Page 37 - Kutnar, Andreja, et al., eds., 2015. Proceedings of the 1st COST Action FP1307 International Conference - Life Cycle Assessment, EPDs, and modified wood. University of Primorska Press, Koper.
P. 37
  the
  European
  context
  actual
  and
  updated
  environmental
  data
  is
  brought
  out
  through
 
environmental
 product
 declaration
 (EPD)
 programmes.
 There
 are
 several
 national
 or
 field
 related
 
programmes,
  as
  EPD-­‐Norway
  in
  Norway,
  IBU
  EPDs
  in
  Germany,
  and
  Wood
  for
  Good
  in
  UK.
  EPDs
 
are
  completed
  according
  to
  normative
  standards;
  general
  standard
  ISO
  12025
  and
  construction
 
products
  related
  EN
  15804
  and
  ISO
  91930.
 
  A
  short
  literature
  review
  based
  on
  valid
  EPDs
  is
 
present
 in
 Table
 1.
 

Table
 1:
 
L  iterature
 based
 comparison
 of
 cladding
 materials,
 production
 stage
 (A1–3)
 


  Unit
  Sawn
 timber
  Sawn
 timber
  Sawn
 timber
  Heat
 treated
 
(pine)
 1
  (softwood)
 2
  (softwood)
 3
 
sawn
 timber
 
(pine)
 4
 

Density
  kg/m3
  420
  420
  413
  420
 

MC
  %
  15
  15
  15
  5
 

PERE
  MJ
  2270
  853
  1330
  2761
 

PENR
  MJ
  6850
  1650
  330
  7697
 

GWP
  kg
 CO2
 -­‐e
  -­‐672
  -­‐679
  -­‐784
  -­‐258
 
ODP
  kg
 CFC11
 -­‐e
 
0,00000551
  0,00000000298
  0,000000000497
  0,0000461
 

POCP
  kg
 C2H4
 -­‐e
  0,0203
  0,0486
  0,0825
  0,12
 
AP
  kg
 SO2
 -­‐e
  0,339
  0,612
  0,242
  2,12
 
EP
  kg
 PO43-­‐
 -­‐e
  0,0752
  0,106
  0,0493
  1,88
 
ADPE
  kg
 Sb
 -­‐e
  0,0000948
  0,00000781
  0,0000142
  0,000402
 

ADPF
  MJ
  623
  1390
  318
  7794
 

Data
  sources
  1)
  EPD-­‐Norway
  2)
  Wood
  for
  Good
  3)
  IBU
  4)
  EPD-­‐Norway.
  Abbreviations:
  MC
  Moisture
  content,
  PERE
  Use
  of
  renewable
  primary
  energy,
  PENR
  Use
  of
  non-­‐renewable
 
primary
  energy,
  GWP
  Global
  Warming
  Potential,
  ODP
  Ozone
  Depletion
  Potential,
  POCP
  Photochemical
  Ozone
  Creation
  Potential,
  AP
  Acidification
  Potential,
  EP
  Eutrophication
 
Potential,
 ADPE
 Abiotic
 Depletion
 Potential
 (Elements),
 ADPF
 Abiotic
 Depletion
 Potential
 (Fossil).
 

Based
  on
  these
  EPDs,
  a
  comparison
  between
  different
  products
  is
  difficult.
  Regarding
  energy
 
consumption,
  primary
  energy
  increases
  by
  approximately
  15%
  in
  heat
  treated
  timber
  compared
 
to
  kiln
  dried
  sawn
  timber
  (EPD-­‐Norway).
  The
  ThermoWood
  Handbook
  (2003)
  also
  reports
  a
  25%
 
increase
 in
 energy
 demand
 during
 the
 drying
 phase.
 Therefore
 wood
 modification
 should
 prolong
 
the
  service
  life
  of
  the
  product
  to
  correspond
  (in
  minimum)
  to
  the
  increase
  in
  environmental
 
impacts
  during
  production
  in
  order
  to
  make
  the
  modification
  environmentally
  meaningful.
 
Emissions
  are
  always
  energy
  production
  related
  and
  cannot
  be
  compared
  directly.
  A
  more
 
detailed
  comparison
  for
  whole
  life
  cycles
  of
  products
  would
  be
  needed
  more
  specific
  data
  and
 
assumptions
 for
 the
 use
 stage.
 

References
 

EPD-­‐Norway.
  2015.
  EPD
  Skurlast
  av
  gran
  eller
  furu.
  Available
  at
  http://www.epd-­‐
norge.no/getfile.php/PDF/EPD/Byggevarer/NEPD-­‐307-­‐179
 
NO%20Skurlast%20av%20gran%20eller%20furu%20GK.pdf
 

EPD-­‐Norway.
  2014.
  EPD
  Termotre
  av
  gran
  og
  furu.
  Available
  at
  http://www.epd-­‐
norge.no/getfile.php/PDF/EPD/Byggevarer/NEPD00259N%20Termotre-­‐av-­‐gran-­‐og-­‐
furu%20MoelvenWood%20GODKJENT.pdf
 

IBU
  EPD.
  2015.
  EGGER
  Schnittholz
  technisch
  getrocknet.
  Available
  at
  http://construction-­‐
environment.com/download/CY84e88afX14dbf344596X31f5/Schnittholz_trocken.pdf
 

ThermoWood
 Handbook.
 2003.
 International
 ThermoWood
 Association.
 66
 p.
 

Wood
  for
  Good
  Lifecycle
  Database.
  2013.
  Kiln
  Dried
  Sawn
  Softwood.
 
  Available
  at
 
http://woodforgood.com/assets/Downloads/Kiln_Dried_Softwood_v1.2_2014-­‐03-­‐18.pdf
 


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