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ABSTRACT
Recen ad ances in ou unde s anding o me hanogen-
esis ha e led o he de elopmen o an ime hanogenic
eed addi i es (AMFA) ha can educe en e ic me hane
(CH4) emissions o a ying ex en s, ia di ec a ge ing
o me hanogens, al e na i e elec on accep o s, o al e -
ing he umen en i onmen . He e we examine cu en
and new app oaches used o he accoun ing (i.e., quan-
i ica ion) o en e ic CH4 aba emen by he use o AMFA
in he li es ock sec o om he indi idual animal o he
global scale. Along wi h his p ocess, ecommenda ions
a e p o ided on how o accoun o he mi iga ion po-
en ial a he animal le el, as well as in a m-scale mod-
els, emissions ading schemes, li e cycle assessmen ,
and ca bon (C) oo p in ing ools, and in egional and
na ional in en o ies. In addi ion, an assessmen o un-
ce ain ies and po en ial ade-o s and o -se ing wi h
he use o AMFA (i.e., e icacy s. e ec i eness, up-
s eam and downs eam emissions) is p o ided. The ac-
coun ing o on- a m en e ic CH4 emissions and bene i s
om he use o AMFA s a s wi h he uminan animal
(wi h es ima es ob ained om a ange o app oaches,
om simple empi ical emission ac o s o equa ions o
complex p ocess-based models) and goes all he way o
na ional and sup ana ional accoun ing. The choice o
me hodologies and le els o complexi y o accoun o
mi iga ion o en e ic CH4 (o o al GHG) emissions in
li es ock sys ems mus be ailo ed o he scale o analysis
aimed, he a ailabili y o inpu da a o ep esen con ex-
ualized condi ions, and he accoun ing objec i es (e.g.,
academic exe cise s. p oduce ’s GHG ce i ica ion s.
na ional GHG in en o y). The accoun ing o en e ic CH4
mi iga ing e ec s needs o conside he AMFA deli e y
me hods and syne gies and ade-o s o GHG emissions
a le els be o e and beyond (ups eam and downs eam)
he animal o ully assess he impac o AMFA use. A
la ge, he accoun ing o me hane aba emen by eed ad-
di i es emains o be ully assessed beyond expe imen al
esul s (e icacy) o add ess p agma ism (e ec i eness),
po en ial o adop ion, and socie al accep ance.
Key wo ds: li e cycle assessmen , ca bon oo p in ,
emission ading schemes, modeling, g eenhouse gases
INTRODUCTION
The e is inc easing ecogni ion ha p essing ac ion
mus ake place o a oid he isks and e ec s o clima e
change. In his p ocess, indi iduals, o ganiza ions, and
go e nmen s a e in oducing measu es o educe GHG
emissions, and we need o be able o comp ehensi ely
quan i y GHG emissions aba emen . En e ic me hane
(CH4) emissions om li es ock sys ems mainly o igina e
om mic obial e men a ion and me hanogenesis occu -
ing in he o es omach o uminan s. Recen ad ances in
Feed addi i es o me hane mi iga ion: Assessmen o eed addi i es
as a s a egy o mi iga e en e ic me hane om uminan s—Accoun ing; How
o quan i y he mi iga ing po en ial o using an ime hanogenic eed addi i es
Agus in del P ado,1,2* Ronaldo E. Viba ,3* F anco M. Bilo o,4 Claudia Fa e in,5,6 Flo encia Ga cia,7
Fábio L. Hen ique,8 Fe nanda Figuei edo G anja Do ilêo Lei e,5 And e M. Mazze o,9
B adley G. Ridou ,10,11 Da id R. Yáñez-Ruiz,12 and And é Bannink13
1Basque Cen e o Clima e Change (BC3), Pa que Cien í ico de UPV/EHU, Leioa, 48940 Spain
2Ike basque—Basque Founda ion o Science, Bilbao, 48009 Spain
3AgResea ch, G asslands Resea ch Cen e, Palme s on No h 4442, New Zealand
4Depa men o Global De elopmen , College o Ag icul u e and Li e Sciences, Co nell Uni e si y, I haca, NY 14850
5Ins i u o Nacional de Tecnología Ag opecua ia (INTA), Buenos Ai es, Balca ce, 7620, A gen ina
6Uni e sidad Nacional de Ma del Pla a, Facul ad de Ciencias Exac as y Na u ales, Funes 3350, 7600, Ma del Pla a, A gen ina
7Uni e sidad Nacional de Có doba, Facul ad de Ciencias Ag opecua ias, 5000 Có doba, A gen ina
8Depa men o Biosciences, College o Ve e ina y Medicine, Uni e si y o he Republic. Mon e ideo, 11600 U uguay
9AgResea ch, Lincoln Resea ch Cen e, Lincoln 7674, New Zealand
10Commonweal h Scien i ic and Indus ial Resea ch O ganisa ion (CSIRO) Ag icul u e and Food, Clay on 3168, Vic o ia, Aus alia
11Uni e si y o he F ee S a e, Depa men o Ag icul u al Economics, Bloem on ein 9300, Sou h A ica
12Es ación Expe imen al del Zaidín, CSIC, 18008 G anada, Spain
13Wageningen Uni e si y & Resea ch, 6700 AH Wageningen, he Ne he lands
J. Dai y Sci. 108:411–429
h ps://doi.o g/10.3168/jds.2024-25044
© 2025, The Au ho s. Published by Else ie Inc. on behal o he Ame ican Dai y Science Associa ion®.
This is an open access a icle unde he CC BY license (h ps://c ea i ecommons.o g/licenses/by/4.0/).
The lis o s anda d abb e ia ions o JDS is a ailable a adsa.o g/jds-abb e ia ions-24. Nons anda d abb e ia ions a e a ailable in he No es.
Recei ed Ap il 15, 2024.
Accep ed Sep embe 24, 2024.
*Co esponding au ho s: agus in.delp ado@ bc3 esea ch .o g
and onaldo. iba @ ag esea ch .co .nz
412
Jou nal o Dai y Science Vol. 108 No. 1, 2025
ou unde s anding o me hanogenesis ha e led o he de-
elopmen o an ime hanogenic eed addi i es (AMFA)
ha can educe en e ic CH4 emissions o a ying ex en s,
ia di ec a ge ing o me hanogens, al e na i e elec on
accep o s, o al e ing he umen en i onmen (Honan e
al., 2022; Belanche e al., 2025; Du mic e al., 2025).
Recen global epo s on uminan ag icul u e and
clima e change ha e included he co-bene i s, isks, and
implemen a ion oppo uni ies and ba ie s (IPCC, 2022),
en i onmen al impac (FAO, 2020; Blonk e al., 2021),
e icacy (Hega y e al., 2021; Honan e al., 2022; FAO,
2023), and acc edi ing me hodology (e.g., VERRA Ve i-
ied Ca bon S anda d; VERRA, 2021) o AMFA and hei
en e ic CH4 aba emen po en ial. The IPCC (2022) epo
emphasizes he obus e idence and p ominen le el o
consensus o p omising AMFA as e ec i e nea - e m
measu es o signi ican en e ic CH4 mi iga ion. Ou
o 10 AMFA o addi i e g oups assessed by Hega y e
al. (2021), 2 o hem, 3-ni ooxyp opanol (3-NOP) and
halogen-me hane con aining d ied Aspa agopsis sp. ( ed
algae), consis en ly achie ed >20% en e ic CH4 aba e-
men , ollowed by die a y ni a e (>10%), wi h o he
AMFA o addi i e g oups gene ally expec ed o achie e
<10% aba emen . Howe e , isks, conce ns, and unce -
ain ies o using AMFA ha e been aised, such as po en-
ial e ec s on pala abili y, oxici y, and animal wel a e;
eeding and adminis a ion cons ain s; legal equi e-
men s o au ho ize hei use (T ica ico e al., 2025); and
he need o supply chains a scale and good manu ac u -
ing p ac ice. In addi ion, he e is an inc easing need o
adequa e accoun ing o hese aba emen s a egies. This
includes he bene i s o educing en e ic CH4 (IPCC,
2022), as well as he po en ial ade-o s and syne gies
in ela ion o CH4 emissions om o he p ocesses. Fo
example, i AMFA supplemen a ion leads o educed eed
diges ibili y, i could po en ially esul in inc eased CH4
emissions om manu e emissions. I is also impo an
o conside o he sou ces o GHG, non-GHG ni ogen
emissions, ups eam emissions o AMFA, and he o e all
pe o mance o uminan s.
This pape examines cu en and new app oaches used
o he accoun ing o en e ic CH4 aba emen by he use
o AMFA in he li es ock sec o om he indi idual
animal o he global scale. Recommenda ions (illus a ed
in Figu e 1) a e p o ided on he me hods o accoun in
a m-scale models, emissions ading schemes (ETS),
li e cycle assessmen (LCA; o en e e ed as ca bon
oo p in when measu ing he GHG impac o a p oduc
h ough e e y phase o i s li e) and in egional and na-
ional in en o ies. The e m “accoun ing” he ein e e s
mos ly o he quan i ica ion o en e ic CH4 aba emen a
di e en scales, and o a lesse ex en , o he quan i ica-
ion o unce ain ies and po en ial ade-o s o o -se ing
wi h AMFA use (i.e., e icacy s. e ec i eness, o he un-
ce ain ies a ec ing e icacy, ups eam and downs eam
emissions).
ACCOUNTING AT DIFFERENT SCALES
The accoun ing o he e icacy o AMFA o mi iga e
en e ic CH4 emissions in uminan li es ock sys ems in-
ol es he use o gene ic es ima es, empi ical equa ions,
o o he modeling app oaches (Dijks a e al., 2025) im-
plemen ed in ools ha may be applied a di e en scales
(animal, he d, a m, egional, and na ional; H is o e al.,
2018; Tedeschi e al., 2022). The in e en ion wi h AMFA
may in ol e a ious compounds wi h di e en modes o
ac ion (Belanche e al., 2025) such as lipids, ionopho es,
phy ochemicals, essen ial oils, algae, elec on accep o s
(i.e., ni a e and sul a e), and 3-NOP o o he me hano-
gen inhibi ing agen s such as b omo o m (Almeida e
al., 2021; Honan e al., 2022). Feed addi i es can educe
en e ic CH4 emission di ec ly, mainly ia educed CH4
p oduc ion (g ams pe day pe cow), wi h an e ec on
emissions yield (g ams pe kilog am o DMI) and in en-
si y (g ams pe kilog am o animal p oduc ; e.g., milk o
BW gain), indi ec ly by imp o ing animal pe o mance
(i.e., by al e ing he amoun s o umen e men ed OM),
o bo h. Posi i e e ec s on animal pe o mance will in-
cen i ize he use o AMFA when he e is no di ec ewa d
o hei use o educe CH4 emissions (Dijks a e al.,
2025), bu his is beyond he scope o his pape .
The accoun ing o CH4 emissions aba emen a any
scale ( om animal and a m-scale accoun ing o na-
ional in en o y) equi es c i ical backg ound da a such
as animal cha ac e is ics, dosage, and cha ac e is ics o
he AMFA and he eed used as a means o deli e y, and
mi iga ion e icacy and e ec i eness wi hin he a ming
sys em. Such in o ma ion should be a ailable, and well-
documen ed e idence is equi ed o be conside ed in any
accoun ing p ocess. En e ic CH4 p edic ion models a y
in le el o de ail and complexi y ep esen ed, anging
om ela i ely simple empi ical (o s a is ical) models o
mo e de ailed and comp ehensi e p ocess-based mecha-
nis ic models ha ep esen he unde lying biological
p ocesses leading o en e ic CH4 emissions (Keb eab e
al., 2016; Dijks a e al., 2025). Addi ionally, C oo p in
and LCA me hodology may be used o p o ide a mo e
holis ic iew o he en i onmen al impac (Cowie e al.,
2012) including on- a m and o - a m emissions, and
ups eam and downs eam e ec s. Hence, he scale o
assessmen , he me hodology used o he accoun ing o
CH4 emissions (H is o e al., 2025), and he olume and
quali y o da a collec ed a e in e ela ed ac o s. When
he assessmen is conduc ed a a smalle scale (i.e., ani-
mal, g oups o animals, he d, o a m), da a equi ed as
inpu o mechanis ic models end o be collec ed mo e
equen ly (o en daily o e en including diu nal aspec s)
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
Jou nal o Dai y Science Vol. 108 No. 1, 2025
413
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
Figu e 1. Summa y o ecommenda ions on how o accoun o en e ic me hane (CH4) aba emen (gene al and ocusing on an ime hanogenic
eed addi i e [AMFA] use) and he associa ed unce ain ies and o he non-CH4 emissions a he animal, a m, li e cycle assessmen (LCA), and
coun ywide scales, as well as in emissions ading schemes (ETS). EF = emission ac o ; = unc ion o . C ea ed by A. del P ado and Sab ina Ga ay;
used wi h pe mission.
414
Jou nal o Dai y Science Vol. 108 No. 1, 2025
compa ed wi h la ge scales ( egion, coun y, con inen ).
In gene al, he mo e de ailed he da a equi ed and equa-
ions o models applied, he g ea e he eliabili y o
na ional accoun ing as a whole ( an Lingen e al., 2019).
Be o e del ing in o a de ailed discussion o he a i-
ous aspec s o accoun ing o en e ic CH4 emissions in
AMFA, his sec ion p o ides a gene al o e iew o he
me hods used a he animal, a m, and b oade scales o
li es ock GHG quan i ica ion.
Animal
The accoun ing o on- a m en e ic CH4 emissions
and bene i s om he use o AMFA s a s wi h he u-
minan animal, and es ima es a e ob ained using a ange
o me hods, om simple empi ical emission ac o s o
equa ions o complex p ocess-based models (Figu e 2).
A he animal scale, ela i ely simple es ima es o en e ic
CH4 emissions a e o en ob ained om p edic ion equa-
ions including DMI, ei he alone o in combina ion wi h
he chemical composi ion o die cons i uen s (e.g., ibe
con en ; Niu e al., 2018). Accoun ing can gain complex-
i y (and o en accu acy) by adding ce ain cha ac e is ics
o he animal, such as BW and animal p oduc (milk,
mea , o ibe ; Keb eab e al., 2016; Dijks a e al., 2025).
Emissions can also be es ima ed acco ding o a se o
de ined da a, wi h es ima es o daily DMI pe animal,
de i ed om abula ed ene gy equi emen s o eeding
s anda ds (o en based on BW, main enance needs, is-
sue g ow h, milk p oduc ion, p egnancy, and ac i i y)
di ided by he ene gy concen a ion o he eed (IPCC,
2019). The diges ible ene gy (DE) alue o a eed can be
es ima ed om OM diges ibili y, o om eed chemical
composi ion and diges ibili y coe icien s in he li e a-
u e. Feed DE can also be es ima ed by using a combina-
ion o chemical composi ion da a and p edic ion equa-
ions. Some mo e ad anced models p edic DE and OM
and ni ogen (N) diges ibili y mechanis ically (Beukes e
al., 2011; Bannink e al., 2018).
An essen ial s ep o he p edic ion o a die -speci ic
en e ic CH4 emission is he calcula ion o a CH4 con-
e sion ac o exp essing a pe cen o eed g oss ene gy
in ake (GEI) con e ed o CH4 (o en e e ed as me h-
ane con e sion ac o , Ym) o a CH4 yield (CH4 p oduced
pe uni o eed in ake). Me hane emission alues a e
ob ained by ei he mul iplying DMI o GEI by a CH4
yield o a ixed CH4 con e sion ac o , o example, Ym
(pe cen age o eed g oss ene gy con e ed o CH4) wi h
alues speci ied in IPCC (2019), espec i ely. Bo h Ym
and CH4 yield alues should be ob ained locally (mos
likely om espi a ion chambe s) o h ough an equa ion
ha migh include die a y ing edien s, chemical compo-
si ion pa ame e s, diges ibili y pa ame e s, and animal
cha ac e is ics. P ocess-based mechanis ic models wi h
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
Figu e 2. Animal, a m, and li e cycle assessmen (LCA) bounda ies o he accoun ing o en e ic me hane (CH4) emissions. Adap ed om Cowie
e al.(2012) by Sab ina Ga ay; used wi h pe mission.
Jou nal o Dai y Science Vol. 108 No. 1, 2025
415
ep esen a ion o umen e men a ion and gas oin es i-
nal diges ion may be used o p edic Ym alues (Bannink
e al., 2011; Huh anen e al., 2015; Dijks a e al., 2025).
Fa m
The a m ep esen s he land scale a which manage-
men decisions on li es ock p oduc ion a e made (Figu e
2). Mos emissions and a iabili y wi hin he li e cycle o
ag icul u al p oduc s o en occu wi hin he a ming sys-
em, ha is, wi hin he a m ga e and no du ing he es
o he li e cycle o li es ock p oduc ion (Oenema e al.,
2003). This is o pa icula ele ance in he case o en-
e ic CH4, which is essen ially he esul o eed quali y,
in ake wi hin a gi en animal ca ego y, and, in he con ex
o his wo k, he use o compounds ha modula e umen
e men a ion. The e o e, a m-le el models and he ac-
cu a e es ima ion o en e ic CH4 emissions play a pi o al
ole in add essing he mi iga ion o GHG emissions in
li es ock ag icul u e. On- a m GHG models ha e been
de eloped and used by he scien i ic communi y, en i-
onmen al au ho i ies, a m consul an s, and a me s o
he accoun ing o en e ic CH4 emissions (see examples
o a m models e e enced in he ollowing pa ag aph).
Those models se e se e al c ucial unc ions, includ-
ing in eg al assessmen o all GHG sou ces and aising
awa eness. They will also ha e o be used o iden i y,
de elop, and p omo e e icacy o al e na i e AMFA and
i is he e o e impo an o pinpoin knowledge gaps,
as well as being able o scale up in o ma ion o policy
de elopmen . Measu emen s on AMFA e icacy a e no -
mally pe o med wi h indi idual animals as expe imen al
uni s (H is o e al., 2025) comp ising di e en animal
ca ego ies o egula o y pu poses (T ica ico e al.,
2025). This basis may di e om he way an indi idual
animal o animal coho s a e ep esen ed in a m-scale
app oaches whe e, o ope a ional pu poses, di e en
simpli ica ions and assump ions a e made. In his case,
AMFA and animal coho speci ica ions and assump ions
need o be well-documen ed.
A he a m scale, on- a m GHG models o e a
b oade di e si y o scope, modeling app oach, and scale
(i.e., om he umen o he si e, he landscape, and he
whole a m; Schils e al., 2007; C osson e al., 2011;
Colomb e al., 2012; del P ado e al., 2013; Keb eab e
al., 2016; Viba e al., 2021). E en hough models a e
usually labeled as empi ical o mechanis ic, i is common
o ind a combina ion o bo h app oaches wi hin a single
model, each applied o di e en componen s (Dijks a e
al., 2025). In gene al, a m-scale models end o ollow
hyb id o empi ical app oaches o in eg a e soil, c op and
pas u e, and li es ock componen s in o a a m amewo k
(Schils e al., 2012). This ype o in eg a ed app oach al-
lows o an o e all es ima e o di ec as well as indi ec
GHG and N emissions including hei ade-o s and
syne gies, and i allows compa isons be ween di e en
p oduc ion sys ems, be ween di e en p oduc ion condi-
ions, o bo h (Schils e al., 2007; del P ado e al., 2013;
Oua aha e al., 2021). When e alua ing GHG mi iga ion
s a egies om li es ock sys ems, models ha a e able
o cap u e in e nal eedbacks and loops o C and N be-
ween a m componen s a e p e e ed (del P ado e al.,
2013) because mi iga ion measu es ha bene i one a m
componen (e.g., en e ic CH4 e men a ion) may a ec
C and N lows in o he componen s, o example, CH4
emissions a he manu e-managemen le el (del P ado
e al., 2013). Mo eo e , modeling app oaches mus be
capable o simula ing he in e ac ions be ween combined
mi iga ion s a egies ha may no necessa ily be addi i e
(del P ado e al., 2010; Owens e al., 2020). Fa m models
can dis inguish how much o he mi iga ion comes om
each s a egy h ough scena io es ing. Fi s a baseline
scena io is simula ed and subsequen ly, simula ions wi h
a m scena ios whe e changes a e in oduced singly and
in a s epwise p ocess a e ca ied ou . Each s ep would in-
oduce a new di e en change in s a egy (e.g., in ol -
ing eed managemen ). The changes, ac ing singly o in
combina ion, a e hen e alua ed on a ms. In addi ion o
he ep esen a ion o he AMFA CH4 mi iga ing e ec ,
ocus is needed on he e ec o AMFA on eed diges -
ibili y, exc e ion, and animal pe o mance (Belanche e
al., 2025; H is o e al., 2025) and how o quan i y hese
e ec s (Dijks a e al., 2025).
Recommenda ions
●P ecisely de ine he aims o any a m-scale mod-
eling e o and wha aspec s and de ails ha a e
ele an a he animal and subanimal scale ha e
and ha e no been co e ed (Dijks a e al., 2025).
The ep esen a i eness o in eg a ed models o en
depends on hei abili y o accu a ely depic a spe-
ci ic a m wi hin a pa icula egion (i.e., he model
cap u es he in icacies o local soil, clima e, a m
managemen , and animal policy da a). This high-
ligh s he limi a ion o a “one-size- i s-all” model
o model assump ions o all a ms. O en, he lack
o speci ici y and logicali y in he ep esen a ion
o he unde lying p ocesses ha lead o GHG and
N emissions a emp agains he in eg a ing and
o e a ching app oach o modeling a he whole-
a m scale because some pa s a e oo simpli ied
and ep esen ed by empi ical app oaches (Oua aha
e al., 2021).
●Conside es ima ing CH4 and ni ous oxide (N2O)
emissions om manu e managemen , land applica-
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
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Jou nal o Dai y Science Vol. 108 No. 1, 2025
ion, and eces and u ine deposi ion ( esul ing om
eed in ake and diges ibili y), as well as manu e
ea men when e alua ing die a y e ec s. These
emissions a e in luenced no only by die cha ac e -
is ics bu also by bio ic and abio ic ac o s.
●Repo he a ailable da a o suppo model e alu-
a ion o alida ion. Gene ally, hese da a will be
limi ed o ew a m componen s.
Li e Cycle Assessmen
Al hough a m-le el GHG emissions balance simula-
ion models all wi hin he ca ego y o sys ems analysis
models and, hus, a emp o explici ly ep esen he lows
and ans o ma ion o C and N, also o he app oaches
a e mainly emission ac o -based and cen e a ound LCA
(C osson e al., 2011; del P ado e al., 2013). Li e cycle
assessmen is gene ally accep ed as a holis ic me hod o
amewo k o e alua e he en i onmen al impac , such
as clima e change o C oo p in as one o he indica o s,
du ing he en i e li e cycle o a p oduc and ela es i o
a unc ional uni exp essed in quan i a i e e ms (Guinée
e al., 2002; de V ies and de Boe , 2010; Figu e 2). The
LCA analysis equi es speci ic da a om he animal and
a m bounda ies o achie e a mo e de ailed and speci ic
assessmen (Figu e 2). The e a e 2 main ypes: a ibu-
ional LCA (aLCA), which assesses he global impac
sha e o a p oduc ’s li e cycle, and consequen ial LCA
(cLCA), which e alua es he consequen ial impac o a
decision (Schaub oeck, 2023). The C oo p in is he sum
o GHG emissions associa ed wi h a p oduc o ac i i y,
exp essed in uni s o ca bon dioxide equi alen s (CO2-
eq; Flachowsky and Kamphues, 2012). The use o LCA o
quan i y he en i onmen al impac o di e en p oduc s
has inc eased in ecen yea s and is o en d i en by de-
mands o accoun abili y om cus ome s, s akeholde s,
and go e nmen egula o s (Beauchemin and McGeough,
2013). The In e na ional S anda ds O ganiza ion (ISO)
o e s guidelines and es ablished benchma ks o he cal-
cula ion and communica ion o he en i onmen al impac
o ood p oduc s.
Coun y
Signa o y coun ies o he Pa is Ag eemen need o
epo annually hei na ional emission GHG in en o y
o he Uni ed Na ions F amewo k Con en ion on Clima e
Change. Simul aneously, clima e ac ion plans o lowe
GHG emissions h ough na ionally de e mined con ibu-
ions (NDC), ha e shown ha abou 36% o coun ies
included li es ock and g assland mi iga ion in e en ions
in hei mos ecen NDC (C umple e al., 2021). A he
na ional in en o y scale, he accoun ing o en e ic CH4
emissions can be ei he simple gene ic and easily acces-
sible, be locally ob ained, o be d i en by p ocess-based
mechanis ic models. The IPCC Guidelines explain he
app oach o he 3 ie s o complexi y in he es ima ion o
en e ic CH4 emissions om uminan li es ock sys ems
(IPCC, 2006, 2019). The choice o which app oach each
coun y uses o hei in en o y is based on da a a ail-
abili y, esea ch o scien i ic esou ces, and mechanis ic
models adap ed o he condi ions. The less ha is known
abou li es ock and eed cha ac e is ics, he mo e unce -
ain he in en o y is likely o be (H is o e al., 2018).
In coun ies whe e an ex ensi e da abase exis s, mos ly
a Tie 2 o adap ed Tie 2 app oach is ollowed, whe eas
in coun ies wi h a de ailed and ex ensi e scien i ic
knowledge base on diges i e and en e ic e men a i e
p ocesses, a Tie 3 app oach may be used. Wi h each ie ,
aiming o ep esen e icacy o a AMFA linkage mus be
made wi h modeling esul s a he animal scale (Dijks a
e al., 2025).
The la es e inemen o he IPCC Guidelines (IPCC,
2019) p oposes di e en Ym alues o hose p oposed by
IPCC (2006) o ca le and bu alo (6.5% o GEI in IPCC
2006) linked o annual milk p oduc ion le els (dai y
animals) and o eed quan i y and quali y. Fo example,
he lowes Ym alue (5.7% o GEI) is associa ed wi h
high p oducing dai y ca le ha a e ed die s wi h >70%
diges ibili y and ha ha e a pe cen age o NDF in DMI
<35%, whe eas he highes Ym alue (7% o GEI) mus
be chosen o nondai y ca le ha g aze on low-quali y
o age die s.
The Tie 2 me hods can use he same app oach as Tie 1
bu wi h coun y- o egion-speci ic ene gy equi emen
models o calcula e emission ac o s (i.e., al e ing Ym
alues; Lassey, 2007; Hellwing e al., 2016; Colombini
e al., 2023). Tie 2 me hods allow o a highe spa ial
and empo al esolu ion and da a li es ock ca ego y
disagg ega ion (i.e., sex, age, managemen , o season;
Kouazounde e al., 2015; Ibidhi e al., 2021; Ndung’u
e al., 2023). Coun ies o en lack su icien da a ela ed
o li es ock o mo e beyond Tie 1. Mos GHG in en o-
ies use he IPCC Tie 1 app oach, which only e lec s
changes in li es ock numbe s. Moni o ing changes in
managemen and p oduc i i y necessi a es using a Tie
2 app oach. The lack o ac i i y da a and incomple e
o poo -quali y da a a e commonly seen as obs acles o
implemen ing he Tie 2 app oach. A ecen e iew e-
ealed ha ou o 140 low- and middle-income coun ies
(LMIC), jus 92 ha e included li es ock- ela ed emis-
sions in hei NDC (FAO and GRA, 2020).
Tie 3 me hods a e o a highe o de o de ail and
esolu ion, and ailo ed o assess a he subna ional o
egional scale, and may, bu do no necessa ily ha e o,
in ol e p ocess-based modeling ha conside s DMI, die
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
Jou nal o Dai y Science Vol. 108 No. 1, 2025
417
chemical composi ion, and eed deg ada ion and e men-
a ion cha ac e is ics o p edic en e ic CH4 emissions
(Viba e al., 2021). Models used in Tie 3 ep esen u-
men e men a ion mechanisms, cap u ing a g ea e po -
ion o he a iabili y om nu i ional and animal ac o s,
wi h enhanced p ecision when using local da a om ex-
pe imen s and alida ed calcula ion me hods (Bannink e
al., 2011; Keb eab e al., 2016). Howe e , he necessa y
da a a e no ypically ga he ed and p omp ly a ailable
and mus be g ounded in p io in si u umen incuba ion
s udies and na ional die componen s a is ics (Bannink
e al., 2011). The e o e, in coun ies whe e no such da a
a e a ailable, a Tie 1 app oach is commonly ollowed,
mos ly in LMIC.
Emissions T ading Schemes
To assis in mee ing hei emissions-aba emen commi -
men s, coun ies a e inc easingly de eloping egional and
na ional ETS, a ool designed o he pu pose o mee ing
domes ic and in e na ional clima e change a ge s. These
ma ke -based schemes aim o c ea e economic incen i es
o emissions educ ion om e ec i e p ac ices imple-
men ed a he leas o e all cos possible (Cowie e al.,
2012). The Regional G eenhouse Gas Ini ia i e (cap and
educe emissions om he powe sec o ) and he Wes e n
Clima e Ini ia i e (collabo a i e de elopmen and imple-
men a ion o ETS p og ams) a e examples o egional
schemes in he Uni ed S a es. Likewise, he Eu opean
ETS (ope a es on cap-and- ade p inciples), Aus alia’s
Ca bon Fa ming Ini ia i e (a olun a y ca bon o se s
scheme) and he New Zealand ETS (all sec o s o New
Zealand’s economy) a e examples o na ional and sup a-
na ional schemes ha ha e di e en scopes and pu poses.
App o ed me hodologies o GHG accoun ing a e essen-
ial o he success o hese schemes (Cowie e al., 2012).
Bu o ou knowledge, e y ew o hese schemes include
li es ock ag icul u e in hei accoun ing sys ems. One o
he ew li es ock ag icul u e schemes includes inco po-
a ing ni a es in Aus alian bee ca le. The me hodology
se s he ules o he emissions aba emen achie ed by
eplacing u ea lick blocks wi h ni a e lick blocks used
in pas u e-based bee ca le sys ems, wi h acc edi a ion
managed by he Aus alian Ca bon C edi Uni scheme
(Aus alian Go e nmen , 2023).
I AMFA a e o be inco po a ed as an aba emen s a -
egy in ETS and he poin o obliga ion is se a he a me
le el, hen he accoun ing app oach in hese ag icul u al
schemes would be simila o ha used o a m-scale
accoun ing (i.e., being able o accoun a he animal
scale). Bu i he poin o obliga ion is se a he (animal
p oduc ) p ocessing le el, hen he accoun ing app oach
would mos likely be simila o ha used o egional o
na ional in en o y accoun ing.
APPROACHES TO THE ACCOUNTING OF ENTERIC
METHANE ABATEMENT BY AMFA
Animal, Fa m, Na ional, and Sup ana ional Scales
Du ing he pas 60 yea s, a wide ange o AMFA ha e
been es ed and expe imen ally included in die s o dai y
cows (de Onda za e al., 2023; Figu e 3A). The ype o
die , AMFA deli e y (in e e y mou h ul o a TMR s.
pulse- ed wi h supplemen s), and p oduc ion sys em (i.e.,
o age- o-concen a e a io, ibe , soluble suga s, s a ch,
and p o ein con en ) will de e mine no only he e ec i e-
ness o he AMFA bu also he sui abili y o such eeding
egimen (Dijks a e al., 2018). Keb eab e al. (2023) in
a ecen me analysis epo ed ha inc eases in NDF and
c ude a concen a ions abo e he a e age in he da a-
base educed e ec i eness o 3-NOP a mi iga ing CH4
p oduc ion and yield, whe eas inc eases in s a ch con en
enhanced 3-NOP e ec i eness in mi iga ing CH4 yield.
In die s ha a e de icien in N, he di e sion o elec on
lows by ni a es in o al e na i e pa hways o H2 use in
he umen (i.e., a educ ion o ammonia) can p o ide
bo h an e ec i e CH4 mi iga ion al e na i e and a sub-
s a e o anabolism and supply o e men able N om
enhanced mic obial p o ein syn hesis (Dijks a e al.,
1998; an Zijde eld e al., 2010). Al hough i has been
a gued ha AMFA may be less e ec i e in uminan s ed
die s ha esul in less CH4 (e.g., die s high in g ains), di-
e a y ac o s did no come o wa d in a me a-analysis o
obse ed a ia ion in he CH4 mi iga ing e ec o added
ni a e (Dijks a e al., 2025). To no e, ex e nal elec on
accep o s may also p oduce oxic end compounds (i.e.,
sul ides, ni a es/ni i es) a ec ing animal pe o mance
(La ham e al., 2016).
To accele a e he de elopmen o e ec i e CH4 mi iga-
ion echnologies, he e is a p essing need o comp ehend
he changes b ough in he umen by he use o AMFA
and hei e ec on CH4 o ma ion (Belanche e al., 2025).
When e alua ing he absolu e educ ion in GHG emis-
sions om he use o a speci ic AMFA, i is c ucial o
accoun o he po en ial educ ion in CH4 yield (g CH4/
kg o DMI), a me ic ha links bo h en e ic CH4 emis-
sions and in ake. A u he e inemen o his me ic is o
exp ess CH4 yield in e ms o CH4 p oduc ion pe uni o
diges ed OM (DOM; g CH4/kg o DOM in ake) because
i p o ides a ine desc ip ion o eed being e men ed
and con ibu ing o he e men a ion p o ile (Beauchemin
e al., 2022).
Wi h an assessmen a he a m scale, a CH4 mi iga ing
e ec could be ep esen ed by a de aul alue o co ec-
ion (Tie 1; see p e ious sec ion). Fo example, assum-
ing he same amoun s o eed a e o e ed o uminan s
(i.e., die s wi h and wi hou AMFA), i would be easible
o apply de aul alues a ound 30% and 10% o en e ic
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
418
Jou nal o Dai y Science Vol. 108 No. 1, 2025
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
Figu e 3. Global da a se o en e ic me hane (CH4) mi iga ion expe imen s, including he use o an ime hanogenic eed addi i es (AMFA), in
lac a ing dai y cows, conduc ed be ween 1963 and 2022 (adap ed om de Onda za e al., 2023). (A) Dis ibu ion o s udies in ol ing animals
supplemen ed wi h he main AMFA ca ego ized by hei die a y composi ion (% o o age). (B) Me hane yield (g CH4/kg o DMI) om animals
ha ecei ed AMFA compa ed wi h he con ol g oup. The bold line in he middle o each box plo ep esen s he median. The box i sel ep esen s
he in e qua ile ange, spanning om he 25 h pe cen ile (bo om o he box) o he 75 h pe cen ile ( op o he box). Whiske s ep esen a ce ain
ange beyond he IQR. The iolin plo gi es a mi o ed densi y dis ibu ion o each g oup, showing he ull dis ibu ion shape and adding dep h o
he aincloud plo , which combines summa y s a is ics (box plo ) wi h da a dis ibu ion ( iolin plo and indi idual poin s). The poin and line in he
cen e o each cloud ep esen s i s mean and SE. The ain ep esen s indi idual da a poin s. (C) Me hane emissions in ensi ies (g CH4/kg o milk)
o AMFA ha show signi ican di e ences in CH4 yield and hei ela ionship wi h indi idual milk p oduc ion (kg o milk pe head [hd] pe day).
3-NOP = 3-ni ooxyp opanol; E. Accep o = elec on accep o ; Reg. = eg ession. C ea ed by F. Bilo o and Sab ina Ga ay; used wi h pe mission.
Jou nal o Dai y Science Vol. 108 No. 1, 2025
419
CH4 yield educ ion (pe kilog am o DMI) in dai y sys-
ems using 3-NOP and lipids, espec i ely (Figu e 3B).
Al hough such de aul alues o CH4 educ ion by AMFA
a e easy o implemen in accoun ing, he assump ion
inhe en ly made is ha condi ions in p ac ice ma ch he
expe imen al condi ions hese alues we e de i ed om
(Dijks a e al., 2025). Because his is o en no he case,
i is expec ed ha his Tie 1 le el o accoun ing o CH4
educ ion will be associa ed wi h a signi ican deg ee o
unce ain y (see he “Unce ain ies” sec ion). I needs
o be no ed ha a gene ic es ima e only applies o he
same a e age dosing and condi ions o he empi ical da a
used o de i e hese es ima es. In any case, he numbe o
expe imen al ials conduc ed in a m condi ions whe e
CH4 measu emen me hods do no in e up hey daily
beha io and ou ine (H is o e al., 2025) and conduc ed
o e longe pe iods o ime (mo e han 12 o 14 wk o a
whole yea ) is expanding ( an Gas elen e al., 2024). This
inc eases he con idence when ansla ing mi iga ion al-
ues ob ained expe imen ally in o p ac ical a ming.
As we mo e om Tie 1 o Tie 2 and Tie 3 app oach-
es, obse ed a ia ion needs o be cap u ed wi h mo e de-
ail and ine esolu ion. In his con ex , a mo e in-dep h
examina ion o nu i ional da a is impe a i e, gi en he
di e si y among li es ock sys ems. Feed in ake, eed
diges ibili y, and CH4 emissions a e posi i ely co ela ed
wi h animal and he d size, g ow h a e, ac i i y, and
p oduc ion le el, and hese di e be ween animal ypes
and eed managemen p ac ices (H is o e al., 2018).
Figu e 3C po ays a dec easing end in CH4 mi iga ion
po en ial o AMFA as he p oduc ion le el, ene gy, and
p o ein con en o he die inc ease. Highe eed qual-
i y and diges ibili y, o en associa ed wi h a educ ion in
e en ion ime in he umen due o as e passage a es
leading o lowe CH4 yields (Beauchemin e al., 2022),
some imes esul in ela i ely modes educ ions in emis-
sions when AMFA a e in oduced. Howe e , he opposi e
(i.e., signi ican educ ions in en e ic CH4 om cows ed
highly diges ible die s) has also been shown, as demon-
s a ed o 3-NOP in a yea -long s udy ( an Gas elen e
al., 2024), and no such indica ions we e seen o ni a e
(Feng e al., 2020).
Recommenda ions
●Inc emen ally imp o ing he esolu ion o a iables
ha in luence he e icacy o AMFA in an emissions
in en o y is essen ial. This will esul in a mo e
p ecise and accu a e assessmen o he e ec s o
AMFA in speci ic ypes o nu i ional managemen ,
as well as in animal and a m sys ems.
●The simples way o inco po a e he e ec o AMFA
in GHG accoun ing sys ems is by using he de aul
uni o pe cen educ ion o CH4 pe amoun o
inges ed eed by he animal (e.g., pe kilog am
o DMI). This pe cen age mus ake in o accoun
he basic in e ac ions be ween eed in ake and he
ype o die , as well as he mode o ac ion, deli e y
me hod, and e ec i e dosage o he AMFA.
●Mo e complex app oaches can imp o e he es i-
ma es o en e ic CH4 educ ion cu en ly a ailable
om me a-analyses. These app oaches can also
a ibu e expec a ions o a ious combina ions o
AMFA and die a y s a egies.
A he a m scale, del P ado e al. (2010) simula ed he
inclusion o lipid-based addi i es (in isola ion and in
combina ion) as one o se e al s a egies o imp o e
dai y a m sus ainabili y in he Uni ed Kingdom using
he whole- a m model SIMSDAIRY (del P ado e al., 2011).
Fo en e ic CH4, he app oach was based on an empi i-
cal equa ion ha included animal DMI and he deg ee
o unsa u a ion o he a y acids in he die wi h CH4
ou pu exp essed pe kilog am o DMI (Gige -Re e din
e al., 2003). O he me a-analyses ha e no es ablished
a clea e ec o ype o a y acid on CH4 aba emen
(e.g., G ainge and Beauchemin, 2011). Due o a ia ion
in he ype o die s, AMFA mode o ac ion, and eeding
managemen (con inemen eeding s. a sole o supple-
men ed g azing sys em), he ex en o which CH4 aba e-
men is e ec i e is ha de o cap u e, and consequen ly
also empi ical equa ions can s ill be poo p edic o s o
GHG emissions in a speci ic a m (Viba e al., 2021).
Recommenda ions
●Include su icien de ail on li es ock and eeding
condi ions, such as compa ing ba n and pas u e
condi ions.
●P o ide a comp ehensi e assessmen o syne gies
and ade-o s wi hin he a ming ope a ion (del
P ado e al., 2013).
●Include e ec s on le el o eed in ake and animal
pe o mance, allowance o me abolizable ene gy
(e.g., Belanche e al., 2025; an Gas elen e al.,
2024), eed diges ibili y, exc e ion o u ine and
eces, as well as manu e cap u e and s o age.
To ou knowledge, GHG emission in en o ies a he
na ional scale a e ye o accoun o he use o AMFA.
O he ypes o addi i es (e.g., o imp o e he diges ibil-
i y o speci ic nu ien s, pa icula ly p o eins) di ec ly
a ec ing eed u iliza ion and animal pe o mance may
ha e been au oma ically inco po a ed due o he highly
empi ical na u e o he ac i i y da a and nu i ional e-
qui emen s. Fo example, he inclusion and accoun ing
o new enzymes and syn he ic amino acids in Spanish
pig die s in he 2007 o 2010 pe iod esul ed in a educ-
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT
426
Jou nal o Dai y Science Vol. 108 No. 1, 2025
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ORCIDS
Agus in del P ado, h ps: / / o cid .o g/ 0000 -0003 -3895 -4478
Ronaldo E. Viba , h ps: / / o cid .o g/ 0000 -0002 -0248 -3603
F anco M. Bilo o, h ps: / / o cid .o g/ 0000 -0002 -3759 -3159
Claudia Fa e in, h ps: / / o cid .o g/ 0000 -0002 -6951 -3029
Flo encia Ga cia, h ps: / / o cid .o g/ 0000 -0002 -0748 -9692
Fábio L. Hen ique, h ps: / / o cid .o g/ 0009 -0008 -6834 -2310
Fe nanda Figuei edo G anja Do ilêo Lei e, h ps: / / o cid .o g/ 0000
-0001 -9004 -6413
And e M. Mazze o, h ps: / / o cid .o g/ 0000 -0002 -1501 -0303
B adley G. Ridou , h ps: / / o cid .o g/ 0000 -0001 -7352 -0427
Da id R. Yáñez-Ruiz, h ps: / / o cid .o g/ 0000 -0003 -4397 -3905
And é Bannink h ps: / / o cid .o g/ 0000 -0001 -9916 -3202
del P ado e al.: ACCOUNTING OF FEED ADDITIVE ENTERIC METHANE ABATEMENT