Environmental Impacts of Multi-Storey Buildings Using Different ...

Environmental Impacts of Multi-Storey Buildings Using Different ... Environmental Impacts of Multi-Storey Buildings Using Different ...

10.07.2015 Views

- 102 -Regional Council has put in place regulations preventing the use of treated timber inparticleboard production.Wood-plastic and wood-cement composites are another potential application of recycledtreated timber. Wood-cement composites can include cement-bonded particleboard, woodfibre cement boards, concrete construction blocks, acoustic barriers and roof tiles. In general,these products perform well, in some cases better than alternatives using untreated wood.Properties such as susceptibility to leaching, bending strength and stiffness can be improved.Wood-plastic composites are at a very early stage and therefore little is known about theirpotential properties. Ultimately however, wood-cement and wood-plastic composites aremerely shifting the problem of difficult waste further along the life cycle. Waste disposal ofthese composites could pose further problems at the end of these products’ lives.Mulch and compost are other potential uses for treated timber waste. However, with thesurface area vastly increased, and a high exposure to water, the risk of leaching of chemicalsfrom CCA-treated timber is likely to be multiplied many times.8.6.4 Extended Producer Responsibility (EPR)Extended producer responsibility (EPR) is a concept which places the responsibility for theend-of-life environmental impacts of a product on the producer. This involves facilitatingreturn of the product to the producer, followed by processing to recycle what is possible andminimise waste. In New Zealand EPR schemes exist for cellphones, unused paint andwhiteware. Internationally, schemes exist for end-of-life vehicles, electronic equipment,packaging, batteries and others. Treated wood would be an excellent target for an EPRscheme as it is a waste that is potentially hazardous, takes up unnecessary space in landfills,and has the potential for energy recovery. Also with the Waste Minimisation (Solids) Billappearing before parliament, producers are becoming aware of the need to be responsible withtheir waste.New Zealand currently has no timber EPR schemes in place for either untreated or treatedtimber.However, the upcoming Waste Minimisation Bill specifies that the Waste MinimisationAuthority will be set up, which will collect a Waste Disposal Levy. This levy will be chargedat the time of disposal of waste, and will fund the authority, as well as funding projects toassist with waste minimisation.The Waste Minimisation Bill contains a section on EPR (though it uses the terms EPR andproduct stewardship interchangeably). This Bill does not propose legislation for compulsoryproduct stewardship/EPR schemes; it focuses on the compulsory participation of a produceronly if a product stewardship/EPR scheme already exists. This participation would includeprovision of collection facilities, and a minimum recycling, reuse or material recovery rate of75% of end-of-life products received at these recycling facilities. The bill also states thatsufficient notice will have to be given if there is an intention to consider the need for aproduct stewardship programme for a product.

- 103 -The Waste Minimisation Bill stemmed from the Ministry for the Environment WasteStrategy. The most relevant part of this strategy to treated timber is the statement: “ByDecember 2008, there will have been a reduction of construction and demolition waste tolandfills of 50 percent of December 2005 levels measured by weight.” This will significantlyaffect wood waste, as inert wastes such as concrete are already sent to clean-fills.8.6.5 Sorting of Timber WasteIdeally, in time, a recycling/disposal technology that can process both treated and untreatedtimber will eventuate. However, if this is not feasible, any recycling of treated timber wastewould have to involve a sorting process to separate treated timber from untreated wood. Anumber of options could offer sorting solutions ranging from visual sorting and PAN stain (astain formulation that can detect copper-containing preservatives), to X-ray fluorescence (anon-destructive characterisation technique that can detect different elements in solid or liquidsamples) and laser-induced breakdown spectroscopy (LIBS; use of a laser to ablate and ionisewood into a plasma).8.6.6 The Way Forward for NZThe Scion conference paper “Extended Producer Responsibility of Treated Timber Waste”(Love, 2007) offers recommendations for the future utilisation of treated timber.New Zealand’s treated timber producers should strive to establish a voluntary EPR schemebefore any legislation is put in place. This would require establishing who the responsibleproducers of treated timber are (wood producers, treatment chemical producers, forestrycompanies) and what processes should be implemented to deal with treated timber waste.There are many different sorting & treatment options available, in varying stages of maturity,and the option that should be chosen depends on whether carbon sequestration, energyproduction or life-cycle thinking are the key priorities and also on ongoing research, such asthat into leaching and decomposition rates for treated wood in landfills.Research would give a clearer idea of whether landfilling is actually an environmentallyacceptable practice for treated timber. At present, nowhere else in the world has landfillingbeen considered an acceptable solution for treated timber waste in the future, due to theunknowns about the behaviour of treated timber in landfills over much longer time periodsEnergy recovery from treated (and untreated) timber waste provides a way to significantlyreduce the volume of wood waste which would normally end up in landfills. The downside tothis is that the sequestration of CO 2 in the timber is no longer a benefit, as CO 2 will bereleased upon incineration, gasification or pyrolysis of the timber. This is still considered a‘carbon neutral’ process as the CO 2 that is released is essentially carbon that the plantabsorbed during its life time. The debate here is between ‘carbon neutral’ processes that couldprovide energy, and carbon-reducing processes that take up space in landfills and couldpotentially leak arsenic into the earth.

- 103 -The Waste Minimisation Bill stemmed from the Ministry for the Environment WasteStrategy. The most relevant part <strong>of</strong> this strategy to treated timber is the statement: “ByDecember 2008, there will have been a reduction <strong>of</strong> construction and demolition waste tolandfills <strong>of</strong> 50 percent <strong>of</strong> December 2005 levels measured by weight.” This will significantlyaffect wood waste, as inert wastes such as concrete are already sent to clean-fills.8.6.5 Sorting <strong>of</strong> Timber WasteIdeally, in time, a recycling/disposal technology that can process both treated and untreatedtimber will eventuate. However, if this is not feasible, any recycling <strong>of</strong> treated timber wastewould have to involve a sorting process to separate treated timber from untreated wood. Anumber <strong>of</strong> options could <strong>of</strong>fer sorting solutions ranging from visual sorting and PAN stain (astain formulation that can detect copper-containing preservatives), to X-ray fluorescence (anon-destructive characterisation technique that can detect different elements in solid or liquidsamples) and laser-induced breakdown spectroscopy (LIBS; use <strong>of</strong> a laser to ablate and ionisewood into a plasma).8.6.6 The Way Forward for NZThe Scion conference paper “Extended Producer Responsibility <strong>of</strong> Treated Timber Waste”(Love, 2007) <strong>of</strong>fers recommendations for the future utilisation <strong>of</strong> treated timber.New Zealand’s treated timber producers should strive to establish a voluntary EPR schemebefore any legislation is put in place. This would require establishing who the responsibleproducers <strong>of</strong> treated timber are (wood producers, treatment chemical producers, forestrycompanies) and what processes should be implemented to deal with treated timber waste.There are many different sorting & treatment options available, in varying stages <strong>of</strong> maturity,and the option that should be chosen depends on whether carbon sequestration, energyproduction or life-cycle thinking are the key priorities and also on ongoing research, such asthat into leaching and decomposition rates for treated wood in landfills.Research would give a clearer idea <strong>of</strong> whether landfilling is actually an environmentallyacceptable practice for treated timber. At present, nowhere else in the world has landfillingbeen considered an acceptable solution for treated timber waste in the future, due to theunknowns about the behaviour <strong>of</strong> treated timber in landfills over much longer time periodsEnergy recovery from treated (and untreated) timber waste provides a way to significantlyreduce the volume <strong>of</strong> wood waste which would normally end up in landfills. The downside tothis is that the sequestration <strong>of</strong> CO 2 in the timber is no longer a benefit, as CO 2 will bereleased upon incineration, gasification or pyrolysis <strong>of</strong> the timber. This is still considered a‘carbon neutral’ process as the CO 2 that is released is essentially carbon that the plantabsorbed during its life time. The debate here is between ‘carbon neutral’ processes that couldprovide energy, and carbon-reducing processes that take up space in landfills and couldpotentially leak arsenic into the earth.

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