Phosphorus recovery and recycling from waste: An appraisal based on a French case study
Introduction
Phosphorus (P) plays a key role in sustainable food, feed, biofuel and fiber production. It is generally applied to agricultural soils through chemical P fertilizers. Such fertilizers are produced from phosphate rock. However, the supply of phosphate rock is limited at the global scale (Cordell et al., 2011, Cordell et al., 2009, Smil, 2000). Currently, 178.5 Mt of phosphate rock, equivalent to 23 Mt of P, is being mined every year, of which 90% is used for food production as fertilizer (approx. 82%) and feed additives (approx. 7%) (IFA, 2011). Due to the increase in food and feed demand, phosphate rock is expected to become increasingly scarce and expensive in the coming years (Cordell et al., 2009). Furthermore, phosphate rock deposits are very unequally distributed since more than 85% of this resource is controlled by only three countries (Morocco, China and the USA) (Van Vuuren et al., 2010). This may lead to severe geopolitical issues on P fertilizer availability and, in turn, on regional food production and food security (Dumas et al., 2011).
Preventing such depletion means limiting P losses and increasing P resource recycling along the food chain. Although rock phosphates are non-renewable at the human time scale, P as an element is recyclable since most of the P used for food production finally ends up in different waste systems, except for the P that becomes fixed in agricultural soils. Recent global phosphorus analyses have highlighted the key role played by the waste sector in P resource recycling (Elser and Bennett, 2011). A recent study has reported that, if collected, the P available from human urine and feces could account for 22% of the global P fertilizer demand (Mihelcic et al., 2011). However, many studies have reported low efficiencies of current waste management systems in recovering and recycling P from waste (Antikainen et al., 2005, Neset et al., 2008, Kalmykova et al., 2012). At the global scale, it is estimated that only 10–50% of P in human excreta is recycled to agricultural soils (Liu et al., 2008, Cordell et al., 2009), leading to large P losses through wastewater or municipal solid waste. These studies conclude that progress in that domain would help to achieve a better closed-loop P cycle and to meet future P demand (Cordell et al., 2011, MacDonald et al., 2012). However, waste streams are often multiple and complex and the related data are dispersed among many different sources. Moreover, availability of accurate figures is scarce in the area of P recovery and recycling from waste, thus creating uncertainty. In addition, waste stream recycling efficiency is often poorly assessed due to incomplete or inaccurate data sources (Cordell et al., 2012). There is, therefore, a need to better characterize these streams in order to assess to what extent the current and potential P recycling from these wastes could help to meet agricultural P demand. We developed such a characterization, using France as a case study, since it typically represents a Western country with a high P-input agriculture, a long food chain driven by affluent diets, and efficient, centralized waste collection and processing. The country scale offered opportunities to use consistent data sources and waste regulations.
The specific objectives of this study were: (1) to quantify P flows along the food processing, household wastewater and municipal waste chains at the country scale; (2) to quantify P recovery, P recycling and P losses at various stages of the waste streams; and (3) to identify opportunities for improved P resource recycling. A particular effort was made to estimate the overall consistency of the results through cross-checking with alternative, independent data sources about average food diets in France and P discharged into fresh water bodies.
Section snippets
System design and study area
The P flows along the food processing waste, household wastewater and municipal waste chains were assessed using a Substance Flow Analysis (SFA) at the country scale for France (Fig. 1). The basic objective of the SFA method is to quantify the pathways of a substance in, out and through a geographically considered system (Brunner and Ma, 2008). This makes it possible to estimate how P flows through the waste system, thereby assessing the contribution of the different waste streams and
P flows in handling waste
An estimated total of 2.3 kt P y−1 was lost to handling waste in 2006 and was considered to be entirely recycled to animal feed or to agricultural soils.
P losses in slaughterhouses
A total of 12.7 kt P y−1 was produced as slaughterhouse waste in 2006 (Fig. 3): 51.2 kt P y−1 entered the slaughterhouses as live animals, of which 37.7 kt P y−1 reached the food processing industry as animal carcasses and offal, and 0.8 kt P y−1 was further processed in the skin industry. The remaining 12.7 kt P y−1 was either further processed (10.7 kt P y−1 as
P recovery and recycling from current waste streams
The results highlighted that most P was recovered from the different waste streams for further processing (Table 2). However, only a moderate P fraction was actually recycled to agricultural soils or to the food and feed industry. Moreover, this fraction depended on the type of waste.
Food processing has been shown to produce a moderate amount of P waste (28 kt P y−1) and to recover it very efficiently. However, only 75% of P waste was actually recycled either in the food and feed industry or to
Conclusions
This paper provides a detailed quantification of P flows along the different waste processing systems in France and their recycling efficiencies to agricultural soils and to the food/feed industry. Results showed that P recovery was generally high from most waste but that the P recycling efficiency to agricultural soils and to the food/feed industry was only 51%: this P recycling efficiency was 74.6% for food processing waste, 43.1% for household wastewater and 47.4% for municipal waste.
Acknowledgements
This work was funded by Bordeaux Sciences Agro (Univ. Bordeaux) and the “Environment and Agronomy” Division of INRA. We thank Gail Wagman for improving the English.
References (73)
- et al.
Stocks and flows of nitrogen and phosphorus in the Finnish food production and consumption system
Agric Ecosyst Environ
(2005) - et al.
Separate collection of household food waste for anaerobic degradation – comparison of different techniques from a systems perspective
Waste Manage
(2012) - et al.
A substance flow analysis of phosphorus in the UK food production and consumption system
Resour Conserv Recycl
(2013) - et al.
The story of phosphorus: global food security and food for thought
Glob Environ Change Policy Dimens
(2009) - et al.
Towards global phosphorus security: a systems framework for phosphorus recovery and reuse options
Chemosphere
(2011) - et al.
The phosphorus mass balance: identifying ‘hotspots’ in the food system as a roadmap to phosphorus security
Curr Opin Biotechnol
(2012) - et al.
Modeling biogeochemical processes of phosphorus for global food supply
Chemosphere
(2011) - et al.
NORIT AirLift MBR: side-stream system for municipal waste water treatment
Desalination
(2007) - et al.
The contribution of food waste to global and European nitrogen pollution
Environ Sci Policy
(2013) - et al.
Improvement of effluent quality for reuse in a dairy farm
Water Sci Technol
(1996)