nvironmentali mpacts ofw ater c onsumption ing …

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1 ENVIRONMENTAL IMPACTS OF WATER CONSUMPTION IN GLOBAL CROP PRODUCTION Stephan Pfister, Peter Bayer, AnneAe Koehler, Stefanie Hellweg ETH Zurich, InsMtute for Environmental Engineering, Ecological Systems Design Group LCA Discussion Forum Lausanne, 21 June 2011

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Page 1: NVIRONMENTALI MPACTS OFW ATER C ONSUMPTION ING …

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ENVIRONMENTAL  IMPACTS  OF  WATER  CONSUMPTION  IN  GLOBAL  CROP  PRODUCTION  

 

 Stephan  Pfister,  Peter  Bayer,  AnneAe  Koehler,  Stefanie  Hellweg  

ETH  Zurich,  InsMtute  for  Environmental  Engineering,    Ecological  Systems  Design  Group  

   

LCA  Discussion  Forum  

Lausanne,    21  June  2011  

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MoMvaMon  

 •  Agriculture  is  globally  the  most  important  sector  concerning  water  consump5on  

•  LCA  increasingly  used  in  decision  making,  but  so  far  o<en  neglect  water-­‐consump5on  

 à  Need  for  comprehensive  tools  to  assess  and  improve  the  environmental  impacts  of  agricultural  products    

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Resource    ExtracMon  

?  

Use  

Recycling  Reuse  

Disposal  

ProducMon  ?  

?  

Resources  

Emissions  

Global  value  chains  

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Inventory  analysis:  Modelling  land  use  and  water  consumpMon    of  crop  produMon  (160  crops)  

•  High  spa5al  resolu5on  (~10  km  resolu5on)  –  Crop  produc5on  in  2000  (Monfreda  et  al.  2008)  

•  Yield  and  crop  cul5va5on  data  based  on  sta5s5cs  and  remote  sensing  

– Water  consump5on:  •  FAO  approach  and  irriga5on  maps  

–  Land  use:  •  based  on  yields  and  growth  periods    

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Detailed  results  available  for  160  individual  crops:  Pfister  et  al.  (2011)  Environmental  impacts  of  water  use  in  global  crop  

producMon:  hotspots  and  trade-­‐offs  with  land  use.  ES&T,  online  

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LCIA:  Water  stress  index  (WSI)  

à    Takes  into  account  water  availability,  use,  and  seasonal/annual  variaMon  in  precipitaMon  .  

Pfister  S,  Köhler  A,  Hellweg  S,  ES&T  43,  4098  –  4104,  2009  (based  on  data  from  Alcamo  et  al.)  

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LCIA:  Land  stress  index  (LSI)  

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LCI  results:  IrrigaMon  water  consumpMon  of  wheat  culMvaMon  

0  0-­‐100  100-­‐200  200-­‐300  300-­‐400  400-­‐500  500-­‐700  700-­‐1000  1000-­‐2000  >2000  

m3  /  ton  

[Volume/output]  

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LCIA  results:  Water  deprivaMon  from  wheat  culMvaMon  

0  0-­‐100  100-­‐200  200-­‐300  300-­‐400  400-­‐500  500-­‐700  700-­‐1000  1000-­‐2000  >2000  

m3  /  ton  

[WSI-­‐weighted  volume/output]  

Ph.D.  S.  Pfister  

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Ph.D.  S.  Pfister  

Tradeoff  between  land  and  water  impacts  of  wheat  culMvaMon  

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SituaMon  in  the  year  2000  

10  

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SituaMon  in  the  year  2000    Tradeoff  between  Water  and  Land  Use  

 

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Outlook  „myEcosystem“    

12  Ph.D.  F.  Verones,  L.  deBaan,  M.  Curran  

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Future  scenarios  

Ph.D.  S.  Pfister  

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Future  scenarios  

           2000                              2050                                    +50%  

   

             

IPCC  A1B  scenario:    9  billion  people  

Ph.D.  S.  Pfister  

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Minimal  land  use  

Minimal  water  consumpMon  

Scenarios  2050  

•  60%  addi5onal  food  energy  supply  –  Intensifica5on:  Full  irrigaMon  and  fer5liza5on  &  50%  food  waste  reducMon  

–  Expansion  on  suitable  area  for  rainfed  agriculture:  •  Maize  and  wheat  (Fischer  et  al.  2000)  

•  Expansion  on  pasture  

15  

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Minimal  land  use  

Minimal  water  consumpMon  

Scenarios  2050  

•  60%  addi5onal  food  energy  supply  –  Intensifica5on:  Full  irrigaMon  and  fer5liza5on  &  50%  food  waste  reducMon  

–  Expansion  on  suitable  area  for  rainfed  agriculture:  •  Maize  and  wheat  (Fischer  et  al.  2000)  

•  Expansion  on  pasture  

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Results  irrigaMon  water  consumpMon  

 Strategies:  –  Intensifica5on    &  waste  reduc5on  

   – Expansion  on  pastures  

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IrrigaMon  

IrrigaMon  

Irriga5on:  +  1125  km3  (64%)  

Irriga5on:  +169  km3  (10%)    

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Expansion:  Land  stress  

•  Mainly  in  Africa  (ca.  2/3)  •  followed  by  South  America  (ca.  1/4)    

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Conclusions  

•  Pressure  on  water  and  land  resources  is  already  high  in  some  areas  and  will  be  amplified  in  the  future  

•  Methods  for  spa5ally  resolved  inventory  and  impact  assessment  are  becoming  available  for  water  and  land  use  à  facilitates  LCA  as  decision-­‐support  tool  for  product-­‐related  decisions  of  retailers,  producers,  consumers  

•  Interna5onal  coopera5on  is  necessary  to  minimize  global  environmental  impacts  

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BACKUP  SLIDES  

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Results  scenarios  Scenario 1 (efficient

intensification)

Scenario 2 (expansion on

pastures)

Scenario 3 (rainfed

expansion)

Scenario 4 (expansion and intensification)

Total Water (km3) 1’203 (+22%) 1’088 (+20%) 1’077 (+20%) 2291 (+42%) Irrigation Water (km3) 1’125 (+64%) 169 (+10%) 142 (+8%) 1’294 (+73%) Average WSI 0.569 0.484 0.479 0.559

Land stress (1000 km2*yr) none 552 (+14%) 534 (+14%) 552 (+14%)

Irrigation water land-stress equivalent (1000 km2*yr)

450 (+64%) 68 (+10%) 57 (+8%) 518 (+73%)

Total land-stress equivalent (land & water) (1000 km2*yr)

450 (+10%) 620 (+14%) 591 (+14%) 1070 (+24%)

Total land-stress equivalent / edible energy produced (m2*yr / 1000 kcal)

0.28 (-13%) 0.23 (-29%) 0.23 (-29%) 0.21 (-33%)

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GIS  IntegraMon  in  a  pilot  solware:  example  of  strawberry  producMon  in  Spain  

 Kestenholz  2008    

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Midpoint  CF:  Water  Stress  Index  (WSI)  

•  Includes:  – Withdrawal  to  availability  (WTA)  

–  Variability  in  precipita5on  (VF)  –  Flow  regula5on  (highly  regulated  =  SRF)  

•  Index  following  logis5c  func5on:  

⎧ ×⎪= ⎨

×⎪⎩

* -

VF WTA for SRFWTAVF WTA for non SRF

( )− ⋅=

+ −*6.4 1

0.01

11 1WTA

WSIe

     

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Water  stress  index  (WSI)  

 

         WSI  

WTA*  

“Open  scale”  

Extreme  

 Severe  

 

   

Moderate    

 No  

 

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Impacts  on  resources  

•  Deple5on  of  water  stocks:  overuse  

•  Desalina5on  as  backup  technology  

>⎧= ⎨

≤⎩

- 1

,

1 0 1

WTAWTA

depletion i

for WTAF

for WTA

Δ = ⋅ ⋅depletion surplus consumptiveRD F MJ WU

Pfister,  Koehler  &  Hellweg  (2009),  ES&T    43(11):  4098–4104  

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Aggregated  damage  factors  For  comparing  overall  relevance  of  water  consump5on  in    “ecoindicator  99”  method  

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Damage  factors  

Impacts  on  human  health  

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Damage  factors  

Impacts  on  human  health  

Impacts  on  ecosystem  quality  

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Damage  factors  

Impacts  on  human  health  

Impacts  on  ecosystem  quality  

Impacts  on  resources  

Pfister  S,  Köhler  A,  Hellweg  S,  ES&T  43,  4098  –  4104,  2009    

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ApplicaMon  to  agriculture:  Inventory  on  high  spaMal  resoluMon  

•  Combining  global  data  sets  in  GIS  –  Climate  data  

–  Official  sta5s5cs  

–  Remote  sensing  data  

•  Calcula5on  of  irriga5on  water  requirements  (IWR)  –  FAO  approach  (on  10km*10km  resolu5on)  

•  Combina5on  with  regional  characteriza5on  factors  –  E.g.  midpoint:  Water  stress  index  (WSI;  Pfister  et  al.  2009)  

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Trade-­‐off  water  -­‐  land  

Water  footprint  (m3  /  kg)  

Land

 footprint  (m

2  yr

  /  kg)  

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Pasture  food  losses  

•  44%  of  meat  energy  from  pasture/grassland/rangeland  

•  6%  of  pasture  /  natural  land  change  

pasture  output  change    (NPP0  weighted)  

animal  feed  change    (43.9  %  pasture)  

change  food  energy  (15.1%  animal  products)  

sc2   -­‐6.1%   -­‐2.7%   -­‐0.4%  SC3   -­‐3.7%   -­‐1.6%   -­‐0.2%