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8/7/2019 Rising Atmospheric CO2 and Human Nutrition: Toward Globally Imbalanced Plant Stoichiometry
1/5
TRENDS in Ecology & Evolution Vol.17 No.10 October 2002
http://tree.trends.com 0169-5347/02/$ see front matter 2002 Elsevier Science Ltd. All ri ghts r eserved. PII: S0169-5347(02)02587-9
457Opinion
The increas ing concentr at ion of atm ospheric car bon
dioxide CO2
and t he quality of our n utr ition ar e two
importa nt pr oblems tha t we ar e currently facing.
A link between t hese t wo problems, however, is not
apparent . Indeed, intensive and num erous studies on
th e effects of high [CO2] on plan ts h ave covered a wide
ra nge of issues, but its effects on plant s toichiometr y
(i.e. elementa l composition) h ave r eceived very litt le
at tent ion. Yet, plan ts a re t he foundat ion of our food
supply. The low concentr at ions of several essen tial
micronutr ients, su ch as iron (Fe), iodine (I) and
zinc (Zn), in m odern crops cont ribut e to th e pr oblem of
micronutr ient ma lnut rition (i.e. hidden h unger ), which
diminishes t he hea lth a nd economy of over th e half of
the worlds populat ion. Her e, by using t he t heory of
ecological stoichiometr y, I can link h igh [CO2] with plant
stoichiometry and t he quality of human nut rition. The
tools of ecological st oichiomet ry a re chem ical element s
and t heir rat ios in organisms and t he environment.
How can stoichiomet ry provide insight?
Analysing biological dynam ics from a chemical
element perspective has a dvantages in both its
simplicity a nd rigor ([1], I. Loladze, Ph D th esis,
Arizona Sta te Un iversity 2001). Acell contains
th ousands of complex subst an ces, but a ll life requires
~32 different chemical element s [2]. Life continuously
assem bles an d disassembles complex substa nces,
but it can n either create n or decompose chemical
elements, a nd it cannot convert one element into
another. These elementa l laws are rat her
self-evident, but ar e frequent ly overlooked in our
perception of biological dynam ics. Yet t he univer sa lity
an d cert aint y of these laws, which ar e valid on all
organizational scales, from molecules t o the
biospher e, provide a un ified fra mework th at h elps to
reveal pattern s hidden on disparate organizational
scales. The stoichiometr ic ar gumen t th at I discuss
here dr aws on mu ltiple scales, from t he str ucture of
carbohydrates t o a plant cell to an a gricultur al plot t o
globally r ising [CO2].
The need for essential elements and the problem of
micronutrient malnutrition
The hum an body needs at least 24 chemical elements.Although some of the element s, such as chromium (Cr),
Fe, I, s elenium (Se), or zin c (Zn), compr ise 3.5 billion people, mostly in th e developing world,
an d impa irs t he cognitive developmen t of children ,
causes productivity and educational losses, an d
increases morbidity and m ater nal morta lity[4].
Iodine deficiency is a public health problem in a t
least 130 count ries, with over seven hu ndr ed million
people sufferin g from goitre a nd t ens of millions
afflicted by brain dam age an d cretinism [4]. Near ly
half of the worlds population is a t r isk of ina dequat e
Zn inta ke [5]. Deficiencies of oth er ess ent ial
elements ar e also widespread, even in industr ial
count ries, but often a re not ma nifested in overt
clinical syndromes.
Global imbalance of essential elements and
plant stoichiometry
Hu ma n a ctivities profoundly alter th e global cycles of
several essential element s [1,7]. The pursu it of
higher agricultural yields, rath er tha n crop
qua lity, fertilizes soil disproportionat ely with N,
phosphoru s (P), an d potassiu m (K). Fossil-fuel
burn ing adds N and sulphur (S) via atmospheric
deposition a nd, together with changes in land use,
increas es [CO2]. Thus, hu man activities have been
alter ing the pool of a few essentia l elements in s evere
Rising atmosphericCO
2and human
nutrition:towardglobally imbalancedplant stoichiometry?Irakli Loladze
Terrestrial vascular plants obtain t heir major constituent carbon (C) from
atmospheric carbon dioxide (CO2), but draw all other chemical elements largely
from the soil.Concentrations of these elements,however, do not change inunison wit h steadily increasing concentrations of CO
2[CO
2]. Thus, relative to
pre-industrial times, modern plants are experiencing a global elemental
imbalance. Could this imbalance affect the element al composition of plants,
the most important food source on Earth? Apart from an overall decline in
nitrogen concentrat ion, very little is known about the effects of high [CO2]
on other chemical elements, such as iron, iodine and zinc,w hich are already
deficient in the diets of the half of human population. Here,I apply stoichiometric
theory to argue that high [CO2], as a rule,should alter the elemental
composition of plants, thus affecting the quality of human nutrition.The first
compilation, to my knowledge,of published data supports the claim and shows
an overall decline of the (essential elements):C ratio. Therefore,high [CO2]
could intensify the already acute problem of micronutrient malnutrition.
Published on line: 8 August 2002
Irakli Loladze
Dept of Ecology and
Evolutionary Biology,
Princeton University,
Princeton, NJ 08544, USA.
e-mail:
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disproportion to others. Relative to pr e-industr ial
times, we ha ve been ra pidly creating a global
elemental imbalance. Can th is imbalance, in tur n,
affect u s by alter ing th e stoichiometr y of our
funda men ta l food source plant s? To an swer th is
question, I concentr at e her e on the role of rising [CO2]
for t he following thr ee rea sons.
First , unlike the contr oversy surr ounding the
effects of [CO2] on climate chan ge, the increase
in [CO2] itself is confirm ed by several indepen dent
sources [8]. Curr ently, every terr estrial plant is
exposed to ~30% higher [CO2] relative to
pre-indust rial times; during t his century [CO2]
levels could double or t riple over pre-indus tr ial
levels [8]. This increase is inst an ta neous on a
geological times cale and is unpr ecedented in th e
history of the hu man species. Because a modern tr ee
might experience th e doubling of [CO2] over its
lifetim e, such an increas e is also very fast on
evolutiona ry an d even ont ogenet ic tim escales.
Second, plant s build the bulk of their dry weight by
fixing C from CO2. Third, because of the gaseouspropert ies of CO
2and high mixing ra tes in the
atm osphere, no other h uma n impact compares to
rising [CO2] in its u niform ity. Plant s worldwide,
both agricultural a nd wild, are exposed to very
similar [CO2] concentra tions. For these r easons,
global pat tern s in th e changes of plant
stoichiomet ry can preva il in spite of local
environmen tal heterogeneity (tempera tur e,
hu midity, fert ilizers, et c.).
Plants in enriched CO2
atmospheres
The effects of high [CO2] on plant stoichiometry ha ve
received little a tten tion, but its effects on other plan tcharacteristics have been t horoughly studied.
Fr ee-Air CO2
Enr ichment (FACE) experiment s
have been r unn ing at 32 locations worldwide and
>2700 studies have been published in t he past decade
alone [9]. Doubling ambient [CO2] gener ally
stimulat es photosynthesis, enhan ces plant growth
and increases agricultura l yields, on a verage,
by 41% [1013]. These ben efits, however, become
quest iona ble if enr iched [CO2] alters crop
stoichiomet ry. Tha t chem ical composition of plant s
can change under increased [CO2] has been
suggested [e.g. 1,7,10], but m uch of th e experimen ta l
work h as ignored chemical elements and has
inst ead focused on complex compoun ds, ma ny of
which show litt le consisten cy in th eir res ponse to
high [CO2] [14,15]. Aclear pat ter n, however, exists
for N, t he only element wh ose concentr at ions in
plant s un der condit ions of high [CO2] have been
stu died extensively. The meta -ana lysis of th e
concentra tions of N in aboveground plant tissues
revealed, on average, a 14%decline in its
concentra tions under high [CO2] levels [16].
Microelement s, such as F e, I, and Zn, in plants a re
vital for hu man health, but little is known about
their response to high [CO2]. Not a single stu dy,
to my kn owledge, ana lyses th e effects of high [CO2]
on t he concentra tions of Se, which is an important
ant ioxidant, or Cr, which is extr emely import ant in
th e regula tion of blood-suga r levels and wh ich is
probably deficient in hu man nut rition [17].
The obscur ity of data might explain why no
compr ehen sive review exists a bout th e effects of
high [CO2
] on plan t st oichiomet ry an d why its role in
micronut rient ma lnutr ition has not been addressed.
As St erner and Elser [1] point out the limited and
diffuse da ta on element al compositionresult in
little awareness a nd little ability to perceive patter ns
of int erest , which in tu rn resu lt in little new da ta
being genera ted a nd little effort at compiling those
alr eady ava ilable. In lieu of rea l experiment s on
plant stoichiometry un der increased [CO2],
I ha ve run a th ought experim ent (see below).
Such experimen tsa re conventionally reser ved for
inherent ly simpler ph ysical ra ther tha n biological
system s, but th e reliance on stoichiomet ry simplifies
th e biology an d pr ovides su fficient rigor to gain
an insight in to the effect of increa sed [CO2] onplan t stoichiometr y.
A FACE thought experiment
Two un der pinn ings of ecological stoichiomet ry ar e
useful when ru nn ing a FACE experiment :
(1) a self-evident but importa nt fact tha t organisms
cannot creat e or convert elements ; and (2) the
proportions of element s in a pla nt cell can vary
widely, largely becaus e of th e pres ence of a lar ge
centra l vacuole, which is unique to plant cells [1];
for exam ple, Fe or Zn conten t can vary t enfold or m ore
in gra ss forage [18].
Suppose tha t a terr estrial vascular plant , forexample wheat , has been grown on two plots, Aa nd B,
in ident ical conditions, except t ha t [CO2] is ambient
in Abu t is doubled in B. If th e dry weight of th e
sta nding st ock in B is % higher tha n in A, are th e
stoichiometr ies of A plant s and B plant s different?
Even th ough t he a mounts of each individual element
in the soil were th e sam e in the two plots, th e higher
bioma ss in plot B is the r esult of stim ulat ed
photosynthesis tha t increased carbohydrat e
production. If the increase in car bohydrat es, the
chief const ituen t of plan ts, ha d been the only differen ce
between t he t wo plots, then the C, oxygen (O)
an d hydr ogen (H) cont ent in B plan ts would differ
very litt le from th at in A plant s (Box 1, Eqn II ). But
every other element would ha ve decreased by %
(Box 1, Eqn I II), which pr ovides a baseline
estimate of the potential shift in the plan t
stoichiometr y. This un derlines t he dichotomy
between C, O, H (which constitu te >90% of the d ry
weight of plant s) and other elements. Hen ce, pattern s
in t he chan ges of plant chemical composition should
be more evident on t he chemical scale of elemen ts
rat her t han on the coarser scales of complex
compounds , man y of which cont ain C, O, H a nd other
elements simultaneously.
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The dilution by carbohydrat es, however,
is unlikely to be the only difference between Aa nd
B plants. B plants might a dapt t o doubled [CO2]
by changing their tr an spira tion, root:shoot ra tio,
root morphology, root activit y or symbiotic
association with m ycorrhizae. Could t hese a dapta tions
equalize the stoichiometr ies of A and B plan ts byincreasing th e net uptake of every element by the
same percentage as t he net increase in C? I argue
here tha t these adapta tions could alter the %
decline caused by carbohydra te dilut ion,
but will not neut ra lize it.
The plots A and B a re monocultur es, as are m ost
sta ple crop fields; thus , by employing an y of the
adapt ations listed above, an individual B plant is
unlikely to gain an y advanta ge relative to its
almost iden tical neighbours . Moreover, none of th e
adaptationsper se can change the total ma ss of
any element in th e plot (except C, O an d H),
but t hey do alter condit ions in t he soil, including the
stoichiomet ry of soil nea r r oots a nd soil moistu re.
Because elements differ in their diffusion r ates and
upta ke kinetics, the net upta ke of each element
cannot increase by the sam e percentage. For
example, at higher concentra tions, [CO2] diffus es
into leaves more easily, thu s ena bling plant s to
nar row stomat al apert ures a nd consequently to lose
less water, tha t is to decreases t ra nspirat ion. This
effect has been well documen ted in experimen ts
with d oubled [CO2] on both C3 (e.g. rice and wh eat )
and C4 (e.g. maize and su garcane) plants with an
avera ge 23% redu ction of tr an spira tion [1113].
Reduced tr anspir ation leads to redu ced ma ss flow in
th e soil an d it can a lso increa se soil moistu re [19].
Thus, the two primary mechanisms that tran sport
element s to th e vicinity of roots, mas s flow and
diffusion, ar e alter ed in plot B. Mass flow is genera lly
more important for m obile elements, such as N,
an d diffusion is more import an t for imm obile
elements, such as P. Hence, the change in upt ake
rat es should be different among elements in plot B.
Fur ther more, increased photosynthesis puts
different ial interna l demands on elements . For
example, under h igh [CO2], plant dem and can
increas e for P but decrease for N [20,21]. To
summ ar ize, B plant s have higher C fixation ra tes,
altered intern al elementa l deman ds and chan ged
availability of elements n ear roots. Ther efore, A and
B plant s should differ not only in C:(oth er elemen ts)
rat ios but a lso in the r atios among other elements
(e.g. C:N, N:P an d P:Zn should also be different ).
In other words, th e change in t he st oichiometr y of
B plants should be nonuniform across element s.
Hence, A plants h aving the sam e stoichiometr y asB plants s hould be an exception. (If plant bioma ss
decreases in h igh [CO2], then a similar ar gument
can again sh ow that plant st oichiometr y chan ges.)
Ther efore, th e conclusion is tha t high [CO2],
as a rule, alters plant st oichiometr y.
Are overall patterns possible?
The above ar gument su ggests tha t th e chan ge in the
concentr at ion of elements (except C, O an d H) moves
in an opposite direction to the change in biomass,
but it does not exclude th e possibility th at levels of
some elements can increase or rem ain un changed
with an increase in biomass under high [CO2]. Forhum an n utr ition, however, it is importan t to know
whether overall patt erns would exist in high [CO2]
world. Terrest rial vascular plan ts worldwide sha re
what is funda ment ally the same physiology and ar e
exposed to essent ially the sam e [CO2], suggest ing
tha t overall patter ns in th e chan ges of plant
stoichiometr y ar e possible. Apa rticularly distur bing,
but plausible patter n is one in which the
concentr at ions of essen tial element s, including
those tha t ar e already deficient in t he diets of the
ha lf of the worlds populat ion, decreas e in plan ts.
As suggested a bove, both increased carbohydr at e
accumu lation and reduced mass flow can lead to this
patt ern. All else being equal, this pat tern would
mea n lower (nut rit ional value):(caloric value) of
crops an d the a ggra vation of the micronut rient
malnu trition problem. It would also increase th e
imperat ive to breed rice, wheat and other staple
crops with superior ability to concentr ate essential
elements such a s Fe, Zn, I and Se [6].
What do the scant published data reveal?
Motivat ed by the conclusion of th e th ought
experiment , I sea rched exten sively for p ublished
dat a on t he effects of high [CO2] on t he elemental
+1
TRENDS in Ecology & Evolution Vol.17 No.10 October 2002
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459Opinion
In ecological stoichiometry, elemental vectors are very useful because theyprovide a simple m eans wi th w hich to apply the power of mass balance laws toevery element.
Let (a1,a
2,,a
n),(b
1,b
2,b
n) and (c
1,c
2,c
3,0,0) denote elemental vector s
for dr y A plants, dry B plants and carbohydrates respectively, where the firstthree term s represents carbon (C), oxygen (O) and hydrogen (H) concentration s
and other t erms represent concentrations of every other element. Then
.
Let Mdenote the total dry weight of A p lants. If the % increase in bi omass ofB plants is solely because of the increase in carbohydrates, then m ass balanceyield s (Eqn I):
M(a1,a
2,,a
n) + M(c
1,c
2,c
3,0,0) = (1 + )M(b
1,b
2,,b
n) [Eqn I]
Thus, and . The percentage change in
concentration s of C, O and H is but because
the content of these three elements in plants and carbohydrates is similar,(i.e. a
i c
i), it follo ws that (Eqn II)
ai bi, i= 1,2,3 [Eqn II]
For the rest of th e elements, the percentage change equals to (Eqn III)
[Eqn III]..,...,4,1
1 nja
b
j
j=
+
=
1,2,3,1
1 =
+
= ia
ca
a
b
i
ii
i
i
.,...,4,1
nja
bj
j =
+
=
1,2,3,
1=
+
+= i
cab iii
1111
=== n
i
n
i
n
i cba
Box 1.Elemental vectors:the shift in the stoichiometry of B plants
because of carbohydrate dilution
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composition of plant s. The data ar e sur prisingly
scant . I hope that the scarcity and importance of the
dat a will encour age the genera tion of new dat a on the
changes in plan t st oichiomet ry caused by a globally
altered environment. It is star tling that, among
thousa nds of publications on doubled [CO2], only one
investigated it s effects on the gr ain s toichiometr y of
rice, the worlds m ost importa nt crop [22]. This st udy
foun d decrea sed concentr at ions of four out of five
meas ur ed elements in br own rice grains (N, onavera ge, dropped by 14%, P by 5%, Fe by 17%, Zn by
28%, but calcium (Ca) increa sed by 32%). One can
only hope tha t subsequ ent st udies will not show such
a distu rbing drop in th e levels of Fe and Zn. If high
[CO2] does decrease F e or Zn cont ent in var ious r ice
cultivars, even by a few percent, th e consequen ces for
the economy and h ealth of regions with str ong dietar y
dependence on rice, such as south east Asia, could be
dra stic. For exam ple, rice provides 76% of all calorie
inta kes for Ban gladesh [3], the worlds eighth most
populous count ry, wher e micronut rient deficiency
alrea dy lowers by 5% its gross domest ic product [23].
For t he worlds second m ost import an t crop,
wheat, dat a a re a lso very limited, but exist for a t
least five cultivar s. All th ree st udies sh ow
stat istically significant changes in grain
stoichiomet ry [2426] (Fig. 1). On a vera ge, the
concent ra tion of every measu red elemen t except
K declined. No similar da ta , to my knowledge,
has been published on other import ant crops such as
ma ize or r ye. Ironically, relat ively more da ta exist on
nonstaple crops [2735] and other terr estrial
vascular pla nt s [21,3647], par ticular ly on their
foliar content . All stu dies foun d sta tist ically
significan t chan ges in the st oichiomet ry of plan t
tissu es. Although t he levels of a few element s
increased in some stu dies, the concentra tion of every
element , on aver age, decrea sed (Fig. 1). (Note th at
th e decrease in foliar N is close to the 14% decrease
seen for N in aboveground pa rt s, as r eported in a
meta -analysis by Cotr ufo et al. [16].) I will not
cont empla te her e on th e consequences of th ese
changes to hum an nu trition and health , but I hope
tha t it is clear t hat further resear ch on th e effects of
high [CO2] on plan t st oichiomet ry is vital.
Further questions
Are th ere positive aspects of high [CO2] for h uma n
nutr ition, other t han the expected increases in
agricultur al yields? Some vitam ins, such as A or C,
are based entirely on t he elements C, O an d H; hence,
an increase in t he levels of those vita mins is n ot
const ra ined s toichiometr ically. For example,
vitamin C increa sed by 5% in ora nge juice har vested
from optima lly fertilized tr ees grown under
twice-am bient [CO2] [15]. If th e overa ll conten t of
elements (except C, O an d H) decrea ses, then it ispossible tha t levels of harm ful heavy metals, such as
lead (Pb) or m ercur y (Hg), would follow th e sa me
tr end. If high [CO2], however, aggra vates t he dieta ry
deficiency of essential elemen ts t hen none of the
above mentioned or an y oth er ben efits could induce
hum an bodies to ma ke up th e deficit.
Do changes in plan t st oichiomet ry th emselves
persist over year s? Becau se sta ple crops ha ve a life
span of only a few months, t his quest ion is m ore suited
for per ennia ls. In leaves of ora nge tr ees, declines
in the concentra tions of several elements t hat had
been monitored after 30 mont hs of exposur e to
twice-am bient [CO2], gradu ally diminished over th esubsequen t five year s [33]. These tr ees, however,
were always well water ed and optimally fert ilized,
and t herefore an elementa l imbalance in their
surr oundings was subsided. In Norway spr uce,
however, the changes in st oichiomet ry of needles
persist ed even in fert ilized trees over the four yea rs
exposur e to twice-ambien t levels of [CO2] (th e
experiment u sed 'bra nch bag' CO2
exposure
technique) [42]. Only one stu dy compa red m odern
plant s with t hose growing at h istorically lower
am bient [CO2]. Herba rium specimens of 13 plant
species were an alysed for 12 element s [48], including
Fe, Zn and Ca. All element s ar e cur ren tly at lower
levels than at any time in the past t hree centuries;
notably, stomata l density has a lso decreased.
(The differences in other en vironment al conditions,
however, might also have cont ribut ed to these chan ges.)
This raises an importan t question of whether the
curr ent h igher [CO2] has already contr ibuted to the
existing hidden hu nger problem. Over longer
timescales, ha ve historic fluctua tions of [CO2]
affected h erbivores by changing th e stoichiometr y of
their r esource? It is known t hat changes in plant
quality in t wice-ambient [CO2] can st rongly affect
her bivorous in sects [49,50]. Fr om a s toichiometr ic
TRENDS in Ecology & Evolution Vol.17 No.10 October 2002
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460 Opinion
TRENDS in Ecology & Evolution
N P K Ca S Mg
Element
Changeinmeanconcentration(%)
Fe Zn Mn Cu
25.0
15.0
5.0
5.0
Fig. 1. Changes (%) in the mean concentration of essential elements in plants grow n in twi ce-ambient
atmosph eric [CO2] relative to those grow n at ambient levels [all plants (foli ar), green; wheat (grains),
yellow ]. The figure is based on 25 studies covering 19 herbaceous and 11 woody plant species,
and five wh eat cultivars [21,2447], in which mult iple elements w ere measured under increased
concentration s of atmosph eric carbon diox ide [CO2]. If several [CO
2] levels were repor ted, the data for
the levels closest to the ambi ent and twice-amb ient were used. The studies wit h superenriched or
naturally high [CO2] were excluded. Mu ltipl e data for a single species or a cultiv ar were averaged
before calculating m eans. Error bars indicate the standard error of the mean; for foliar data, n= 30 for
nitro gen (N), phosphoro us (P), and potassium (K), 29 for calcium (Ca), 26 for magnesium (Mg),
14 for iron (Fe) and manganese (Mn), 12 for zinc (Zn), 9 for sulphu r (S) and copper (Cu); for wh eat
grains,n= 5 for N, P, K, Ca, Mg, Fe and Zn, and 3 for S and Mn. Up on requ est, I will gl adly pr ovide a
detailed table wit h all the data on which this figur e is based.
Acknowledgements
I thank M. Iarova for help
in the data compilation
and discussions. I am also
grateful to S. Levin,
E.Palson, N. Yarova,
E.Zea, and three
anonymous reviewers for
helpful comm ents. This
work was supported by
NSF grant DEB-0083566.
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TRENDS in Ecology & Evolution Vol.17 No.10 October 2002
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461Opinion
perspective, all her bivores a re similar, thu s such
effects should not be confined only to insects.
Rumin an ts, including livestock, an d oth er gra zers
could a lso be affected. Therefore, it is imper at ive to
recognize and quant ify at the ear ly stage how the
changing environment shifts th e stoichiometr y of
plants th e foundat ion of hum an n utr ition an d the
base of virtu ally all food webs in na tur e.
References
1 Stern er, R.W. and Elser, J.J. (2002)Ecological
St oichiometry: Th e Biology of Elem ents from
Molecules to th e Biosphere , Princeton
University Press
2 Williams, R.J.P. and Fr aust o da Silva, J.R.R.
(1996) The N atural S election of the Chem ical
Elem ents: The E nvironment and Lifes Chemistry ,
Clarendon Press
3 Food and Agriculture Organizat ion of the
United N ations (2000)Food Bal ance Sheets
FAOSTAT Database, available at
http://apps.fao.org
4 ACC/SCN (Administr ative Commit tee on
Coordinat ion, Subcommittee on Nu trit ion) and
Inter nat ional Food Policy Research Institut e
(2000) Fourth Report on the World N utrition
Situation , United Nations
5 Brown, K.H. an d Wuehler, S.E., eds (2000)Zinc
and H um an H ealth: The Results of Recent Trials
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