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พฤศจิกายน 19, 2010

Fertilizer Best Management Practices.Front Cover

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

———————————–

* Fertilizer Best Management Practices, Front Cover.

* Contents.

* Acknowledgements.

*Nutrient use efficiency – measurement and management.

* Right product, right rate, right time and right place … the foundation of best management practices for fertilizer.

* Balanced fertilization for sustainable use of plant nutrients.

* Site-specific nutrient management.

* Integrated farming and integrated plant nutrient management.

* “Teaspoon feeding”: precise plant nutrition through advanced application methods.

* Fertilizer best management practices in the context of product stewardship.

* Can we define a global framework within which fertilizer best management practices can be adapted to local conditions?.

* Fertilizer best management practices: what level of adaptation to local conditions is realistic in a developing country context?.

* Adoption of fertilizer best management practices: the need for a sociological approach.

* Changing farmers’ behavior in developing countries for a wider adoption of fertilizer best management practices – experience in Thailand.

* Farmers’ behavior and codes of fertiliser best management practices in India–viewpoint of Tata Chemicals Ltd.

* Preliminary synthesis of farmers’ attitudes and preferences towards nutrient application in China and India.

* Stewardship of crop protection products : maximising benefits and minimising risks.

* An economic evaluation of best management practices for crop nutrients in Canadian agriculture.

* Fertilizer best management practices in South America’s agricultural systems.

* Voluntary farm management qualification under the French official “Agriculture Raisonnée” scheme.

* Voluntary initiatives undertaken by the fertiliser industry of New Zealand.

* Fertcare® – putting best practice into stewardship.

* Principles, dissemination and performance of fertilizer best management practices developed in China.

* Voluntary initiatives and regulations for fertiliser best management practices in India.

* Fertilizer best management practices in Pakistan.

* Fertilizer best management practices in Southeast Asia.

* Global assessment of the situation of fertilizer best management practices.

* Possible entry points for action, an FAO overview.

* Strategies for controlling nitrogen emissions from agriculture: regulatory, voluntary and economic approaches.

* Fertilizer Best Management Practices, Back Cover.

Fertilizer Best Management Practices.

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

Fertilizer Best
Management Practices
General Principles,
Strategy for their Adoption and
Voluntary Initiatives vs Regulations
Papers presented at the IFA International Workshop
on Fertilizer Best Management Practices
7-9 March 2007, Brussels, Belgium
International Fertilizer Industry Association
Paris, France, 2007

Fertilizer Best Management Practices.

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

The designation employed and the presentation of material in this
information product do not imply the expression of any opinion
whatsoever on the part of the International Fertilizer Industry
Association. This includes matters pertaining to the legal status of
any country, territory, city or area or its authorities, or concerning
the delimitation of its frontiers or boundaries.
28, rue Marbeuf, 75008 Paris, France
Tel: +33 1 53 93 05 00 Fax: +33 1 53 93 05 45/ 47
publications@fertilizer.org www.fertilizer.org

Fertilizer Best Management Practices.Contents

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

———————————–

* Fertilizer Best Management Practices, Front Cover.

* Contents.

* Acknowledgements.

*Nutrient use efficiency – measurement and management.

* Right product, right rate, right time and right place … the foundation of best management practices for fertilizer.

* Balanced fertilization for sustainable use of plant nutrients.

* Site-specific nutrient management.

* Integrated farming and integrated plant nutrient management.

* “Teaspoon feeding”: precise plant nutrition through advanced application methods.

* Fertilizer best management practices in the context of product stewardship.

* Can we define a global framework within which fertilizer best management practices can be adapted to local conditions?.

* Fertilizer best management practices: what level of adaptation to local conditions is realistic in a developing country context?.

* Adoption of fertilizer best management practices: the need for a sociological approach.

* Changing farmers’ behavior in developing countries for a wider adoption of fertilizer best management practices – experience in Thailand.

* Farmers’ behavior and codes of fertiliser best management practices in India–viewpoint of Tata Chemicals Ltd.

* Preliminary synthesis of farmers’ attitudes and preferences towards nutrient application in China and India.

* Stewardship of crop protection products : maximising benefits and minimising risks.

* An economic evaluation of best management practices for crop nutrients in Canadian agriculture.

* Fertilizer best management practices in South America’s agricultural systems.

* Voluntary farm management qualification under the French official “Agriculture Raisonnée” scheme.

* Voluntary initiatives undertaken by the fertiliser industry of New Zealand.

* Fertcare® – putting best practice into stewardship.

* Principles, dissemination and performance of fertilizer best management practices developed in China.

* Voluntary initiatives and regulations for fertiliser best management practices in India.

* Fertilizer best management practices in Pakistan.

* Fertilizer best management practices in Southeast Asia.

* Global assessment of the situation of fertilizer best management practices.

* Possible entry points for action, an FAO overview.

* Strategies for controlling nitrogen emissions from agriculture: regulatory, voluntary and economic approaches.

* Fertilizer Best Management Practices, Back Cover.

Contents
Part 1. General principles of fertilizer best management practices
Nutrient use effi ciency – measurement and management 1
A. Dobermann
Right product, right rate, right time and right place … the
foundation of best management practices for fertilizer 29
T.L. Roberts
Balanced fertilization for sustainable use of plant nutrients 33
L. Cissé
Site-specifi c nutrient management 47
R.J. Buresh and C. Witt
Integrated farming and integrated plant nutrient management 57
C. Drummond
“Teaspoon feeding”: precise plant nutrition through advanced
application methods 67
E. Barak and S. Raban
Fertilizer best management practices in the context of product
stewardship 71
J. Lammel
Can we defi ne a global framework within which fertilizer best
management practices can be adapted to local conditions? 77
P.E. Fixen
Fertilizer best management practices: what level of adaptation to
local conditions is realistic in a developing country context? 87
J. Ryan

Fertilizer Best Management Practices.Contents

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

Part 2. Strategy for the adoption of fertilizer best management practices
Adoption of fertilizer best management practices: the need for a
sociological approach 99
F.G. Palis, R.J. Buresh, G.R. Singleton and R.J. Flor
Changing farmers’ behavior in developing countries for a wider
adoption of fertilizer best management practices – experience in
Thailand 111
K. Soitong
Farmers’ behavior and codes of fertiliser best management practices
in India – viewpoint of Tata Chemicals Ltd 121
B.B. Singh
Preliminary synthesis of farmers’ attitudes and preferences towards
nutrient application in China and India 127
H. Magen, P. Imas and S.K. Bansal
Stewardship of crop protection products: maximising benefi ts and
minimising risks 139
K.A. Jones
Part 3. Voluntary initiatives vs regulations
An economic evaluation of best management practices for crop
nutrients in Canadian agriculture 145
R. Larson
Fertilizer best management practices in South America’s agricultural
systems 153
R. Melgar and E. Daher
Vountary farm management qualifi cation under the French offi cial
“Agriculture Raisonnée” scheme 163
P. Eveillard
Voluntary initiatives undertaken by the fertiliser industry of New
Zealand 167
H. Furness
Fertcare® – putting best practice into stewardship 177
N. Drew

Fertilizer Best Management Practices.Contents

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

Principles, dissemination and performance of fertilizer best
management practices developed in China 193
F.S. Zhang, M.S. Fan and W.F. Zhang
Voluntary initiatives and regulations for fertiliser best management
practices in India 203
R.K. Tewatia
Fertilizer best management practices in Pakistan 213
N. Ahmad
Fertilizer best management practices in Southeast Asia 221
R.J. Buresh, C. Witt and J.M.C. Pasuquin
Global assessment of the situation of fertilizer best management
practices 231
A. Krauss
Possible entry points for action, an FAO overview 239
J. Poulisse
Strategies for controlling nitrogen emissions from agriculture:
regulatory, voluntary and economic approaches 245
M.A. Sutton, J.W. Erisman and O. Oenema

Fertilizer Best Management Practices.Acknowledgements

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

———————————–

* Fertilizer Best Management Practices, Front Cover.

* Contents.

* Acknowledgements.

*Nutrient use efficiency – measurement and management.

* Right product, right rate, right time and right place … the foundation of best management practices for fertilizer.

* Balanced fertilization for sustainable use of plant nutrients.

* Site-specific nutrient management.

* Integrated farming and integrated plant nutrient management.

* “Teaspoon feeding”: precise plant nutrition through advanced application methods.

* Fertilizer best management practices in the context of product stewardship.

* Can we define a global framework within which fertilizer best management practices can be adapted to local conditions?.

* Fertilizer best management practices: what level of adaptation to local conditions is realistic in a developing country context?.

* Adoption of fertilizer best management practices: the need for a sociological approach.

* Changing farmers’ behavior in developing countries for a wider adoption of fertilizer best management practices – experience in Thailand.

* Farmers’ behavior and codes of fertiliser best management practices in India–viewpoint of Tata Chemicals Ltd.

* Preliminary synthesis of farmers’ attitudes and preferences towards nutrient application in China and India.

* Stewardship of crop protection products : maximising benefits and minimising risks.

* An economic evaluation of best management practices for crop nutrients in Canadian agriculture.

* Fertilizer best management practices in South America’s agricultural systems.

* Voluntary farm management qualification under the French official “Agriculture Raisonnée” scheme.

* Voluntary initiatives undertaken by the fertiliser industry of New Zealand.

* Fertcare® – putting best practice into stewardship.

* Principles, dissemination and performance of fertilizer best management practices developed in China.

* Voluntary initiatives and regulations for fertiliser best management practices in India.

* Fertilizer best management practices in Pakistan.

* Fertilizer best management practices in Southeast Asia.

* Global assessment of the situation of fertilizer best management practices.

* Possible entry points for action, an FAO overview.

* Strategies for controlling nitrogen emissions from agriculture: regulatory, voluntary and economic approaches.

* Fertilizer Best Management Practices, Back Cover.

Acknowledgements
Th e IFA Executive Committee decided in 2006 to launch an initiative on fertilizer best
management practices (FBMPs). One component of that initiative was the organization
of an International Workshop on Fertilizer Best Management Practices, which
took place from 7 to 9 March 2007 in Brussels, Belgium. Th e workshop gathered some
40 participants from all continents and relevant stakeholder categories. It was aimed
at (i) defi ning the general principles of FBMPs and the strategy for their wider adoption;
(ii) defi ning the role of the fertilizer industry in developing and promoting FBMPs
and listing priority areas for action; (iii) exchanging information on experiences;
(iv) reviewing achievements and identifying gaps; and (v) understanding the actors and
identifying the key partners. Th e workshop was conducted under the leadership of the
Convenor of the IFA Task Force on Fertilizer Best Management Practices, Mr. R. Sinha
from DSCL, India.
Th is book is a collection of all the papers submitted by the speakers. In addition to this
book, all the papers and slides presented at the workshop are available in PDF format on
IFA’s website at www.fertilizer.org/ifa/publicat/bap/2007_brussels_fb mp.asp. No paper
has been received for three contributions presented at the workshop, but the corresponding
slides can be downloaded online.
Th e papers published in this book have been reviewed and edited by A. Krauss,
K. Isherwood and P. Heff er. Many thanks to C. Aholou-Pütz and H. Ginet for the layout
of the book and of the graphics in preparation for printing.

Fertilizer Best Management Practices.p1

ผ่านทาง ifa-FBMP – Windows Live.

Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

———————————–

* Fertilizer Best Management Practices, Front Cover.

* Contents.

* Acknowledgements.

*Nutrient use efficiency – measurement and management.

* Right product, right rate, right time and right place … the foundation of best management practices for fertilizer.

* Balanced fertilization for sustainable use of plant nutrients.

* Site-specific nutrient management.

* Integrated farming and integrated plant nutrient management.

* “Teaspoon feeding”: precise plant nutrition through advanced application methods.

* Fertilizer best management practices in the context of product stewardship.

* Can we define a global framework within which fertilizer best management practices can be adapted to local conditions?.

* Fertilizer best management practices: what level of adaptation to local conditions is realistic in a developing country context?.

* Adoption of fertilizer best management practices: the need for a sociological approach.

* Changing farmers’ behavior in developing countries for a wider adoption of fertilizer best management practices – experience in Thailand.

* Farmers’ behavior and codes of fertiliser best management practices in India–viewpoint of Tata Chemicals Ltd.

* Preliminary synthesis of farmers’ attitudes and preferences towards nutrient application in China and India.

* Stewardship of crop protection products : maximising benefits and minimising risks.

* An economic evaluation of best management practices for crop nutrients in Canadian agriculture.

* Fertilizer best management practices in South America’s agricultural systems.

* Voluntary farm management qualification under the French official “Agriculture Raisonnée” scheme.

* Voluntary initiatives undertaken by the fertiliser industry of New Zealand.

* Fertcare® – putting best practice into stewardship.

* Principles, dissemination and performance of fertilizer best management practices developed in China.

* Voluntary initiatives and regulations for fertiliser best management practices in India.

* Fertilizer best management practices in Pakistan.

* Fertilizer best management practices in Southeast Asia.

* Global assessment of the situation of fertilizer best management practices.

* Possible entry points for action, an FAO overview.

* Strategies for controlling nitrogen emissions from agriculture: regulatory, voluntary and economic approaches.

* Fertilizer Best Management Practices, Back Cover.

Nutrient use effi ciency – measurement
and management
A. Dobermann
University of Nebraska-Lincoln, USA; adobermann2@unl.edu
Nutrients in the global scheme
Mineral fertilizers have sustained world agriculture and thus global population and
wealth growth for more than 100 years (Smil, 2001; Stewart et al., 2005). Th eir contribution
to increasing crop yields has spared millions of hectares of natural ecosystems that
otherwise would have been converted to agriculture (Balmford et al., 2005). However,
lacking, imbalanced, inappropriate or excessive use of nutrients in agricultural systems
remains a concern. Nutrient mining is a major cause for low crop yields in parts of the
developing world, particularly Africa. In other situations, nutrients such as nitrogen
(N) and phosphorus (P) oft en move beyond the bounds of the agricultural fi eld because
the management practices used fail to achieve good congruence between nutrient supply
and crop nutrient demand (van Noordwijk and Cadisch, 2002). If left unchecked,
such losses may bear signifi cant costs to society (Mosier et al., 2001). Hence, increasing
nutrient use effi ciency continues to be a major challenge for world agriculture.
Th is paper tries to summarize how the use effi ciency of N, P and potassium (K) from
mineral fertilizer is commonly defi ned and measured, what needs to be considered for
interpreting such values, and how it can be improved through soil, crop and fertilizer
management. It focuses on cereal systems because those consume the bulk of the
world’s fertilizer, but the principles discussed are similar in all agricultural crops. Where
possible, attempts are made to discuss diff erences between developed and developing
countries. Two key messages emerge: (i) Nutrient use effi ciencies measured under practical
farming conditions are mostly lower than those reported from research experiments,
but information on current levels of fertilizer use and nutrient use effi ciency by
diff erent crops, cropping systems and world regions remains insuffi cient; (ii) Numerous
technologies for increasing nutrient use effi ciency exist. Th ey have been evaluated thoroughly,
but adoption by farmers is lagging behind.
Measuring nutrient use effi ciency
Agronomic indices for short-term assessment of nutrient use effi ciency
Table 1 summarizes a set of simple indices that are frequently used in agronomic research
to assess the effi ciency of applied fertilizer (Novoa and Loomis, 1981; Cassman
et al., 2002), mainly for assessing the short-term crop response to a nutrient. A practical
example is illustrated in Figure 1. Other indices are sometimes used (Gourley et al.,
1993; Huggins and Pan, 1993), but they have no additional advantages for understanding
fertilizer best management practices (FBMPs). More detailed studies on the fate

Fertilizer Best Management Practices.p2

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Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

Table 1. Indices of nutrient use effi ciency, their calculation using the difference method,
and their interpretation.
Index Calculation Interpretation Nitrogen in cereals
RE = Apparent crop
recovery effi ciency
of applied nutrient
(kg increase in N
uptake per kg N
applied)
RE=(U – Uo)/F • RE depends on the
congruence between plant
demand and nutrient release
from fertilizer.
• RE is affected by the application
method (amount,
timing, placement, N form)
and factors that determine
the size of the crop nutrient
sink (genotype, climate,
plant density, abiotic/biotic
stresses).
0.30–0.50 kg/kg;
0.50–0.80 kg/kg
in well-managed
systems, at low
levels of N use,
or at low soil N
supply
PE = Physiological
effi ciency of applied
N
(kg yield increase
per kg increase in
N uptake from fertilizer)
PE=(Y– Yo)/(U– Uo) • Ability of a plant to transform
nutrients acquired
from fertilizer into economic
yield (grain).
• Depends on genotype,
environment and management.
• Low PE suggests sub-optimal
growth (nutrient defi
ciencies, drought stress,
heat stress, mineral toxicities,
pests).
40–60 kg/kg;
>50 kg/kg in
well-managed
systems, at low
levels of N use,
or at low soil N
supply
IE = Internal utilization
effi ciency of
a nutrient
(kg yield per kg nutrient
uptake)
IE=Y/U • Ability of a plant to transform
nutrients acquired
from all sources (soil, fertilizer)
into economic yield
(grain).
• Depends on genotype,
environment and management.
• A very high IE suggests defi
ciency of that nutrient.
• Low IE suggests poor internal
nutrient conversion due
to other stresses (nutrient
defi ciencies, drought stress,
heat stress, mineral toxicities,
pests).
30–90 kg/kg;
55-65 kg/kg is
the optimal range
for balanced
nutrition at high
yield levels

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Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

AE = Agronomic
effi ciency of applied
nutrient
(kg yield increase
per kg nutrient applied)
AE=(Y – Yo)/F or
AE=RE x PE
• Product of nutrient recovery
from mineral or organic
fertilizer (RE) and the effi -
ciency with which the plant
uses each additional unit of
nutrient (PE).
• AE depends on management
practices that affect
RE and PE.
10–30 kg/kg;
>25 kg/kg in
well-managed
systems, at low
levels of N use,
or at low soil N
supply
PFP = Partial factor
productivity of
applied nutrient
(kg harvested product
per kg nutrient
applied)
PFP=Y/F or
PFP=(Yo/F) + AE
• Most important for farmers
because it integrates the use
effi ciency of both indigenous
and applied nutrients.
• High indigenous soil nutrient
supply (Yo) and high
AE are equally important for
PFP.
40–80 kg/kg;
>60 kg/kg in
well-managed
systems, at low
levels of N use,
or at low soil N
supply
F – amount of (fertilizer) nutrient applied (kg/ha)
Y – crop yield with applied nutrients (kg/ha)
Yo – crop yield (kg/ha) in a control treatment with no N
U – total plant nutrient uptake in aboveground biomass at maturity (kg/ha) in a plot that
received fertilizer
U – total nutrient uptake in aboveground biomass at maturity (kg/ha) in a plot that received
no fertilizer

of nutrients in agro-ecosystems oft en involve isotopes, which are particularly useful for
understanding loss, immobilization, fi xation and release mechanisms.
In fi eld studies, nutrient use effi ciencies are either calculated based on diff erences in
crop yield and/or nutrient uptake between fertilized plots and an unfertilized control
(‘diff erence method’, Table 1), or by using isotope-labeled fertilizers to estimate crop and
soil recovery of applied nutrients. Time scale is usually one cropping season. Spatial scale
for measurement is mostly a fi eld or plot. For the same soil and cropping conditions,
nutrient use effi ciency generally decreases with increasing nutrient amount added (Figure
1). Crop yield (Y) and plant nutrient accumulation/uptake (U) typically increase
with increasing nutrient addition (F) and gradually approach a ceiling (Figures 1a and
1c). Th e level of this ceiling is determined by the climatic-genetic yield potential. At low
levels of nutrient supply, rates of increase in yield and nutrient uptake are large because
the nutrient of interest is the primary factor limiting growth (de Wit, 1992). As nutrient
supply increases, incremental yield gains become smaller because yield determinants
other than that nutrient become more limiting as the yield potential is approached.
Because each of the indices in Table 1 has a diff erent interpretation value, fertilizer
research should include measurements of several indices to understand the factors governing
nutrient uptake and fertilizer effi ciency, to compare short-term nutrient use effi
ciency in diff erent environments, and to evaluate diff erent management strategies. Th e

Fertilizer Best Management Practices.p4

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Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

Figure 1. Response of irrigated maize to N application at Clay Center, Nebraska,
USA: (a) relationship between plant N uptake (U) and N rate and the recovery
efficiency of fertilizer N at four N rates; (b) relationship between grain yield (Y)
and plant N uptake (U) and the physiological (PE) and internal efficiency (IE) of
fertilizer N; (c) relationship between grain yield (Y) and N rate (F) and the
agronomic efficiency (AE) and partial factor productivity (PFP) of applied N.
Dashed lines indicate maximum profit (Dobermann and Cassman, 2004).

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Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

The publication can be downloaded from IFA’s web site.
IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

‘diff erence method’ is simple and cost-effi cient, which makes it particularly suitable for
on-farm research. However, sampling and measurement must be done with great care.
Interpretation must also consider potentially confounding factors. For example, agronomic
effi ciency (AE) and apparent recovery effi ciency (RE) are not appropriate indices
of nutrient use effi ciency when comparing cropping practices such as crop establishment
methods or diff erent water management regimes when the crop yield in control
treatments (Yo) diff ers signifi cantly because of these management practices. In these
instances, partial factor productivity (the ratio of grain yield/nutrient amount applied,
PFP) is a more appropriate index for making comparisons. Likewise, comparisons of
RE and physiological effi ciency (PE) among genotypes should use agronomically fi t
varieties and avoid comparison with ‘inferior germplasm’ not adapted to the particular
growth conditions. Caution is required when using AE, RE or PE for assessing trends in
nutrient use effi ciency in long-term experiments because depletion of indigenous soil
nutrient resources in permanent nutrient omission plots (0-N, 0-P or 0-K plots) will
lead to overestimation of the true nutrient use effi ciency in fertilized plots. For nitrogen,
results obtained with the ‘diff erence method’ may also be confounded by added-N
interactions, i.e. diff erences in N mineralization rates from soil organic matter and crop
residues between +N and 0-N plots.
Agronomic indices only provide accurate assessment of nutrient use effi ciency for
systems that are at relatively steady-state with regard to soil nutrient content and where
diff erences in root systems between unfertilized and fertilized crops are relatively small.
For example, nitrogen in roots as well as any net accumulation of N from fertilizer
in soil organic matter and its eff ect on the indigenous soil N supply for subsequently
grown crops cannot be easily accounted for. Th is may lead to an underestimation of the
overall system level effi ciency of applied N inputs. In the example shown in Table 2, the
average PFP of applied N suggested that the recommended management system was
more N-effi cient than the intensively managed system because it produced 70 kg grain/
kg N applied (or 0.88 kg grain N/kg N applied) as opposed to 50 kg grain/kg N (or 0.65
kg grain N/kg N applied) in the intensive system. However, when the net change in soil
N was included, both systems had nearly the same system level N use effi ciency (0.92-
1.01) because fertilizer-N contributed to build-up of soil organic matter in the intensive
system. Over time, this will increase soil N supply, reduce the need for fertilizer, and
increase PFPN. Nutrient budgeting and isotope methods should be used to assess the
fate of nutrients in the entire soil-crop-atmosphere system over diff erent time periods
and at diff erent scales.
Nutrient budgets for medium- to long-term assessment
Nutrient budgeting approaches are used to evaluate system-level nutrient use effi ciency
and to understand nutrient cycling by estimating input, storage and export processes by
mass balance. A surplus or defi cit is a measure of the net depletion (output > input) or
enrichment (output < input) of the system, or simply of the ‘unaccounted for’ nutrient.
Th is approach is used in studies on the fate of nutrients, for medium- to long-term assessment
of FBMPs, nutrient fl ows and their respective impact on soil and the environment
in managed or natural ecosystems, and for regulatory purposes in industrialized
countries.

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Table 2. Nitrogen use effi ciency in a long-term experiment with irrigated continuous
maize systems (CC) managed at recommended (-rec) and intensive (-int) levels of plant
density and fertilizer inputs. Total amounts for a fi ve-year period (2000-2005) at Lincoln,
Nebraska, USA.
2000-2005 CC-rec CC-int
Average maize yield (t/ha/yr) 14.0 15.0
Fertilizer-N input (kg N/ha) 1005 1495
Nitrogen removal with grain (kg N/ha) 880 970
Measured change in total soil N (kg/ha) 139 404
N unaccounted for (kg/ha) 14 121
NUE 1: partial factor productivity (kg grain/kg N applied) 70 50
NUE 2: kg grain N/kg N applied 0.88 0.65
NUE 3: kg grain N + change in soil N/kg N applied 1.01 0.92

Nutrient budgets can be constructed for diff erent time periods at any scale, ranging
from small fi elds to whole countries or the globe. Budgets constructed for the purpose
of guiding and regulating agricultural management or for policy decisions oft en consist
of simple mass balances. For proper interpretation, methodologies must be clearly described
and budgets should include statements about scales and uncertainties associated
with the estimates (Oenema et al., 2003). General methodologies for this have been
proposed in recent years (Smaling and Fresco, 1993; Roy et al., 2004), but the degree of
detail depends on the purpose of budgeting and on the resources available to collect the
information. Generally speaking, nutrient budgets for larger regions are oft en highly
uncertain because of imprecise available information on key processes such as fertilizer
input by diff erent crops and cropping systems, N input from atmospheric deposition
and biological N fi xation, and gaseous, leaching and runoff losses.
Most common are partial budgets that do not include all inputs or outputs or make
assumptions about those that are diffi cult to quantify at the scale of interest. For a correct
interpretation, nutrient budgets must be compared with the nutrient stock in the
soil and its availability. A negative nutrient balance on a soil that has excessive levels of
that nutrient is not necessarily bad. Likewise, a neutral nutrient balance indicates that
the total stock in the soil does not change, but the ‘quality’ of the stock, and hence soil
fertility, may still alter. Hence, a diff erentiation between ‘available’ and ‘not-immediately
available’ nutrients is useful in nutrient balance studies, but has only been attempted
occasionally (Janssen, 1999; Hoa et al., 2006). Table 3 shows diff erent K balances for
an irrigated rice system in South Vietnam. Partial K budgets resulted in K balance estimates
that were too negative because of neglected K inputs via rain, irrigation water
and sediments. Irrespective of fertilizer-K input, large annual K input from sediments
resulted in a positive balance of total K, but most of this was not plant-available

Fertilizer Best Management Practices.p7

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Table 3. Comparison of partial and complete K input-output budgets in two treatments
of a long-term experiment with irrigated double-cropping of rice at Omon, Vietnam.
NP: no K fertilizer; NPK: 150 kg K/ha/yr (Hoa et al., 2006).
K budget (kg K/ha/yr) NP NPK
Balance of soluble K (partial budget) -92 22
Balance of soluble K (complete budget) -69 44
Balance of labile K (NH4-acetate K, complete budget) -66 47
Balance of non-labile K (NaTPB-K, complete budget) -58 55
Balance of total K (complete budget) 251 364
Partial budget: Inputs: fertilizer; Outputs: crop K removal with grain and straw
Complete budget: Inputs: fertilizer, rain water, irrigation water, sediments from annual fl ood;
Outputs: crop K removal with grain and straw, leaching, runoff, sediment removal

Current status of nutrient use effi ciency
Nitrogen
World consumption of N fertilizers has averaged 83-85 million metric tonnes (Mt) in
recent years, with nearly 60% of that amount applied to cereal crops (Table 4). At a global
scale, cereal production (slope = 31 Mt/year), cereal yields (slope = 45 kg/year), and
fertilizer N consumption (slope = 2 Mt/year) have all increased in a near-linear fashion
during the past 40 years. However, signifi cant diff erences exist among world regions
with regard to N use effi ciency (Table 4). At global or regional scales, PFPN (Table 1) is
the only index of N use effi ciency that can be estimated more easily, although not very
precisely because of uncertainties about the actual N use by diff erent crops and about
crop production statistics. Because PFP is a ratio, it always declines from large values at
small N application rates to smaller values at high N application rates. Th us, diff erences
in the average cereal PFPN among world regions depend on which cereal crops are
grown, their attainable yield potential, soil quality, amount and form of N application,
and the overall timeliness and quality of other crop management operations.
Globally, PFPN in cereal production has decreased from 245 kg grain/kg N applied
in 1961/65, to 52 kg/kg in 1981/85, and is currently about 44 kg/kg. Th is decrease in
PFPN occurs as farmers move yields higher along a fi xed response function unless off -
setting factors, such as improved management that remove constraints on yield, shift
the response function up. In other words, an initial decline in PFPN is an expected
consequence of the adoption of N fertilizers by farmers and not necessarily bad within
a system context.
In many developed countries, cereal yields have continued to increase in the past 20
years without signifi cant increases in N fertilizer use, or even with substantial declines
in N use in some areas. Th is has resulted in steady increases of PFPN in Western Europe
(rainfed cereals systems), North America (rainfed and irrigated maize), Japan and
South Korea (irrigated rice) since the mid 1980s (Dobermann and Cassman, 2005). At

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Fertilizer Best Management Practices. First edition, IFA, Paris, France, August 2007

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IFA : International Fertilizer Industry Association – Fertilizer Best Management Practices .
To obtain paper copies, contact IFA.

present, average cereal yields in these regions are 60 to 100% above the world average,
even though the N rates applied are only 30 to 60% above world average rates (Table 4).
High yields and high PFPN in these regions result from a combination of fertile soils, favorable
climate and excellent management practices. Investments in crop improvement
(high yielding varieties with stress tolerance), new fertilizer products and application
technologies, algorithms and support services for better fertilizer recommendations,
better soil and crop management technologies, extension education, and local regulation
of excessive N use by both the public and the private sector have contributed to the
increase in N use effi ciency (Cassman et al., 2002; IFA, 2007). It is likely that this trend
will continue.
In developing regions, N fertilizer use was small in the early 1960s and increased
exponentially during the course of the Green Revolution. Th e large increase in N use
since the 1960s resulted in a steep decrease in PFPN in all developing regions. Regional
N rates on cereals range from less than 10 kg N/ha in Africa to more than 150 kg N/ha
in East Asia (Table 4) and, with the exception of Africa, PFPN continues to decline in
all developing regions at rates of –1 to –2%/year (Dobermann and Cassman, 2005). Th e
very high PFPN in Africa (122 kg/kg N applied) and Eastern Europe/Central Asia (84
kg/kg) are indicative of unsustainable soil N mining due to low N rates used at present.
In some countries, e.g. India, PFPN seems to have leveled off in recent years, but in
many other developing countries it continues to decline because public and private sector
investments in better technologies, services and extension education are far below
those made in developed countries. Except for research and limited on-farm demonstrations,
there are no documented cases for country-scale increase in N use effi ciency
in a developing country that could be ascribed to adoption of better N management
technologies.
How does this compare with more detailed fi eld-level measurements of N use effi -
ciency? A clear distinction must be made between fi eld experiments conducted under
more controlled conditions in research stations and values measured on-farm, under
practical farming conditions (Table 5). Th e latter are scarce in the literature, but from
the few available studies it is clear that actual N use effi ciency is substantially lower in
most farms than what is achieved in research experiments. For example, in the worldwide
research trials summarized by Ladha et al. (2005), the average REN in research
plots was 46% in rice, 57% in wheat and 65% in maize, with a ‘global’ mean of 55% (Table
5). Th is is even higher than Smil’s (1999) estimate, who suggested that, on a global
scale, about half of all anthropogenic N inputs on croplands are taken up by harvested
crops and their residues. In contrast, the few available on-farm studies suggest that average
REN values are more commonly in the 30-40% range (Table 5). Similar diff erences
between research trials and on-farm studies occur for other indices of N use effi ciency
(Table 5). Notably, average PFPN in on-farm studies conducted in developing countries
ranged from 44 to 49 kg/kg N, which is close to the estimated ‘global’ average of 44
kg/kg N (Table 4).
Lower N use effi ciency in farmers’ fi elds is usually explained by a lower level of management
quality under practical farming conditions and greater spatial variability of
factors controlling REN, PEN and PFPN (Cassman et al., 2002). Th is is further supported

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