Means 15 16 17 18 19 20 21 22 23 24 25 26 27 Critical Range 9.554 9.593 9.629 9.661 9.691 9.718 9.743 9.767 9.789 9.809 9.828 9.846 9.862 Means with the same letter are not significantly different. Duncan Grouping Mean N treatment A 67.840 5 26 B B B 58.600 5 23 52.817 6 1 C 41.150 6 16 D D D D D 33.000 6 15 29.417 6 14 28.425 4 27 E E E E E 13.317 6 8 8.550 6 17 7.883 6 11 F F F 103 F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F F 7 E E E E E E 6.017 6 9 4.650 6 20 4.433 6 24 3.717 6 18 3.667 6 12 3.583 6 22 3.417 6 13 3.333 6 5 3.150 6 21 2.900 6 19 2.633 6 10 2.617 6 2 2.233 6 6 2.167 6 7 1.533 6 3 1.433 6 4 1.200 6 25 Decay Resistance of OSB to T. versicolor 12:53 Friday, May 23, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for weight_loss NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 131 Error Mean Square 45.63696 Critical Value of Studentized Range 5.34438 Minimum Significant Difference 14.983 Harmonic Mean of Cell Sizes 5.806452 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping Mean A A A 67.840 5 26 58.600 5 23 52.817 6 1 41.150 6 16 33.000 6 15 29.417 6 14 28.425 4 27 13.317 6 8 8.550 6 17 7.883 6 11 6.017 6 9 B B B D D D D D D D C C C E E E E E E E N treatment 104 E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E 28, 2008 4.650 6 20 4.433 6 24 3.717 6 18 3.667 6 12 3.583 6 22 3.417 6 13 3.333 6 5 3.150 6 21 2.900 6 19 2.633 6 10 2.617 6 2 2.233 6 6 2.167 6 7 1.533 6 3 1.433 6 4 1.200 6 25 Mold Resistance at 2 weeks 43 13:00 Monday, April The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 28, 2008 156 90 Mold Resistance at 2 weeks 44 13:00 Monday, April The GLM Procedure Dependent Variable: rating_1 DF Sum of Squares Mean Square F Value Model <.0001 25 99.5000000 3.9800000 8.35 Error 64 30.5000000 0.4765625 Corrected Total 89 130.0000000 > F > F Source Source treatment <.0001 > F Source treatment <.0001 R-Square Coeff Var Root MSE rating_1 Mean 0.765385 20.71005 0.690335 3.333333 DF Type I SS Mean Square F Value 25 99.50000000 3.98000000 8.35 DF Type III SS Mean Square F Value 25 99.50000000 3.98000000 8.35 Pr Pr Pr 105 28, 2008 Mold Resistance at 2 weeks 47 13:00 Monday, April The GLM Procedure Duncan's Multiple Range Test for rating_1 NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 64 Error Mean Square 0.476563 Harmonic Mean of Cell Sizes 3.25 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range 1.082 1.138 1.175 1.202 1.223 1.240 1.254 1.265 1.275 1.284 1.291 1.298 1.304 26 Number of Means Critical Range 1.341 15 16 17 18 19 20 21 22 23 24 25 1.309 1.313 1.318 1.321 1.325 1.328 1.331 1.333 1.335 1.338 1.339 Means with the same letter are not significantly different. Duncan Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B E E E E E E E E E A A A A A A A A A A A A A A A A A A A A A A A D D D D D D D D D D D D D D D D D D D Mean N treatment 5.0000 3 10 4.3333 3 9 4.3333 3 11 4.3333 3 20 4.3333 3 13 4.3333 3 8 4.3333 3 15 4.3333 3 16 C C C C C C C C C C C C C C C C C C C C C C C C C 4.0000 3 17 4.0000 3 18 4.0000 3 19 3.8333 6 26 3.6667 3 1 3.6667 3 14 3.6667 3 3 3.6667 3 12 F F F F F F 3.6667 3 4 3.3333 3 2 3.0000 3 5 3.0000 3 21 3.0000 3 6 2.5000 6 23 2.0000 3 22 1.6667 3 7 106 F F F 28, 2008 1.5000 6 24 1.3333 6 25 Mold Resistance at 2 weeks 49 13:00 Monday, April The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_1 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 64 Error Mean Square 0.476563 Critical Value of Studentized Range 5.43738 Minimum Significant Difference 2.0821 Harmonic Mean of Cell Sizes 3.25 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping E E E E E E E E E E E E E E E E E B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B D D D D D D D D D D D D D D D D D D D D D D D A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 5.0000 3 10 4.3333 3 9 4.3333 3 11 4.3333 3 20 4.3333 3 13 4.3333 3 8 4.3333 3 15 4.3333 3 16 4.0000 3 17 4.0000 3 18 4.0000 3 19 3.8333 6 26 3.6667 3 1 3.6667 3 14 3.6667 3 3 3.6667 3 12 3.6667 3 4 3.3333 3 2 3.0000 3 5 3.0000 3 21 3.0000 3 6 2.5000 6 23 2.0000 3 22 1.6667 3 7 1.5000 6 24 1.3333 6 25 107 28, 2008 Mold Resistance at 2 weeks 43 13:00 Monday, April The GLM Procedure Class Level Information Class Levels treatment 24 25 26 Values 26 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 28, 2008 156 90 Mold Resistance at 2 weeks 44 13:00 Monday, April The GLM Procedure Dependent Variable: rating_1 DF Sum of Squares Mean Square F Value Model <.0001 25 99.5000000 3.9800000 8.35 Error 64 30.5000000 0.4765625 Corrected Total 89 130.0000000 > F > F Source R-Square Coeff Var Root MSE rating_1 Mean 0.765385 20.71005 0.690335 3.333333 Source treatment <.0001 > F Source treatment <.0001 28, 2008 DF Type I SS Mean Square F Value 25 99.50000000 3.98000000 8.35 DF Type III SS Mean Square F Value 25 99.50000000 3.98000000 8.35 Mold Resistance at 2 weeks 47 Pr Pr Pr 13:00 Monday, April The GLM Procedure Duncan's Multiple Range Test for rating_1 NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 64 Error Mean Square 0.476563 Harmonic Mean of Cell Sizes 3.25 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range 1.082 1.138 1.175 1.202 1.223 1.240 1.254 1.265 1.275 1.284 1.291 1.298 1.304 26 Number of Means Critical Range 15 16 17 18 19 20 21 22 23 24 25 1.309 1.313 1.318 1.321 1.325 1.328 1.331 1.333 1.335 1.338 1.339 108 1.341 Means with the same letter are not significantly different. Duncan Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B E E E E E E E E E 28, 2008 49 A A A A A A A A A A A A A A A A A A A A A A A D D D D D D D D D D D D D D D D D D D Mean N treatment 5.0000 3 10 4.3333 3 9 4.3333 3 11 4.3333 3 20 4.3333 3 13 4.3333 3 8 4.3333 3 15 4.3333 3 16 C C C C C C C C C C C C C C C C C C C C C C C C C 4.0000 3 17 4.0000 3 18 4.0000 3 19 3.8333 6 26 F F F F F F F F F 3.6667 3 1 3.6667 3 14 3.6667 3 3 3.6667 3 12 3.6667 3 4 3.3333 3 2 3.0000 3 5 3.0000 3 21 3.0000 3 6 2.5000 6 23 2.0000 3 22 1.6667 3 7 1.5000 6 24 1.3333 6 25 Mold Resistance at 2 weeks 13:00 Monday, April The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_1 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 64 Error Mean Square 0.476563 Critical Value of Studentized Range 5.43738 Minimum Significant Difference 2.0821 Harmonic Mean of Cell Sizes 3.25 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. 109 Tukey Grouping E E E E E E E E E E E E E E E E E 28, 2008 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B D D D D D D D D D D D D D D D D D D D D D D D A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 5.0000 3 10 4.3333 3 9 4.3333 3 11 4.3333 3 20 4.3333 3 13 4.3333 3 8 4.3333 3 15 4.3333 3 16 4.0000 3 17 4.0000 3 18 4.0000 3 19 3.8333 6 26 3.6667 3 1 3.6667 3 14 3.6667 3 3 3.6667 3 12 3.6667 3 4 3.3333 3 2 3.0000 3 5 3.0000 3 21 3.0000 3 6 2.5000 6 23 2.0000 3 22 1.6667 3 7 1.5000 6 24 1.3333 6 25 Mold Resistance at 3 weeks 57 13:00 Monday, April The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 28, 2008 58 156 156 Mold Resistance at 3 weeks 13:00 Monday, April The GLM Procedure Dependent Variable: rating_2 > F Source Model <.0001 DF Sum of Squares Mean Square F Value 25 73.3910256 2.9356410 9.35 Pr 110 > F Error 130 40.8333333 Corrected Total 155 114.2243590 R-Square Coeff Var Root MSE rating_2 Mean 0.642516 13.76850 0.560449 4.070513 Source treatment <.0001 > F Source treatment <.0001 28, 2008 0.3141026 DF Type I SS Mean Square F Value 25 73.39102564 2.93564103 9.35 DF Type III SS Mean Square F Value 25 73.39102564 2.93564103 9.35 Mold Resistance at 3 weeks 61 Pr Pr 13:00 Monday, April The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_2 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 0.314103 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 1.2166 Means with the same letter are not significantly different. Tukey Grouping B B B B B B B B B A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A Mean N treatment 4.8333 6 8 4.6667 6 9 4.5000 6 19 4.5000 6 10 4.5000 6 13 4.5000 6 6 4.5000 6 15 4.5000 6 20 4.5000 6 11 4.5000 6 16 4.3333 6 5 4.3333 6 18 4.1667 6 17 4.1667 6 14 4.1667 6 3 4.1667 6 12 4.1667 6 21 111 B B B B B B B B B B B B B B A A A A A A A A A A A A D D D 28, 2008 C C C C C 4.1667 6 26 4.0000 6 4 4.0000 6 22 4.0000 6 2 3.8333 6 7 3.6667 6 1 3.0000 6 23 2.5000 6 24 1.6667 6 25 Mold Resistance at 4 weeks 73 13:00 Monday, April The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 28, 2008 156 156 Mold Resistance at 4 weeks 74 13:00 Monday, April The GLM Procedure Dependent Variable: rating_3 DF Sum of Squares Mean Square F Value Model <.0001 25 33.89743590 1.35589744 5.18 Error 130 34.00000000 0.26153846 Corrected Total 155 67.89743590 > F > F Source Source treatment <.0001 > F Source treatment <.0001 28, 2008 77 R-Square Coeff Var Root MSE rating_3 Mean 0.499245 11.73231 0.511408 4.358974 DF Type I SS Mean Square F Value 25 33.89743590 1.35589744 5.18 DF Type III SS Mean Square F Value 25 33.89743590 1.35589744 5.18 Mold Resistance at 4 weeks Pr Pr Pr 13:00 Monday, April The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_3 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. 112 Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 0.261538 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 1.1101 Means with the same letter are not significantly different. Tukey Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B 28, 2008 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A D D D D D C C C C C C C C C C C C C C C C C C C Mean N treatment 4.8333 6 9 4.8333 6 10 4.8333 6 13 4.8333 6 12 4.8333 6 6 4.6667 6 11 4.6667 6 8 4.6667 6 26 4.5000 6 15 4.5000 6 5 4.5000 6 21 4.5000 6 4 4.5000 6 18 4.5000 6 16 4.5000 6 20 4.3333 6 19 4.3333 6 1 4.3333 6 14 4.3333 6 2 4.1667 6 7 4.1667 6 3 4.1667 6 17 4.0000 6 22 3.6667 6 23 3.3333 6 24 2.8333 6 25 Mold Resistance at 6 weeks 80 13:00 Monday, April The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 28, 2008 81 Mold Resistance at 6 weeks 156 156 13:00 Monday, April 113 The GLM Procedure Dependent Variable: rating_4 DF Sum of Squares Mean Square F Value Model <.0001 25 22.74358974 0.90974359 6.96 Error 130 17.00000000 0.13076923 Corrected Total 155 39.74358974 > F > F Source Source treatment <.0001 > F Source treatment <.0001 28, 2008 R-Square Coeff Var Root MSE rating_4 Mean 0.572258 7.623347 0.361620 4.743590 DF Type I SS Mean Square F Value 25 22.74358974 0.90974359 6.96 DF Type III SS Mean Square F Value 25 22.74358974 0.90974359 6.96 Mold Resistance at 6 weeks 84 Pr Pr Pr 13:00 Monday, April The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_4 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 0.130769 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 0.785 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A A A A A A A A A A A A A A A A A A A A A A A A A 5.0000 6 9 5.0000 6 2 5.0000 6 19 5.0000 6 20 5.0000 6 13 5.0000 6 6 5.0000 6 7 5.0000 6 8 5.0000 6 11 5.0000 6 12 4.8333 6 5 4.8333 6 10 4.8333 6 21 114 B B B B B A A A A A A A A A A A A A A A A A A A A A A C C C 4.8333 6 22 4.8333 6 3 4.8333 6 16 4.8333 6 26 4.8333 6 4 4.6667 6 1 4.6667 6 15 4.6667 6 17 4.6667 6 18 4.5000 6 14 4.3333 6 23 3.8333 6 24 3.3333 6 25 Mold Resistance at 8 weeks 1 09:42 Wednesday, April 9, 2008 The GLM Procedure Class Level Information Class Levels treatment 4 Values 23 24 25 26 Number of Observations Read Number of Observations Used 24 24 Mold Resistance at 8 weeks 2 09:42 Wednesday, April 9, 2008 The GLM Procedure Dependent Variable: rating_5 DF Sum of Squares Mean Square F Value Model 0.0001 3 6.12500000 2.04166667 11.67 Error 20 3.50000000 0.17500000 Corrected Total 23 9.62500000 > F > F Source Source treatment 0.0001 > F Source treatment 0.0001 R-Square Coeff Var Root MSE rating_5 Mean 0.636364 9.561829 0.418330 4.375000 DF Type I SS Mean Square F Value 3 6.12500000 2.04166667 11.67 DF Type III SS Mean Square F Value 3 6.12500000 2.04166667 11.67 Pr Pr Pr 115 Mold Resistance at 8 weeks 4 09:42 Wednesday, April 9, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for rating_5 NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha Error Degrees of Freedom Error Mean Square Critical Value of Studentized Range Minimum Significant Difference 0.05 20 0.175 3.95829 0.676 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A A A 5.0000 6 26 4.6667 6 23 C C C 4.1667 6 24 3.6667 6 25 B B B 3, 2008 Modulus of Elasticity 1 17:22 Monday, March The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 3, 2008 156 156 Modulus of Elasticity 2 17:22 Monday, March The GLM Procedure Dependent Variable: modulus_of_elasticity DF Sum of Squares Mean Square F Value Model <.0001 25 25345754.97 1013830.20 3.07 Error 130 42880443.33 329849.56 Corrected Total 155 68226198.31 > F > F Source R-Square Coeff Var Root MSE modulus_of_elasticity Mean 0.371496 12.73405 574.3253 4510.154 Source treatment <.0001 > F Source DF Type I SS Mean Square F Value 25 25345754.97 1013830.20 3.07 DF Type III SS Mean Square F Value Pr Pr Pr 116 treatment <.0001 3, 2008 25 25345754.97 1013830.20 Modulus of Elasticity 5 3.07 17:22 Monday, March The GLM Procedure Tukey's Studentized Range (HSD) Test for modulus_of_elasticity NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 329849.6 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 1246.7 Means with the same letter are not significantly different. Tukey Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B 1 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 5236.0 6 25 5181.5 6 7 5152.8 6 19 4945.8 6 6 4901.5 6 17 4897.5 6 14 4790.0 6 20 4786.3 6 8 4762.0 6 16 4665.0 6 15 4595.3 6 5 4580.7 6 24 4566.2 6 11 4509.7 6 13 4435.3 6 26 4298.8 6 12 4290.5 6 10 4277.8 6 3 4261.2 6 1 4223.0 6 18 4137.2 6 23 4110.8 6 9 4094.3 6 21 3960.3 6 22 3873.3 6 2 3731.0 6 4 Bending Strenth - Modulus of Rupture 14:10 Monday, 117 March 3, 2008 The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 156 156 Bending Strenth - Modulus of Rupture 2 14:10 Monday, March 3, 2008 The GLM Procedure Dependent Variable: modulus_of_rupture DF Sum of Squares Mean Square F Value Model 0.0117 25 1360079239 54403170 1.89 Error 130 3744443141 28803409 Corrected Total 155 5104522380 > F > F Source R-Square Coeff Var Root MSE modulus_of_rupture Mean 0.266446 20.19666 5366.881 26573.12 Source treatment 0.0117 > F Source treatment 0.0117 5 DF Type I SS Mean Square F Value 25 1360079239 54403170 1.89 DF Type III SS Mean Square F Value 25 1360079239 54403170 1.89 Pr Pr Pr Bending Strenth - Modulus of Rupture 14:10 Monday, March 3, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for modulus_of_rupture NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 28803409 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 11650 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A A A A A 31769 6 17 31759 6 19 30789 6 15 118 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A 30187 6 14 29842 6 11 29077 6 6 28672 6 25 28038 6 26 27874 6 16 27696 6 24 27279 6 20 26984 6 13 26983 6 3 26924 6 12 26514 6 8 26399 6 18 25739 6 23 25355 6 10 24230 6 1 23224 6 5 23156 6 9 22742 6 22 22710 6 4 22557 6 21 22209 6 7 22197 6 2 Internal Bond Strength - Maximum Stress (kPa) 1 18:13 Monday, March 3, 2008 The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 156 156 Internal Bond Strength - Maximum Stress (kPa) 2 18:13 Monday, March 3, 2008 The GLM Procedure Dependent Variable: max_stress_kPa DF Sum of Squares Mean Square F Value Model <.0001 25 810439.392 32417.576 4.70 Error 130 897127.015 6900.977 > F Source Pr 119 Corrected Total > F 155 R-Square Coeff Var Root MSE max_stress_kPa Mean 0.474617 36.49722 83.07212 227.6122 Source treatment <.0001 > F 1707566.407 Source treatment <.0001 DF Type I SS Mean Square F Value 25 810439.3919 32417.5757 4.70 DF Type III SS Mean Square F Value 25 810439.3919 32417.5757 4.70 Pr Pr Internal Bond Strength - Maximum Stress (kPa) 5 18:13 Monday, March 3, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for max_stress_kPa NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 6900.977 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 180.32 Means with the same letter are not significantly different. Tukey Grouping E E E E E E E E E E E E E E E E E E E E E E B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B D D D D D D D D D D D D D D D D D D D D D D D D D D D D A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C F F F F F F F F F F F F Mean N treatment 341.82 6 15 310.22 6 16 300.78 6 13 299.72 6 26 299.18 6 14 290.15 6 25 286.95 6 17 281.47 6 24 270.53 6 11 256.62 6 12 254.40 6 19 254.40 6 4 247.05 6 1 244.23 6 9 242.32 6 23 229.97 6 20 224.55 6 8 212.12 6 18 198.73 6 3 120 E E E E E E E E E E E B B B B B D D D D D D D D D A C C C C C C C F F F F F F F F F F F F F 189.03 6 2 142.77 6 10 138.65 6 7 123.38 6 22 116.82 6 21 95.35 6 5 66.72 6 6 Thickness Swelling at 2 Hours 1 16:50 Thursday, March 6, 2008 The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 156 156 Thickness Swelling at 2 Hours 2 16:50 Thursday, March 6, 2008 The GLM Procedure Dependent Variable: swelling_2h DF Sum of Squares Mean Square F Value Model <.0001 25 425.0056410 17.0002256 3.94 Error 130 561.4166667 4.3185897 Corrected Total 155 986.4223077 > F > F Source Source treatment <.0001 > F Source treatment <.0001 5 R-Square Coeff Var Root MSE swelling_2h Mean 0.430856 28.94010 2.078122 7.180769 DF Type I SS Mean Square F Value 25 425.0056410 17.0002256 3.94 DF Type III SS Mean Square F Value 25 425.0056410 17.0002256 3.94 Pr Pr Pr Thickness Swelling at 2 Hours 16:50 Thursday, March 6, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for swelling_2h NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher 121 Type II error rate than REGWQ. Alpha Error Degrees of Freedom Error Mean Square Critical Value of Studentized Range Minimum Significant Difference 0.05 130 4.31859 5.31704 4.5109 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A 13.850 6 6 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B 9.000 6 16 8.200 6 8 8.167 6 14 8.000 6 15 7.683 6 9 7.650 6 10 7.617 6 13 7.433 6 17 7.417 6 11 7.383 6 22 7.283 6 19 7.283 6 12 7.017 6 18 6.983 6 20 6.950 6 21 6.567 6 3 6.467 6 23 6.167 6 7 6.083 6 5 6.033 6 2 5.983 6 4 5.700 6 24 5.650 6 1 5.233 6 25 4.900 6 26 Thickness Swelling at 24 Hours 1 10:56 Monday, April 28, 2008 The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read 156 122 Number of Observations Used 155 Thickness Swelling at 24 Hours 2 10:56 Monday, April 28, 2008 The GLM Procedure Dependent Variable: swelling_24h DF Sum of Squares Mean Square F Value Model <.0001 25 812.430419 32.497217 6.08 Error 129 689.355000 5.343837 Corrected Total 154 1501.785419 > F > F Source R-Square Coeff Var Root MSE swelling_24h Mean 0.540976 13.56770 2.311674 17.03806 Source treatment <.0001 > F Source treatment <.0001 DF Type I SS Mean Square F Value 25 812.4304194 32.4972168 6.08 DF Type III SS Mean Square F Value 25 812.4304194 32.4972168 6.08 Pr Pr Pr Thickness Swelling at 24 Hours 5 10:56 Monday, April 28, 2008 The GLM Procedure Duncan's Multiple Range Test for swelling_24h NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 129 Error Mean Square 5.343837 Harmonic Mean of Cell Sizes 5.954198 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range 2.651 2.790 2.882 2.950 3.003 3.046 3.082 3.112 3.138 3.160 3.181 3.198 3.214 26 Number of Means Critical Range 3.327 15 16 17 18 19 20 21 22 23 24 25 3.229 3.242 3.254 3.265 3.275 3.284 3.292 3.300 3.308 3.315 3.321 Means with the same letter are not significantly different. Duncan Grouping B B B A A A A A C Mean N treatment 21.317 6 16 20.767 6 6 20.200 5 15 123 B B B B B B B B B B B B B B B B B B E E E E E E E E E E E E E E E E E E E E E E E G G G G G G G G G G G G G G G G G G G A A A A A A A A A A A A D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D C C C C C C C C C C C C C C C C C C C C C C C C C C F F F F F F F F F F F F F F F F F F F F F F F F F I I I I I I I I I I I H H H H H H H H H H H 19.050 6 19 18.733 6 14 18.533 6 8 18.500 6 17 18.433 6 11 18.283 6 13 17.800 6 9 17.750 6 22 17.717 6 18 17.300 6 10 17.267 6 20 17.233 6 2 17.033 6 12 16.950 6 21 16.700 6 3 16.700 6 4 15.183 6 5 14.983 6 1 14.750 6 23 14.133 6 7 13.567 6 25 12.600 6 24 12.033 6 26 Thickness Swelling at 24 Hours 7 10:56 Monday, April 28, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for swelling_24h NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 129 Error Mean Square 5.343837 Critical Value of Studentized Range 5.31794 Minimum Significant Difference 5.038 Harmonic Mean of Cell Sizes 5.954198 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping B B B A A A A A A A C Mean N treatment 21.317 6 16 20.767 6 6 20.200 5 15 19.050 6 19 124 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B E E E E E E E E E E E E E E E E E E E E E E E E E 27, 2008 D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C F F F F F F F F F F F F F F F F F F F F F 18.733 6 14 18.533 6 8 18.500 6 17 18.433 6 11 18.283 6 13 17.800 6 9 17.750 6 22 17.717 6 18 17.300 6 10 17.267 6 20 17.233 6 2 17.033 6 12 16.950 6 21 16.700 6 3 16.700 6 4 15.183 6 5 14.983 6 1 14.750 6 23 14.133 6 7 13.567 6 25 12.600 6 24 12.033 6 26 Moisture Content at 0 Hours 1 12:02 Tuesday, May The GLM Procedure Class Level Information Class Levels treatment 24 25 26 Values 26 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 27, 2008 156 156 Moisture Content at 0 Hours 2 12:02 Tuesday, May The GLM Procedure Dependent Variable: mc_0h DF Sum of Squares Mean Square F Value Model <.0001 25 28.54108974 1.14164359 16.29 Error 130 9.10833333 0.07006410 Corrected Total 155 37.64942308 > F Source R-Square Coeff Var Root MSE mc_0h Mean 0.758075 2.908135 0.264696 9.101923 Pr 125 > F Source treatment <.0001 > F Source treatment <.0001 27, 2008 DF Type I SS Mean Square F Value 25 28.54108974 1.14164359 16.29 DF Type III SS Mean Square F Value 25 28.54108974 1.14164359 16.29 Moisture Content at 0 Hours 5 Pr Pr 12:02 Tuesday, May The GLM Procedure Tukey's Studentized Range (HSD) Test for mc_0h NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 0.070064 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 0.5746 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A 9.6500 6 22 9.5167 6 7 9.4333 6 21 9.3833 6 12 9.3500 6 8 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B C C C 9.3333 6 11 9.3333 6 14 9.3167 6 6 9.3167 6 2 9.3000 6 16 9.2833 6 13 9.2833 6 18 9.2667 6 17 9.2333 6 15 9.2000 6 1 9.2000 6 19 9.1833 6 20 9.1667 6 5 9.1167 6 3 9.1000 6 10 9.0500 6 9 9.0333 6 4 8.2167 6 24 8.2167 6 26 126 C C C C 27, 2008 8.1333 6 25 8.0333 6 23 Moisture Content at 2 Hours 8 12:02 Tuesday, May The GLM Procedure Class Level Information Class Levels treatment 24 25 26 Values 26 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 27, 2008 156 156 Moisture Content at 2 Hours 9 12:02 Tuesday, May The GLM Procedure Dependent Variable: mc_2h > F Source Model <.0001 > F Sum of Squares Mean Square F Value 25 6209.78494 248.39140 4.10 60.61358 Error 130 7879.76500 Corrected Total 155 14089.54994 R-Square Coeff Var Root MSE mc_2h Mean 0.440737 36.75171 7.785472 21.18397 Source treatment <.0001 > F DF Source treatment <.0001 27, 2008 DF Type I SS Mean Square F Value 25 6209.784936 248.391397 4.10 DF Type III SS Mean Square F Value 25 6209.784936 248.391397 4.10 Moisture Content at 2 Hours 12 Pr Pr Pr 12:02 Tuesday, May The GLM Procedure Tukey's Studentized Range (HSD) Test for mc_2h NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 130 Error Mean Square 60.61358 Critical Value of Studentized Range 5.31704 Minimum Significant Difference 16.9 Means with the same letter are not significantly different. Tukey Grouping Mean N treatment A 51.717 6 6 127 B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B 27, 2008 25.050 6 16 22.117 6 15 21.650 6 23 21.567 6 14 21.517 6 2 20.750 6 18 20.617 6 11 20.567 6 8 20.500 6 12 20.450 6 1 20.400 6 3 19.767 6 17 19.583 6 13 19.583 6 4 19.567 6 22 19.517 6 19 19.183 6 21 19.067 6 26 19.000 6 20 18.633 6 10 18.367 6 5 18.367 6 9 18.250 6 24 17.517 6 7 17.483 6 25 Moisture Content at 24 Hours 15 12:02 Tuesday, May The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 27, 2008 16 156 150 Moisture Content at 24 Hours 12:02 Tuesday, May The GLM Procedure Dependent Variable: mc_24h DF Sum of Squares Mean Square F Value Model <.0001 24 9630.45627 401.26901 4.40 Error 125 11402.60167 91.22081 Corrected Total 149 21033.05793 > F Source Pr 128 > F R-Square Coeff Var Root MSE mc_24h Mean 0.457872 20.41996 9.550959 46.77267 Source treatment <.0001 > F Source treatment <.0001 27, 2008 DF Type I SS Mean Square F Value 24 9630.456267 401.269011 4.40 DF Type III SS Mean Square F Value 24 9630.456267 401.269011 4.40 Moisture Content at 24 Hours 19 Pr Pr 12:02 Tuesday, May The GLM Procedure Tukey's Studentized Range (HSD) Test for mc_24h NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 125 Error Mean Square 91.22081 Critical Value of Studentized Range 5.29216 Minimum Significant Difference 20.635 Means with the same letter are not significantly different. Tukey Grouping E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 69.283 6 6 60.683 6 16 59.883 6 15 55.833 6 23 52.550 6 14 51.133 6 18 49.883 6 2 48.800 6 11 48.717 6 8 47.050 6 17 46.717 6 3 46.667 6 19 45.867 6 12 45.167 6 1 44.550 6 4 43.617 6 13 43.033 6 22 41.300 6 21 40.983 6 20 39.367 6 9 129 E E E E E E E E E E 13, 2008 D D D D D D D D C C 39.267 6 24 38.900 6 10 38.117 6 25 37.350 6 5 34.600 6 7 Dry Room Moisture Content 1 15:50 Tuesday, May The GLM Procedure Class Level Information Class Levels treatment 24 25 26 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 13, 2008 157 154 Dry Room Moisture Content 2 15:50 Tuesday, May The GLM Procedure Dependent Variable: dry_mc DF Sum of Squares Mean Square F Value Model <.0001 25 12.14524892 0.48580996 41.48 Error 128 1.49916667 0.01171224 Corrected Total 153 13.64441558 > F > F Source Source treatment <.0001 > F Source treatment <.0001 13, 2008 5 R-Square Coeff Var Root MSE dry_mc Mean 0.890126 2.102215 0.108223 5.148052 DF Type I SS Mean Square F Value 25 12.14524892 0.48580996 41.48 DF Type III SS Mean Square F Value 25 12.14524892 0.48580996 41.48 Dry Room Moisture Content Pr Pr 15:50 Tuesday, May The GLM Procedure Duncan's Multiple Range Test for dry_mc NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha Error Degrees of Freedom Error Mean Square Pr 0.05 128 0.011712 130 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range .1248 .1314 .1357 .1389 .1414 .1434 .1451 .1465 .1477 .1488 .1498 .1506 .1513 26 Number of Means Critical Range .1566 15 16 17 18 19 20 21 22 23 24 25 .1520 .1526 .1532 .1537 .1542 .1546 .1550 .1554 .1557 .1561 .1564 Means with the same letter are not significantly different. Duncan Grouping F F F F F F F F F F F F F F F F F F F F F F F F F C C C C C C C C C C C C C C C E E E E E E E E E E E E E 7 N treatment A 5.61667 6 7 B B B B B B B B B B B B B 5.41667 6 10 5.38333 6 6 5.38333 6 9 5.36667 6 22 5.33333 6 21 5.30000 6 2 5.28333 6 5 5.26667 6 13 5.26667 6 8 5.23333 6 16 5.20000 6 18 5.18333 6 1 5.18333 6 12 H H H H H H H H H H H H H H H H H H H H H H H H H H H I I I I I I I 13, 2008 Mean D D D D D D D D D D D D D G G G G G G G G G G G G G G G G G G G G G G G G G G G 5.18333 6 3 5.18333 6 14 5.16667 6 19 5.16667 6 15 5.15000 6 17 5.13333 6 4 5.13333 6 20 5.12500 4 11 4.56667 6 25 4.56667 6 24 4.55000 6 23 4.50000 6 26 Dry Room Moisture Content 15:50 Tuesday, May The GLM Procedure Tukey's Studentized Range (HSD) Test for dry_mc NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. 131 Alpha 0.05 Error Degrees of Freedom 128 Error Mean Square 0.011712 Critical Value of Studentized Range 5.31886 Minimum Significant Difference 0.2372 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B A A A A A A A E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E E D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D F F F F F F F 13, 2008 Mean C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C N treatment 5.61667 6 7 5.41667 6 10 5.38333 6 6 5.38333 6 9 5.36667 6 22 5.33333 6 21 5.30000 6 2 5.28333 6 5 5.26667 6 13 5.26667 6 8 5.23333 6 16 5.20000 6 18 5.18333 6 1 5.18333 6 12 5.18333 6 3 5.18333 6 14 5.16667 6 19 5.16667 6 15 5.15000 6 17 5.13333 6 4 5.13333 6 20 5.12500 4 11 4.56667 6 25 4.56667 6 24 4.55000 6 23 4.50000 6 26 Wet Room Moisture Content 1 15:38 Tuesday, May The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 157 154 132 13, 2008 Wet Room Moisture Content 2 15:38 Tuesday, May The GLM Procedure Dependent Variable: wet_mc DF Sum of Squares Mean Square F Value Model <.0001 25 10.55858225 0.42234329 21.53 Error 128 2.51083333 0.01961589 Corrected Total 153 13.06941558 > F > F Source R-Square Coeff Var Root MSE wet_mc Mean 0.807885 1.008780 0.140057 13.88377 Source treatment <.0001 > F Source treatment <.0001 13, 2008 DF Type I SS Mean Square F Value 25 10.55858225 0.42234329 21.53 DF Type III SS Mean Square F Value 25 10.55858225 0.42234329 21.53 Wet Room Moisture Content 5 Pr Pr Pr 15:38 Tuesday, May The GLM Procedure Duncan's Multiple Range Test for wet_mc NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 128 Error Mean Square 0.019616 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Number of Means 2 3 4 5 6 7 8 9 10 11 12 13 14 Critical Range .1615 .1700 .1756 .1798 .1830 .1856 .1878 .1896 .1912 .1926 .1938 .1949 .1959 26 Number of Means Critical Range .2027 15 16 17 18 19 20 21 22 23 24 25 .1967 .1975 .1983 .1989 .1995 .2001 .2006 .2011 .2015 .2020 .2024 Means with the same letter are not significantly different. Duncan Grouping C C C C C C C E Mean N treatment A 14.76667 6 26 B B B B B B B B B 14.18333 6 18 14.16667 6 3 14.11667 6 17 14.06667 6 4 14.01667 6 1 D D D 133 C C C C C C C C G G G G G G G G G G G G G G G H H H H H H H H H H H H H H H L L L L L L L L L 13, 2008 E E E E E E E E E E E E E E E E E E B B B B D D D D D D D D D D D D F F F F F F F F F F F F F F F F F J J J J J J J J J J J J J I I I I I I I I I I I I I I I I I K K K K K K K K K K K K K 14.01667 6 20 14.00000 6 22 13.98333 6 19 13.98333 6 25 13.92500 4 11 13.90000 6 21 13.86667 6 7 13.85000 6 2 13.85000 6 10 13.80000 6 9 13.80000 6 15 13.78333 6 8 13.71667 6 6 13.70000 6 13 13.68333 6 12 13.61667 6 5 13.60000 6 23 13.56667 6 16 13.55000 6 24 13.48333 6 14 Wet Room Moisture Content 7 15:38 Tuesday, May The GLM Procedure Tukey's Studentized Range (HSD) Test for wet_mc NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 128 Error Mean Square 0.019616 Critical Value of Studentized Range 5.31886 Minimum Significant Difference 0.307 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping F F F F F F F C C C C C C C C C C C C C E E E E E E E E E Mean N treatment A 14.76667 6 26 B B B B B B B B B B B B B B B 14.18333 6 18 14.16667 6 3 14.11667 6 17 14.06667 6 4 14.01667 6 1 14.01667 6 20 14.00000 6 22 13.98333 6 19 H D D D D D D D D D D D G G G 134 F F F F F F F F F F F F F F F F F F F F C C C C C C C C E E E E E E E E E E E E E E E E E E K K K K K K K K K K K K K K K K K K K K K K K B B B B B B I I I I I I I I I I I I I I I I I I I I I I I H H H H H H H H H H H H H H H H H H H H H H H H J J J J J J J J J J J J J J J J J J J J J J J D D D D D D D D D D D D L L L L L L L L L L L L L L L L L G G G G G G G G G G G G G G G G G G G G G G 13.98333 6 25 13.92500 4 11 13.90000 6 21 13.86667 6 7 13.85000 6 2 13.85000 6 10 13.80000 6 9 13.80000 6 15 13.78333 6 8 13.71667 6 6 13.70000 6 13 13.68333 6 12 13.61667 6 5 13.60000 6 23 13.56667 6 16 13.55000 6 24 13.48333 6 14 Linear Change due to Moisture Content 1 15:44 Tuesday, May 27, 2008 The GLM Procedure Class Level Information Class treatment 24 25 26 Levels 26 Values 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Number of Observations Read Number of Observations Used 157 154 Linear Change due to Moisture Content 2 15:44 Tuesday, May 27, 2008 The GLM Procedure Dependent Variable: change_in_length DF Sum of Squares Mean Square F Value Model <.0001 25 0.23960877 0.00958435 3.15 Error 128 0.39007500 0.00304746 Corrected Total 153 0.62968377 > F > F Source R-Square Coeff Var Root MSE change_in_length Mean 0.380522 39.34006 0.055204 0.140325 Source DF Type I SS Mean Square F Value treatment 25 0.23960877 0.00958435 3.15 Pr Pr 135 <.0001 > F Source treatment <.0001 DF Type III SS Mean Square F Value 25 0.23960877 0.00958435 3.15 Pr Linear Change due to Moisture Content 5 15:44 Tuesday, May 27, 2008 The GLM Procedure Duncan's Multiple Range Test for change_in_length NOTE: This test controls the Type I comparisonwise error rate, not the experimentwise error rate. Alpha 0.05 Error Degrees of Freedom 128 Error Mean Square 0.003047 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Number of Means 9 10 Critical Range .07474 .07536 2 3 4 5 6 7 8 .06367 .06701 .06923 .07086 .07213 .07316 .07401 Number of Means 18 19 Critical Range .07841 .07865 11 12 13 14 15 16 17 .07591 .07639 .07682 .07720 .07755 .07786 .07815 26 Number of Means Critical Range .07990 20 21 22 23 24 25 .07887 .07907 .07926 .07944 .07960 .07976 Means with the same letter are not significantly different. Duncan Grouping B B B B B B B B B B B B B B B B B B B A A A A A A A A A D D D D D D D D D D D D D D D D D D D D D D C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 0.24500 6 19 0.21500 6 8 0.19000 6 7 0.19000 6 14 0.18833 6 12 0.16167 6 10 0.15833 6 23 0.15500 6 13 0.15250 4 11 0.14500 6 9 0.14333 6 20 0.13833 6 15 0.13667 6 21 0.13333 6 16 0.13000 6 6 0.12833 6 17 136 D D D D D D D D D D D D D D D D D D D C C C C C C C 0.12167 6 3 0.12000 6 2 0.11667 6 1 0.11167 6 26 0.11000 6 25 0.10000 6 22 0.09667 6 4 0.09000 6 24 0.09000 6 18 0.08500 6 5 Linear Change due to Moisture Content 7 15:44 Tuesday, May 27, 2008 The GLM Procedure Tukey's Studentized Range (HSD) Test for change_in_length NOTE: This test controls the Type I experimentwise error rate, but it generally has a higher Type II error rate than REGWQ. Alpha 0.05 Error Degrees of Freedom 128 Error Mean Square 0.003047 Critical Value of Studentized Range 5.31886 Minimum Significant Difference 0.121 Harmonic Mean of Cell Sizes 5.886792 NOTE: Cell sizes are not equal. Means with the same letter are not significantly different. Tukey Grouping B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B B A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C C Mean N treatment 0.24500 6 19 0.21500 6 8 0.19000 6 7 0.19000 6 14 0.18833 6 12 0.16167 6 10 0.15833 6 23 0.15500 6 13 0.15250 4 11 0.14500 6 9 0.14333 6 20 0.13833 6 15 0.13667 6 21 0.13333 6 16 0.13000 6 6 0.12833 6 17 0.12167 6 3 0.12000 6 2 137 B B B B B B B B B B C C C C C C C C C C C C C C C C 0.11667 6 1 0.11167 6 26 0.11000 6 25 0.10000 6 22 0.09667 6 4 0.09000 6 24 0.09000 6 18 0.08500 6 5