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DANTES Akzo Nobel examples Johan Widheden

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Presentation on theme: "DANTES Akzo Nobel examples Johan Widheden"— Presentation transcript:

1 DANTES Akzo Nobel examples Johan Widheden
Vem är du, din grupp och ditt företag? Varför är ni med i DANTES?

2 Akzo Nobel Multi-national, market driven, technology based company created in 1969. Serving customers with healthcare products, coatings and chemicals 13 bln euros net sales in 2003 More than employees Operates in 80 countries

3 Sustainable Development group
Klas Hallberg Karin Sanne Malin Bogeskär Anna-Lena Palm Johan Widheden Life Cycle Assessments Environmental Product Declarations Eco-efficiency analyses Environmental Risk Assessments Environmental Impact Assessments Transport and energy analyses Provide different environmental services, such as:

4 Registration, Evaluation and Authorisation of CHemicals
EU New chemicals policy - REACH Registration, Evaluation and Authorisation of CHemicals Merging of 2 current systems for new (1980-) and existing (-1980) chemicals into a new system Registration of all chemicals >10 tonne/year in a central database Main responsibility for collecting and evaluating data lies on the producers and importers of chemicals Legislation 2 years from now (2007?) Progressively installed, completed 2018 99% of the chemicals are existing chemicals, for which there are not the same requirements as for the new chemicals. For these existing chemicals we do not have enough knowledge

5 Risk Characterisation Ratio
Environmental Risk Assessment (ERA) Data evaluation Exposure assessment Effect assessment PEC = Predicted Environmental Concentration PNEC = Predicted No-Effect Concentration RCR < 1 No risk! ERA life cycle The basis for all of the calculations are presented in the Technical Guidance Document (TDG) for new and existing chemicals. Risk Characterisation Ratio RCR = PEC / PNEC

6 ERA results Scenario RCRwater RCRsoil RCRsed Production <1
<<1 Formulation Use Not enough data

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8 ERA of the use of a flotation agent
Flows of water and contaminants in a mining area

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10 Life Cycle Assessment (LCA) + ERA
Including all activities from cradle to grave Potential environmental impacts from activities, e.g.: Resource use Global warming Wastes ERA including production, formulation, use and waste of chemical Risk of impacts on ecosystems (living organisms) from releases of a chemical product, Difficult to include direct effects of substances on ecosystems and humans

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13 Sustainable Development
Ecology and Economy Sustainable Development Planet People Profit Eco-efficiency Eco-efficiency - the ratio of economic creation to ecological destruction

14 The BASF Eco-Efficiency Analysis method
Developed by BASF and has been usedby them and other companies for a couple of years now. Environmental impact to total cost for the customer. Always a comparison!

15 Ecological impact Energy Land use Emissions Raw materials
Wastes Water emissions Air emissions Land use Emissions Raw materials Developed within a chemical company: Environmental aspects from a life cycle perspective, Safety aspects also from a similar perspective and human health aspects. Raw materials: weighting factor depending on depletion rate of the earth’s resources Land use: 5 categories of increasing ecological severity (weighting factor) Energy: MJ primary energy source per functional unit (unit benefit) Emissions: Wastes: 4 categories depending on landfill costs Water: weighting factors based on threshold limits (Critical Water Volume; dilution factor) Air: weighting factors based on substance’ potential to effect categories (GWP, ODP, POCP and AP) Risk potential: (severity x probability) risk factors for different risk occurrences within production, use and disposal Toxicity potential: 6 categories of increasing severity based on R-phrases for the produced substance as well as its constituent substances Toxicity potential Risk potential

16 Weighting factors Relevance weighting Societal weighting
- based on public and expert opinions on the relative importance of environmental, health and safety impact categories - differs between regions and countries Relevance factor the life cycle based effect categories (functional unit compared to region) Societal factor for all (value of reduction), which differs between countries, based on public and expert opinions on the relative importance of environmental impact categories.

17 Societal weighting factors
An example of the societal weighting factors.

18 Included costs depend on functional unit (benefit)
Costs analysis Included costs depend on functional unit (benefit) Costs for the end customer sales price + costs during use + disposal costs Varies depending on e.g. the durability of the product Societal costs could be included

19 Eco-efficiency evaluation of colorants
Comparing the BASF eco-efficiency method with a study made by Akzo Nobel

20 Environmental and economic impact
LCA-based environmental impact Consumption of energy Consumption of resources Land use Emissions Economic impact Environmental costs e.g. environmental taxes, tests, investments on site Weighting method According to “EPS” Cradle to gate. No health or safety related impacts. The EPS method is based on the definition of five safeguard subjects and the willingness to pay for protecting them. The five safeguard subjects, human health, biological diversity, ecosystem production capacity, abiotic resources and cultural and recreational values are based on the UN’s Rio declaration. [Steen 1999] The safeguard subjects are divided in sub-categories, called unit effects. Unit effects could for example be: pollution-caused decreased production of 1 kg of crop, seed, wood or fish. Each unit effect has an economic value described as the willingness to pay to avoid the negative effects defined by the unit effect. Costs for the company, not the customer.

21 Eco-efficiency results
0,0 1,0 2,0 0,8 1,2 Cost (normalized) Environmental impact (normalized) Old Colorant New Colorant

22 Other findings Eco-efficiency analysis not time consuming if based on collected LCA data Environmental costs found to be a relatively large part of the total costs of the studied colorants Environmental costs of the surfactants (used in the colorants) 4,5% – 6,5% of the sales price (~1% normally reported)

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