Martina
Peters
*a and
Niklas
von der Assen
b
aBayer AG, Corporate Technology & Manufacturing, 51368 Leverkusen, Germany. E-mail: martina.peters@bayer.com
bRWTH Aachen University, Schinkelstraße 8, 52062 Aachen, Germany
More than 200 years later, volunteer fire departments are common practice, while the superordinate principle of “prevention” is still questioned every now and then – especially when it comes to environmental topics. Yet, in United States politics in 1990, the Pollution Prevention Act yielded a national policy focusing on the prevention of pollution at the source rather than the treatment of pollutants after formation. Coined by Paul Anastas as “Green Chemistry” and applied far beyond the United States borders, it comprises the design of chemical products and processes that reduce or eliminate the use and generation of hazardous substances.
Based on this, Paul Anastas and John Warner formulated the so-called “12 Principles of Green Chemistry” (Fig. 1) in 1998 – in a narrow interpretation, guidelines for chemists seeking to lower the ecological footprint of their products.2 The first principle – It is better to prevent waste than to treat or clean up waste after it is formed – is often referred to as overarching. An example: no or less waste is achieved by higher atom economy (#2, #9), by avoidance of unnecessary auxiliary substances (#5) and energy-related waste/pollution (#6).
Fig. 1 The 12 Principles of Green Chemistry2 |
To provide an answer to these questions it is important to keep in mind the overall system boundaries as well as the multi-dimensionality of environmental impacts. Waste prevention is of course desirable, but only if it is more profitable, environmentally reasonable as well as cost-efficient than waste treatment. Although often taken for granted, the answer is not always crystal clear as the following example shows:
In the synthesis of the antiepileptic drug rufinamide, a new process pathway via 2,6-difluorobenzyl chloride instead of the corresponding bromide was identified to produce less waste (lower process mass intensity) and cause a lower ozone depletion potential. However, a comprehensive life cycle assessment showed that the new (not fully optimized) route causes higher impacts in all other considered environmental categories.4
To judge whether waste prevention is “better”, it is not enough to simply add the amounts of generated waste as in the ‘process mass intensity’ (PMI) or E-factor. It is often also not sufficient to consider a single factor describing the “badness” of waste as in the EQ-factor.5 The “badness” of waste and the “betterness” of waste prevention have multiple, often contradictory dimensions. We can conclude that waste prevention is clearly better than waste treatment only if prevention is more reasonable in all environmental and economical dimensions.
The easiest approach to waste prevention would be to not produce the product itself. While this is typically not feasible, it might be feasible to produce entirely novel products with higher quality and longer product lifetime so that lower amounts of this product are required to fulfill a certain function. Another approach is to prevent the product from becoming harmful waste, e.g. by making plastics bio-degradable. Along this line of thought, we need to rethink the concept of waste by turning existing waste into a new resource. The idea is not new: in the 1970s, Richard Buckminster Fuller stated that “…pollution is nothing but resources we are not yet harvesting”. In its simplest form, this concept is realized in the usage of waste in waste incineration for thermal energy recovery. A more sophisticated example is the utilization of carbon dioxide for the production of polymers as in the “Dream Production” project.7 In the purest form of this concept, also referred to as ‘cradle-to-cradle’, nothing is waste(d) and all material cycles are fully closed.8
We believe that the principle is still valid but we have to understand it more widely, going from a limited mass-based view of waste to more holistic thinking: (1) consider the multi-dimensional quality of waste. (2) Move from “waste per kg product” towards “waste per function delivered” and thus, we should aim at improving product quality and functionality. (3) Look at the overall life cycle: next to waste from production, we also need to consider the end-of-life waste after product consumption, including recycling of hitherto perceived wastes into valuables as well as to design for recyclability.
This journal is © The Royal Society of Chemistry 2016 |