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WRAP: Comprehensive life-cycle analysis of WRAP: Comprehensive life-cycle analysis of plasterboard plasterboard A new study conducted by WRAP (Waste and Resources Action Programme) has assessed the environmental impact of plasterboard, including a detailed evaluation of the CO 2 emissions associated with every stage of the product’s life-cycle. Dave Marsh, construction project manager at WRAP, outlines the findings of this new study, the most extensive to be conducted in the UK to date. Ad Index Subscribe Contents Graph 1: Life-cycle stages and their contribution to CO 2 emissions. A s part of its work to facilitate and encourage greater reduction and recycling of waste plasterboard, WRAP commissioned a comprehensive life-cycle as- sessment (LCA) which investigated the environmental impact of one standard sheet of Type A plasterboard – the most common plasterboard product used in the UK. e findings of the study now enable the plaster- board manufacturing and recycling sectors to identify where the CO 2 emissions are greatest and therefore where positive interventions could be made to reduce the environmental impact of the product and improve materials resource efficiency. One of the headline findings reported in the study was that over the entire life-cycle, each sheet of the baseline plasterboard assessed was found to cause the emission of the equivalent of 12kg of CO 2 . As shown in Graph 1, the life-cycle stages contributing the high- est emissions were production of conventional gypsum (the typical mix of natural and synthetic gypsum used in the UK); plasterboard production; and landfill dis- posal of waste plasterboard. e study evaluated three scenarios with different levels of recycled gypsum content in the plasterboard. e baseline scenario was the average mix of gypsum currently used in conventional Type A plasterboard production in the UK, which already includes around 10.5% recycled gypsum from waste plasterboard. A second scenario saw the content of recycled gypsum increased to 15%; and a third scenario involved the content of recycled gypsum increased to 25% – the maximum level of inclusion currently considered to be feasible. e study showed that using more recycled gypsum from waste plasterboard in the manufacture of the new plasterboard contributed to a small reduction in the associated CO 2 emissions during the course of that product’s lifecycle. is results from avoiding the need to produce, transport and pre-process conventional gypsum and avoiding landfill disposal of the waste plasterboard through recycling. While this benefit was only small when compared to the overall CO 2 impacts of plasterboard manufacture, it is significant in that it indicates that increasing the content of recycled gypsum in plasterboard has no negative CO 2 impact. When considering the waste stage of the plasterboard life-cycle, processing it to produce recycled gypsum was found to have lower global warming potential than disposal of it in mixed waste landfill. is aspect of the study is sig- nificant in that it opens up the potential of future work being conducted to quantify the benefits of the open loop recycling of waste plasterboard into products and applications other than plasterboard. is would further support a number of initiatives led by WRAP over the last three years in developing these alternative markets for recycled gypsum; this is already considered important as in the UK more waste plasterboard is currently produced that could be feasibly used back into the manufacture of new plasterboard. Both open and closed loop recycling routes are required to maximise diversion of plas- terboard waste from landfill. Dave Marsh Construction project manager, Waste and Resources Action Programme, WRAP global gypsumMAGAZINE 24 global global gypsum gypsumMAGAZINE MAGAZINEMay 2008 0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 Gypsum production (conventional) Gypsum transport(conventional) Gypsum preprocessing (conventional) Gypsum production (recycled process waste) Gypsum production (closed loop recycled post-consumer waste) Other recycling outputs Gypsum preprocessing (recycled) Stucco production (gypsum calcining) Facing paper production Plasterboard production Packaging and distribution Collection and transport for recycling Collection and transport for disposal Disposal kg CO 2 -equivalents 25% recycled content (low transport) 25% recycled content (high transport) Baseline (low transport) Baseline (high transport)

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Page 1: WWRAP: Comprehensive life-cycle analysis of RAP ... Comprehensive life-cycle analysis of RAP: ... gypsum and avoiding landfi ll disposal of the waste plasterboard through recycling

WRAP: Comprehensive life-cycle analysis of WRAP: Comprehensive life-cycle analysis of plasterboardplasterboard

A new study conducted by WRAP (Waste and Resources Action Programme) has assessed the environmental impact of plasterboard, including a detailed evaluation of the CO2 emissions associated with every stage of the product’s life-cycle. Dave Marsh, construction project manager at WRAP, outlines the fi ndings of this new study, the most extensive to be conducted in the UK to date.

Ad IndexSubscribeContents

Graph 1:Life-cycle stagesand theircontribution to CO2 emissions.

As part of its work to facilitate and encourage greater reduction and recycling of waste plasterboard,

WRAP commissioned a comprehensive life-cycle as-sessment (LCA) which investigated the environmental impact of one standard sheet of Type A plasterboard – the most common plasterboard product used in the UK. Th e fi ndings of the study now enable the plaster-board manufacturing and recycling sectors to identify where the CO2 emissions are greatest and therefore where positive interventions could be made to reduce the environmental impact of the product and improve materials resource effi ciency.

One of the headline fi ndings reported in the study was that over the entire life-cycle, each sheet of the baseline plasterboard assessed was found to cause the emission of the equivalent of 12kg of CO2. As shown in Graph 1, the life-cycle stages contributing the high-est emissions were production of conventional gypsum (the typical mix of natural and synthetic gypsum used in the UK); plasterboard production; and landfi ll dis-posal of waste plasterboard.

Th e study evaluated three scenarios with diff erent levels of recycled gypsum content in the plasterboard.

Th e baseline scenario was the average mix of gypsum currently used in conventional Type A plasterboard production in the UK, which already includes around 10.5% recycled gypsum from waste plasterboard. A second scenario saw the content of recycled gypsum increased to 15%; and a third scenario involved the content of recycled gypsum increased to 25% – the maximum level of inclusion currently considered to be feasible.

Th e study showed that using more recycled gypsum from waste plasterboard in the manufacture of the new plasterboard contributed to a small reduction in the associated CO2 emissions during the course of that product’s lifecycle. Th is results from avoiding the need to produce, transport and pre-process conventional gypsum and avoiding landfi ll disposal of the waste plasterboard through recycling. While this benefi t was only small when compared to the overall CO2 impacts of plasterboard manufacture, it is signifi cant in that it indicates that increasing the content of recycled gypsum in plasterboard has no negative CO2 impact.

When considering the waste stage of the plasterboard life-cycle, processing it to produce recycled gypsum

was found to have lower global warming potential than disposal of it in mixed waste landfi ll. Th is aspect of the study is sig-nifi cant in that it opens up the potential of future work being conducted to quantify the benefi ts of the open loop recycling of waste plasterboard into products and applications other than plasterboard. Th is would further support a number of initiatives led by WRAP over the last three years in developing these alternative markets for recycled gypsum; this is already considered important as in the UK more waste plasterboard is currently produced that could be feasibly used back into the manufacture of new plasterboard. Both open and closed loop recycling routes are required to maximise diversion of plas-terboard waste from landfi ll.

Dave Marsh Construction project manager, Waste and Resources Action Programme, WRAP

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Page 2: WWRAP: Comprehensive life-cycle analysis of RAP ... Comprehensive life-cycle analysis of RAP: ... gypsum and avoiding landfi ll disposal of the waste plasterboard through recycling

globalgypsum MAGAZINE

26 globalgypsum MAGAZINE May 2008

Minimising the amount of waste being produced is the most prefer-able waste option – and sits at the top of the waste hierarchy. Th e study specifi cally investigated this scenario and the fi ndings clearly reinforce it by showing that reducing the amount of plasterboard waste being generated on construction sites was a key factor in reducing plas-terboard’s environmental impact. In global warming terms, the study found that a saving of up to 158t of CO2 equivalents could be achieved by reducing waste from 15% to 5% on a UK£750,000 example contract. Th is saving equated to 62kg of CO2 equivalents per ton of plasterboard used and – even though the size of the contract could be seen as a mod-est example – has the same eff ect as removing 50 cars from UK roads for one year.

Crucially, for manufacturers operating take-back schemes for waste plasterboard, the study found that the distance waste plasterboard travels is also extremely relevant in determining the range of the prod-uct’s environmental impact. Th e approach taken for this LCA was to model two alternative scenarios representing extremes for the UK for the total transport distance for the plasterboard waste to the recycler and the onward transport of the recycled gypsum to its point of use. With these param-eters set at extremes of

50km (shortest distance) and 450km (longest distance), it was determined that transporta-tion was a key contributor to environmental impacts in several key areas, including the emission of greenhouse gases.

Th e overall environmental impact of waste plaster-board could thus be reduced by decreasing the distances travelled by the waste collected and the recycled gypsum powder that is produced. Th is suggests that the use of bulking stations would bring about reductions in emis-sions by enabling larger loads and reducing the number of individual vehicle movements.

Also commonly called ‘cradle-to-grave’ or ‘cradle-to-cradle’ assessments, the LCA encompassed all the steps and processes in the product’s life, from production and its use of raw materials, through product manufacture, distribution and packaging, installation, use and fi nally, disposal or recycling. It tested a number of scenarios including waste reduction on site, and increasing the content of recycled gypsum in plasterboard manufac-ture.

Th e study incorporated information provided by a number of bodies including the Gypsum Products Development Association (GPDA) which represents the UK’s three plasterboard manufacturers: British Gyp-sum, Knauf Drywall, and Lafarge Plasterboard. It also included input from plasterboard recyclers and waste management companies. Th e high quality of the infor-mation and data provided made the study the most up to date of its type.

Th e LCA provides UK plasterboard manufacturers with a new evidence base to support their drive towards the 2010 targets set as part of the Ashdown Agreement, a voluntary agreement by the manufacturers to reduce plasterboard going to landfi ll. Th ese targets include re-ducing the amount of production waste being sent to landfi ll to 10,000t/y and increasing takeback and recy-cling of plasterboard to 50% of new construction waste arisings.

Under the infl uence of the Ashdown Agreement and other sustainability drivers, manufacturers are already taking signifi cant strides towards establishing methods of minimising the amount of plasterboard waste pro-duced and increasing the amount of plasterboard waste that is recycled.

Th e environmental benefi ts of reducing wastage of plasterboard are further enhanced through recycling any plasterboard waste that does arise, and can be max-imised by ensuring the distances travelled by both the waste and the recycled materials produced are kept as short as possible.

Th e full report – Life-cycle Assessment of Plaster-board – can be downloaded as a .pdf document free from the WRAP website – www.wrap.org.uk/plaster-board.