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N° d’ordre : 4439 THÈSE Présentée à L’UNIVERSITÉ DE BORDEAUX 1 ÉCOLE DOCTORALE : Sciences et Environnements Par Muhammad NADEEM Pour obtenir le grade de Docteur Spécialité : Ecologie évolutive, fonctionnelle et des communautés Remobilisation des réserves en phosphore du grain et prélèvement du phosphore exogène pendant la germination et la croissance juvénile du maïs (Zea mays L.) Soutenue le : 16/12/2011 Après avis de : M. Jean-Christophe AVICE Prof. Université Caen Rapporteur M. Christophe SALON DR, INRA Dijon Rapporteur Devant la commission d’examen formée de : M. Jean-Christophe AVICE Prof. Université Caen Rapporteur M. Christophe SALON DR, INRA Dijon Rapporteur M. Abraham ESCOBAR GUTIERREZ CR, INRA Lusignan Examinateur M. Olivier TURC CR, INRA Montpellier Examinateur M. Alain MOLLIER CR, INRA Bordeaux Co-directeur de thèse M. Sylvain PELLERIN DR, INRA Bordeaux Directeur de thèse INRA ENITAB, UMR 1220 TCEM Transfert sol-plantes et Cycles des Éléments Minéraux dans les écosystèmes cultivés, 71 avenue Edouard Bourlaux, BP 81, 33883 Villenave d'Ornon, France.

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Page 1: L’UNIVERSITÉ DE BORDEAUX 1ori-oai.u-bordeaux1.fr/pdf/2011/NADEEM_MUHAMMAD_2011.pdf · Muhammad NADEEM Pour obtenir le grade de Docteur Spécialité : Ecologie évolutive, fonctionnelle

N° d’ordre : 4439

THÈSE

Présentée à

L’UNIVERSITÉ DE BORDEAUX 1ÉCOLE DOCTORALE : Sciences et Environnements

Par

Muhammad NADEEMPour obtenir le grade de

DocteurSpécialité : Ecologie évolutive, fonctionnelle et des communautés

Remobilisation des réserves en phosphore du grain et prélèvement

du phosphore exogène pendant la germination et la croissance

juvénile du maïs (Zea mays L.)

Soutenue le : 16/12/2011

Après avis de :

M. Jean-Christophe AVICE Prof. Université Caen RapporteurM. Christophe SALON DR, INRA Dijon Rapporteur

Devant la commission d’examen formée de :M. Jean-Christophe AVICE Prof. Université Caen RapporteurM. Christophe SALON DR, INRA Dijon RapporteurM. Abraham ESCOBAR GUTIERREZ CR, INRA Lusignan ExaminateurM. Olivier TURC CR, INRA Montpellier ExaminateurM. Alain MOLLIER CR, INRA Bordeaux Co-directeur de thèseM. Sylvain PELLERIN DR, INRA Bordeaux Directeur de thèse

INRA ENITAB, UMR 1220 TCEM Transfert sol-plantes et Cycles des Éléments Minéraux dans les écosystèmes cultivés, 71 avenue Edouard Bourlaux, BP 81, 33883 Villenave d'Ornon, France.

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THESIS

Presented at

UNIVERSITY OF BORDEAUX 1Sciences and Environments Graduate School

By

Muhammad NADEEMFor the Degree of

DoctorSpeciality: Functional and Community Ecology

Remobilization of seed phosphorus reserves and exogenous

phosphorus uptake during germination and early growth stages of

maize (Zea mays L.)

16th December 2011

Examination Commission M. Jean-Christophe AVICE Prof. University of Caen ExaminerM. Christophe SALON DR, INRA Dijon ExaminerM. Abraham ESCOBAR GUTIERREZ CR, INRA Lusignan ExaminerM. Olivier TURC CR, INRA Montpellier ExaminerM. Alain MOLLIER CR, INRA Bordeaux Co-superviserM. Sylvain PELLERIN DR, INRA Bordeaux Superviser

INRA ENITAB, UMR 1220 TCEM Soil-plant Transfer and the nutrient and trace element cycle in cultivated ecosystems, 71 avenue Edouard Bourlaux, BP 81, 33883 Villenave d'Ornon, France.

N° d’ordre : 4439

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Dedicated

to

My Dearest Parents

who are the part of my soul and whose love,

affection and confidence enabled

me to achieve this goal

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ii

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Acknowledgements

If all the trees were pens and oceans were ink, the praise of almighty ALLAH (subhanahu wa ta’ala), the ultimate source of knowledge to mankind, would never end. I therefore, start my acknowledgement as a word of thank to almighty ALLAH (subhanahu wa ta’ala), WHO bestowed me with the potential and ability to contribute a drop of material to the existing ocean of scientific knowledge. I also offer my humblest thanks from the deepest core of my heart to the Holy Prophet MUHAMMAD (peace be upon him), WHO is forever a torch of guidance and knowledge for humanity as a whole.

I would like to express my sincerest gratitude to my supervisor Prof. Dr. Sylvain PELLERIN for his continue support, guidance and also for his vast knowledge that helped me to complete this project in time. I also owe a debt of gratitude for my co-supervisor Dr. Alain MOLLIER for his worthy ideas, guidance, motivation and enthusiasm that helped me a lot to accomplish the objectives of my Ph.D research work. I would never have imagined such a best advisor and mentor for my Ph.D studies. I have no hesitation to say that I learned a lot from him.

I would like to extend my sincere regards to my thesis committee members Dr. Carolyne DURR (INRA Anger), Dr. Marie-Hélène MACHEREL (University of Anger) and Dr. Marie-Pascale PRUD'HOMME (University of Caen) for their kind guidance and for giving valuable advice during my PhD studies.

Thanks are due for Dr. Christian MOREL for providing valuable suggestions and help during my experiments especially for working with 32P. I am also thankful to Mr. Alain VIVES and Mr. Loïc PRUD'HOMME for their useful suggestions and guidance during the greenhouse and growth chamber experiments and for laboratory analysis. They did their best in this regard. My sincere thanks also go to the technical staff in the laboratory and especially Ms. Anne GALLET-BUDNEK, Ms. Sylvie MILIN and Ms. Sylvie BUSSIERE who assisted me a lot during my studies.

Words do not count easy to pay reverent thanks and compliments to my father Abdul Ghafoor, mother Shameem Akhtar, brothers Amin, Anwer, Saleem, Naeem and my sisters Rubina, Farzana, Rehana for their love, affection, amicable attitude, prayers for my success, consistent encouragement and cordial cooperation through my life. I am also thankful to all my Pakistani friends in Bordeaux and to all my fellows of lab, office and coffee room who always wished me for success. The sweet memories of these three years will always be with me. I am also thankful to Higher Education Commission, Pakistan for awarding me scholarship for my Ph.D studies in France. In the end I would like to express my affection and thankfulness for TCEM INRA Bordeaux for providing me an opportunity to complete my Ph. D work in this research unit.

Muhammad Nadeem

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REMOBILIZATION OF SEED PHOSPHORUS RESERVES AND EXOGENOUS

PHOSPHORUS UPTAKE DURING GERMINATION AND EARLY GROWTH STAGES

OF MAIZE (Zea mays L.)

Summary

Phosphorus (P) is an essential element for plant growth. Many studies have shown a very early seedling response to the limitation on the availability of P. During germination and early growth, the seedling P demand may be satisfied by the remobilization of seed P reserves and exogenous P uptake by developing roots. The objective of the thesis was to study the relative contribution of remobilization of seed P reserves, the exogenous P uptake by seedling roots and the interaction between these two processes. Various experiments were conducted to i) study the kinetics of the remobilization of seed P reserves, ii) identify precisely the beginning of exogenous P uptake by seedling roots, iii) quantify the relative contribution P fluxes in developing seedlings and iv) the interaction between these two P fluxes. Seeds with low and high P reserves were cultivated at different levels of exogenous P availability for the growth period of four weeks. The exogenous P was labelled with radioactive P (32P) to identify and quantify the P flux in young seedlings coming from exogenous P uptake and seed P reserves remobilization. Initially, 86% of P in the form of phytate and 13% C of seed reserves is localised in scutellum regardless of P initial seed P reserves. Four days after germination, 98% of seed phytate reserves are hydrolyzed. The kinetics of seed phytate hydrolysis was independent of seed P reserves and exogenous P availability. The hydrolyzed forms of phytate were temporarily stored in the seed before being translocated towards newly growing seedling compartments. The exogenous P uptake started soon after the radicle emergence (4th day) and depend mainly on the availability of exogenous P in the growth medium. The beginning of exogenous P uptake and its intensity was not influenced by the seed P reserves remobilization. The proportion of distribution of remobilized seed P reserves and the exogenous P uptake was similar among seedling shoot and roots. The whole seed and seedling P budget showed the significant P losses from germinating seeds by P efflux with the beginning of phytate hydrolysis in seeds. We proposed a model for the seed P remobilization and exogenous P uptake during germination and early growth. Assuming no interaction between seed P reserves remobilization and exogenous P uptake, the simulations were found to be in close agreement with experimental data. Our results showed the importance of exogenous P availability in growth medium during early growth stages regardless of seed P reserves.

Key-words: maize, germination, phosphorus, phytate, remobilization, P-uptake, isotope, ecophysiology, mineral nutrition.

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REMOBILISATION DES RESERVES EN PHOSPHORE DU GRAIN ET

PRELEVEMENT DE PHOSPHORE EXOGENE PENDANT LES PHASES DE

GERMINATION ET DE CROISSANCE JUVENILE DU MAÏS (Zea mays L.)

Résumé

Le phosphore (P) est un élément indispensable pour la croissance des plantes. De nombreux travaux montrent des réponses très précoces à une limitation de la disponibilité en P. Pendant la germination et la croissance juvénile, la demande en P des plantules peut être satisfaite par la remobilisation des réserves en P des graines et le prélèvement racinaire. Les objectifs de la thèse sont d’étudier la contribution respective de la remobilisation des réserves en P des graines et du prélèvement racinaire de P à l’alimentation en P des plantules de maïs, et les interactions entre ces deux processus. Différentes expériences ont été conduites pour i) étudier les cinétiques de la remobilisation des réserves en P des graines, ii) identifier précisément le début du prélèvement de P exogène par les racines, iii) quantifier la contribution relative de ces flux à l’alimentation en P de la plantule, iv) comprendre les interactions entre ces flux. Des graines riches et des graines pauvres en P on été cultivées à différents niveaux de disponibilités P exogènes pendant quatre semaines. Le traçage isotopique du P exogène (32P) a été utilisé pour quantifier le flux de prélèvement et calculer le flux de remobilisation du P des graines. Initialement, 86% du P sous forme phytate et 13% du C de la graine est localisé dans le scutellum indépendamment du niveau de richesse en P de la graine. 4 jours après le semis, 98% des phytates des graines sont hydrolysés. La cinétique d’hydrolyse des phytates est indépendante de la richesse en P des graines et de la disponibilité en P dans le milieu. Le P issu de l’hydrolyse des phytates est stocké temporairement dans la graine avant d’être transporté vers les organes en croissance de la plantule. Le prélèvement de P exogène commence dès l’émergence de la radicule (4ième jour) et dépend de la disponibilité en P dans le milieu. L’initiation du prélèvement et son intensité ne dépend pas du flux de remobilisation des réserves en P de la graine. Le P issu de la remobilisation et du prélèvement est distribué dans les mêmes proportions entre les parties ariennes et racinaires. Un bilan de P à l’échelle de la plantule entière et de la graine a permis de mettre en évidence un efflux de P depuis la graine vers l’extérieur pendant la phase d’hydrolyse des phytates. La modélisation des flux de P pendant la germination et la croissance précoce permet de rendre compte des observations sous l’hypothèse d’absence d’interaction entre les flux de remobilisation et de prélèvement de P bien que ces deux processus se chevauchent dans le temps. Nos résultats démontrent l’importance de la disponibilité locale en P dans le milieu pendant les stades précoces indépendamment du niveau de richesse en P des graines.

Mots-clés: maïs, germination, phosphore, phytate, remobilisation, prélèvement de P, isotope, écophysiologie, nutrition minérale.

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TABLE OF CONTENTS

Acknowledgements ....................................................................................................................... iii

Summary ......................................................................................................................................... v

Résumé ......................................................................................................................................... vii

TABLE OF CONTENTS ................................................................................................................ 1

LIST OF ABBREVIATIONS ......................................................................................................... 5

LIST OF FIGURES ........................................................................................................................ 7

LIST OF TABLES ........................................................................................................................ 13

1. INTRODUCTION ..................................................................................................................... 15

2. BIBLIOGRAPHIC REVIEW ................................................................................................... 19

2.1. Germination ........................................................................................................................ 19

2.1.1. Types of germination ................................................................................................... 19

2.1.2. Factors affecting germination ...................................................................................... 20

2.1.2.a. Water .................................................................................................................... 20

2.1.2.b. Temperature ......................................................................................................... 21

2.1.2.c. Hydrothermal models ........................................................................................... 22

2.2. Maize seed and its structure ................................................................................................ 22

2.3. Early seedling growth and seed reserves remobilization .................................................... 24

2.3.1. Germination, early growth and seed carbon remobilization ........................................ 25

2.3.2. Germination, early growth and mineral reserves remobilization ................................ 26

2.3.2.a. Nitrogen ............................................................................................................... 26

2.3.2.b. Phosphorus .......................................................................................................... 26

[i.] Phosphorus in seeds ................................................................................................ 26

[ii.] Phytate biosynthesis and accumulation in seeds .................................................... 27

[iii.] Functions of phytate ............................................................................................... 29

[iv.] Phytate in seeds ..................................................................................................... 29

[v.] Factors effecting seed phytate and P concentrations ............................................... 29

[vi.] Activity of phytase during germination and early growth .................................... 30

[vii.] Phytase activity and effect of different factors .................................................... 31

[viii.] Seed phytate loss ................................................................................................. 33

[ix.] Mobilization of seed P reserves during germination and early growth ................. 34

1

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[x.] Effect of seed P on early seedling growth ............................................................... 36

2.4. Maize seedling root growth and exogenous phosphorus uptake ........................................ 37

[i.] Growing maize seedling roots .................................................................................. 37

[ii.] Exogenous P uptake by growing seedling roots .................................................... 39

2.5. Conclusions of bibliographic review .................................................................................. 41

2.6. Objectives of thesis studies ................................................................................................. 42

2.6.1. General representation of studied system .................................................................... 42

2.6.2. Research plan ............................................................................................................... 43

3. MATERIALS AND METHODS ............................................................................................... 45

3.1. Experiment 1 (greenhouse study 2010) .............................................................................. 45

3.1.1. Experimental layout ..................................................................................................... 45

3.1.2. Seed sowing ................................................................................................................ 45

3.1.3. Nutrient solution composition ..................................................................................... 46

3.1.4. Labeling of nutrient solution ....................................................................................... 46

3.1.5. Seedling growth conditions ......................................................................................... 47

3.1.6. Irrigation ..................................................................................................................... 48

3.1.7. Seedling harvest ........................................................................................................... 48

3.1.8. Statistical analysis ........................................................................................................ 50

3.2. Experiment 2 (growth chamber study 2010) ...................................................................... 51

3.2.1. Experimental layout and selection of maize seeds ...................................................... 51

3.2.2. Seed sowing ................................................................................................................ 51

3.2.3. Nutrient solution composition ..................................................................................... 51

3.2.4. Labeling of nutrient solution ....................................................................................... 52

3.2.5. Seedling growth conditions ......................................................................................... 52

3.2.6. Irrigation ..................................................................................................................... 54

3.2.7. Seedling harvest ........................................................................................................... 54

3.2.8. Statistical analysis ........................................................................................................ 55

3.3. Growth measurements and chemical analysis .................................................................... 56

3.3.1. Morphological analysis ................................................................................................ 56

3.3.1.a. Root and leaf morphology .................................................................................... 56

3.3.1.b. Fresh and lyophilized seedling biomass .............................................................. 56

3.3.2. Chemical analysis ........................................................................................................ 56

3.3.2.a. Phosphorus determination .................................................................................... 57

3.3.2.b. Exogenous P uptake and its allocation using 32P labeling .................................. 57

2

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3.3.2.c. Phytate and phytate-P determination ................................................................... 57

3.3.2.d. Carbon and nitrogen analysis ............................................................................... 58

3.3.3. Endogenous seed P exportation flux ............................................................................ 58

3.3.4. P efflux from germinating seeds and growing maize seedling roots ........................... 58

3.4. Control of experimental procedures ................................................................................... 59

3.4.1. P loss from seeds by imbibition ................................................................................... 59

3.4.2. P sorption properties of perlite ..................................................................................... 60

3.4.3. Base temperature for maize germination ..................................................................... 60

3.4.4. P sorption on seedling roots ......................................................................................... 62

3.4.5. Specific activity induced background noise ................................................................ 63

4. RESULTS AND DISCUSSIONS .............................................................................................. 65

4.1. Relative contribution of seed phosphorus reserves and exogenous phosphorus uptake to

maize (Zea mays L.) nutrition during early growth stages ........................................................ 65

4.1.1. Objectives .................................................................................................................... 65

4.1.2. Results ......................................................................................................................... 65

4.1.2.a. Seedling growth ................................................................................................... 65

4.1.2.b. Seed and seedling C content ................................................................................ 66

4.1.2.c. Remobilization of seed P reserves and exogenous P uptake ............................... 69

4.1.2.d. Remobilization of seed N reserves and seedling N accumulation ....................... 70

4.1.2.e. Phytate and phytate-P ........................................................................................... 71

4.1.2.f. Relative contribution of seed P and exogenous P uptake to seedling P nutrition 72

4.1.2.g. Relationship between P and N remobilization ..................................................... 75

4.1.3. Discussion .................................................................................................................... 76

4.1.3.a. Carbon remobilization and seedling growth ........................................................ 76

4.1.3.b. Phytate hydrolysis and relative contribution of P to growing seedlings .............. 76

4.1.3.c. Relationship between P and N remobilization ..................................................... 77

4.2. Maize (Zea mays L.) endogenous seed phosphorus remobilization is not influenced by

exogenous phosphorus during germination and early growth stages ........................................ 78

4.2.1. Objectives .................................................................................................................... 78

4.2.2. Results .......................................................................................................................... 78

4.2.2.a. Early seedling growth .......................................................................................... 78

4.2.2.b. Accumulation of P in seedlings .......................................................................... 80

4.2.2.c. Seed phytate-P hydrolysis ................................................................................... 82

4.2.2.d. Endogenous seed P remobilization and export flux ............................................ 84

3

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4.2.2.e. Exogenous P uptake by growing seedling roots .................................................. 85

4.2.2.f. P efflux and whole seedling P budget .................................................................. 85

4.2.3. Discussion .................................................................................................................... 89

4.2.3.a. Effect of endogenous and exogenous P on seed P remobilization and seedling

growth 89

4.2.3.b. Effect of endogenous and exogenous P on uptake of exogenous P .................... 90

4.2.3.c. Whole seedling P budget ...................................................................................... 91

4.2.3.d. What explains early P deficiency in maize often reported in the literature? ....... 92

4.3. Modelling of seed P reserves remobilization and exogenous P uptake .............................. 93

4.3.1. Seed phytate hydrolysis module .................................................................................. 96

4.3.2. Seedling growth module .............................................................................................. 98

4.3.3. Seedling P demand module .......................................................................................... 98

4.3.4. Exogenous P uptake by roots module ........................................................................ 100

4.3.5. Effective P fluxes and total P balance module .......................................................... 101

4.4. Model output ..................................................................................................................... 104

4.4.1. Seed phytate hydrolysis ............................................................................................. 104

4.4.2. Seed non phytate-P .................................................................................................... 105

4.4.3. Seedling P demand and seedling P accumulation ...................................................... 106

4.4.4. Seed P export and root P uptake ................................................................................ 108

4.4.5. Seed P efflux .............................................................................................................. 110

4.5. Discussion ........................................................................................................................ 111

5. GENERAL DISCUSSION AND PROSPECTIVES .............................................................. 113

BIBLIOGRAPHIC REFERENCES ........................................................................................... 117

APPENDIX ................................................................................................................................. 125

Appendix I: Prélèvement et conservation de grains de maïs avec des teneurs en phosphore

différenciées ............................................................................................................................. 125

Appendix II: Dosage des phytates par chromatographie ionique en milieu HCl 0.65M. Mode

opératoire MO-ANA-65 .......................................................................................................... 127

Appendix III: Nadeem M, Mollier A, Morel C, Vives A, Prud’homme L, Pellerin S (2011)

Relative contribution of seed phosphorus reserves and exogenous phosphorus uptake to maize

(Zea mays L.) nutrition during early growth stages. Plant Soil 346 (1-2):231-244.

doi:10.1007/s11104-011-0814-y .............................................................................................. 133

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LIST OF ABBREVIATIONS

TT : Thermal time (Cumulated degree days after sowing)

DAS : Days after sowing

PAR : Photosynthetically active radiation (µmol m-2 sec-1)

RH : Relative humidity (%)

DW : Dry weight (g seedling-1)

C+M : Coleoptile+mesocotyle

SE : Standard error

LS : Seeds with low endogenous seed P reserves (506 µg P seed-1)

HS : Seeds with high endogenous seed P reserves (952 µg P seed-1)

0P : No exogenous P

LP : Low exogenous P (100 µmol P L-1)

HP : High exogenous P (1000 µmol P L-1)

Endo-P : Endogenous seed P

Exo-P : Exogenous P

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LIST OF FIGURES

Figure 1.1: Global map of agronomic P imbalances for the year 2000 expressed per unit of

cropland area in each 0.5° grid cell. The P surpluses and deficits are each classified according to

quartiles globally (0-25th, 25-50th, 50-75th and 75-100th percentiles, MacDonald et al., 2011).

.......................................................................................................................................................15

Figure 1.2: Peak phosphorus curve indicating that production will eventually reach a maximum,

after which it will decrease (Cordell et al., 2009)..........................................................................16

Figure 1.3: Effect of P on leaf area index, in maize seedlings during early growth stage (Plénet et

al., 2000)........................................................................................................................................17

Figure 2.1: Epigeal and hypogeal germination in monocot and dicot seed...................................19

Figure 2.2: Water uptake in seeds during germination (Bewley and Black 1994)........................21

Figure 2.3: Internal structure of maize seed..................................................................................23

Figure 2.4: Germination, emergence and seedling establishment.................................................25

Figure 2.5: Phytic acid (myo-inositol-1, 2, 3, 4, 5, 6-hexakisphosphate or Ins. P6).....................27

Figure 2.6: Biosynthetic pathways to phytic acid (myo-inositol-1, 2, 3, 4, 5, 6-hexakisphosphate

or Ins. P6) in the eukaryotic cell. A, Structure of phytic acid. B, Structure of Ins. The numbering

of the carbon atoms follows the "D-convention" (Loewus and Murthy, 2000). C, Bio-chemical

pathway of phytic acid (Raboy et al. 2000):..................................................................................28

Figure 2.7: Changes in the myo-inositol hexa- (IP6), penta- (IP5), tetrat- (IP4), and tri- (IP3)

phosphate during germination of barley seeds (Centeno et al. 2001)............................................31

Figure 2.8: Phytate level (□) and phytase activity (∇) during barley germination (Greiner et al.

2000)..............................................................................................................................................32

Figure 2.9: The effect of germination temperature on phytase activity during barley germination

(Sung et al. 2005)...........................................................................................................................33

Figure 2.10: Changes in levels of various phosphorus fractions in the cotyledons of young pea

seedlings during early development (Guardiola and Sutcliffe 1971)............................................35

Figure 2.11: Photographs of maize seed (a) 2 days, (b) 3 days, (c) 4 days, (d) 5 days, and (e and

f) 7 days after germination. C, coleoptile; CN, coleoptile node; CO, coleorhizae; FL, first leaf;

M, mesocotyl; NR, nodal root; PR, primary root; S, scutellum; SL, second leaf; SSR, scutellum

seminal root (Singh et al, 2010).....................................................................................................38

Figure 2.12: Maize seedling system, including seed P reserves, growing seedling and exogenous

nutrient solution P..........................................................................................................................43

7

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Figure 3.1: Individual pot and sowing of maize seeds..................................................................46

Figure 3.2: Outer view of greenhouse experiment 2010...............................................................47

Figure 3.3: Climatic conditions during first experiment, (photosynthetically active radiation

"PAR" on left axis, temperature "T" and relative humidity "RH" on right axis)..........................48

Figure 3.4: A growing maize seedling during early growth..........................................................49

Figure 3.5: Desorption of 32P and washing of maize seedling roots............................................50

Figure 3.6: Growing maize seedlings in pots placed in plastic trays on iron stands in growth

chamber experiment in 2010..........................................................................................................53

Figure 3.7: Climatic conditions during second experiment, (photosynthetically active radiation

"PAR" on left axis, temperature "T" and relative humidity "RH" on right axis)..........................54

Figure 3.8: Loss of seed P by imbibition (% loss of initial seed P). .............................................59

Figure 3.9: Initial P concentrations added in perlite solution suspension and final P

concentrations in perlite solution suspension after 24 hours. Dashed line is the 1:1 line. Blue dots

are measured data and the solid line is the linear regression line..................................................60

Figure 3.10: Germination rate hour-1 calculated as the inverse of the time to reach 50 %

germination as a function of the temperature. The calculated base temperature for maize

germination was 9.64°C. ...............................................................................................................61

Figure 3.11: P sorption on maize seedling roots during germination and early growth. Data are

means and vertical bars indicate ±se for n = 3 replications...........................................................62

Figure 4.1: Changes in total seedling C (■), seed C remobilization (●), seedling C accumulation

(▲) and seed C loss (∆) in maize seedlings expressed in mg seedling-1 during germination and

early growth stages. Time is expressed in cumulated degree days after sowing. Data are means

and vertical bars indicate ± se for n = 3.........................................................................................67

Figure 4.2: Changes in C content (mg C seedling-1) on the left axis (● and solid lines) and in P

content (µg P seedling-1) on the right axis (○ and dashed lines) in the endosperm (a), scutellum

(b), leaves (c) and roots (d) during early growth of maize. Time is expressed in cumulated degree

days after sowing. Data are means and vertical bars indicate ± se for n = 3.................................68

Figure 4.3: Changes in total seedling P content (●), in shoot and root P content (▲) and in

exogenous P uptake from the nutrient solution calculated according to 32P-activity measured in

the seedling (∆). Data are means and vertical bars indicate ±se for n = 3 replications.................70

Figure 4.4: Changes in total quantity of seed (●), seedling (▲), endosperm () and scutellum (○)

nitrogen (mg seedling-1) contents in maize seeds and seedlings during germination and early

8

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growth stages. Time is expressed in cumulated degree days after sowing. Data are means and

vertical bars indicate ± se for n = 3................................................................................................71

Figure 4.5: Variation in total P (µg P seed-1) and phytate-P (µg phytate-P seed compartment-1)

reserves in different compartments of the maize seed during early growth stages. Remobilization

of total seed P reserves (●); Scutellum phytate-P reserves (∆) and endosperm phytate-P (□). Data

are means and vertical bars indicate ±se for n = 3 replications.....................................................72

Figure 4.6: Allocation of exogenous P uptake (gray arrows on the right) calculated using 32P

labeling of the nutrient solution and distribution of remobilized seed P reserves (dark arrows on

the left) to seedling compartments after 298 cumulated degree days (23 DAS). The width of the

arrows represents the quantity of P flowing toward different seedling compartments. Values

inside the different compartments represent P accumulation in (+) or remobilization from (-)

each compartment. Values in italics represent P content in the seed and in the seedling after 298

cumulated degree days (23 DAS). P fluxes are expressed in µg P seedling-1. Data are means and

vertical bars indicate ± se for n = 3 replications............................................................................74

Figure 4.7: Rate of P, C and N remobilization in maize seed during early growth stages

calculated as the ratio of P (○), C (●) and N (∆) content in seed to their initial content. Data are

means and vertical bars indicate ±se for n = 3 replications...........................................................75

Figure 4.8: Seed biomass remobilization (g) in maize seeds during germination and early growth

stages: Low endogenous seed P in seedlings (LS) with no exogenous P (○), low exogenous P

(□), high exogenous P (∆), high endogenous seed P seedlings HS with no exogenous P (●), low

exogenous P (■) high exogenous P (▲) treatments. Data are means and vertical bars indicate ±

se for n = 3 replications.................................................................................................................79

Figure 4.9: Seedling biomass accumulation (g) in maize seedlings during germination and early

growth stages: Low endogenous seed P in seedlings (LS) with no exogenous P (○), low

exogenous P (□), high exogenous P (∆), high endogenous seed P seedlings HS with no

exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and

vertical bars indicate ± se for n = 3 replications............................................................................79

Figure 4.10: Phosphorus accumulation (µg P) in maize seedlings during germination and early

growth stages: A. Low endogenous seed P in seedlings (LS) with no exogenous P (○), low

exogenous P (□), high exogenous P (∆) and B. high endogenous seed P seedlings HS with no

exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and

vertical bars indicate ± se for n = 3 replications............................................................................80

9

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Figure 4.11: Seedling phosphorus concentrations (mg P g–1) in maize seedlings during

germination and early growth stages. Low endogenous seed P seedlings (LS) with no exogenous

P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P seedlings (HS)

with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments, grown for 530

cumulated degree days after sowing. Data are means and vertical bars indicate ± se for n = 3

replications.....................................................................................................................................82

Figure 4.12: Scutellum phytate-P hydrolysis (µg P) in maize seeds during germination and early

growth stages. Inset, Phytate-P in the scutellum (ratio of scutellum phytate-P content to initial

scutellum phytate-P content) as a function of cumulated degree days after sowing. Low

endogenous seed P seeds with no exogenous P (○), low exogenous P (□), high exogenous P (∆)

and high endogenous seed P seeds with no exogenous P (●), low exogenous P (■) high

exogenous P (▲) treatments, grown for 530 cumulated degree days after sowing. Data are means

and vertical bars indicate ± se for n = 3 replications.....................................................................83

Figure 4.13: Quantity of endogenous seed P (µg P) exported from the seed to maize seedlings

during germination and early growth stages. Low endogenous seed P seedlings with no

exogenous P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P

seedlings with no exogenous P (●), low exogenous P (■) and high exogenous P (▲) grown for

530 cumulated degree days after sowing. Data are means and vertical bars indicate ± se for n = 3

replications.....................................................................................................................................84

Figure 4.14: Exogenous phosphorus (µg P) uptake in maize seedlings during germination and

early growth stages. Low endogenous seed P seedlings with no exogenous P (○), low exogenous

P (□), high exogenous P (∆) and high endogenous seed P seedlings with no exogenous P (●), low

exogenous P (■) high exogenous P (▲). Data are means and vertical bars indicate ± se for n = 3

replications.....................................................................................................................................86

Figure 4.15: Phosphorus efflux (µg P) from germinating maize seeds and growing seedling roots

during germination and early growth stages. A) Low endogenous seed P seedlings with no

exogenous P (○), low exogenous P (□), high exogenous P (∆) and B) high endogenous seed P

seedlings with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data

are means and vertical bars indicate ± se for n = 3 replications....................................................86

Figure 4.16: (A-C: LS treatments) Allocation of exogenous P uptake (gray arrows on the right)

calculated using 32P labeling of the nutrient solution and distribution of remobilized seed P

reserves (dark arrows on the left) to seedling compartments and calculation of efflux after 530

cumulated degree days. The width of the arrows represents the quantity of P flowing toward

10

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different seedling compartments. Values inside the different compartments represent P

accumulation in (+) or remobilization from (-) each compartment. P fluxes are expressed in µg P

seedling-1. Data are means and vertical bars indicate ±se for n = 3 replications..........................87

Figure 4.17: (A-C: HS treatments). Allocation of exogenous P uptake (gray arrows on the right)

calculated using 32P labeling of the nutrient solution and distribution of remobilized seed P

reserves (dark arrows on the left) to seedling compartments and calculation of efflux after 530

cumulated degree days. The width of the arrows represents the quantity of P flowing toward

different seedling compartments. Values inside the different compartments represent P

accumulation in (+) or remobilization from (-) each compartment. P fluxes are expressed in µg P

seedling-1. Data are means and vertical bars indicate ±se for n = 3 replications..........................88

Figure 4.18: Flow diagram of main processes that determine P dynamics in maize seed during

germination and early growth. Arrows indicate the P fluxes between different seed, seedling and

exogenous P uptake.......................................................................................................................94

Figure 4.19: Graphical display of the model of P dynamic in maize seed during germination and

early growth build with ModelMaker software.............................................................................96

Figure 4.20: Observed and modelled scutellum (●) and endosperm (▲) phytate-P hydrolysis in

scutellum and endosperm of maize seeds (HPHS) during germination and early growth stages

(R² = 0.974)....................................................................................................................................97

Figure 4.21: Observed leaf P concentrations (●) in HPHS seedlings and dilution P curve obtained

by non-linear fitting in HPHS seedlings during germination and early growth stages.................99

Figure 4.22: Relationship between seedling root P influx and seedling root lengths (HPLS and

HPHS seedlings) in maize seedlings. HPHS seedlings (▲) and HPLS seedlings (∆) and non

linear fitting curve (—) of HPHS and HPLS (– –)......................................................................101

Figure 4.23: Time courses of modelled phytate-P hydrolysis (µg seed-1) in LS and HS seeds

treated with three exogenous P availabilities (0P, LP and HP) during germination and early

growth stages...............................................................................................................................104

Figure 4.24: Modelled changes in non phytate-P (µg seed-1) in LS and HS maize seeds during

germination and early growth stages. .........................................................................................105

Figure 4.25: Seedling P demand and effective seedling P accumulation rate (µg day-1) in

growing maize seedlings during germination and early growth stages. A. Seedling P demand and

seedling P accumulation in LS seedlings treated with three exogenous P availabilities (0P, LP

HP), Right. HS seedlings treated with three exogenous P availabilities (0P, LP HP).................106

11

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Figure 4.26: Time courses of modelled seedling P concentrations (µg g-1 DW) in LS and HS

seedlings treated with three exogenous P treatments (0P, LP, HP) during germination and early

growth stages...............................................................................................................................107

Figure 4.27: Observed and modelled seedling P concentrations (mg g-1 DW) in growing maize

seedlings on 530 cumulated degree days after sowing................................................................107

Figure 4.28: Modelled seedling P accumulation (µg seedling-1) originated from endogenous seed

P reserves and exogenous P uptake in growing maize seedlings during germination and early

growth stages. HS seedling treated with HP and LP exogenous P availabilities (A and B), LS

seedlings treated with HP and LP exogenous P availabilities (C and D). ..................................108

Figure 4.29: Time courses of seed P export rate (µg seed-1 day-1) in LS (dashed lines) and HS

(solid lines) seeds treated with three exogenous P treatments (0P, LP, HP) during germination

and early growth stages................................................................................................................109

Figure 4.30: Time courses of observed (Obs) and modelled (Mod) exogenous P uptake in LS (A)

and HS (B) seedlings treated with two exogenous P availabilities during germination and early

growth stages in maize.................................................................................................................109

Figure 4.31: Time courses of modelled seed P efflux (µg seed-1) in LS (dashed lines) and HS

(solid lines) seed treated with three exogenous P treatments (0P, LP, HP) during germination and

early growth stages......................................................................................................................110

12

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LIST OF TABLES

Table 2.1: Mean concentration of total phosphorus and phytate percentage of some crop feeds

(Bagheri and Gueguen 1983; Nelson 1980; Sauveur 1983; Simons 1979)...................................30

Table 2.2: Phytate content changes (mg 100 g–1 DW)* after soaking whole seeds for 24 hours

(Lestienne et al. 2005)...................................................................................................................34

Table 4.1: Radicle length, root length and number of visible leaves during early growth of maize

seedlings. Values are means (±SE) of 3 replications.....................................................................66

Table 4.2: Values of selected variables for maize seedlings at 530 cumulated degree days after

sowing with two rates of endogenous P (LS "low seed P " and HS "high seed P") subjected to

three rates of exogenous P (Exo-P) availability (OP "control exogenous P", LP "low exogenous

P" and HP "high exogenous"). F-test significances of Endo-P (endogenous seed P), Exo-P and

Endo-P x Exo-P interaction are indicated (NS = not significant). Different letters in the same line

indicate significant differences at the 0.05 probability level.........................................................81

Table 4.3: Different variables and parameters of maize seed phytate-P hydrolysis and exogenous

P uptake during germination and early growth stages.................................................................103

13

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14

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1. INTRODUCTION

Phosphorus (P) is a vital nutrient that helps the plant to complete its normal life cycle. It is the

second macro element after nitrogen which frequently limits the crop growth and development.

Because of frequent agronomic P imbalances, about 29% of the global cropland area has overall

P deficit (MacDonald et al. 2011) as shown Figure 1.1.

Figure 1.1: Global map of agronomic P imbalances for the year 2000 expressed per unit of cropland area in each 0.5° grid cell. The P surpluses and deficits are each classified according to quartiles globally (0-25th, 25-50th, 50-75th and 75-100th percentiles, MacDonald et al., 2011).

Phosphorus makes up to 0.2% of plant's dry weight (Schachtman et al. 1998). It is highly

mobile in plants therefore when deficient it may be translocated from old plant tissues to actively

growing young seedling tissues. As a structural component of many coenzymes, phospholipids

and phosphoproteins, it is involved in several key plant functions including energy generation,

nucleic acid synthesis, photosynthesis, glycolysis, respiration, membrane synthesis and stability,

enzyme activation/inactivation, carbohydrate metabolism, and nitrogen fixation.

Despite of its prime importance, P is the least mobile and available nutrient in soil.

Applied P to soils in the form of organic or inorganic fertilizer sources reacts with clay, iron and

aluminium compounds and is converted readily to less available forms by the process of fixation.

Although agronomic inputs of P fertilizers exceeds the P removal by crops at world level, P

deficit covered almost 30% of global cropland area (MacDonald et al. 2011). Inorganic P

fertilizers therefore the major input in crop production. Mined rock phosphate is the primary

15

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source of P fertilizers and approximately 90% of all mined rock phosphate is used for agriculture

(Cordell et al. 2009; Tiessen 2008).

Global cereal production has doubled in the past 40 years mainly from the increased

yields resulting from greater inputs of fertilizer, water, pesticides, new crop strains and other

technologies of the green revolution (Tilman et al. 2002; Tilman et al. 2001). Double production

of cereal crops resulted in the increased consumptions of phosphorus fertilizers for 3.5 times (9

Tg in 1960 to 40 Tg today) and this high consumption of non-renewable resource of P will lead

to complete depletion of P in 50 to 100 years (Abelson 1999; Cordell et al. 2009; Vance et al.

2003). Peak P production is projected to occur in 2035 to 2040 (Cordell et al. 2009) as shown in

Figure 1.2.

The efficiency of P fertilizer to increase the soil available P and to increase the crop yield

is largely dependent on soil conditions (Johnston and Richards 2003). The use of these inorganic

P fertilizers is also quite inefficient with less than 20% of applied inorganic P being absorbed by

plants during their first growing season (Plaxton and Tran 2011). The remaining inorganic P

become immobile in the soil or leaches into pollutes nearby surface waters (Plaxton and Tran

2011), causing eutrophication in aquatic ecosystem (Bennett et al. 2001; Runge-Metzger 1995).

Figure 1.2: Peak phosphorus curve indicating that production will eventually reach a maximum, after which it will decrease (Cordell et al., 2009).

16

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Considering the economic and environmental unavailability and increasing demand of P,

a more efficient use of P fertilizers seems to be very important for sustainable agricultural

production. To improve the P fertilization strategies in agriculture requires a better understanding

and modelling of the P acquisition by crops.

Many studies have demonstrated that an early P nutrition is the most critical step because

it is involved in all energy requiring processes. Although crops absorb only small quantities of P

in their 2-3 weeks of early growth, this early accumulation of P is extremely important for

maximum dry mater and grain yield at maturity. In general, under low P availability plant

biomass accumulation decreases (Lynch et al. 1991; Mollier and Pellerin 1999; Ozanne et al.

1969; Plénet et al. 2000b) and root morphology is modified (Lambers et al. 2006). Plénet et al

(2000a) showed that the leaf area index in maize seedlings was effected markedly when the

seedlings were grown with different P fertilizers availabilities in soil as shown in Figure 1.3. The

P deficiency slowed the rate of leaf appearance in the corn, as well as reducing leaf size,

particularly that of lower leaves (Assuero et al. 2004; Colomb et al. 2000; Plénet et al. 2000a).

Under these conditions, an increase in root:shoot ratio has been reported, possibly due to a higher

allocation of assimilates to roots (Mollier and Pellerin 1999), which increases the exposed root

surface area for P uptake.

0

1

2

3

4

5

6

7

0 200 400 600 800 1000 1200 1400 1600 1800 2000 2200

Thermal time (°C days)

LAI (

m² l

eaf

m-2

)

P0P1.5P3

1996 a

Figure 1.3: Effect of P on leaf area index, in maize seedlings during early growth stage (Plénet et al., 2000).

17

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Phosphorus deficiency can also reduce protein and nucleic acid synthesis that leads to the

accumulation of soluble N compounds, particularly amide, in the tissue (Glass et al. 1980). The

reduction in total dry matter and grain yield due to a limited supply of P between planting and

six leaf stage was observed in field grown maize crop (Barry and Miller 1989). The allocation of

dry matter to the grain at later development stages was enhanced by early season P nutrition in

corn (Gavito and Miller 1998). Phosphorus effect on leaf morphogenesis and expansion in early

stages of maize development could play a role in the persistent effects of reduced leaf growth

and solar radiation interception on C nutrition of plant. The indirect effect of P deficiency on C

assimilation may reduce subsequent emergence and elongation of roots, which would have an

additional impact on P uptake capacity (Pellerin et al. 2000).

Phosphorus is absorbed by the seedling roots mostly in the ionic forms of either H2PO4–1

or HPO4–2 depending upon the pH of soils, but most preferable form is H2PO4

–1 at pH 7. The P

uptake poses a problem for plant roots, since the concentration of P in the soil solution rarely

exceeds 10 µM (Bieleski 1973) but plant requirements are quite high. Several mathematical

models simulating phosphorus uptake from soil by single root to whole seedling root system and

crop response have been developed (Baldwin et al. 1973; Claassen and Barber 1976; Mollier et

al. 2008; Nye and Marriott 1969). These modelling efforts have led to a better understanding of

nutrient uptake by roots in the absence of other limiting factors and integrate the processes

controlling soil P supply, the uptake by root system and the relationship between crop growth

and P uptake. These nutrient uptake modelling approaches successfully predict the exogenous P

uptake, but generally do not account for germination and early seedling growth, although it is the

most critical period for crop P nutrition.

Germination is the first step in successful life cycle of a plant and incorporates those

events that commence with the uptake of water by quiescent dry seeds and terminate with the

elongation of embryonic axis (Bewley 1997). The demand of P increases dramatically during the

period of rapid cell division such as seed germination and early seedling growth, however the

root system development and root absorption capacities are still limited during this period. If soil

P availability is low, the root uptake capacity may not be sufficient to cope the crop P

requirements; this raises the question of seed P reserves remobilization, their relative

contribution to maize seedling P requirements versus that of exogenous P uptake by the

developing maize seedling roots during early growth stages. The general objective of this study

was to quantify the relative contributions of seed P reserves remobilisation and exogenous P

uptake by roots to the seedling P nutrition, to identify the main factors controlling both processes

and to propose a way to model them.

18

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2. BIBLIOGRAPHIC REVIEW

2.1. Germination

Germination is the first step in the successful life cycle of a plant. It is a complex phenomenon in

which the mature dry seeds pass from a state of quiescence, where the metabolism is virtually

halted, in a state of intense metabolic activity. By definition, germination incorporates those

events that commence with the uptake of water by quiescent dry seed and terminate with the

elongation of embryonic axis (Bewley 1997). The visible sign that the germination is complete,

is usually the penetration of structures surrounding the embryo by radicle (Bewley 1997). Early

events associated with seed germination include solute leakage, commencement of respiration,

DNA repair and synthesis of mitochondria, and protein synthesis extant mRNAs and newly

synthesized mRNAs (Bewley 1997).

2.1.1. Types of germination

There are two types of germination based on the fate of the cotyledons, on whether the

cotyledons grow above the ground surface or remain below the ground surface (Figure 2.1). The

term epigeal is referred to germination type when the cotyledons rose above the ground surface

by hypocotyle where they continue to provide nutritive support to the growing points till

cotyledons reserves are exhausted. It is characteristics of canola, field beans, alfalfa, red clover

and pine seeds. Epigeal germination is considered evolutionarily more primitive than hypogeal

germination. The hypogeal germination is a characteristic of maize, wheat, rye, oat, broad bean

and pea seeds, where the cotyledons were remained below the ground surface and support the

seedlings (Miller 2001).

Figure 2.1: Epigeal and hypogeal germination in monocot and dicot seed.

19

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2.1.2. Factors affecting germination

Seed germination depends on both internal and external factors. Besides the basic requirement

for water, oxygen and an appropriate temperature, the seed may also be sensitive to other factors

such as light or darkness. Oxygen is required for aerobic respiration which can be assisted with

anaerobic respiration if needed. The internal factors which affect the seed germination include

hormonal control and seed dormancy.

2.1.2.a. Water

The role of water is of paramount importance and basic requirement for germination. It is

essential for enzyme activation, breakdown, translocation, and use of stored reserves material

(Miller 2001). The imbibition begins as soon as the seeds are placed in the soil, provided the

water content of soil that surrounds it should be sufficient. Imbibition of seeds depends upon the

difference of water potential in seeds and the surrounding environment of seeds. The seed

imbibtion triggers the hormonal changes that will lead to reactivation of enzymes. These

processes leads to the penetration of radicle through seed covering and leads to visible

germination (Bewley and Black 1994).

Water uptake in maize seeds is triphasic, with a rapid initial uptake (phase I), and then a

plateau phase (phase II), followed by a second substantial uptake (phase III), as shown in the

Figure 2.2. The first phase corresponds to a rapid imbibition, during which the tissues of the dry

seed absorb water quickly. One of the first change upon imbibition is the resumption of

respiratory activity, which can be detected within minutes (Bewley 1997). The influx of water

into cell of dry seeds during phase I results in temporary structural perturbations, particularly to

membranes, which lead to an immediate and rapid leakage of solutes and low molecular weight

metabolites into the surrounding imbibition solution (Bewley 1997). This is symptomatic of a

transition of the membrane phospholipids components from the gel phase achieved during

maturation drying to the normal, hydrated liquid-crystalline state (Crowe and Crowe 1992).

20

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Figure 2.2: Water uptake in seeds during germination (Bewley and Black 1994).

The length of phase II is affected by imbibition temperature and water potential of the

medium in which the seeds are imbibed (Manz et al. 2005; Schopfer and Plachy 1984). The

phase III occurs only when germination is completed as the embryo elongates and breaks

through its covering structures (Bewley 1997; Manz et al. 2005). In addition to the restoration of

transcriptional and translational machineries, the germination is mainly marked by the

mobilization of stored seed reserves (Lawrence et al. 1990; Le Deunff 1975), which have been

accumulated throughout the ripening period. By the end of imbibition phase (phase I), the

reserves of the cotyledons or endosperm began to be hydrolyzed (Obroucheva and Antipova

1997), to be truly mobilized during the post-germinative growth (Bewley 1997) and used in the

development of the future seedling.

2.1.2.b. Temperature

Germination is a complex process involving many individual reactions and phases, each of

which is affected by temperature as it is widely accepted that temperature regulates germination

(Miller 2001). The relationship between germination rate or elongation of the seedling tissues as

a function of temperature have been widely studied in many species (Carberry and Campbell

1989; Covell et al. 1986; Gummerson 1986; Marshall and Squire 1996; Squire 1999). On the

basis of these results, the effect of temperature on seed germination can be expressed in terms of

cardinal temperature: that is minimum, optimum, and maximum temperature at which

germination will occur. The rate of germination increases as the temperature increase from

minimal to optimum range but it again goes decreasing when temperature goes higher than

optimum to maximum range (Covell et al. 1986; Gummerson 1986) and particularly in maize,

21

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seed germination and vigour increased when day/night growth temperature was increased from

22/16 to 27/21 °C, but they decreased in response to high temperatures 33/27 °C (Modi and

Asanzi 2008).

2.1.2.c. Hydrothermal models

Temperature plays a critical role in the timing of many plant processes including seed

germination and thermal time is frequently considered an acceptable term used for complex

biological time period. Water uptake is clearly essential for seed germination and initial water

uptake into dry seeds is a physical process, viewed as satisfying the seed matric potential. At

reduced water potentials, progress towards germination is progressively reduced (Allen 2003).

Analogue to thermal time “hydrotime” quantitatively describes the rate of progress towards

germination as function seed water potential.

For the seed germination modelling, the effect of temperature and water potential can be

combined into a single term “hydrothermal time” (Allen 2003; Alvarado and Bradford 2002;

Bradford 1990; Finch-Savage et al. 2005; Gummerson 1986; Rowse and Finch-Savage 2003).

Hydrothermal models form the basic for many current efforts to predict the seed germination. A

key feature of these models is that each seed accumulates hydrothermal time (quantified progress

towards germination) according to the temperature and water potential of incubation in relation

to minimum temperature and water potential at which seed can progress. A key advantage of

hydrothermal models is that their equations apply to the entire seed population and lead to

simultaneous predictions of germination rate and percentage (Allen 2003). Hydrothermal

modelling efforts provide a theoretical framework for quantifying the effects of temperature and

water potential on seed and seedling processes under both controlled and natural conditions.

2.2. Maize seed and its structure

Seed occupies a critical position in the life history of higher plants (Bewley and Black 1994). A

seed is a small embryonic plant enclosed in covering called seed coat, with some stored food.

The seed is the product of ripening ovule of gymnosperm and angiosperm plants which occur

after pollination and some growth within mother plants. The formation of the seed completes the

process of reproduction of seed plants.

Basically the seed is composed on three main parts including embryo, stored food

materials and seed coat. The embryo is an immature plant from which a new plant will grow

under proper conditions. The embryo has one cotyledon or seed leaf in monocotyledonous seeds

22

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(maize, rice, rye etc.) whereas has two cotyledons in almost all dicotyledonous seeds (pea, mung,

beans etc.). The radicle is the embryonic root, while the plumule is the embryonic shoot. The

embryonic stem above the point of attachment of the cotyledon is the epicotyle and the

embryonic stem below the point of attachment is termed as hypocotyle.

Maize seed is a monocotyledonous and in mature maize seeds, the embryo and

endosperm alike are enclosed in the dry covering of the seed, whereas the embryo is triply

protected (Fincher and Stone 1986; Sargant and Robertson 1905). During seed development, the

outer endosperm is differentiated into the aleurone layer, a morphologically and functionally

distinct layer that may be one to several cells thickness, depending upon the species (Fincher and

Stone 1986), as shown in Figure 2.3. Although aleurone and starchy endosperm share a common

origin, only the cells of the aleurone layer remain alive after storage reserves of endosperm are

deposited and the seed matures and dries (Fincher 1989).

The whole embryo is seen lying against one face of the endosperm. The endosperm is a

starchy structure and occupies the bulk of seed and represents the nutrient store that mobilizes

during germination to nourish the growing seedlings. Thus starchy endosperm constitutes the

targeted tissue for enzymes secreted by the aleurone and scutellum (Fincher 1989). The second

covering is formed of the scutellum, a cushion like structure which is wrapped round the

embryonic axis and still conceals the greater part of it in the first days of germination (Figure

2.3). Finally, the each growing part of embryo has its own sheath: the coleoptile encloses the

plumule and the coleorhiza the radicle (Figure 2.3). The insertion of these sheaths on the axis,

and of the axis on the scutellum is shown in Figure 2.3.

Figure 2.3: Internal structure of maize seed.

23

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The scutellum is in contact with endosperm over the whole of its dorsal surface. It

supplies food to other parts of embryo from the stores laid up in its own tissues, and from those

of the endosperm. The contents of the endosperm are by degrees dissolved and absorbed by the

scutellum, which transmits them in solution to the growing parts of embryo (Sargant and

Robertson 1905).

2.3. Early seedling growth and seed reserves remobilization

The appearance of the radicle makes the end of germination and the beginning of establishment,

a period that ends when the seedlings have exhausted the food reserves stored in the seed.

Germination and establishment are two critical phases in the life of a plant. Germination vigour

and seedling emergence depend upon the amount and availability of seed endosperm reserves

and on soil conditions. Shoot and root growth of seedlings occurre at the expense of these seed

reserves. Seed dry weight decrease with an increase in root and shoots dry weight. The seed dry

weight loss during germination was greater than the increase in roots and shoot dry weights. The

difference was assumed to be lost due to respiration (Bouaziz and Hicks 1990).

Initially plant lives on seed reserves (heterotrophic stage) with external supply having

little effect and a last stage (autotrophic stage) occurs when the growth rate is determined by the

nutrient supply from surrounding environment (Grant et al. 2001). When the coleoptile breaks

through the soil surface, following by unfolding of the first cotyledon leaf, the seedling begins to

cease its dependence on endosperm (Finch-Savage 1995). The young seedlings obtain their

autotrophic independence for C, i.e. the photosynthetic ability to provide the growing tissues

with enough organic molecules, after a heterotrophic phase during which the only source of C is

located in the seminal reserve tissues. These two stages of seedling growth have been clearly

identified by Whalley et al., (1966) as illustrated in Figure 2.4., but a little is know about the

other nutrient like phosphorus and the dependence of seedling on seed P reserves and external P

uptake during early .

24

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Figure 2.4: Germination, emergence and seedling establishment.

2.3.1. Germination, early growth and seed carbon remobilization

Deleens et al. (1984) conducted an experiment for 15 days at 25/22 °C day and night

temperature. She reported that decrease in maize seed reserves during germination and early

growth exhibits three phases: a rapid decrease up to the 10 th day after germination, a steady state

from the 11th to the 13th day and ultimately a very slow decrease. The main part of seed carbon

pool is used for the early development of the plant. The leaves of 7 day old seedlings are entirely

made up of carbon coming from seed reserves indicating a heterotrophic stage. Up to the 10 th

day, both sources (heterotrophic + autotrophic) participate in leaf growth; the increase of the

autotrophic part is faster and this period corresponds to transitional growth stage. In leaves of 10

days old seedling the flow of carbon from heterotrophic and autotrophic sources is quantitatively

equal. In leaves of older seedling carbon provided by photosynthetic activity (autotrophic) is

much more important, while the root growth through the 9th day results from seed originating

carbon. On the 10th day newly autotrophic carbon is incorporated, first slowly but after the 13 th

day this source becomes more and more dominant for leaves as well as for the roots (Deleens et

al. 1984). The duration of different stages including heterotrophic, transitional and autotrophic

depend upon the temperature which directly influence the germination and early growth stages

(Covell et al. 1986; Miller 2001; Modi and Asanzi 2008; Squire 1999).

A B C

See

dlin

g dr

y w

eigh

t

Stagesi l a 4f

A B C

See

dlin

g dr

y w

eigh

t

Stagesi l a 4f

A = Heterotrophic stage

B = Transition stage

C = Autotrophic stage

i = Imbibition

l = Emergence

a = Self nutrition

4f = 4 leaf stage

25

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2.3.2. Germination, early growth and mineral reserves remobilization

2.3.2.a. Nitrogen

Nitrogen (N) is the key nutrient along with phosphorus for obtaining maximum final crop

harvest and quality. It plays a pivotal role in many critical functions such as photosynthesis as it

is a major component of amino acids, several vitamins and also it is necessary for enzymatic

reactions. Nitrogen is mobile in plants and it translocated from older plant parts to young plant

tissues.

The maize endosperm is a major storage house of seed nitrogen (Harvey and Oaks 1974).

The degradation of major storage proteins, zein and glutelin, in maize endosperm begins during

2nd day of germination. The protein most abundant in the mature endosperm is degraded most

rapidly. Zein and glutelin loss begun after 20 hours of germination, but total protein loss was not

apparent till 60 hours of germination (Harvey and Oaks 1974). A rapid decrease in endosperm

protein was recorded after 80 hours of germination until the endosperm protein reserves were

depleted (Harvey and Oaks 1974).

2.3.2.b. Phosphorus

[i.] Phosphorus in seeds

Phosphorus in seeds, is stored primarily in the form of phytic acid (Lott et al. 1995; Park et al.

2006; Zhu et al. 2001). Phosphorus and phytic acid concentration are closely correlated

(Lockhart and Hurt 1986). In literature the term phytic acid has been used interchangeably with

the term phytate or phytin. It occurs widely in plant tissues but is concentrated in seed or grain

tissues (Raboy 1990). As a primary storage form of phosphorus in plant seeds, phytic acid

represents 50% to 80% of total P in mature seeds and accounts for 1% to several percent of the

dry weight (Lott 1984; Raboy 1997). Inorganic P and cellular P (a component of cellular

membranes, DNA, RNA, etc) are other forms of P in seeds and generally referred to as

“available P” (Raboy 2001; Raboy et al. 2000).

Phytate is a strong chelating agent and nearlly all the phytate found in mature seeds is

bound to minerals such as K+, Mg++, Ca++, Zn+, Ba++, and Fe+++. Phytate forms a complex salt of

myo-inositol hexakisphosphoric acid (myo-inositol 1-, 2-, 3-, 4-, 5-, 6-hexakisphosphate or Ins.

P6) (O'Dell et al. 1972; Ullah and Gibson 1988). The stability of salt formed with phytate is in

the order of Cu++ > Zn+ > Mn++ > Fe++ > Ca++ (Lott et al. 2000; Sauveur 1989). Phytate is

26

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associated with anti-nutrient character in seeds as it binds the calcium, magnesium and zinc

however it has a potential to contribute significantly to seed performance (Modi and Asanzi

2008). It has been estimated that about 65% of the total elemental P applied every year in world

agriculture ends up in the phytic acid molecules (Lott et al. 2000).

[ii.] Phytate biosynthesis and accumulation in seeds

The phytate molecule is composed of a glucose ring with six phosphates (Figure 2.5). Free myo-

inositol and glucose 6-phosphate play an important role in the formation of phytate as

demonstrated in Figure 2.6. Phytate has chemical formula C6H18O24P6 and molecular weight of

660 g mole–1. The biosynthetic pathway to phytic acid can be summarized as consisting of two

parts: inositol supply and subsequent inositol polyphosphate (Raboy et al. 2000).

Figure 2.5: Phytic acid (myo-inositol-1, 2, 3, 4, 5, 6-hexakisphosphate or Ins. P6).

27

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Figure 2.6: Biosynthetic pathways to phytic acid (myo-inositol-1, 2, 3, 4, 5, 6-hexakisphosphate or Ins. P6) in the eukaryotic cell. A, Structure of phytic acid. B, Structure of Ins. The numbering of the carbon atoms follows the "D-convention" (Loewus and Murthy, 2000). C, Bio-chemical pathway of phytic acid (Raboy et al. 2000):(1), D-Ins(3)-P1 (or L-Ins[1]-P1) synthase; (2), D-Ins 3-phosphatase (or L-Ins 1-phosphatase); (3), D-Ins 3-kinase (or L-Ins 1-kinase); (4), Ins P- or polyP kinases; (5), Ins (1,3,4,5,6) P5 2-kinase or phytic acid-ADP phosphotransferase; (6), PtdIns synthase; (7), PtdIns and PtdIns P kinases, followed by PtdIns P-specific phospholipase C, and Ins P kinases; (8), D-Ins(1,2,3,4,5,6) P6 3-phosphatase; (9) D-Ins(1,2,4,5,6) P5 3-kinase; (10), D-Ins(1,2,3,4,5,6) P6 5-phosphatase; (11), D-Ins(1,2,3,4,6) P5 5-kinase; (12), pyrophosphate-forming Ins P6 kinases; (13), pyrophosphate-containing Ins PolyP-ADP phosphotransferases

Phytate rapidly accumulates in seeds during the ripening period (Abernethy et al. 1973;

Anderson and Wolf 1995; Gifford-Steffen and Clydesdale 1993) accompanied by other storage

substances such as starch and lipids. In seeds, phytate is usually found in organelles called

protein bodies, where it generally constitutes an inclusion, the globoid (Pernollet 1978). These

organelles are localized in the aleurone layer in cereals and in the endosperm and cotyledons in

legumes and oilseeds. In cereal grains, phytates are concentrated in the germ and aleurone layers

(O'Dell et al. 1972).

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[iii.] Functions of phytate

The phytate is supposed to perform two primary functions in seeds and growing seedlings. It

plays a significant role in providing mineral nutrients and inositol used in the growth of seedlings

as well as in the maintenance of inorganic phosphate homeostasis in developing seeds and

seedlings (Lott 1984; Lott et al. 1995). Regulation of cellular inorganic phosphate concentration

may play an important role in starch synthesis, accumulation and in the function of other

metabolic pathways (Strother 1980).

[iv.] Phytate in seeds

In maize, nearly 90% of the phytic acid is accumulated in embryo (O'Dell et al. 1972) and about

10% in the aleurone layers, while maize endosperm contains only trace amount of phytic acid

(Cheng Wang et al. 1959; Lott et al. 1995; Simwemba et al. 1984). In wheat and rice about 90%

of the caryopsis phytate-P is stored in the aleurone layer and about 10% in the embryo (Lott et al.

1995). In normal and quality protein hybrids of maize, the major part of maize seed phytate-P

was concentrated in embryo tissues as compared to endosperm (Modi and Asanzi 2008).

[v.] Factors effecting seed phytate and P concentrations

Phytate and P concentrations in seeds of a given species may vary because of many factors,

including cultivar, soil fertility status, and climatic conditions (Horvatic and Balint 1996; Miller

et al. 1980; Raboy et al. 1991). The interaction of phosphorus nutrition and environmental

factors with respect to phytate accumulation in seeds has been reported (Raboy and Dickinson

1993; Steiner et al. 2007). Low temperature stress during seed development hastens the

formation of phytic acid (Horvatic and Balint 1996) and the supply of inorganic phosphorus

(Raboy and Dickinson 1993).

The concentrations of total phosphorus and their phytate percentage in different crops are

shown in Table 2.1. The phytate-P percentage ranges from 55% to 77% of total P in different

crop and especially maize 67% of the total phosphorus is in the form of phytate. High soil P

levels displayed a significantly higher phytate-P and inorganic P concentrations in maize seeds,

while increasing growth temperature caused greater accumulation of inorganic P, but it

decreased myo-inositol (Modi and Asanzi 2008). Phosphorus nutrition enhanced seed

performance of maize (Modi and Asanzi 2008), and all variations in seed total P can be

accounted by variation in phytic acid P (Raboy et al. 1989; Raboy and Dickinson 1984).

29

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Table 2.1: Mean concentration of total phosphorus and phytate percentage of some crop feeds (Bagheri and Gueguen 1983; Nelson 1980; Sauveur 1983; Simons 1979).

Crops

Phosphorus total Phytate

(g kg–1) (% P total)Oat 3.4 55

Wheat 3.3 60-77Maize 2.7 67Barley 3.5 56-72

Rye 3.4 65Sorghum 3.0 60-70

[vi.] Activity of phytase during germination and early growth

Mobilization of phytate in germinating seeds is due to phytase activity, a special type of

phosphatase that can release phosphate from phytic acid as well as from other phosphorylated

substrates. Phytase (myo-inositol hexakisphosphohydrolases) is a phytate specific phosphatase

that hydrolyses phytate to inositol and free orthophosphate that releases phosphate from phytate.

Phytases are found naturally in plants and microorganisms particularly fungi (Wyss et al. 1999).

Maize is the first plant for which phytase gene isolation has been reported (Maugenest et

al. 1999). The principal function of the phytase in seeds or grains is to produce inorganic

phosphate from phytate during germination. Dephosphorylation of phytic acid to a series of myo-

inositol esters and inorganic phosphate is catalyzed by the enzyme phytase (Hegeman and

Grabau 2001; Loewus and Murthy 2000; Pilu et al. 2003; Urbano et al. 2000). This

decomposition of phytate in germination seeds may provide P, myo-inositol and mineral cations

for the rapidly growing seedlings (Loewus and Murthy 2000; Raboy et al. 1991). The young

seedling utilizes the myo-inositol as a substrate for the myo-inositol oxidation pathway and

ultimately for cell wall polysaccharides formation (Oberleas and Harland 1981).

Phytases act in a stepwise manner to carry out the hydrolysis of phytic acid (Urbano et al.

2000). They catalyze phosphate monoester hydrolysis of phytic acid, which results in the

stepwise formation of myo-inositol pentakis-, tetrakis-, tris-, bis-, and monophosphates, as well as

the liberation of inorganic phosphate. Two types of phytase have been identified which initiate

the hydrolysis of phytate at either the 3- or 6- position of the inositol ring. The plant phytases

preferentially hydrolize the phosphoester bond at 6-position of the myo-inositol residue (Greiner

et al. 2000; Greiner et al. 2001; Turk et al. 2000). Usually, but not invariably, microbial phytase

falls into the first category and plant phytase in the second category (Turk et al. 2000).

30

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Centeno et al. (2001) showed that inositol hexakisphosphate was the major inositol

phosphate in rye and barley cereals, representing more than 90% of the total myo-inositol

phosphates (Figure 2.7). The concentration of myo-inositol pentaphosphate (IP5) was only 8% of

total phytate, whereas IP4 was 2 and 1% for rye and barley, respectively. IP3 was not detected in

ungerminated seeds. During the course of germination, IP6 and IP5 were rapidly degraded in rye

and barley, and IP4 was only a short living intermediate, which was increased during hydrolysis

and degraded to IP3 (Figure 2.7).

Figure 2.7: Changes in the myo-inositol hexa- (IP6), penta- (IP5), tetrat- (IP4), and tri- (IP3)

phosphate during germination of barley seeds (Centeno et al. 2001).

[vii.] Phytase activity and effect of different factors

In the non germinated seeds a low phytase activity has been detected (Greiner et al. 2001; Sung

et al. 2005). With the imbibition of water, the metabolic processes in the seeds start, and after 72

hours of germination, the phytase activity in maize, millet, sorghum, and sweet maize had

increased 3 to 6 fold as compared to the initial values. In soybean seed germination, a

pronounced increase in phytase activity accompanies a concomitant decrease in phytic acid, with

maximal phytase activity attained at approximately 10 days after germination (Ullah and Gibson

1988). The most pronounced decrease in phytic acid content was found in rice, millet, and

mungbean, where only 34%, 44%, and 50% of the initial content remained after germination for

72 hours and this is due to the phytase activity (Egli et al. 2002).

In growing maize seedlings, the phytase activity increased from day 1st to day 5th

(Laboure et al. 1993). No significant phytase activity could be detected at zero time. Phytase

activity reaches a plateau between day 5th and 7th (Laboure et al. 1993). Similar results were

31

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reported by Greiner et al. (2000) in barley seedlings. He stated that maximum phytase activity in

growing barley seedlings was observed on 4th day during germination and the myo-inositol

phosphates decreased (Figure 2.8).

□ myo-Inositol phosphates Phytase activity

□ myo-Inositol phosphates Phytase activity

Figure 2.8: Phytate level (□) and phytase activity (∇) during barley germination (Greiner et al. 2000).

Temperature has a positive effect on the phytase activity. The phytase activity increases

with increase in temperature, and phytate hydrolysis quickly (Sung et al. 2005). The level of

phytase activity in barley reached its maximal value, 4 days after germination at 20-25°C and 7

days after germination at 15°C (Sung et al. 2005) as shown in Figure . The maximum phytase

activity in maize seedlings was observed at pH 4.8 in maize (Laboure et al. 1993). Phytase

activity diminished sharply on both the acid and alkaline sides of the optimum pH value and was

very low outside the range of pH 4-6. Inorganic phosphate caused some inhibition in phytase

activity even at the lowest concentration tested (0.56 mM). At concentration of 1.45 mM and

1.91 mM, phytase activity was reduced by 42 percent from the level obtained in the absence of

inorganic phosphate (Guardiola and Sutcliffe 1971).

Different cations were tested for their effect on phytase activity from 0.25 to 2 mM

(Laboure et al. 1993). Only Ca++ was found to exert a light stimulatory effect, approximately

35% over the control at 2 mM. Mg++ and Mn++ had no effect, whereas Zn++ and Fe+++ were

inhibitory for phytase activity (Laboure et al. 1993).

□ myo-Inositol phosphates

∇ Phytase activity

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● 15°C

■ 20°C

▲ 25 °C

● 15°C

■ 20°C

▲ 25 °C

Figure 2.9: The effect of germination temperature on phytase activity during barley germination (Sung et al. 2005).

[viii.] Seed phytate loss

Different processes such as soaking, cooking, germination and fermentation cause a decrease in

phytate contents in legumes (Khalil and Mansour 1995; Reddy et al. 1978; Sandberg and

Svanberg 1991). Soaking led to a significant reduction in the phytate content of millet, maize,

rice and soybean seeds (Lestienne et al. 2005). Depending upon the botanical origin of seeds, a

significant reduction in phytate content (between 17% and 28%) was obtained by soaking whole

seeds for 24 hours at 30 °C (Lestienne et al. 2005). Two groups were distinguished on the basis

of phytate loss by soaking: millet, maize, rice and soybean which showed a significant reduction

in phytate content, and sorghum, cowpea and mungbean which showed no significant reduction

as shown in Table 2.2. The phytate was hydrolyzed either directly in seeds by phytase or in the

water after leaching into the soaking medium (Lestienne et al. 2005).

During soaking, the phytase activity of all cereals (barley, maize, millet, oat, rice, rye

sorghum, sweet maize and wheat) decreased. The decrease ranged from 10% of the initial value

for millet and rye to about 60% of the initial values for barley. Phytase activity did not change

significantly during soaking of legumes and oilseeds, with exception of a 40% reduction in lentil.

Some of this loss could be explained by leaching and, assuming that the distribution of phytase

within legume seeds is similar to the distribution of phytic acid (that is in the cotyledons), the

33

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losses due to leaching can be expected to be less than in cereals where phytic acid and phytase

are primarily localized in the aleurone layer (Egli et al. 2002).

Table 2.2: Phytate content changes (mg 100 g–1 DW)* after soaking whole seeds for 24 hours (Lestienne et al. 2005).

Varieties

Phytate content

% Phytate lossUnsoaked Soaked

Millet 762 ± (66)a 550 ± (18)b 28Maize 908 ± (97)a 721 ± (16)b 21

Sorghum 925 ± (81)a 882 ± (44)a 4Rice 1084 ± (12)a 904 ± (81)b 17

Soybean 878 ± (130)a 678 ± (32)b 23Cowpea 559 ± (44)a 624 ± (42)a Apparent increase

Mung bean 236 ± (36)a 225 ± (12)a 8*Values are means±(SD). Means with a different letter in the same row are significantly different at P≤0.05, as assessed by Duncan's multiple range test.

The effect of germination is different than soaking. Germination resulted in decreased

phytase activity in most of the cereals with the exception of maize, millet, sorghum, and sweet

maize had increased 3 to 6 fold as compared to the initial values (Egli et al. 2002). The

germination process caused a significant increase of phytase activity in rye (up to 112%) and

barley (up to 212%) and a reduction in the phytate phosphorus content (up to 84%). During the

course of germination, inositol-6-phosphate and inositol 5-phosphate were rapidly degraded in

rye (88% and 79%) and barley (67% and 52%), and inositol 4-phosphate was only a short living

intermediate, which was increased during hydrolysis and degraded to inositol 3-phosphate

(Centeno et al. 2001).

In cowpea, horse gram, moth bean, mung bean, soybean and pearl millet seeds, phytate

phosphorus was between 42% and 61% of the total P of all the seeds. In general, 4%-11% of

phytate phosphorus decreased during soaking, 17%-27% during boiling and 14%-22% during

germination of seeds. Reduction in inositol 6-phosphate content was 13-19% during soaking,

27%-30% during boiling and 32%-56% during pearl millet seed germination (Dave et al. 2008).

[ix.] Mobilization of seed P reserves during germination and early growth

Changes in the levels of various phosphorus fractions and phytase activity in the cotyledons of

young pea seedlings was studied by Guardiola and Sutcliffe (1971). With the imbibition, the

phosphorus remobilization from seed reserves starts. The phosphorus lost in garden pea

cotyledons could be recovered quantitatively in the shoot and root. At first the phosphorus

remobilization from cotyledons is slow but increased gradually to a maximum rate after about 10

34

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days from the time of seed soaking (Guardiola and Sutcliffe 1971) as shown in Figure 2.10. The

level of phytic acid phosphorus did not change significantly during the first 2 days of

germination but it decreased rapidly between days 4 and 10. By day 15, practically all of phytic

acid had disappeared (Guardiola and Sutcliffe 1971). Thereafter the rate of transport declined

and there was very little loss of phosphorus by the cotyledons after 22 days by which time the

amount remaining had been reduced to about 17 percent of the original content (Guardiola and

Sutcliffe 1971).

Figure 2.10: Changes in levels of various phosphorus fractions in the cotyledons of young pea seedlings during early development (Guardiola and Sutcliffe 1971).

First in the seeds, the inorganic phosphorus is a minor fraction of total seed P (Figure

2.10). There was only a small quantity of inorganic phosphate in the resting seed and after 2 days

it began to increase by the activity of phytase, which hydrolyse the phytic acid releasing their

inorganic phosphorus (Guardiola and Sutcliffe 1971). The level of inorganic phosphorus reaches

a maximum level about 10 days after germination. From then on it decreased, but at a slower rate

than did the total acid soluble phosphorus. After 25 days of germination inorganic phosphate

accounted for almost all the phosphorus in the acid soluble fraction and for three quarters of all

35

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phosphorus in the cotyledons. On the other hand, nucleic acid and protein phosphorus levels

decreased from the start of germination. The rate of decrease of nucleic acid phosphorus was

most rapid at first and decreased progressively with time, whereas protein phosphorus declined

at an almost linear rate for about 15 days after germination and hardly changed thereafter

(Guardiola and Sutcliffe 1971).

[x.] Effect of seed P on early seedling growth

The seed P reserves have a significant effect on early seedling growth. In subterranean clover,

the seedling emergence was 35% greater from soil for the high P seed (0.75%; w/w), than the

lower P seed (0.48%; w/w) and this effect was independent of external P supply (Thomson and

Bolger 1993). Leaf emergence was faster and shoot dry weight was also higher in seeds with

high P reserves, but only when external P supply was deficient for the plant growth (Thomson

and Bolger 1993). Seedlings also emerge more quickly from high P seed, as after six days of

sowing, 35% of high P seed had emerged compared with 24% of low P seed. Phosphorus

concentrations in the shoot of two week old seedlings were 32-51% higher for higher P seed,

although by the four weeks plants grown from high and low P seed had similar concentrations of

P in their shoots (Thomson and Bolger 1993). Similar results were also reported by Ros et al.

(1997) in rice seedlings and De Marco (1990) in wheat.

36

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2.4. Maize seedling root growth and exogenous phosphorus uptake

[i.] Growing maize seedling roots

The root system determines the capacity of a plant to access soil water and nutrients. In cereals

such as maize, the root system is formed from the seminal roots that appear at germination and

nodal, crown or adventitious roots that arise later from nodes of the shoot (Esau 1967). The root

system development of maize has been relatively well studied and roots have been variously

described as primary, seminal, nodal or axile and have often been associated with descriptors of

their point of origin, such as coleorhizae, scutellar node, coleoptillar node, and mesocotyle (Cahn

et al. 1989; Ho et al. 2004; Hochholdinger et al. 2004; Hund et al. 2007; Mollier and Pellerin

1999; Singh et al. 2010). In maize, a primary root, and a coleoptile had emerged by 2 days after

germination (Figure 2.11). The primary root emerged from the lower end of the seed through the

coleorhizae, whereas the coleoptile emerged at the upper end of the seed. Scutellar seminal roots

had also emerged from the scutellum by 2 days after germination and four scutellar seminal roots

were evident by day 3 (Singh et al. 2010). The maize produced 3-7 seminal (primary and

scutellum) roots and coleoptile nodal roots emerged at the 2nd leaf stage (Singh et al. 2010). The

studies throughout their life cycle indicate that the root system grows into the soil at about 2-3

cm day–1 (Dardanelli et al. 1997; Manschadi et al. 2008). Seminal roots play an important part in

initial water and nutrient uptake and establishment of seedlings, whereas nodal roots dominate

during the later stages of growth. It is important to note that seed P reserve mobilization and P

uptake by young root system are likely to overlap in time.

37

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Figure 2.11: Photographs of maize seed (a) 2 days, (b) 3 days, (c) 4 days, (d) 5 days, and (e and f) 7 days after germination. C, coleoptile; CN, coleoptile node; CO, coleorhizae; FL, first leaf; M, mesocotyl; NR, nodal root; PR, primary root; S, scutellum; SL, second leaf; SSR, scutellum seminal root (Singh et al, 2010).

38

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[ii.] Exogenous P uptake by growing seedling roots

Efficient nutrient uptake from soil by roots is a critical issue for plants given that in many

environments nutrients have poor availability especially phosphorus and may be deficient for

optimal growth. Although soils generally contain a large amount of total P, only a small

proportion is immaterially available for plant uptake. Plants obtain P as orthophosphate anions

(predominantly as H2PO4–1 or HPO4

–2 depending upon the pH of soils) from soil solution. In most

soils the concentration of orthophosphate in solution is low typically between 1 to 5 µM

(Bieleski 1973) and must therefore be replenished from other pools of soil P to satisfy the plant P

requirements. Orthophosphate is rapidly depleted in the immediate vicinity of plant roots, and as

such a large concentration gradient occurs across the rhizosphere between bulk soil and the root

surface (Gahoonia et al. 1997; Tinker and Nye 2000).

For nutrients present at low concentrations in soil solution and/or with poor diffusivity,

root growth proliferation into new regions of soil and release of root exudates are of particular

importance (Barber 1995; Darrah 1993). The availability of P in rhizosphere is influenced

significantly by changes in pH and root exudates which can either directly or indirectly affect

nutrient availability and/or microbial activity (Richardson 1994). The reactions controlling the

amount of inorganic P in solution include dissolution-precipitation of P bearing minerals,

adsorption-desorption of phosphate on soil surfaces, and the hydrolysis of organic matter

(Comerford 1999; Hinsinger 2001; Matar et al. 1992). Competition for nutrient uptake across

different plant species, between different roots and with microorganisms is also significant

(Hodge 2004). The rate of root growth and plasticity of root architecture along with development

of the rhizosphere, through either root growth or extension of root hairs, are clearly important for

effective exploration of soil and interception of nutrients (Lynch 1995).

The P uptake is generally modeled by Michaelis-Menten equation linking root P uptake

to P concentration in soil solution. The P uptake mainly occurred by diffusion process which

resulted from concentration gradient difference between soil solution and root P concentrations.

The intensity of P uptake was mainly dependent on the soil solution P availability (Bhadoria et

al. 2004; Elliott et al. 1984) and the root surface exposed (Anghinoni and Barber 1980).

Most of the inorganic P taken up by roots is loaded into the xylem and subsequently

translocated into shoot. Within plant cells, P is a major component of nucleic acids, membrane

lipids, and phosphorylated intermediates of energy metabolism. Thus, the cellular inorganic P

homeostasis is essential for physiological and biochemical processes. Under P deficiency, plants

can develop adaptive responses not only to facilitate efficient inorganic P acquisition and

39

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translocation, but also to utilize efficiently stored P by adjusting inorganic P recycling internally,

limiting P consumption, and reallocating P from older tissues to young and actively growing

tissues.

40

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2.5. Conclusions of bibliographic review

Phosphorus nutrition of maize is crucial during early growth stages as it is involved in different

metabolic processes and has a main role in the cellular energy transfer. During early growth

stages, P might be supplied by two processes including seed P reserves remobilization and

exogenous P uptake by developing maize seedling roots. The phosphorus in maize seeds is

stored in the form of phytate during the repining period. Most of the phytate is stored in germ

instead of endosperm. The P content in seeds may vary depending upon numerous factors. The

hydrolysis of phytate is controlled by phytase activity. Phytase activity is very high just after the

beginning of seed imbibition. This suggests that phytate hydrolysis may occur very early during

germination. However it was shown that phytase activity was inhibited by inorganic P. The

question also arises of possible interaction between C, N and P remobilization since they are not

localized in the same seed compartments. P losses are also likely to occur during germination

and early growth stages. The root growth is exponential during early growth stages but P uptake

per unit length of root is limited by the low diffusivity of P ions in soil solution and strongly

depends on the P concentrations. The question arises at which time the exogenous P uptake

begins. Both processes; seed P reserves remobilization and exogenous P uptake are likely to

overlap in time.

Here are some questions that arise during this study.

What is the remobilization kinetics of maize endogenous seed P reserves?

What is the possible relationship between carbon, nitrogen and phosphorus

remobilization in germinating seeds?

At which time the young growing seedling roots start the uptake of exogenous P? As

soon as the seedling radicle emerges? Or after the utilization of all seed P reserves?

Do both processes (seed P reserves remobilization and exogenous P uptake) have an

effect on each other or if are they controlled independently?

What is the relative contribution of endogenous seed P reserves and exogenous P uptake

in seedling P nutrition?

41

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2.6. Objectives of thesis studies

The objective of PhD studies is to study the remobilization of endogenous seed P reserves and

the effect of exogenous P uptake to maize nutrition during early growth stages. Experimentations

with different P concentration in maize seeds and nutrient solution will be carried out to measure

the flow of P in maize seedlings from endogenous seed reserves and from nutrient solution.

Isotopic techniques will be used to quantify the P flux from exogenous nutrient solution and

from phytate decomposition.

Analysis of the experimental data may lead us to develop a mechanistic and conceptual

model. This model may explain the seed P reserves remobilization and exogenous P uptake in

maize seed and seedlings during germination and early growth stages, respectively. For better

understanding of whole system of maize growth from germination to maturity, this model will be

included in the P uptake model FUSSIM_P_Maize (Mollier et al. 2008). This model

(FUSSIM_P_Maize) integrates the processes controlling the soil P supply (mobilization and

transport in the rhizosphere), the uptake by the root system (according to the P soil availability

and crop P requirement determined by environmental conditions), and relationships between the

crop growth response and the amount of P absorbed. The different parts of the model are highly

interactive and the feedbacks are explicitly accounted for. The first version of the model was

successfully evaluated on field maize crop for the vegetative period (5 visible leaves to 16 leaves

stage) in a range of soil P availability. The results of this study will add knowledge for our

understanding about seed P reserves remobilization and start of exogenous P uptake by young

seedling roots along with relative contribution of two P sources to maize seedling nutrition

during germination and early growth stages.

2.6.1. General representation of studied system

To study the remobilization of endogenous seed phosphorus reserves and effect of exogenous P

uptake to maize nutrition during the early growth stages, the system is divided into three main

compartments namely endogenous seed P reserves, developing growing seedling and exogenous

P availability clearly defined in Figure 2.12.

42

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The endogenous seed P reserves start to remobilize with the imbibition of seeds and

nourish the seedling with P. The growing developing seedling is composed of root and shoots

which develop in the response of seed reserves remobilization and exogenous nutrient uptake.

The third part of system is composed on exogenous P availability along with other necessary

nutrients (Figure 2.12).

Figure 2.12: Maize seedling system, including seed P reserves, growing seedling and

exogenous nutrient solution P.

2.6.2. Research plan

The proposed research plan combines two experimental studies and a modelling approach. In the

first step an experiment will be carried out to study the seed P reserves remobilization and

exogenous P uptake. The maize seeds will be grown with labelled nutrient solution of P to follow

the seed P reserves remobilization kinetics and start of exogenous P uptake by growing seedling

roots. The relative contribution of seed P reserves and exogenous P uptake to maize seedling P

nutrition will be determined.

43

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In second step, an experiment will be carried out to know the effect of endogenous and

exogenous P availabilities on seed P reserves remobilization and exogenous P uptake. In this

experiment, maize seeds with different endogenous seed P reserves will be sown with different

exogenous P availabilities in pots in growth chamber. The start of exogenous P uptake and seed

P reserves remobilization will be followed by labelling of exogenous nutrient solution P. the

interactions between seed P reserves remobilization and exogenous P uptake will be especially

studied.

In third step, a model will be proposed. The main objective of the modelling work was to test the

overall consistency of assumptions based on the experimental work results. Comparing

simulated results with observed values obtained on independent data sets was not performed

during the PhD thesis.

44

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3. MATERIALS AND METHODS

3.1. Experiment 1 (greenhouse study 2010)

A pot experiment was carried out in greenhouse, specified for radioisotope utilization between

March and April 2010, at INRA Bordeaux, France. The objectives of this study were

To know the exact time of exogenous P uptake by growing seedling roots.

o As soon as seedling radicle emerges?

o After the utilization of all endogenous seed P reserves?

To evaluate the relative contribution of maize seed P reserves and exogenous P uptake to

maize seedling nutrition during early growth stages.

3.1.1. Experimental layout

The seedlings were grown in pots for 23 days of growth period (298 cumulated degree days after

sowing). Homogenous maize seeds (cv. DKC-5783), (0.27 g to 0.35 g in weight) were selected

for this study. Before sowing, the seeds were separated into groups of nine for each pot and

imbibed for 5 minutes in a plastic tray containing filter papers and distilled water. In preliminary

experiment we verified that P loss by imbibition is negligible. See paragraph 3.4.1 for details.

3.1.2. Seed sowing

Opaque polypropylene pots (10*10*14 cm) were used to sow maize seeds (cv. DKC-5783). All

pots were filled with perlite (150 g pot–1). Perlite was chosen as substrate to sow maize seeds due

to its low buffer capacity (99.9% added P remains in the nutrient solution). On March 15, 2010

(~ 10:00 AM), the imbibed seeds were sown in perlite at 2 cm sowing depth. The sowing

position of each seed in the pot was noted as shown in Figure 3.1. To know the exact timings of

P uptake and repartitioning of total seedling P in different seedling compartments, it was

necessary to measure the accurate amount of P sorbed on seedling root surface and the

background noise of radioactivity. There were total 57 pots out of which (i) 42 pots were used to

follow the kinetics of P uptake, (ii) 9 pots to measure the amount of sorbed P on seedling root

surface and (iii) 6 pots to determine the background noise of radioactivity. These pots were

placed in four plastic trays to avoid leakage of nutrient solution and radioactivity on greenhouse

floor.

45

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3.1.3. Nutrient solution composition

A complete P nutrient solution (500 µmol P L–1 i.e. 15.38 mg P L–1) containing all the necessary

micro and macro nutrients, was used to grow the maize seedlings (Anghinoni and Barber 1980;

Bhadoria et al. 2004). The nutrient solution consisted of 500 µM P as NaH2PO4.2H2O, 1 mM

NO3 as Ca(NO3)2.4H2O, 0.2 mM K as KCl, 0.1 mM Mg as MgSO4.7H2O, 46 µM B as H3BO3, 9.1

µM Mn as MnCl2.4H2O, 0.8 µM Zn as ZnSO4.7H2O, 0.3 µM Cu as CuSO4.5H2O, 0.5 µM Mo as

(NH4)6Mo7O24.4H2O; 2 mg L–1 Fe was added as Sequestrene-138 Fe (water soluble granules with

6% Fe in chelated form). The pH of the nutrient solution was adjusted to 6.4 with NaOH (1 g

100 mL–1 of distilled water) solution.

Figure 3.1: Individual pot and sowing of maize seeds.

3.1.4. Labeling of nutrient solution

Phosphorus radioisotope (32P) was used to determine the start of exogenous P uptake by growing

seedling roots and to follow its repartition within different seedling compartments during

germination and early growth stages. Accordingly, the relative contribution of remobilized P

from phytate to the P content of seed compartments was calculated. A measured quantity of 32P

(Rt0 = 1738 kBq) was added to 19 liters of nutrient solution for labelling and the initial specific

activity (SAt0) was 0.183 kBq (µmol P) –1. The labeled nutrient solution (290 mL) was added to

each pot to reach 90% saturation capacity of the perlite (150 g pot–1). The nutrient solution was

added to pots in three times within 3 minutes, so that perlite can absorb nutrient solution. The

labeled nutrient solution was added to 51 pots and the same volume of identical nutrient solution

without labeling was added to the remaining six pots.

46

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3.1.5. Seedling growth conditions

The plastic trays holding the pots were placed on a table in greenhouse and the whole

experimental area was covered with a plastic sheet to keep the temperature constant throughout

the growth period (Figure 3.2). Four light lamps (High Pressure Sodium Lamp-400W) suspended

over the pots provided light at a photoperiod of 18/6 hours of light and dark. Air temperature and

the temperature inside the pots were measured with 0.2 mm diameter copper-constantan

thermocouples. Air relative humidity was measured with a relative humidity probe (HMP35AC,

Vaisala, Finland). Photosynthetically active radiation (PAR) was recorded with a PAR Sensor

(SKP 215, Skye Instruments, Llandrindod Wells, UK and JYP-1000, SDEC, France).

All sensors were connected to a data logger (21X, Campbell Scientific, UK).

Measurements were taken every 15 minutes, but only hourly average values were recorded. The

Figure 3.3 shows an example of recorded values during one experimental day. The average air

temperature, relative humidity and light intensity during the experiment were 25 °C, 43% and

246 µmol m–2 sec–1, respectively.

Figure 3.2: Outer view of greenhouse experiment 2010.

47

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0

50

100

150

200

250

300

350

400

0:00 4:48 9:36 14:24 19:12 0:00

Time (One day duration)

PA

R (µ

mol

m–2

s–1

)

0

10

20

30

40

50

60

70

T (°

C) a

nd R

H (%

)

PAR

Temperature (T)Relative hum idity (RH)

Figure 3.3: Climatic conditions during first experiment, (photosynthetically active radiation "PAR" on left axis, temperature "T" and relative humidity "RH" on right axis).

Thermal time (TT) in cumulated degree days after sowing was calculated on a daily basis as

follows;

+= bTTnTxTT

2Equation 3-1

where Tx is the maximum daily air temperature (in °C), Tn is the minimum daily air temperature

(in °C) and Tb is the base temperature (10 °C), any maximum temperature exceeding 30 °C was

set at 30 °C (Bonhomme et al. 1994).

3.1.6. Irrigation

Throughout the experiment period, all pots were irrigated on the basis of water lost from the pots

by evapotranspiration. On each day, six randomly chosen pots from plastic trays were weighed

(g) and average weight loss was compensated by adding the same volume of water to all the

pots.

3.1.7. Seedling harvest

The experiment was carried out for 298 cumulated degree days after sowing and seedlings were

harvested 14 times during this whole growth period. The initial seed biomass, total P, phytate

48

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and phytate-P reserves were measured in 18 seeds (3 replications of 6 seeds). After sowing, the

seedlings were harvested each day (~ 10:00 AM) during the first week and every other day

thereafter started from 16 March 2010. At each harvest, three pots were selected from different

positions in the plastic trays and six seedlings (Figure 3.4) were sampled from each pot. When

necessary, seedlings presenting growing problems were discarded.

Figure 3.4: A growing maize seedling during early growth.

The six selected seedlings were washed with a 400 mL solution of 0.5 mM CaSO4 at 4 °C

for 1 minute to remove all the perlite from the seedling roots as shown in Figure 3.5. Next, the

seedlings were placed for 4 minutes at 4 °C in a 400 mL of solution containing high P (500 µmol

P L–1) and CaSO4 (0.5 mM) for the desorption of 32P from the seedling roots (Rubio et al. 2004).

49

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Desorption of 32P

Washing with 400 mL of 0.5 mM

CaSO4 + 0, 100, 500 or 1000 µmol PL– 1

at 4°C for 4 minutes (experiment 1 and 2)

Seedling compartments1. Endosperm2. Scutellum3. Coleoptile+mesocotyle4. Roots5. Leaves

32P sorbed on roots

Seedling Removal of Perlite

Washing with 400 mL of 0.5 mM CaSO4 at

4°C for 1 minute

Root Scanning (WinRhizo)

32P determination in washing solution

1 5432

Desorption of 32P

Washing with 400 mL of 0.5 mM

CaSO4 + 0, 100, 500 or 1000 µmol PL– 1

at 4°C for 4 minutes (experiment 1 and 2)

Seedling compartments1. Endosperm2. Scutellum3. Coleoptile+mesocotyle4. Roots5. Leaves

32P sorbed on roots

Seedling Removal of Perlite

Washing with 400 mL of 0.5 mM CaSO4 at

4°C for 1 minute

Root Scanning (WinRhizo)

32P determination in washing solution

32P determination in washing solution

1 5432

Figure 3.5: Desorption of 32P and washing of maize seedling roots.

3.1.8. Statistical analysis

The mean values resulted from the measurement of three biological replications of six plants.

Statistical analyses were performed with R language environment for statistical computing and

graphics, version 2.9.1 (R Development Core Team, 2009). Means were compared using

Student’s test at the 0.05 probability level.

50

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3.2. Experiment 2 (growth chamber study 2010)

The second study was conducted in growth chamber during November and December 2010, at

INRA Bordeaux, France. The objectives of this study were to know the effect of endogenous and

exogenous P availability on

The endogenous seed P reserves remobilization.

The beginning of exogenous P uptake and its intensity.

The interaction of the endogenous and exogenous P availability and effect on each other

during germination and early growth stages.

3.2.1. Experimental layout and selection of maize seeds

The maize seeds (cv. DKC-5783) with low (LS) and high (HS) endogenous seed P reserves were

used in this experiment. The seeds were harvested from long term P fertilization experiment

cultivated with irrigated maize and located at experimental site of Pierroton in Southwest of

France (lat. 44° 44′ 30″; long. 0° 46′ 59″; alt. 55m). Experimental field received 11.5 kg ha–1 and

88.40 kg ha–1 P fertilization for obtaining low and high seed P reserves, since 2003 (see for

detail, experimental protocol PX032 in Appendix I). Homogenous seeds from LS and HS

treatments with same initial seed weight (0.33 g ± 0.001) were selected for this experiment. The

initial endogenous seed P was 506 µg P seed–1 and 952 µg P seed–1 for LS and HS seeds,

respectively.

3.2.2. Seed sowing

Before sowing, the LS and HS seeds were separated into groups of nine for each pot. On 9th

November 2010 (~ 10:00 AM), these seeds were sown in perlite (120 g pot–1) at 2 cm sowing

depth in opaque polypropylene pots (10*10*14 cm) with three exogenous nutrient solution P

availabilities. The three exogenous P availabilities were 0, 100 µmol P L–1 and 1000 µmol P L–1

for no P (0P), low (LP) and high exogenous P (HP), respectively. There were total 183 pots, 90

pots were cultivated with LS seeds and other 90 pots with HS seeds. The remaining 3 pots used

to determine the radioactivity induced background noise.

3.2.3. Nutrient solution composition

Three complete nutrient solutions of P containing all the necessary micro and macro nutrients

were used to grow the maize seedlings (Bhadoria et al. 2004) with three exogenous P

51

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concentrations. The nutrient solutions consisted of 1 mM NO3 as Ca(NO3)2.4H2O, 0.2 mM K as

KCl, 0.1 mM Mg as MgSO4.7H2O, 46 µM B as H3BO3, 9.1 µM Mn as MnCl2.4H2O, 0.8 µM Zn

as ZnSO4.7H2O, 0.3 µM Cu as CuSO4.5H2O, 0.5 µM Mo as (NH4)6Mo7O24.4H2O, 2 mg L–1 Fe

was added as Sequestrene-138 Fe (water soluble granules with 6% Fe in chelated form). The

exogenous P concentrations were 0, 100 µmol P L–1 or 1000 µmol P L–1 as NaH2PO4.2H2O for

0P, LP and HP, respectively. The pH of the all three nutrient solutions was adjusted to 6.4 with

NaOH (1 g 100 mL–1 of distilled water) solution.

3.2.4. Labeling of nutrient solution

In order to correctly distinguish the two P fluxes coming from endogenous seed P reserve

remobilization and exogenous P uptake in newly growing maize seedlings and their effect on

each other according to their origin, the exogenous P was labeled with 32P. The exogenous P was

labeled with radioactive P (32P) to quantify the exogenous P uptake and to follow the endogenous

seed P remobilization kinetics and the partitioning of seedling P in different seedling

compartments during early growth stages. Out of a total 183 pots i) 180 pots with 32P labeling

were used to monitor the endogenous seed P reserves remobilization kinetics and exogenous P

uptake and ii) three pots without 32P labeling sown with HS and HP to determine radioactivity

induced background noise on last seedling harvest.

An initial measured quantity (Rt0), 1561 kBq and 1669 kBq of 32P was added in 16 L of

0P and LP solutions, respectively while 1667 kBq was added in 15 liters of HP solution for

labeling of exogenous P. The initial specific activity (SAt0) was 1.043 kBq (µmol P) –1 and 0.111

kBq (µmol P) –1 in LP and HP labeled nutrient solutions, respectively. The labeled nutrient

solution (210 mL pot–1 of 0P, LP and HP) was added to total 180 pots to reach the 90% saturation

capacity of perlite and the same volume (210 mL pot–1) of HP nutrient solution without labeling

was added to the remaining three pots sown with HS seeds to know the radioactivity induced

background noise. Out of total 90 LS seed pots, each 30 pots were irrigated with labeled nutrient

solution of 0P, LP and HP, respectively. Similarly out of 90 pots treated with HS seeds, each 30

pots were irrigated with labeled nutrient solution of 0P, LP and HP, respectively.

3.2.5. Seedling growth conditions

All the pots were placed in the plastic trays on fixed iron stands with growth chamber walls as

shown in Figure 3.6. The growth chamber ground surface was covered with plastic sheet to

avoid any contamination of 32P. The photoperiod was kept as 18/6 hours of light and dark

52

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throughout the seedling growth period. Air temperature and the temperature inside the pots were

measured with copper-constantan thermocouples (0.2 mm diameter). Air relative humidity was

measured with a relative humidity probe (HMP35AC, Vaisala, Finland). Photosynthetically

active radiation (PAR) was recorded with a PAR Sensor (SKP 215, Skye Instruments,

Llandrindod Wells, UK and JYP-1000, SDEC, France). All sensors were connected to a data

logger (21X, Campbell Scientific, UK).

Figure 3.6: Growing maize seedlings in pots placed in plastic trays on iron stands in growth chamber experiment in 2010.

Measurements were taken every 15 minutes, but only hourly average values were recorded. The

Figure 3.7 shows an example of recorded values during one experimental day. During the

experiment the average air temperature, relative humidity and light intensity were 28 °C, 49%

and 657 µmol m–2 sec–1, respectively. Thermal time (TT) in cumulated degree days after sowing

was calculated on daily basis as follows:

( )∑=

=

−=29

1

d

dbd TTTT

Equation 3-2

where dT is the daily air temperature (in °C) as average of hourly recorded air temperature each

day. Any hourly air temperature exceeding 30 °C was set at 30 °C (Bonhomme et al. 1994). Tb

(10 °C) is the base temperature (Eagles and Hardacre 1979).

53

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0

100

200

300

400

500

600

700

800

900

00:0

0

06:0

0

11:0

0

16:0

0

21:0

0

Time (One day duration)

PA

R (µ

mol

cm

-2 s

ec-1

)

0

10

20

30

40

50

60

T (°

C) a

nd R

H (%

)

PAR

Tem perature (T)

Relative humidity (RH)

Figure 3.7: Climatic conditions during second experiment, (photosynthetically active radiation "PAR" on left axis, temperature "T" and relative humidity "RH" on right axis).

3.2.6. Irrigation

The pots were irrigated with water on the basis of water lost from the pots by evapotranspiration

throughout the experiment on daily basis. Pots of last seedling harvest were weighed (g) on each

day to estimate the average weight loss due to evapotranspiration, and weight loss was recovered

by adding same volume of water to each pot.

3.2.7. Seedling harvest

The experiment was carried out for 530 cumulated degree days after sowing and 10 seedling

harvests were taken during these four weeks of early growth period. The initial seed biomass,

total P, phytate and phytate-P reserves were determined in 18 seeds (3 replications of 6 seeds) in

each LS and HS seeds. The seedlings were harvested (~ 10:00 AM) after 16, 34, 52, 71, 89, 126,

163, 199, 309 and 530 cumulated degree days after sowing. At each seedling harvest, three pots

within each treatment were selected and six homogenous seedlings were sampled from each pot.

For all treatments, the six homogenous selected seedlings were washed first with a 400 mL

solution of 0.5 mM CaSO4 at 4 °C for 1 minute to remove all the perlite from the seedling roots

(Figure 3.5). Next the seedlings were placed at 4 °C in a 400 mL of solution containing P (0,

54

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100 µmol P L–1 or 1000 µmol P L–1, depending upon the exogenous P treatment) and CaSO4 (0.5

mM) for the desorption of 32P from the seedling roots for 4 minutes (Rubio et al. 2004).

3.2.8. Statistical analysis

In second experiment the treatments were defined as the factorial combination of two

endogenous seed P levels (LS, HS) and three exogenous nutrient solutions P availabilities (0P,

LP, HP). The treatments were applied in a completely randomized block design with three

replicates and ten seedling harvests dates. Data were analyzed by ANOVA using R language

environment for statistical computing and graphics, version 2.9.1 (R Development Core Team,

2009). Means were compared using Tukey’s test at the 0.05 probability level.

55

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3.3. Growth measurements and chemical analysis

In both early mentioned experiments some similar morphological and chemical analysis were

performed as explained below.

3.3.1. Morphological analysis

After washing, the seedlings were placed on a glass plate and separated into five different

seedling compartments including endosperm, scutellum, roots, coleoptile+mesocotyle and leaves

with a spatula in both experiments as shown in Figure 3.5. The following compartments were

also used for data analysis: the seed (comprising endosperm and scutellum), the seedling

(comprising leaves, roots and coleoptile+mesocotyle), and total seedling (comprising leaves,

roots, coleoptile + mesocotyle, endosperm and scutellum). All the results in this study are

expressed on the basis of each seedling in each pot.

3.3.1.a. Root and leaf morphology

At each seedling harvest, the length of the radicle (cm seedling-1) and the length of the leaf (cm

seedling-1) of each seedling were measured by scale. Then the whole root system was scanned

and root length (cm seedling-1), root volume (cm3 seedling-1) and root surface area (cm² seedling-

1) were measured using WinRHIZO Pro V.2005a (Instrument Regent, Quebec, Canada).

3.3.1.b. Fresh and lyophilized seedling biomass

After scanning, the fresh biomass (g seedling-1) of each seedling compartment (endosperm,

scutellum, leaf, root, coleoptile+mesocotyle) was determined. The seedling samples were than

lyophilized for 24 hours and their lyophilized weight (g seedling-1) was measured.

3.3.2. Chemical analysis

In both experiments, each seedling compartment was ground separately in a micro-vibrant

grinder (Retsch MM400 mixer mill, Retsch GmbH, Haan, Germany). Endosperm seed

compartment ground for 45 seconds at 25 frequency and scutellum seed part ground for 35

seconds at frequency value of 13. Leaves, roots and coleoptile+mesocotyle seedling

compartments were grinded for 45 seconds for frequency value of 20. After grinding the seedling

compartments were divided into two parts, one part was used to determine phosphorus in

seedling compartments and other for phytate, C and N analysis.

56

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3.3.2.a. Phosphorus determination

Phosphorus content was determined in all seedling compartments by an adaptation of malachite

green colorimetric technique (Van Veldhoven and Mannaerts 1987). One part of each ground

sample was weighed and then reduced to ashes at 550 °C for 5 hours. The resulting ashes were

dissolved in 5 mL distilled water and placed on a hotplate to evaporate until only a few drops

were left. P content was measured colorimetrically after P mineralization with HNO3 (Van

Veldhoven and Mannaerts 1987). The total seedling P content was the sum of the respective

amounts of P in each seedling compartment.

3.3.2.b. Exogenous P uptake and its allocation using 32P labeling

Assuming that no 32P/31P-fractionation occurred during exogenous P uptake by growing seedling

roots and P transport within the seedling (Fardeau 1993; Schjørring and Jensén 1984), the

amount of P in the seedling compartment taken up from the nutrient solution (Pexo) was

calculated as follows:

=⇒

=

ns

t

texo

exo

t

ns

t

PRr

PPr

PR

Equation 3-3

where Rt/Pns is specific activity SAt measured at time t in the nutrient solution, rt is 32P-activity

measured in the mineralized seedling compartment at harvest time t. Rt and Pns are the amount of

carrier-free 32P and 31P measured in the nutrient solution, respectively. The Rt and rt values were

calculated using half life and these values were counted using a scintillation cocktail (Insta-gel

Plus Packard, PerkinElmer) using a Packard TR 2100 (Canberra Industries, Meriden, CT). The

mineralized sample of each seedling sample (10 mL) was added with scintillation cocktail liquid

(10 mL) and placed in Packard TR 2100 for the standard counting time of 20 minutes.

3.3.2.c. Phytate and phytate-P determination

Phytate contents were measured in the scutellum and endosperm compartments of maize seeds at

each harvest in both experiments. The second part of lyophilized ground samples of endosperm

(50 mg) and scutellum (30 mg) were placed in 1.5 mL Eppendorf tubes. Phytate was extracted

from the endosperm with 1 mL of 0.65 M HCl and from the scutellum with 0.60 mL of 0.65 M

HCl (Lorenz et al. 2007; Pontoppidan et al. 2007; Reichwald and Hatzack 2008). The samples

were shaken (SRT-2 Roller Mixer) overnight at room temperature and then centrifuged at 12000

rpm for 20 minutes. The samples were filtered with a 2 mL syringe and filter (0.2 µm cellulose

57

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acetate membrane). Phytate was determined by ion chromatography (IC) using a hydroxide

eluent prepared by an eluent generator with a column designed to determine common inorganic

anions (for details see Appendix II). Phytate content was converted into phytate-P by dividing

phytate content by 3.548 (Raboy and Dickinson 1984).

3.3.2.d. Carbon and nitrogen analysis

C and N was analyzed in all seedling compartments on each seedling harvest in first experiment

and only on last seedling harvest in second experiment. The C and N analysis was performed

with a C and N analyser (Flash EA-1112, Organic Elemental Analyser) using the dynamic flash

combustion technique (modified Dumas method). A ground lyophilized sample of each seedling

compartment (3 mg) was weighed in a small tin capsule and placed in the combustion reactor by

an autosampler. Samples were combusted at 900 °C to release their C and N in gaseous form. C

and N concentration were then measured using a separation column and a TCD detector.

3.3.3. Endogenous seed P exportation flux

In second experiment, the P exportation flux from endogenous seed P towards newly growing

seedlings and P efflux was calculated on the basis of difference between initial endogenous seed

P and endogenous seed P at each seedling harvest in all P treatments.

Exported endogenous seed P = (Endogenous Seed P)t0 – (Endogenous seed P)t

Equation 3-4

3.3.4. P efflux from germinating seeds and growing maize seedling

roots

In second experiment, the P efflux from germinating seeds and growing seedling roots was

calculated considering the exogenous P uptake and endogenous seed P remobilization at each

seedling harvest. The cumulated P efflux was calculated as the difference between the P lost

from seed plus accumulated exogenous P uptake assessed by 32P activity measured in seedling,

and the accumulated P in seedlings.

Cumulated P efflux = (P lost from seed + Exogenous P uptake) – Seedling accumulated P

Equation 3-5

58

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3.4. Control of experimental procedures

3.4.1. P loss from seeds by imbibition

Phosphorus loss during imbibition of seeds was reported in previous studies. Dave et al., (2008)

reported that 4-11% of phytate phosphorus decreased during soaking of whole legume seeds. A

preliminary experiment was carried out to know the effect of maize seed imbibition on seed P

loss. The 20 maize seeds (cv. DKC-5783) of homogenous seed size were selected for this

experiment. 100 mL distilled water was taken in a glass beaker (200 mL capacity) and 3 mL of

this distilled water was taken as initial reading of P determination (S0). The maize seeds were

imbibed in remaining 97 mL of distilled water for the duration of 180 minutes. The seeds were

stirred, so that all the seeds should be mixed thoroughly. The first sampling from seed imbibition

solution (S1) was carried out after 5 minutes of imbibition of seeds in distilled water. In the same

pattern, the 7 samplings (S2 …. S7) were carried out after 30, 60, 90, 120, 150, and 180 minutes

of imbibition. For each sampling 3 mL solution was taken from imbibition solution and the

remaining solution was considered as final for the next sampling for final calculations of volume

of water. The phosphorus was determined in each sample of seed imbibed water and in seeds

after 180 minutes of imbibition. After 180 minutes of imbibition, the seed P loss was less than

0.4% of initial seed P reserves as explained in the Figure 3.8, therefore the imbibition of seeds

for 5 minutes was considered as good to initiate the germination during the further studies.

0.00%

0.10%

0.20%

0.30%

0.40%

0.50%

0 50 100 150 200

Seed imbibition time (minutes)

µg P

rele

ased

/ µg

P in

itial

in th

e gr

ain

(%)

Figure 3.8: Loss of seed P by imbibition (% loss of initial seed P).

59

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3.4.2. P sorption properties of perlite

Perlite was used as a substrate to sow maize seedlings during the studies. A preliminary

experiment was carried out to determine the buffer capacity of perlite. Different concentrations

of P were added to substrate/solution suspension (1 g perlite 10 mL-1 solution suspension) in

small flacons. The flacons with perlite and solution suspension were left for agitation for 24

hours at room temperature.

y = 1.0053x - 0.3201R2 = 0.9995

0

20

40

60

80

100

120

0 20 40 60 80 100 120

Initial P concentration (µg P mL-1)

Fina

l P c

once

ntra

tion

(µg

P m

L-1) 1:1 line

Figure 3.9: Initial P concentrations added in perlite solution suspension and final P concentrations in perlite solution suspension after 24 hours. Dashed line is the 1:1 line. Blue dots are measured data and the solid line is the linear regression line.

The P was determined in solution suspension after 24 hours. The added P in perlite

solution suspension was found in solution after 24 hours showing that there was no sorption of P

on perlite and all the added P remained in solution after 24 hours as shown in Figure 3.9. Due to

the very low buffer capacity, the perlite was used for further studies for sowing of maize

seedlings.

3.4.3. Base temperature for maize germination

A preliminary experiment was conducted to determine the base temperature for maize seed

germination. The experiment was carried out at four different temperatures and three endogenous

seed P levels over a growth period of 7 days after imbibition. The maize seeds with three

endogenous seed phosphorus levels ( low P, intermediate P and high P) were sown at

60

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temperature range of 15 °C, 20 °C, 25 °C and 30 °C. In this study, the germination was defined

as when the seed has a visible seedling radicle. The maize seeds were placed in petri dishes on

moist filter papers and covered with one layer of filter paper to keep them moist. The petri dishes

were placed in the incubators at four different temperatures (15 °C, 20 °C, 25 °C and 30 °C).

Each phosphorus level was replicated three times in each temperature.

y = 0.0018x - 0.0169R2 = 0.8783

0.000

0.005

0.010

0.015

0.020

0.025

0.030

0.035

0.040

0.045

0 5 10 15 20 25 30 35

Temperature (°C)

Ger

min

atio

n ra

te h

our-1

50Linéaire (50)

9.64°C

Figure 3.10: Germination rate hour-1 calculated as the inverse of the time to reach 50 % germination as a function of the temperature. The calculated base temperature for maize

germination was 9.64°C.

The distilled water was added to petri dishes from time to time to keep the moisture level at

optimum. The temperature was maintained uniform in each treatment during the experiment in

incubators. One each day, germination was noted at different times. The percent germination is

noted on the basis of total number of seeds germinated on each time. Germination percentage is

about more than 88% in all temperature and phosphorus treatments. The results showed that at

15 °C the maximum seeds were germinated on 4th day, at 20 °C on 3 rd day, on 25 °C and 30 °C

on 2nd day after imbibition, respectively. The germination is favoured at more than 20 °C, and

the optimum temperature for maize may be between 25 °C and 30 °C. The coleoptile emergence

from germinating seed is also favoured by more temperature and minimum at 15 °C, being

optimum at 25 °C. Temperature also has a positive effect on fresh seedling biomass which is

maximum at 30 °C. The base temperature calculated on the basis of germination rate per hour

61

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was 9.64 °C as shown in Figure 3.10. Therefore a base temperature of 10°C was used for

calculations.

3.4.4. P sorption on seedling roots

The amount of P sorbed on the root free space was estimated by measuring 32P release in the

rinsing solution at 10, 98 and 224 cumulated degree days after sowing only in first experiment.

Three pots were sampled and six homogenous seedlings selected from each pot. Seedlings were

washed with 0.5 mM CaSO4 at 4 °C for 1 minute to remove the perlite.

0

2

3

5

6

0 50 100 150 200 250 300 350

Thermal time (cumulated degree days after sowing)

P s

orbe

d (µ

g se

edlin

g-1)

Figure 3.11: P sorption on maize seedling roots during germination and early growth. Data are

means and vertical bars indicate ±SE for n = 3 replications.

The seedlings were then placed in a high P solution (500 µmol P L–1) also containing 0.5

mM CaSO4 for 4 minutes at 4 °C to desorb 32P from the root free space. Seedlings were then

removed from the washing solution and 32P was counted in the washing solution. The root length

was measured by scanning the whole root system as described earlier. The total P sorption

calculated from specific activity and 32P counting was 5 µg P seedling-1 as shown in Figure 3.11.

The average amount of P sorbed on the root free space was always less than 0.009 µg P cm–1 of

seedling root, so it was considered as negligible in the second experiment. In second experiment,

the 32P sorbed on seedling roots was not determined in washing solution because it was

negligible during first experiment.

62

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3.4.5. Specific activity induced background noise

As the calculation of exogenous P uptake by 32P labelling might be influenced by background

noise caused by specific activity in the seedlings, the specific activity induced background noise

was measured in all seedling compartments at two seedling harvests in first and on last seedling

harvest in second study. Background noise of specific activity was measured at 70 and 273

cumulated degree days after sowing in first experiment and on 530 cumulated degree days in

second experiment in pots that had received nutrient solution without 32P labeling. The six

homogenous seedlings were selected from each pot and these seedlings were washed first with a

400 mL solution of 0.5 mM CaSO4 at 4 °C for 1 minute to remove all the perlite from the

seedling roots.

Next the seedlings were placed at 4 °C in a 400 mL of solution containing P (0, 100 µmol

P L–1, 500 µmol P L–1 or 1000 µmol P L–1, depending upon the exogenous P treatment in

experiment 1 and 2) and CaSO4 (0.5 mM) for the desorption of 32P from the seedling roots for 4

minutes (Rubio et al. 2004). Seedlings were separated into different seedling compartments.

The seedling compartments were reduced to ashes at 550°C and mineralized with HNO3

(Van Veldhoven and Mannaerts 1987). The mineralized solution (10 mL) was placed in Packard

TR 2100 along with scintillation cocktail liquid (10 mL) for 20 minutes. As no significant 32P

activity (<47 cpm) was detected in the different compartments of seedlings grown in the nutrient

solution without labeling, specific activity induced background noise was considered to be zero

in both experiments.

63

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64

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4. RESULTS AND DISCUSSIONS

4.1. Relative contribution of seed phosphorus reserves and exogenous

phosphorus uptake to maize (Zea mays L.) nutrition during early growth

stages

4.1.1. Objectives

The objective of this first study was to characterize the kinetics of the two processes that supply

phosphorus to the developing maize seedling i.e. the remobilization of seed P reserves and

exogenous P uptake, and to evaluate their relative contribution to the young maize seedling P

supply. Although P, carbon (C) and nitrogen (N) are stored in different compartments of the seed

(P in the scutellum; C and N in the endosperm), we examined whether their remobilization

follows the same kinetics. The results of this study are presented here and were published in

Plant and Soil (Nadeem et al. 2011). The complete article is attached in Appendix III.

4.1.2. Results

4.1.2.a. Seedling growth

The radicle emerged from the maize seed along with the mesocotyle and coleoptile, the latter

having first enclosed seedling leaf at 26 cumulated degree days after sowing (Table 4.1).

Seminal roots and radicle appeared and elongated at 41 cumulated degree days. The first

seedling leaf emerged from the soil and became visible at this time. At the end of the experiment,

the seedlings had four visible leaves. Total root length and lateral root length were 572 cm

seedling–1 and 366 cm seedling–1, respectively at 298 cumulated degree days.

65

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Table 4.1: Radicle length, root length and number of visible leaves during early growth of maize seedlings. Values are means (±SE) of 3 replications.

Thermal

time

Age

(days)

Root length

(cm/seedling)

Number of

visible

leaves

Cumulated

degree

days

Radicle

length

Total root

length

Root

length

(Ø<0.04)

Root

length

(Ø>0.04)

10 126

2 3 ± 0.2 4 ± 0.441 3 4 ± 0.3 11 ± 3 1 ± 0.2 10 ± 1 156 4 6 ± 0.5 25 ± 2 7 ± 1 18 ± 1 170

5 8 ± 0.2 39 ± 6 11 ± 4 28 ± 3 198 7 9 ± 2 133 ± 22 76 ± 12 56 ± 10 2126

9 11 ± 0.6 206 ± 4 114 ± 3 92 ± 2 3152 11 12 ± 0.9 294 ± 7 172 ± 7 122 ± 1 3176 13 18 ± 1 362 ± 9 223 ± 5 138 ± 12 3202

15 19 ± 1 456 ± 29 273 ± 19 183 ± 12 3224 17 20 ± 0.1 499 ± 44 301 ± 26 198 ± 18 3248

19 19 ± 1 543 ± 31 336 ± 26 207 ± 5 4273 21 22 ± 1 541 ± 20 329 ± 13 212 ± 7 4298

23 20 ± 0.2 572 ± 26 366 ± 16 206 ± 10 4

4.1.2.b. Seed and seedling C content

Total C reserves remained significantly unchanged during the first 26 cumulated degree days

after sowing as shown in Figure 4.1. They started to decrease from 26 until 98 cumulated degree

days after sowing and increase thereafter. The seed C reserves showed a rapid remobilization

from 26 cumulated degree days after sowing till 176 cumulated degree days which largely

translocated towards seedling compartments. The seedling C accumulation was started soon after

radicle emergence from 26 cumulated degree days after sowing and increase thereafter. The seed

C loss was calculated by the difference of initial seed C reserves and seed C reserves at each

seedling harvest. The difference of seed C loss and seedling C accumulation was higher up to 89

66

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cumulated degree days after sowing (Figure 4.1) and assumed to be lost through respiration. This

difference started to decrease after 89 cumulated degree days when the seedlings had two visible

leaves on 98 cumulated degree days after sowing. From 202 cumulated degree days after sowing,

the seedling C accumulation was higher than seed C loss and this period corresponded to the

transition from heterotrophy to autotrophy for C.

Cumulated degree days after sowing

0 50 100 150 200 250 300 350

Qua

ntity

of C

(mg

C)

0

20

40

60

80

100

120

140

Total CSeed CSeedling CSeed C loss

Figure 4.1: Changes in total seedling C (■), seed C remobilization (●), seedling C accumulation (▲) and seed C loss (∆) in maize seedlings expressed in mg seedling-1 during germination and early growth stages. Time is expressed in cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3.

We considered two maize seed compartments, namely, endosperm and scutellum. Prior to

germination, 87% (w/w) of initial seed C reserves were localized in the seed endosperm and the

remainder in the seed scutellum. Endosperm C reserves remained significantly unchanged during

the first 26 cumulated degree days after sowing (Figure 4.2a). A sharp decrease in endosperm C

reserves was observed from 41 to 176 cumulated degree days and 79% of initial endosperm C

reserves were remobilized before 176 cumulated degree days. Endosperm C reserves remained

unchanged thereafter with a minimum content of around 20 mg C in the endosperm. In contrast,

scutellum C reserves were much lower than those in the endosperm and were remobilized

rapidly during the first 41 cumulated degree days after sowing and slowly thereafter (Figure 4.2

b). The scutellum was in close contact with the embryo.

67

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(a) Endosperm

mg

C s

eedl

ing-1

0

20

40

60

80

100

120

µg P

see

dlin

g-1

0

200

400

600

800C contentP content

(b) Scutellum

mg

C s

eedl

ing-

1

0

20

40

60

80

100

120

µg P

see

dlin

g-1

0

200

400

600

800

(c) Leaf

mg

C s

eedl

ing-

1

0

20

40

60

80

100

120

µg P

see

dlin

g-1

0

200

400

600

800

(d) Root

Cumulated degree days after sowing

0 50 100 150 200 250 300 350

mg

C s

eedl

ing-

1

0

20

40

60

80

100

120µg

P s

eedl

ing-1

0

200

400

600

800

Figure 4.2: Changes in C content (mg C seedling-1) on the left axis (● and solid lines) and in P content (µg P seedling-1) on the right axis (○ and dashed lines) in the endosperm (a), scutellum (b), leaves (c) and roots (d) during early growth of maize. Time is expressed in cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3.

68

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The fast initial remobilization of scutellum C reserves was associated with the demand

for C by the growing embryo. Of the total seed C remobilized, 68% was remobilized from the

endosperm and only 8% from the scutellum up to 176 cumulated degree days after sowing.

Seedling leaf C content started to increase with the emergence of first visible leaf on the

seedling at 41 cumulated degree days (Figure 4.2 c), while seedling root C content started to

increase on 26 cumulated degree days when the radicle emerged (Figure 4.2 d). From 41 to 98

cumulated degree days, the shoot to root C ratio increased sharply to 0.89 and remained constant

thereafter indicating that the distribution of remobilized C reserves and C assimilated

photosynthetically between shoot and root compartments remained unchanged. The

coleoptile+mesocotyle (C+M) is a smaller but important seedling compartment that helps the

first leaf to emerge and reach the light. C+M C content increased from 41 cumulated degree days

and after the emergence of the first leaf from the surface, then C content remained constant

throughout the growth period. After 298 cumulated degree days after sowing, 45%, 53% and 3%

of accumulated seedling C (104 mg seedling–1) was distributed among seedling leaves, roots and

C+M compartments, respectively.

4.1.2.c. Remobilization of seed P reserves and exogenous P uptake

Before germination, a large proportion of maize seed P reserves were located in the scutellum

rather than in the endosperm, i.e. the reverse of C reserves. The initial P content of the scutellum

was about 86% (w/w) of total maize seed P reserves, and the remaining 14% was localized in the

endosperm. The endosperm P reserves were remobilized rapidly at 26 cumulated degree days

after sowing and thereafter, a slow remobilization was observed until 202 cumulated degree days

after sowing (Figure 4.2 a), after which endosperm P content remained unchanged.

Slow remobilization of scutellum P reserves was observed until 26 cumulated degree

days after sowing. Immediately after 41 cumulated degree days, scutellum P reserves were

rapidly remobilized until 202 cumulated degree days (Figure 4.2 b). Remobilization of total seed

P reserves increased from 10 cumulated degree days to reach its maximum value at 70 cumulated

degree days (data not shown), thereafter the remobilization rate decreased as the seed P reserves

were exhausted. At 202 cumulated degree days, 92% and 84% of initial scutellum and

endosperm P reserves were remobilized; 78% of total seed remobilized P originated from the

scutellum and only 12% from the endosperm. All the P remobilized in the maize seed

compartments was quantitatively recovered in different seedling compartments.

69

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Maize seedling leaf P content started to increase from 41 cumulated degree days after sowing

with the emergence of the first visible leaf (Figure 4.2 c), while seedling root P content started to

increase from 26 cumulated degree days with the emergence of the radicle (Figure 4.2 d).

Cumulated degree days after sowing

0 50 100 150 200 250 300 350

µg P seedling

-1

0

200

400

600

800

1000

Total seedling PShoot and root PShoot and root exogenous P

Figure 4.3: Changes in total seedling P content (●), in shoot and root P content (▲) and in exogenous P uptake from the nutrient solution calculated according to 32P-activity measured in the seedling (∆). Data are means and vertical bars indicate ±SE for n = 3 replications.

Total maize seedling P content remained significantly unchanged up to 98 cumulated degree

days after sowing (Figure 4.3) and then started to increase significantly from 126 cumulated

degree days, suggesting that exogenous P uptake from nutrient solution had begun. The exact

time of the beginning of exogenous root P uptake from the nutrient solution was established and

P uptake quantified by 32P-activity measurements in the seedling. Up to 56 cumulated degree

days, no 32P-activity was detected in maize seedlings. 32P-activity was detected in seedlings at 70

cumulated degree days, indicating that exogenous root P uptake was underway. Exogenous root

P uptake increased continuously thereafter. After 298 cumulated degree days, 24% of seedling P

content was provided by exogenous P uptake whereas 76% by seed P reserves remobilization.

4.1.2.d. Remobilization of seed N reserves and seedling N accumulation

The total seed N reserves started to remobilize from 26 cumulated degree days after sowing as

shown in Figure 4.4. A rapid decrease in total seed N reserves was observed from 26 cumulated

70

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degree days after sowing to 176 cumulated degree days after sowing and thereafter remained

almost unchanged. Before germination, 77% of these total seed N reserves in maize were

concentrated in the endosperm and the remaining 23% in the scutellum (Figure 4.4).

Cumulated degree days after sowing

0 50 100 150 200 250 300 350

Qua

ntity

of N

(mg

N)

0

1

2

3

4

Seed NEndosperm NScutellum NSeedling N

Figure 4.4: Changes in total quantity of seed (●), seedling (▲), endosperm ( ) and scutellum (○) nitrogen (mg seedling-1) contents in maize seeds and seedlings during germination and early growth stages. Time is expressed in cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3.

The remobilized seed N reserves were translocated towards seedling compartments. The

seedling N accumulation started to increase from 26 cumulated degree days after sowing and

increase thereafter. The seedling N accumulation followed the similar pattern of C and up to 298

cumulated degree days after sowing, 3 mg N was accumulated in seedling.

4.1.2.e. Phytate and phytate-P

In the maize seed most P is stored in the scutellum mainly in the form of phytate. Initially, the

maize seed had 2.61 mg g–1 DW of phytate-P. As shown in Figure 4.5, 98% of seed phytate-P

was initially localized in the scutellum and remaining 2% in the endosperm. Phytate-P started to

hydrolyze from the 1st DAS via phytase activity. The phytate-P stored in maize scutellum and

endosperm was rapidly converted into organic phosphorus and mineral nutrients, which became

available for newly developing seedlings.

71

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Cumulated degree days after sowing

0 50 100 150 200 250 300 350

P an

d ph

ytat

e-P

con

tent

(µg

P se

edlin

g-1)

0

200

400

600

800

Endosperm phytate-PScutellum phytate-PTotal seed P

Figure 4.5: Variation in total P (µg P seed-1) and phytate-P (µg phytate-P seed compartment-1) reserves in different compartments of the maize seed during early growth stages. Remobilization of total seed P reserves (●); Scutellum phytate-P reserves (∆) and endosperm phytate-P (□). Data are means and vertical bars indicate ±SE for n = 3 replications.

The rapid depletion of the phytate-P fractions in the maize scutellum was observed from 10 to

126 cumulated degree days after sowing and practically all the phytate-P had been depleted by

224 cumulated degree days in the maize scutellum. Whereas in the maize endosperm, all the

phytate-P was hydrolyzed during the 1st DAS. The phytate-P in the scutellum was hydrolyzed

earlier and more rapidly than seed P was remobilized and sent to the growing seedling (Figure

4.5). Non phytate-P, calculated as the difference between total seed P and the phytate-P

remaining in the seed, increased sharply between 41 and 98 cumulated degree days and

decreased thereafter, showing that phytate-P was hydrolyzed and remained there in seeds. Later

on, when the seedling organs were developing, it was translocated to them.

4.1.2.f. Relative contribution of seed P and exogenous P uptake to

seedling P nutrition

A flow chart representing the relative contribution of seed P reserve remobilization and

exogenous P uptake (calculated from 32P-activity measurements) to seedling P nutrition is shown

72

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in Figure 4.6. At the end of the experiment (298 cumulated degree days after sowing), total

maize seedling P contents were 811 µg P distributed most among seedling leaves and roots

rather than seedling C+M. Exogenous P uptake from the nutrient solution was 197 µg P (arrows

on the right) while remobilized seed P was 614 µg P (arrows on the left). The width of arrows

indicates the quantity of P flowing to the different seedling compartments. The flow of

exogenous P to the seed endosperm and scutellum was zero. Exogenous P passed directly from

seedling roots to seedling leaves. Remobilized seed P reserves played a significant role in

fulfilling seedling P requirements and contributed more to seedling P nutrition than uptake of

exogenous P. More than 95% of scutellum phytate was hydrolysed while 60% of total seed P

reserves were exported towards seedlings till 98 cumulated degree days after sowing. Up to 176

cumulated degree days after sowing, 87% of total seed P reserves were exported towards the

young seedlings. A total of 77% of the P in leaves originated from remobilized seed P reserves

and only 23% of P in leaves came from exogenous P uptake. Similarly, 73% of seedling root P

came from remobilized seed P reserves and the remaining 27% from exogenous P uptake. C+M

was a small part of the seedling and was mainly composed of remobilized seed P (83%) rather

than exogenous P uptake. Respectively 54%, 44% and 2% of exogenous P uptake from the

nutrient solution was distributed to the seedling leaves, roots and C+M, while 60%, 37% and 3%

of the remobilized seed P flux was allocated to seedling leaves, roots and C+M, respectively.

The flow of remobilized seed P was calculated as the sum of seed scutellum and seed endosperm

P remobilized from the whole seed. The flow of remobilized P from the seed after 298 cumulated

degree days was 628 µg P seed–1 i.e. not significantly different from 614 µg P seed–1, while 34 µg

P remained in the seed.

73

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Figure 4.6: Allocation of exogenous P uptake (gray arrows on the right) calculated using 32P labeling of the nutrient solution and distribution of remobilized seed P reserves (dark arrows on the left) to seedling compartments after 298 cumulated degree days (23 DAS). The width of the arrows represents the quantity of P flowing toward different seedling compartments. Values inside the different compartments represent P accumulation in (+) or remobilization from (-) each compartment. Values in italics represent P content in the seed and in the seedling after 298 cumulated degree days (23 DAS). P fluxes are expressed in µg P seedling -1. Data are means and vertical bars indicate ± SE for n = 3 replications.

- 614 (±23)

Remobilized P

+ 228 (±10)

+ 19 (±1)

+367 (±21)

Exogenous P

+ 86 (±4)

+ 4 (±1)

Seedling P

811 (±26)

Seed P

34 (±2)

0

+ 107 (±5)

Leaves

+ 474 (±26)

C+M

+ 23 (±2)

Roots

+ 314 (±14)

Scutellum

- 545 (±17)

Endosperm

- 83 (±4)

External P

197 (±3)

23%

%

17%

%

27%

%

77%

83%

%

73%

%

74

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4.1.2.g. Relationship between P and N remobilization

The initial seed N concentration was 12 mg g–1 seed DW. The remobilization of seed N and its

accumulation in the seedling during early growth stages resembled that of C (Figure 4.4).

Phosphorus was mainly localized in the maize scutellum while C and N were localized in the

endosperm. Phosphorus, C and N were rapidly remobilized during germination and early growth

and displayed similar remobilization kinetics, although the three elements were localized in

different seedling compartments as shown in Figure 4.7.

Cumulated degree days after sowing

0 50 100 150 200 250 300 350

Rat

e of

rem

obili

zatio

n of

see

d re

serv

es

0.0

0.2

0.4

0.6

0.8

1.0

1.2

CN P

Figure 4.7: Rate of P, C and N remobilization in maize seed during early growth stages calculated as the ratio of P (○), C (●) and N (∆) content in seed to their initial content. Data are means and vertical bars indicate ±SE for n = 3 replications.

75

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4.1.3. Discussion

4.1.3.a. Carbon remobilization and seedling growth

Shoot and root growth of seedlings take place at the expense of seed reserves. In our experiment,

seed C reserves, which were mainly localized in the endosperm, started to decrease from 26

cumulated degree days after sowing. From the start of the experiment until 98 cumulated degree

days, the loss of seed C reserves was greater than the accumulation of C in the seedling and the

difference was assumed to be lost through respiration. At 98 cumulated degree days, the

difference between the decrease in seed C reserves and seedling C accumulation decreased

indicating that photosynthesis had started in the two visible leaves. These results are in

accordance with those of Deleens et al. (1984) who reported a significant contribution of

photosynthetic C to maize seedling growth at 98 cumulated degree days. A net positive

accumulation of seedling C was observed after 202 cumulated degree days.

The decrease in C reserves in maize seeds during early growth occurred in three stages:

first, reserves remained unchanged until 26 cumulated degree days, second, a rapid decrease

occurred from 26 to 176 cumulated degree days, and thereafter no change was observed in seed

C reserves. Deleens et al., (1984) also reported three stages in the depletion of seed C reserves.

4.1.3.b. Phytate hydrolysis and relative contribution of P to growing

seedlings

In agreement with other studies, in our experiment phytate was found to be the main form of P

stored in the maize seeds and was localized in the scutellum rather than in the endosperm or

embryo (Lorenz et al. 2007; Lott et al. 1995; Modi and Asanzi 2008; Park et al. 2006). A sharp

drop in phytate reserves was observed between the 2nd and the 7th day after sowing (98 cumulated

degree days after sowing). This is consistent with the results of Laboure et al., (1993) who

showed that in germinating maize seeds, maximum phytase activity occurred between the 5 th and

7th day after imbibition. Hydrolyzed forms of P were temporarily stored in the seed before being

translocated to the growing organs, suggesting that the hydrolysis of phytate was not a limiting

step for seedling P supply (Figure 4.5).

All the P remobilized from seed P reserves was quantitatively recovered in different

seedling compartments. As already pointed out by Hall and Hodges (1966) that phytate break

down in seed accounts primarily for the increase in inorganic P of the roots and shoots. Four

days after sowing (56 cumulated degree days) the maize seedling only contained P originating

76

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from seed P reserves. Exogenous P uptake measured by 32P enrichment in seedling roots was

only observed on the 5th day after sowing (70 cumulated degree days). From 70 cumulated

degree days on, both sources (remobilized seed P reserves and exogenous P uptake) contributed

to fulfil seedling P requirements, although the seed P reserve was the main source. After 202

cumulated degree days, only exogenous P supported seedling growth as seed P reserves were

exhausted. Like the three stages of C proposed by Deleens et al. (1984), three different growth

stages of dependence on seed P reserves and exogenous P uptake can be defined. Up to the 5 th

day after sowing (70 cumulated degree days), the maize seedling depended exclusively on seed P

reserves (heterotrophic stage for P). The transition stage started when the seedling started to

depend on seed P reserves and exogenous P uptake between the 5th and the 15th day after sowing

(from 70 to 202 cumulated degree days). Thereafter, only exogenous P (autotrophic stage for P)

fulfilled seedling P requirements. More P remobilized from seed P reserves was translocated to

seedling leaves than to seedling roots. Similarly, more exogenous P was translocated to seedling

leaves than to seedling roots. This indicates that leaf P requirements are higher than root

requirements during early growth, which corresponds to the appearance of P deficiency

symptoms on seedling leaves during early growth stages.

4.1.3.c. Relationship between P and N remobilization

Nitrogen was mainly concentrated in the maize endosperm and a sharp drop in maize endosperm

N reserves was observed from 26 cumulated degree days. Similar results were reported by

Harvey and Oaks (1974), who showed that total nitrogen in the mature endosperm decreased

most rapidly from the 2nd day after germination on. Although N and P were located in different

seed compartments (i.e. in the endosperm and scutellum, respectively), they displayed similar

remobilization kinetics during early growth of maize seedlings.

77

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4.2. Maize (Zea mays L.) endogenous seed phosphorus remobilization is

not influenced by exogenous phosphorus during germination and early

growth stages

4.2.1. Objectives

As the remobilization of endogenous seed P and the uptake of exogenous P overlap in time

(Nadeem et al. 2011), the question arises whether these processes have an effect on each other or

if they are independently controlled. Our objectives were to study the effect of the availability of

endogenous and exogenous P on i) the remobilization of endogenous seed phosphorus, ii) the

beginning of uptake of exogenous P and its intensity, iii) their interaction and its effect on the

development of young maize seedlings during germination and early growth. Exogenous P was

labeled with 32P to distinguish the two fluxes of P, (one remobilized from endogenous seed

reserves and the other uptake of exogenous P) in young maize seedlings and their effect on each

other according to their origin. The results were submitted for publication in Plant and Soil. The

paper was accepted for publication with revisions on 21st October 2011.

4.2.2. Results

4.2.2.a. Early seedling growth

Prior to germination, the seed dry biomass reserves were largely localized (90%, w/w) in the

endosperm rather than in the scutellum despite endogenous seed P reserves in LS and HS seeds.

Remobilization of the seed dry biomass reserves started at 34 cumulated degree days after

sowing in all P treatments (Figure 4.8). A rapid remobilization of seed biomass reserves was

noted from 34 to 309 cumulated degree days after sowing. The availability of endogenous or

exogenous P had no significant effect on the remobilization of seed dry biomass during

germination and early growth stages.

The emergence of the seedling radicle on 34 cumulated degree days after sowing was

independent of the P availability of either endogenous or exogenous source. Seedling biomass

started to accumulate 34 cumulated degree days after sowing with the emergence of seedling

radicle. The first seedling leaf become visible at 71 cumulated degree days after sowing and at

530 cumulated degree days, seedlings had five visible leaves (Table 4.2).

78

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Cumulated degree days after sowing

0 100 200 300 400 500 600

See

d bi

omas

s (g

)

0.00

0.05

0.10

0.15

0.20

0.25

0.30

0PLSLPLSHPLS0PHS LPHS HPHS

Figure 4.8: Seed biomass remobilization (g) in maize seeds during germination and early growth stages: Low endogenous seed P in seedlings (LS) with no exogenous P (○), low exogenous P (□), high exogenous P (∆), high endogenous seed P seedlings HS with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and vertical bars indicate ± SE for n = 3 replications.

A regular increase in accumulated seedling biomass was observed throughout the growth

period (Figure 4.9). The availability of endogenous or exogenous P had no significant effect on

the accumulation of seedling dry biomass (Table 4.2) during germination and early growth

stages.

Cumulated degree days after sowing

0 100 200 300 400 500 600

See

dlin

g bi

omas

s (g

)

0.00

0.05

0.10

0.15

0.20

0.25

0PLSLPLSHPLS0PHS LPHS HPHS

Figure 4.9: Seedling biomass accumulation (g) in maize seedlings during germination and early growth stages: Low endogenous seed P in seedlings (LS) with no exogenous P (○), low exogenous P (□), high exogenous P (∆), high endogenous seed P seedlings HS with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and vertical bars indicate ± SE for n = 3 replications.

79

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4.2.2.b. Accumulation of P in seedlings

The seedlings started to accumulate P with the emergence of the seedling radicle. P accumulated

rapidly in LS seedlings from 34 cumulated degree days after sowing to 199 cumulated degree

days after sowing in all exogenous P treatments and thereafter an increase was only observed in

the HP treatment (Figure 4.10 A). A regular increase in accumulated P in the seedling was

observed in HS seedlings from 34 cumulated degree days after sowing until 530 cumulated

degree days after sowing (Figure 4.10 B).

The growing seedlings accumulated significantly more P in HP than in 0P or LP

treatments with available exogenous P despite endogenous P reserves in the seed. Less P

accumulated in the seedling than the initial amount of endogenous seed P in LS and HS

seedlings in 0P and LP treatments with exogenous P, whereas more accumulated P in the

seedling in LS and HS seedlings treated with HP exogenous P, indicating net P accumulation at

whole plant level. Accumulation of P in the seedling was significantly affected by the

availability of endogenous and exogenous P at 530 cumulated degree days. HS seedlings had

significantly more accumulated P (959 µg, 637 µg and 596 µg in HP, LP and 0P exogenous P

treatments, respectively) than LS seedlings (267 µg, 324 µg and 582 µg P in 0P, LP and HP

exogenous P treatments, respectively) as shown in Table 4.2.

Cumulated degree days after sowing

0 100 200 300 400 500 600

See

dlin

g P

(µg

P)

0

200

400

600

800

1000

1200

0PLSLPLSHPLS

Cumulated degree days after sowing

0 100 200 300 400 500 600

0PHSLPHSHPHS

0

A B

Figure 4.10: Phosphorus accumulation (µg P) in maize seedlings during germination and early growth stages: A. Low endogenous seed P in seedlings (LS) with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and B. high endogenous seed P seedlings HS with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and vertical bars indicate ± SE for n = 3 replications.

80

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LS HS Significance

0P LP HP 0P LP HP Endo-P Exo-P

Endo-P

xExo-P

Number of visible leaves 5.3a 5.5a 5.2a 4.7a 5a 5a NS NS NS

Seedling dry weight (g) 0.18a 0.21a 0.21a 0.21a 0.23a 0.22a NS NS NS

Seedling P accumulation

(µg P)267a 324a 582b 596b 637b 959c * * NS

Table 4.2: Values of selected variables for maize seedlings at 530 cumulated degree days after sowing with two rates of endogenous P (LS "low seed P " and HS "high seed P") subjected to three rates of exogenous P (Exo-P) availability (OP "control exogenous P", LP "low exogenous P" and HP "high exogenous"). F-test significances of Endo-P (endogenous seed P), Exo-P and Endo-P x Exo-P interaction are indicated (NS = not significant). Different letters in the same line indicate significant differences at the 0.05 probability level.

81

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The initial P concentration was 8 mg g-1 seedling DW in LS and HS seedlings (Figure

4.11). Concentrations of P in the seedling decreased from 8 mg g-1 to 1 - 4 mg g-1 seedling DW in

LS and HS seedlings up to 309 cumulated degree days after sowing. P concentrations in the

seedling were higher in HP than in 0P and LP exogenous P treatments despite endogenous P

seed P reserves.

Cumulated degree days after sowing

0 100 200 300 400 500 600

See

dlin

g P

con

cent

ratio

n (m

g P

g-1

)

0

2

4

6

8

10

0PLSLPLSHPLS0PHS LPHS HPHS

Figure 4.11: Seedling phosphorus concentrations (mg P g–1) in maize seedlings during germination and early growth stages. Low endogenous seed P seedlings (LS) with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P seedlings (HS) with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments, grown for 530 cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3 replications.

4.2.2.c. Seed phytate-P hydrolysis

Before germination, the LS and HS seeds had 1.8 mg g-1 DW and 2.7 mg g-1 DW phytate-P,

respectively. The phytate-P was mainly localized in the scutellum rather than in the endosperm

(79% w/w in LS scutellum, vs. 91% w/w in HS scutellum) and one reverse case of seed dry

biomass distribution among seed compartments (91% w/w in LS endosperm, vs. 88% w/w in HS

endosperm). Phytate-P in the scutellum and endosperm started to hydrolyze at 16 cumulated

degree days after sowing. In LS and HS seeds, a rapid hydrolysis of phytate-P reserves in

seedling scutellum was observed up to 89 cumulated degree days after sowing (Figure 4.12).

Almost 98% of phytate-P in the scutellum and endosperm was hydrolyzed at 89 cumulated

82

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degree days after sowing despite the availability of endogenous or exogenous P. The speed of

hydrolysis of phytate-P in the seed was slightly faster in LS than in HS seeds but was clearly

independent of exogenous P (Figure 4.12, Inset). The hydrolysis of phytate-P in the scutellum

and endosperm was not strongly affected by the availability of endogenous P in the seed during

germination and early growth stages.

Cumulated degree days after sowing

0 100 200 300 400 500 600

Scu

tellu

m P

hyta

te-P

(µg

P)

0

200

400

600

800

0PLSLPLSHPLS0PHS LPHS HPHS

Cumulated degree days after sowing

0 100 200 300 400 500 600

Rel

ativ

e P

hyta

te-P

0.0

0.2

0.4

0.6

0.8

1.0

Figure 4.12: Scutellum phytate-P hydrolysis (µg P) in maize seeds during germination and early growth stages. Inset, Phytate-P in the scutellum (ratio of scutellum phytate-P content to initial scutellum phytate-P content) as a function of cumulated degree days after sowing. Low endogenous seed P seeds with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P seeds with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments, grown for 530 cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3 replications.

83

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4.2.2.d. Endogenous seed P remobilization and export flux

The scutellum is the main P storing compartment of maize seed (86%; w/w) (before the

endosperm) irrespective of reserves of endogenous seed P (LS or HS seeds). The remobilization

of scutellum P reserves started at 16 cumulated degree days after sowing whereas the endosperm

P reserves started to remobilize later at 34 cumulated degree days after sowing. Remobilization

of endogenous seed P in LS and HS and export fluxes started from 16 cumulated degree days

after sowing in all exogenous P treatments (Figure 4.13). The export flux of endogenous seed P

was similar up to 89 cumulated degree days after sowing despite the availability of endogenous

or exogenous P; subsequent differences were due to initial endogenous seed P stocks.

Phosphorus exported from the seed displayed exactly the same kinetics regardless the

availability of exogenous P (Figure 4.13). The difference between LS and HS seeds reflected the

differences of initial endogenous seed P stocks.

Cumulated degree days after sowing

0 100 200 300 400 500 600

P exported from

the seed (µg P)

0

200

400

600

800

1000

0PLSLPLSHPLS0PHS LPHS HPHS

Figure 4.13: Quantity of endogenous seed P (µg P) exported from the seed to maize seedlings during germination and early growth stages. Low endogenous seed P seedlings with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P seedlings with no exogenous P (●), low exogenous P (■) and high exogenous P (▲) grown for 530 cumulated degree days after sowing. Data are means and vertical bars indicate ± SE for n = 3 replications.

84

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4.2.2.e. Exogenous P uptake by growing seedling roots

There was no significant uptake of exogenous P in the zero exogenous P treatment (0P), (Figure

4.14). No 32P activity was observed in seedling roots until 52 cumulated degree days after sowing

in either endogenous or exogenous P treatments. At 71 cumulated degree days after sowing,

significant 32P activity was observed in seedling roots in treatments with available exogenous P

despite the availability of endogenous seed P, indicating that uptake of exogenous P was already

underway, and increased thereafter (Figure 4.14). At the last sampling date, uptake of exogenous

P was slightly higher in the HS than in the LS treatment, but the difference was not statistically

significant. The uptake of exogenous seedling P was significantly affected by the availability of

exogenous P, while endogenous P in the seed had no effect on the uptake of exogenous P during

germination and early growth. The seedlings took up significantly more exogenous P in HP than

in LP.

4.2.2.f. P efflux and whole seedling P budget

The whole P budget in growing maize seedlings was calculated considering the P exported from

germinating seeds, exogenous P uptake and seedling P accumulation. In all treatments, the

amount of P that accumulated in the seedling was less than the sum of P exported from the seed

plus the P that was taken up. This result shows that a proportion of P exported from the seed was

not allocated to the growing seedling but was released outside. The P efflux started to increase

from 16 cumulated degree days after sowing with the imbibition of seeds and was higher at 52

cumulated degree days after sowing (Figure 4.15). The P efflux was 127 µg, 98 µg and 109 µg P

seedling-1 in LS seedlings whereas it was 184 µg, 181 µg and 150 µg P seedling-1 in HS seedlings

up to 52 cumulated degree days after sowing in 0P, LP and HP treatments, respectively. At 530

cumulated degree days after sowing, the P efflux was 205 µg, 189 µg and 172 µg P seedling-1 in

LS seedlings and 192 µg, 304 µg and 282 µg P seedling -1 in HS seedlings in 0P, LP and HP

treatments with available exogenous P, respectively as shown in Figure 4.16 and Figure 4.17.

Initial non phytate inorganic P was calculated in seeds based on fresh biomass, and showed that

initial concentrations of non phytate inorganic P in seeds (507 µg mL -1 and 1372 µg mL-1 in LS

and HS seeds, respectively) were much higher than the inorganic P supplied in exogenous P

treatments (3 µg mL-1 and 30 µg mL-1 in LP and HP treatments, respectively). The difference in

the concentrations of internal and external inorganic P in seeds probably resulted in the efflux of

inorganic P from seeds by diffusion to maintain homeostasis of inorganic P between the seeds

and their surroundings.

85

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Cumulated degree days after sowing

0 100 200 300 400 500 600

Exo

geno

us P

upt

ake

(µg

P)

0

100

200

300

400

500

0PLSLPLSHPLS0PHS LPHS HPHS

Figure 4.14: Exogenous phosphorus (µg P) uptake in maize seedlings during germination and early growth stages. Low endogenous seed P seedlings with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and high endogenous seed P seedlings with no exogenous P (●), low exogenous P (■) high exogenous P (▲). Data are means and vertical bars indicate ± SE for n = 3 replications.

Cumulated degree days after sowing

0 100 200 300 400 500 600

Cum

ulat

ed P

effl

ux (µ

g P

)

0

100

200

300

400

500

600

0PLSLPLSHPLS

Cumulated degree days after sowing

0 100 200 300 400 500 600

0PHSLPHSHPHS

A B

0

Figure 4.15: Phosphorus efflux (µg P) from germinating maize seeds and growing seedling roots during germination and early growth stages. A) Low endogenous seed P seedlings with no exogenous P (○), low exogenous P (□), high exogenous P (∆) and B) high endogenous seed P seedlings with no exogenous P (●), low exogenous P (■) high exogenous P (▲) treatments. Data are means and vertical bars indicate ± SE for n = 3 replications.

86

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Figure 4.16: (A-C: LS treatments) Allocation of exogenous P uptake (gray arrows on the right) calculated using 32P labeling of the nutrient solution and distribution of remobilized seed P reserves (dark arrows on the left) to seedling compartments and calculation of efflux after 530 cumulated degree days. The width of the arrows represents the quantity of P flowing toward different seedling compartments. Values inside the different compartments represent P accumulation in (+) or remobilization from (-) each compartment. P fluxes are expressed in µg P seedling-1. Data are means and vertical bars indicate ±SE for n = 3 replications.

0

+ 304 (±26)

33%

62% 67%

5%

28%

+ 21 (±2)

+ 7 (±1)

+ 1 (±0)

+ 13 (±2)

Exogenous P uptake

P efflux: 189 µg P seedling-1

LP*LS

- 493 (±9)

Remobilised P

+ 86 (±1)

+ 15 (±2)

+ 203 (±2)

Seedling P + 325 (±27)

Seed P + 14 (±3)

Leaves + 216 (±32)

C+M + 16 (±2)

Roots +93 (±2)

Scutellum - 434 (±9)

Endosperm - 58 (±0)

94%

94%

92%

Exogenous P

6%

6%

8%

5%

0

+ 312 (±25)

32%

64% 69%

5%

26%

+ 268 (±8)

+ 85 (±5)

+ 10 (±0)

+ 173 (±3)

Exogenous P uptake

P efflux: 171 µg P seedling-1

HP*LS

- 485 (±16)

Remobilised P

+ 80 (±5)

+ 16 (±1)

+ 216 (±14)

Seedling P + 582 (±29)

Seed P + 22 (±3)

Leaves + 389 (±15)

C+M + 27 (±1)

Roots +166 (±14)

Scutellum - 431 (±10)

Endosperm - 53 (±4)

56%

59%

48%

Exogenous P

44%

37%

52%

4%

+ 267 (±10)

P efflux = 205 µg P seedling-1

OP*LS

- 471 (±16)

Remobilised P

+ 79 (±6)

+ 21 (±8)

+ 167 (±10)

Seedling P + 267 (±10)

Seed P + 35 (±11)

Leaves + 167 (±10)

C+M + 21 (±8)

Roots + 79 (±6)

Scutellum - 417 (±17)

Endosperm - 54 (±1)

63%

8%

29%

A B C

87

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Figure 4.17: (A-C: HS treatments). Allocation of exogenous P uptake (gray arrows on the right) calculated using 32P labeling of the nutrient solution and distribution of remobilized seed P reserves (dark arrows on the left) to seedling compartments and calculation of efflux after 530 cumulated degree days. The width of the arrows represents the quantity of P flowing toward different seedling compartments. Values inside the different compartments represent P accumulation in (+) or remobilization from (-) each compartment. P fluxes are expressed in µg P seedling-1. Data are means and vertical bars indicate ±SE for n = 3 replications.

+ 596 (±16)

P efflux: 193 µg P seedling-1

OP*HS

- 788 (±33)

Remobilised P

+ 204 (±19)

+ 36 (±87)

+ 356 (±52)

Seedling P + 596 (±16)

Seed P + 163 (±21)

Leaves + 356 (±52)

C+M + 36 (±7)

Roots +204 (±19)

Scutellum - 749 (±18)

Endosperm - 40 (±38)

60%

6%

34%

0

+ 596 (±63)

47%

51% 53%

6%

41%

+ 41 (±8)

+ 19 (±3)

+ 1 (±0)

+ 21 (±5)

Exogenous P uptake

P efflux: 304 µg P seedling-1

LP*HS

- 899 (±12)

Remobilised P

+ 246 (±22)

+ 38 (±3)

+ 313 (±44)

Seedling P + 637 (±61)

Seed P + 53 (±8)

Leaves + 333 (±44)

C+M + 39(±3)

Roots +265 (±19)

Scutellum - 802 (±11)

Endosperm - 98 (±2)

94%

97%

93%

Exogenous P

6%

3%

7%

2%

0

+ 586 (±5)

45%

52% 52%

9%

39%

+ 373 (±68)

+ 169 (±22)

+ 10 (±1)

+ 195 (±44)

Exogenous P uptake

P efflux: 281 µg P seedling-1

HP*HS

- 867 (±32)

Remobilised P

+ 230 (±13)

+ 50 (±8)

+ 305 (±31)

Seedling P + 959 (±71)

Seed P + 85 (±17)

Leaves + 500 (±76)

C+M + 60(±7)

Roots +399 (±10)

Scutellum - 782 (±29)

Endosperm - 86 (±20)

61%

83%

58%

Exogenous P

39%

17%

42%

3%

A B C

88

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4.2.3. Discussion

4.2.3.a. Effect of endogenous and exogenous P on seed P remobilization

and seedling growth

Early seedling growth occurs at the expense of seed reserves and their allocation among different

tissues of the new seedling. As the scutellum is in close contact with the embryo (Fincher and

Stone 1986), scutellum P reserves were remobilized first while endosperm reserves remains

unchanged up to 34 cumulated degree days after sowing in all P treatments. The seed biomass

reserves displayed exactly the same remobilization kinetics irrespective of the availability of

endogenous or exogenous P. In the present study no significant effect of endogenous or

exogenous P was observed on remobilization of dry biomass reserves in the seed or on the

accumulation of dry biomass in the seedling.

Seedling growth was similar in all P treatments. This result is consistent with the fact that

the concentration of P in the seedling was higher than the level (1 mg g -1 DW) at which the

increase in leaf area and in leaf length would be impaired due to P shortage during early growth

stages (Assuero et al. 2004; Plénet et al. 2000a). Although exogenous P was absent in the 0P

treatment, the P supply from remobilization of endogenous seed P satisfied seedling P

requirements during at least 530 cumulated degree days after sowing. Despite similar seedling

growth, HP seedlings accumulated much more P than LP seedlings, clearly demonstrating luxury

P accumulation.

Phytate was found to be a stored form of P in maize seeds and was localized mainly in

the scutellum rather than in the endosperm or embryo as reported by other authors (Lorenz et al.

2007; Lott et al. 1995; Modi and Asanzi 2008; Nadeem et al. 2011; Park et al. 2006). The initial

concentration of endogenous P in the seed only slightly affected the initial distribution of phytate

between the scutellum and the endosperm. The rate of hydrolysis of seed phytate-P was not

affected by the availability of exogenous P and very slightly affected by the amount of

endogenous P (Figure 4.12 inset). This is consistent with previous results which have shown that

hydrolysis of phytate-P depends on the synthesis of phytase and on phytase activity (Laboure et

al. 1993; Wyss et al. 1999), which are controlled by seed soaking, imbibition (Centeno et al.

2001; Egli et al. 2002; Lestienne et al. 2005) and temperature (Sung et al. 2005). Inorganic

phosphate was shown to reduce phytase activity (Guardiola and Sutcliffe 1971) but the absence

of effect of exogenous P concentrations on phytate hydrolysis kinetic in our experiment is

consistent with the fact that no P transfer was observed from external solution to the seed, as

89

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confirmed by specific activity measurements (Figure 4.16 and Figure 4.17). Conversely the

temporary accumulations of non phytate P may explain slower kinetic of phytate P hydrolysis in

HS seeds.

The export flux of endogenous P in the seed in LS and HS seeds was similar up to 89

cumulated degree days after sowing irrespective of the availability of endogenous or exogenous

P (Figure 4.13). The difference in the export flux of endogenous P in LS and HS seeds was only

due to the concentration of endogenous P in the seed after 89 cumulated degree days after

sowing. Hall and Hodges (1966) suggested that the breakdown of phytate in germinating seeds

accounts primarily for the increase in inorganic P in the roots and shoot. The hydrolyzed forms

of P were temporarily stored in seeds (Nadeem et al. 2011) and were then translocated towards

growing maize seedlings. The rapid remobilization of endogenous P in the seed during early

growth corresponds to the dramatic increase in the demand for P by the seedling during periods

of rapid cell division, such as seed germination and early growth (Hegeman and Grabau 2001).

4.2.3.b. Effect of endogenous and exogenous P on uptake of exogenous P

Significant P uptake was observed in seedling roots at 71 cumulated degree days after sowing in

treatments with available exogenous P (in LP and HP exogenous P treatments). The seedling

roots started to take up exogenous P soon after the radicle emerged, in accordance with previous

results (Nadeem et al. 2011). The intensity of exogenous P uptake was mainly dependent on the

availability of exogenous P (Bhadoria et al. 2004; Elliott et al. 1984) and on the root surface area

exposed to exogenous P (Anghinoni and Barber 1980). In the 0P treatment, no significant gross

P uptake was detectable using labeling. In this treatment, as the concentration of exogenous P

was lower than the concentration at which net P influx ceases (e.g. Cmin~0.04 – 4 µM), P efflux

from roots may have occurred (Anghinoni and Barber 1980; Bhadoria et al. 2004). Because of

higher concentrations of exogenous P (1000 µM P) in the HP treatment, exogenous P uptake was

higher than in the LP treatment (Figure 4.14). In HP and LP exogenous treatments, similar P

absorption fluxes were observed in LS and HS seedlings, although concentrations of P were

higher in HS seedlings than in LS seedlings (Figure 4.14). There was no negative effect of the

concentration of P in the seedling on the intensity of absorption of exogenous P. This result

supports the conclusion that the demand for P by the seedlings was fully satisfied during

germination and early growth in LP and HP treatments.

90

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4.2.3.c. Whole seedling P budget

By comparing accumulated P in the seedling and export of P from the seed plus uptake of

exogenous P, we demonstrated that a significant amount of P was lost via efflux. Losses of P

reached 40%, 37% and 33% in LS seedlings and 20%, 32% and 30% of initial endogenous seed

P in HS seedlings in the 0P, LP and HP exogenous P treatments, respectively. Lestienne et al.

(2005) showed that 21% of initial seed phytate was lost when whole maize seeds were soaked

for 24 hours, which released inorganic P from the seeds. The amount of P efflux depended on

initial concentration of endogenous P in the seed and occurred mainly during the first 52

cumulated degree days after sowing. This result suggests that P efflux from seeds occurs during

imbibition and germination, as seedlings have small root systems. Bewley (1997) suggested that

the influx of water into cells of dry seeds during imbibition results in temporary disturbance of

the structure, particularly that of membranes, leading to immediate and rapid leakage of solutes

and low molecular weight metabolites into the surrounding imbibition solution. The structural

disturbances associated with seed imbibition combined with high release of inorganic P due to

phytate hydrolysis during germination may contribute to P release into the external medium.

As soon as the seedlings started to accumulate biomass after leaf emergence, the P efflux

decreased, suggesting allocation of inorganic P towards seedling organs. P efflux is a component

of net P uptake in whole plants (Elliott et al. 1984) and is at least partially under metabolic

control. P efflux from roots is part of the mechanism whereby plants maintain a P balance

(Bieleski and Ferguson 1983). P releases due to phytate hydrolysis and to the export of inorganic

P from the seed were greater than seedling P requirements, resulting in losses of P from seeds.

Given that ratios of internal to external concentrations of inorganic P ranged from 16 to 457, the

diffusion process may cause loss of endogenous P from seeds. The period of P losses from

germinating seeds and growing seedling roots was similar in LS and HS seedlings despite the

availability of exogenous P, as already reported by Elliott et al. (1984).

Up to 52 cumulated degree days after sowing, remobilization of endogenous seed P

satisfied seedling P requirements in all exogenous P treatments. Similar results were reported by

Barry and Miller (1989) and Nadeem et al. (2011). From 71 cumulated degree days after sowing,

both sources of P (including endogenous and exogenous P) started to concomitantly fulfill

seedling P requirements, whereas only endogenous seed P reserves supported seedling growth in

the treatment with no exogenous P (0P). The seedling P originating from endogenous or

exogenous P sources was largely translocated towards seedling leaves rather than seedling roots

91

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as already explained in Nadeem et al. (2011). This high translocation rate suggests high P

requirements by seedling leaves during early growth.

Further research is needed to improve our understanding of the remobilization of P in the

seed and its allocation towards the seedling. Our results suggest that seed P remobilization is

closely related to germination processes independently of both seed P content and external P

availability. Consequently, we need to study how external factors controlling germination (i.e.

water availability and temperature) affect both seed P remobilization and seedling P

requirements. Seedling P requirements during early growth stages also need to be characterized

for better prediction of how long seed P remobilization -including seed P release into the external

medium- is able to sustain the seedling growth.

4.2.3.d. What explains early P deficiency in maize often reported in the

literature?

Early symptoms of P deficiency have often been reported in the literature (Colomb et al.

2000; Grant et al. 2005; Grant et al. 2001; Plénet et al. 2000b; Rodriguez et al. 1998) and may be

due to low soil P and environmental conditions like cool temperatures that slow down enzyme

activity associated with anabolic metabolism, including phytase activity, as reported by Modi

and Asanzi (2008). The study results suggest that the hydrolysis of seed P reserves started soon

after imbibition. The seed phytate hydrolysis and remobilization of seed P reserves was not

influenced significantly by exogenous or endogenous P availabilities during germination and

four weeks of early growth. However a significant loss in P was observed via efflux, mainly

from germinating maize seeds. Moreover, the loss of P was independent of exogenous P

availability. On the whole, these results suggest that although hydrolysis of seed phytate-P is not

a limiting step to providing P to the growing seedling, the rapid hydrolysis of phytate favors P

losses probably by diffusion during germination. This may explain the often reported P

deficiencies in maize seedlings during germination and early stages, especially in low P soils

where root uptake is limited by exogenous P availability. An early increase in root length enables

the seedlings to explore a greater soil volume and to access more exogenous P in the soil (Goss

et al. 1993). Under low soil P availability, the early root growth enabled by hydrolysis of seed P

reserves or increased root growth associated with high seed P content may be insufficient to

overcome the limitation of soil P supply to the roots, especially when there was a significant P

loss by P efflux from germinating seeds.

92

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4.3. Modelling of seed P reserves remobilization and exogenous P

uptake

Mathematical modelling has been used as a powerful research tool in many fields of scientific

activities. A model is usually a simplification of the real system designed to be more convenient

to work with. The essential characteristics of the real system should appear in the model. It

should therefore resemble the system and reproduce its dynamic behaviour (Thornley and

Johnson 1990). Modelling has been applied to a wide range of agronomic and plant

physiological processes (Brunel et al. 2009; Escobar-Gutierrez et al. 1998; Mollier et al. 2008;

Thornley and Johnson 1990). During the last four decades, several mathematical models

simulating the P uptake by roots from soil have been developed but to our knowledge, the

modelling approach has not been used in studies of remobilization of seed P reserves and

exogenous P uptake during germination and early growth stages in maize seedlings.

Our objective was to develop a model that represents the growing maize seedling which

acts as a whole system where P can flow between different compartments of the system. During

germination and early growth, the seedling acts as sink whereas seed P reserves and exogenous P

as source for seedling P demand. The whole modelled system is composed on 3 main

compartments namely i) seed P reserves (mainly in the form of phytate-P and non phytate-P)

which hydrolyse during germination, ii) a growing seedling, composed on root and shoot, iii) the

availability of exogenous P in nutrient solution and 2 main forms of P: phytate P and non

phytate-P, which is readily available for seedling use (Figure 4.18). The modelling of seed P

reserves remobilization and exogenous P uptake implies considering and integrating the

processes of seed phytate hydrolysis, P export from seed to growing seedlings as non phytate-P

and the uptake of exogenous P by developing seedling roots during germination and early

growth stages. The main features of this model are: i) the seedling system and ii) the working of

each compartment within this system. The P fluxes between different compartments of system

were expressed in µg P seedling-1 day-1. The objective of this modelling approach is to build a

mechanistic and dynamic model that would realistically describe the hydrolysis of seed phytate

reserves in germinating seeds and the uptake of exogenous P by seedling roots during

germination and early growth stages.

93

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Seedling

EndospermPhytate-P

ScutellumPhytate-P

SeedNon phytate-P

P loss

Phytate hydrolysis

Seed

RootDWP

Seedling P

ShootDWP

P remobilization

P uptake

Seedling

EndospermPhytate-P

ScutellumPhytate-P

SeedNon phytate-P

EndospermPhytate-P

ScutellumPhytate-P

SeedNon phytate-P

P loss

Phytate hydrolysisPhytate

hydrolysis

Seed

RootDWP

Seedling P

ShootDWP

P remobilization

P uptakeP uptake

Figure 4.18: Flow diagram of main processes that determine P dynamics in maize seed during germination and early growth. Arrows indicate

the P fluxes between different seed, seedling and exogenous P uptake.

94

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The model consists of five modules closely connected. The first one deals with the

hydrolysis of phytate reserves in seed compartments. The second and third modules describe the

seedling growth and seedling P demand considering the root-shoot growth. The fourth module

deals with the availability of exogenous P in nutrient solution and uptake by growing seedling

roots. The fifth module deals with effective P fluxes and total seedling P balance. The five

modules are integrated to simulate seed phytate-P hydrolysis, exogenous P uptake and seedling P

accumulation according to initial seed P reserves and exogenous P availabilities during

germination and 4 weeks of early growth.

The phytate hydrolysis and exogenous P uptake model was developed for the simulation

of seed phytate hydrolysis and exogenous P uptake using the software ModelMaker (Cherwell

Scientific Publishing Limited, Oxford). The software provides programming tools denominated

with the terms: “compartments,” “variables,” “flows,” “influences,” and “list of parameters”.

“Compartments” can be used to simulate changes in quantity of phytate or P and different P flow

“F” in seed and seedlings. The values in the “list of parameters” are available for the

parameterization, which means that they can be automatically varied in a desired range. For full

description of the software and its documentation, see Walker and Crout (1997). The Figure 4.19

shows a description of phytate-P hydrolysis and exogenous P uptake model in germinating maize

seeds.

95

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Figure 4.19: Graphical display of the model of P dynamic in maize seed during germination and

early growth build with ModelMaker software.

4.3.1. Seed phytate hydrolysis module

We have shown that in maize seed phytate-P reserves are mainly localized in scutellum (86%)

and remaining in endosperm regardless of initial seed P reserves. The phytate hydrolysis model

was designed to test the hypothesis that there was no effect of exogenous P availabilities on

phytate hydrolysis in scutellum and endosperm. The seed imbibition caused a slow hydrolysis of

phytate followed by a rapid hydrolysis and the phytate-P reserves reached a minimal value close

to zero. A logistic model including an initial “acceleration” of hydrolysis rate was used to

simulate seed P reserves according to initial seed P reserves and a constant hydrolysis rate.

We have considered separately endosperm and scutellum with same equations. The time

course of scutellum and endosperm phytate hydrolysis during germination and early growth was

fitted to a decreasing logistic curve whose differential equations can be written:

96

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( )

−××−=

EndokPhytP

PhytPEndoadt

PhytPd EndoEndo

Endo

_1_

Equation 4-6

( )

−××−=

ScutkPhytP

PhytPScutadt

PhytPd ScutScut

Scut

_1_

Equation 4-7

Where Equation 4-6 represents the rate of phytate hydrolysis in endosperm while Equation 4-7

indicates the scutellum phytate hydrolysis rate, respectively. The PhytPEndo and PhytPScut indicate

the instantaneous values of phytate-P in endosperm and scutellum in maize seeds, respectively.

The initial values of phytate stock are different in endosperm and scutellum among LS

and HS seeds. The parameters k_Endo and k_Scut represents the values of initial quantity of

phytate in endosperm and scutellum, respectively in both LS and HS seeds. The parameters

a_Endo and a_Scut are the rate of phytate hydrolysis in endosperm and scutellum, respectively.

The measured data on HPHS seedling treatment were selected to estimate the parameters

a_Endo and a_Scut, respectively (Figure 4.20). The values of parameter (K) for LS and HS seeds

are given in Table 4.3.

0

100

200

300

400

500

600

700

800

0 100 200 300 400 500 600Cumulated degree days after sowing

Phy

tate

-P (µ

g se

ed-1

)

Observed_Scutellum

Observed_Endosperm

Adjusted_Scutellum_HPHS

Adjusted_Endosperm_HPHS

Figure 4.20: Observed and modelled scutellum (●) and endosperm (▲) phytate-P hydrolysis in

scutellum and endosperm of maize seeds (HPHS) during germination and early growth stages

(R² = 0.974).

97

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4.3.2. Seedling growth module

Our results showed no significant effect of endogenous or exogenous P treatments on early

seedling growth. As soon as the radicle emerged from germinating seeds, the seedlings start to

gather biomass. The shoot and root biomass showed a linear relationship with growth period in

all the P treatments during this whole growth period of 4 weeks. By considering the linear

growth curves of shoot and root, their respective growth rate can be written as Equation 4-8 and

Equation 4-9 respectively.

ShootDWadt

dDWShoot _=

Equation 4-8

RootDWadt

dDWRoot _=

Equation 4-9

The a_ShootDW and a_RootDW represents the shoot and root growth rate in g day-1. As

no significant effect of P treatments was observed on seedling growth; therefore the parameters

of HPHS seedling treatment were kept constant for all the remaining treatments for simulation

and their values are given in the Table 4.3.

4.3.3. Seedling P demand module

As seedling growth phenomenon progressed, we observed a decrease in seedling P

concentrations. This pattern of decrease in P concentration is similar to that what observed in

case of N by (Justes et al. 1994). We observed that P was not limiting in HPHS treatment,

consequently we used P dilution curve of HPHS treatment to predict the seedling P demand. The

shoot or the root P demand was calculated considering the relationship (exponential) between

shoot or root P concentration and shoot or root dry biomass accumulation as shown in Figure

4.21. The total seedling P demand is the sums of seedling shoot and roots P demands;

Seedling P demand = Shoot P demand + Root P demand

Equation 4-10

The P concentration in crops has been related to the biomass according to the general

equation:

98

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bWaWP −×=

Equation 4-11

Where W is the amount dry matter (g) accumulation in shoot or roots and P is the

concentrations (µg g-1) of phosphorus in shoot or roots.

Shoot P concentrations and shoot biomass

y = 3.3134x-0.2383

R2 = 0.8714

0

2

4

6

8

10

12

14

0.00 0.02 0.04 0.06 0.08 0.10

Shoot biomass (g seedling-1)

Sho

ot P

con

(mg

g-1)

Figure 4.21: Observed leaf P concentrations (●) in HPHS seedlings and dilution P curve

obtained by non-linear fitting in HPHS seedlings during germination and early growth stages.

The dilution law expressed in Equation 4-11 corresponds to the existence of an allometric

relation between accumulated P and accumulated dry matter in shoots or roots, accounting for

the following equation:( )bWaP −×= 1

Equation 4-12

Where a indicates the amount of accumulated P in seedling shoot or roots while (1-b) shows the

allometric ratio between P accumulated and dry matter accumulation in shoot or roots. Since the

derivation of Equation 4-12 yields:

( )dt

dWWbadtdP b−−= 1

Equation 4-13

99

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Where dtdP

represents the P accumulation rate in seedling shoot or roots, while dt

dWshows the

growth rate of seedling shoot or roots. The values of parameter a and b are giving in Table 4.3

and we used the parameters of HPHS for all other treatments for model simulation.

4.3.4. Exogenous P uptake by roots module

The results showed that seedlings start uptake of exogenous P soon after the radicle emergence

and we observed that seedling root growth was a linear function of the root length (cm) when

drawn against root dry weight (g). Using the equation as mentioned by Claassen and Barber

(1977), the P influx can be written as:

−−

=12

1

2

12luxinf RLRL

RLRL

Ln

1t2tUU

P

Equation 4-14

Where U is the amount of P uptake by seedling roots at time t, whereas RL is the seedling root

length and subscripts refer to the time 1 and 2. By using the above equation we can write:

RLbrateuptake eaRL

dtdPP ×−××==

Equation 4-15

The Equation 4-15 represents the P uptake rate, where a and b refers to the coefficient of

relationship (exponential) between P influx and root length as shown in Figure 4.22 for HPLS

and HPHS seedlings. The values of the coefficients for LP and HP seedlings in available

exogenous P treatments are given in Table 4.3.

100

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P influx and seedling root length

y = 0.160365e-0.002089x

R2 = 0.802709

y = 0.1744e-0.0044x

R2 = 0.4493

0.00

0.05

0.10

0.15

0.20

0.25

0.30

0.35

0 100 200 300 400 500 600 700

Root length (cm seedling-1)

P in

flux

(µg

P c

m-1

day

-1)

HPHSHPLSExponentiel (HPHS)Exponentiel (HPLS)

Figure 4.22: Relationship between seedling root P influx and seedling root lengths (HPLS and

HPHS seedlings) in maize seedlings. HPHS seedlings (▲) and HPLS seedlings (∆) and non

linear fitting curve (—) of HPHS and HPLS (– –).

4.3.5. Effective P fluxes and total P balance module

During germination and early growth, the seedling P demand could be satisfied by

remobilization of seed non phytate-P reserves and exogenous P uptake. We considered the two

cases where if the seedling P demand is less than the seedling exogenous P uptake and

remobilization of seed non phytate-P reserves than seed P export will be equal to:

Seed P export = Seedling P demand – exogenous P uptake

Equation 4-16

In the second case if the seedling P demand is higher than the seedling exogenous P

uptake and remobilization of non phytate-P reserves in seed, than

Seedling accumulation = P uptake + available non phytate-P from seed

Equation 4-17

The total seedling P budget was calculated in all P treatments considering the available

non phytate-P reserves in seeds, the exogenous P uptake and P loss from germinating seeds, as

already shown in previous chapter. A significant quantity of P was lost from germinating seeds

101

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during early growth stages. The Equation 4-18 shows the quantity of P loss from germinating

seeds, where Emax is the maximum quantity of P loss from the seed at time t, while Km is the

time when the Emax value is ½. The values of Emax and Km for LS and HS seeds are giving in

Table 4.3.

+

×=tk

tEPlossm

max

Equation 4-18

102

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Table 4.3: Different variables and parameters of maize seed phytate-P hydrolysis and exogenous P uptake during germination and early growth stages.

Symbol Variable or parameter with units Value SourceLS

seedlingsHS

seedlingsa_ShootDWT_ini_ShootDW

a_RootDWT_ini_RootDW

Shoot growth rate (g day-1)Time when shoot start to gather biomass (days)Root growth rate (g day-1)Time when roots start to gather biomass (days)

0.00341.853

0.00411.8048

FittedFittedFitted

Fitted

Ini_non_PhytEndo

PhytPEndo_ini

Ini_non_PhytScut

PhytPScut_ini

Initial non-phytate P in endosperm (µg seedling-1)Initial phytate P in endosperm (µg seedling-1)Initial non-phytate P in scutellum (µg seedling-1)Initial phytate P in scutellum (µg seedling-1)

0

153

24

413

0

167

126

693

Observed

Observed

Observed

Observed

a_Shoot_P

b_Shoot

a_Root_P

b_Root

Amount of P accumulated in shoot (µg seedling-1)Ratio between P and DW accumulation in shootAmount of P accumulated in root (µg seedling-1)Ratio between P and DW accumulation in root

3.3134

0.2383

1.65

0.3248

Fitted

FittedFitted

Fitted

a_Endo

K_Endoa_ScutK_Scut

Rate of phytate P hydrolysis in endosperm (µg day-1)Maximum phytate P in endosperm (µg seedling-1)Rate of phytate P hydrolysis in scutellum (µg day-1)Maximum phytate P in scutellum (µg seedling-1)

168

543

0.859

174

0.851

732

Fitted

Fitted

Fitted

Fitted

Emaxkm

Maximum export P from seed (µg seed-1)Time to reach Emax at ½ value

193

2.51

321

2.58

Fitted

FittedLP

TreatmentHP

Treatment

a_Uptb_Upt

Coefficients of relationship b/w P influx and root length

0.01204-0.00225

0.1557-0.0027

FittedFitted

103

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4.4. Model output

4.4.1. Seed phytate hydrolysis

The time courses of predicted seed phytate-P hydrolysis in LS and HS seed during germination

and early growth are shown in Figure 4.23. As we observed no significant effect of exogenous P

availabilities (0P, LP and HP) on seed phytate hydrolysis, therefore we applied the parameters of

phytate-P hydrolysis rate (a_Endo and a_Scut) of HPHS seeds to all the remaining treatments for

simulation of observed values of phytate-P at each seedling harvest, whereas the maximum

initial values (K) were of respective seed P reserves for LS and HS seeds. The model provides a

good simulation prediction of seed phytate-P hydrolysis in scutellum and endosperm in both LS

and HS seeds, although the initial seed phytate-P reserves vary between LS and HS seeds. For

each LS and HS seeds, the fitted values of initial phytate-P stock (K_Endo and K_Scut) are giving in

Table 4.3.

0

100

200

300

400

500

600

700

800

900

1000

0 100 200 300 400 500 600

Cumulated degree days after sowing

Phy

tate

-P (µ

g se

ed-1

)

0PLS

LPLS

HPLS

OPHS

LPHS

HPHS

Figure 4.23: Time courses of modelled phytate-P hydrolysis (µg seed-1) in LS and HS seeds

treated with three exogenous P availabilities (0P, LP and HP) during germination and early

growth stages.

104

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4.4.2. Seed non phytate-P

With the imbibition of maize seeds, the stored phytate-P starts to hydrolyse. The results of

experiments 1 and 2 showed that the hydrolyzed forms of phytate-P are temporarily stored in

seeds before translocation towards growing seedlings during germination and early growth

stages. The Figure 4.24 shows the modelled changes in non phytate-P in seeds treated with three

exogenous P availabilities (0P, LP, HP) during germination and early growth stages.

0

50

100

150

200

250

300

350

400

450

500

0 100 200 300 400 500 600

Cumulated degree days after sowing

Non

phy

tate

-P (µ

g P

see

d-1)

0PLS

LPLS

HPLS

0PHS

LPHS

HPHS

Figure 4.24: Modelled changes in non phytate-P (µg seed-1) in LS and HS maize seeds during

germination and early growth stages.

Before germination, there was a low quantity of non phytate-P in both LS and HS seeds.

The quantity of non phytate-P starts to increase as soon as the phytate starts to hydrolyse during

germination process. In experiment 2, we observed that phytate-P in the scutellum and

endosperm started to hydrolyze at 16 cumulated degree days after sowing. In LS and HS seeds, a

sharp increase in hydrolysis of phytate-P reserves in seedling scutellum was observed up to 89

cumulated degree days after sowing (Figure 4.12). These results are consistent with that

maximum phytate hydrolysis was observed on 89 cumulated degree days after sowing in

germinating seeds regardless of exogenous P treatments (as shown in Figure 4.12). The modelled

non phytate-P of HS seeds is almost double than the LS seeds, which is consistent with the

results that initial seed P reserves are almost double in HS seeds as compared to LS seeds. From

89 cumulated degree days after sowing, the quantity of non phytate-P seeds starts to decrease in

seeds, corresponding to the translocation towards newly growing seedlings. The predicted non

105

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phytate-P in HPHS seeds showed that seed non phytate-P was over predicted as compared to the

other treatments. The non phytate-P was translocated towards newly growing seedling earlier in

LS seeds as compared to HS seeds due the initial difference in seed P reserves (Figure 4.24).

Overall the model predicts well both the initial increase in non phytate-P quantity in both LS and

HS seeds during germination and early growth stages of maize and the decrease in non phytate-P

in seed when the seedling P demand increased.

4.4.3. Seedling P demand and seedling P accumulation

The Figure 4.25 (A and B) shows the simulated seedling P demand expressed as daily amount of

P required to fulfil seedling P requirement and the effective seedling P accumulation rate in

maize seedlings during early growth stages for LS and HS treatments. The seedling P demand

was similar in all LS and HS seedlings treated with different exogenous P availabilities. The

seedling P demand was fulfilled in all treatments till 199 cumulated degree days after sowing in

LS seedlings (Figure 4.25 A). As soon as the seed P reserves were exhausted after 199

cumulated degree days after sowing, the seedling P accumulation was observed only in HP

treatment where 78% of the effective P accumulation was observed from exogenous P, while a

very small fraction (8%) in LP treatment. Being rich in endogenous seed P reserves, HS seedling

P demand was overlapped by the effective seedling P accumulation rate till 382 cumulated

degree days after sowing in all exogenous P treatments (Figure 4.25 B) and afterward its only

exogenous P from which the seedling accumulate P to fulfil their demand.

0

20

40

60

80

100

120

0 100 200 300 400 500 600

Cumulated degree days after sowing

See

dlin

g P

dem

and

and

effe

ctiv

e se

edlin

g

P a

ccum

ulat

ion

rate

(µg

day-1

)

Seedling P accum_0PLS

Seedling P demand_0PLSSeedling P accum_LPLS

Seedling P demand_LPLSSeedling P accum_HPLS

Seedling P demand_HPLS

A

0

20

40

60

80

100

120

0 100 200 300 400 500 600

Cumulated degree days after sowing

See

dlin

g P

dem

and

and

effe

ctiv

e se

edlin

g

P a

ccum

ulat

ion

rate

(µg

day-1

) Seedling P accum_0PHSSeedling P demand_0PHSSeedling P accum_LPHSSeedling P demand_LPHSSeedling P accum_HPHSSeedling P demand_HPHS

B

Figure 4.25: Seedling P demand and effective seedling P accumulation rate (µg day-1) in

growing maize seedlings during germination and early growth stages. A. Seedling P demand and

seedling P accumulation in LS seedlings treated with three exogenous P availabilities (0P, LP

HP), Right. HS seedlings treated with three exogenous P availabilities (0P, LP HP).

106

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Consequently, the model predicted that seedling P concentration was firstly reduced in 0PLS and

LPLS and later for 0PHS and LPHS as compared to HP treatments (Figure 4.26). The modelled

and observed seedling P concentrations on 530 cumulated degree days after sowing in growing

maize seedlings treated with three exogenous P treatments, was shown in Figure 4.27. We

observed high seedling P concentrations in HP treatments as compared to 0P or LP in both LS

and HS seedlings. The model over predicted the seedling P concentrations in LS seedlings

whereas in HS seedlings, it seems very close to the observed values.

0

4

8

12

16

20

0 100 200 300 400 500 600

Cumulated degree days after sowing

See

dlin

g P

con

cent

ratio

n (µ

g g-1

) 0PLSLPLSHPLS0PHSLPHSHPHS

Figure 4.26: Time courses of modelled seedling P concentrations (µg g-1 DW) in LS and HS

seedlings treated with three exogenous P treatments (0P, LP, HP) during germination and early

growth stages.

0.0

0.5

1.01.5

2.0

2.5

3.0

3.54.0

4.5

5.0

0P LP HP 0P LP HP

LS LS LS HS HS HS

See

dlin

g P

con

cent

ratio

n (m

g g-1

)

Observed_seedling_Pc

Modelled_seedling_Pc

Figure 4.27: Observed and modelled seedling P concentrations (mg g-1 DW) in growing maize

seedlings on 530 cumulated degree days after sowing.

107

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4.4.4. Seed P export and root P uptake

The modelled seedling P originated from endogenous seed P reserve remobilization and

exogenous P uptake during germination and early growth stages is shown in Figure 4.28 (A-D).

The seed P reserves remobilization remains a major source of seedling P in both LS and HS

seedlings regardless of exogenous P availabilities. During the early five days after sowing, the

remobilization flux has much importance as seedlings are fully dependent on seed P reserves in

all P treatments.

0

100

200

300

400

500

600

700

800

900

1000

0 100 200 300 400 500 600

Cumulated degree days after sowing

P (µ

g se

edlin

g-1)

Seedling_P_HPHS

Uptake_P_HPHS

Seed_P_HPHS

A

0

100

200

300

400

500

600

700

800

900

1000

0 100 200 300 400 500 600

Cumulated degree days after sowing

P (µ

g se

edlin

g-1)

Seedling_P_LPHS

Uptake_P_LPHS

Seed_P_LPHS

B

0

100

200

300

400

500

600

700

800

900

1000

0 100 200 300 400 500 600

Cumulated degree days after sowing

P (µ

g se

edlin

g-1)

Seedling_P_HPLS

Uptake_P_HPLS

Seed_P_HPLS

C

0

100

200

300

400

500

600

700

800

900

1000

0 100 200 300 400 500 600

Cumulated degree days after sowing

P (µ

g se

edlin

g-1)

Seedling_P_LPLS

Uptake P

Seed_P_LPLS

D

Figure 4.28: Modelled seedling P accumulation (µg seedling-1) originated from endogenous seed

P reserves and exogenous P uptake in growing maize seedlings during germination and early

growth stages. HS seedling treated with HP and LP exogenous P availabilities (A and B), LS

seedlings treated with HP and LP exogenous P availabilities (C and D).

The Figure 4.29 shows a maximum seed P export in both LS and HS seeds on 34

cumulated degree days after sowing and decrease thereafter regardless of exogenous P

treatments. The effective ratio of seedling P accumulation and seedling P demand shows that

seedling P demand was fully satisfied till 199 cumulated degree days after sowing in 0PLS and

108

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LPLS seedlings whereas till 309 cumulated degree days after sowing in HPLS seedlings. After

this period it is the exogenous P which fulfils the seedling P requirements in available P

treatments.

0

20

40

60

80

100

120

0 100 200 300 400 500 600

Cumulated degree days after sowing

See

d P

exp

ort r

ate

(µg

seed

-1 d

ay-1

) 0PHS

LPHS

HPHS

0PLS

LPLS

HPLS

Figure 4.29: Time courses of seed P export rate (µg seed-1 day-1) in LS (dashed lines) and HS

(solid lines) seeds treated with three exogenous P treatments (0P, LP, HP) during germination

and early growth stages.

The Figure 4.30 (A) shows the P uptake in LS seedlings treated with LP and HP exogenous P

treatments. The model over predicts the exogenous P uptake than the observed values in LP and

HP exogenous P treatments, while the Figure 4.30 (B) shows that the model predicts accurately

the exogenous P uptake in HS seedlings.

0

100

200

300

400

500

0 100 200 300 400 500 600

Cumulated degree days after sowing

P u

ptak

e (µ

g P

see

dlin

g-1)

Mod_LPLS Obs_LPLS

Mod_HPLS Obs_HPLS

A

0

100

200

300

400

500

0 100 200 300 400 500 600

Cumulated degree days after sowing

P u

ptak

e (µ

g P

see

dlin

g-1)

Mod_LPHS Obs_LPHS

Mod_HPHS Obs_HPHS

B

Figure 4.30: Time courses of observed (Obs) and modelled (Mod) exogenous P uptake in LS

(A) and HS (B) seedlings treated with two exogenous P availabilities during germination and

early growth stages in maize.

109

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4.4.5. Seed P efflux

The modelled seed P efflux in LS and HS seeds treated with three exogenous P availabilities (0P,

LP and H) was shown in Figure 4.31. The model predicts well the seed P efflux during

germination and early growth of maize (Figure 4.15). The seed P efflux start to increase from

very first day after sowing of seeds. From 89 cumulated degree days after sowing the seed P

efflux remains almost similar, as the seed P was being exported towards seedlings and the

quantity of P remaining in seeds decreased. The more seed P efflux was observed in HS seeds as

compared to LS seeds during germination.

0

50

100

150

200

250

300

350

0 100 200 300 400 500 600

Cumulated degree days after sowing

See

d P

effl

ux (µ

g se

ed-1

)

0PLS 0PHSLPLS LPHSHPLS HPHS

Figure 4.31: Time courses of modelled seed P efflux (µg seed-1) in LS (dashed lines) and HS

(solid lines) seed treated with three exogenous P treatments (0P, LP, HP) during germination and

early growth stages.

110

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4.5. Discussion

The modelling is a useful approach to understand the actual processes. The phytate hydrolysis

and exogenous P uptake model gives an overall understanding of seed P reserves hydrolysis and

exogenous P uptake during germination and early growth stages in maize seedlings. The phytate

reserves in seed go under hydrolysis with the imbibition. The maximum phytate hydrolysis was

observed during the first week of maize seedling growth. This hydrolysis caused an increase in

non phytate-P in seeds. Similar results were reported by Centeno et al. (2001) in rye and barley.

He showed that the phytate (IP6) hydrolysis caused an increase of IP5, IP4 and IP3 intermediate

products during germination which ultimately produce phosphate for newly growing seedlings.

The rapid increase in non phytate-P quantity in seeds during the first week caused the P loss by

efflux from seeds. This happens due to the low seedling biomass development with less P need

in first week and the non phytate-P lost by efflux. As soon as the seedlings developed their shoot

and root compartments the P efflux starts to reduce after first week as observed and predicted in

the simulation model. The model gives a better understanding of increase in the quantity of non

phytate-P and P efflux in both LS and HS seeds.

The seedling P demand in LS and HS seedlings was fulfilled only by seed P reserves

remobilization in 0P exogenous P treatments, whereas the exogenous P supports the seedlings to

fulfil their P demand in available exogenous P treatments (LP, HP), although the model over

predict the exogenous P uptake in LS seedlings. The developed model can predict the seedling P

demand, seed P reserves remobilization and exogenous P uptake in germinating maize seedlings

during early growth stages.

The present model predicts the dynamics of seed P reserves and seedling P considering the

hypothesis that there was no interaction between phytate P hydrolysis kinetic and P uptake by

roots. However, we could not simulate the P efflux from germinating maize seeds. We used the

Michaelis Menten equation function to predict the P efflux on a mechanistic way. A further step

would be to couple the proposed model with model of seedling germination and early growth

considering the environmental variables (Temperature, humidity, radiation etc).

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5. GENERAL DISCUSSION AND PROSPECTIVES

Phosphorus is an integral part of living cells and involved in all energy requiring processes like

cell division, energy transfer and photosynthesis. Therefore, P nutrition has a critical importance

in all growing crops during germination and early growth stages. Many previous studies have

shown an early P limitation on early maize crop growth and final yield. Keeping in view the

importance of early maize growth stages, we studied the remobilization of seed P reserves and

exogenous P uptake and their effect on each other during early seedling growth.

We studied two main compartments of maize seed namely endosperm and scutellum. The

maize endosperm is a starchy structure and study results have shown that endosperm contains

almost 87% of C and 77% of N of total seed C and N reserves, respectively. The scutellum is

relatively a small seed compartment; it enclosed the embryo and located on dorsal side of the

endosperm. We have shown that although scutellum is the small part of seed (containing only

13% of seed biomass), it contains almost 86% of total seed phosphorus reserves. The major part

of the maize seed P reserves either in endosperm or scutellum, is in the form of phytate. Phytate

is a complex salt of myo-inositol hexakisphosphate containing six phosphate molecules along

with minerals like calcium, magnesium and zinc etc. The results have shown that the initial seed

P status have no significant effect on the partitioning of phytate among seed scutellum and

endosperm.

During germination, as soon as the seeds are imbibed, the scutellum and endosperm

phytate reserves were started to hydrolyze by the activity of phytase. The phytate hydrolysis

provides inorganic P for the growing seedlings. The study results have shown that the hydrolysis

of phytate was almost not influenced by endogenous seed P reserves and not influenced by

exogenous P availabilities during germination and early growth stages. The remobilization of

seed P reserves displayed similar remobilization kinetics as that of C and N during germination

and early seedling growth, although they are localized in different compartments of maize seeds.

During the first two days of early maize growth, it is the scutellum P reserves which fulfil the

seedling P requirements, being in close contact with embryo. The results of both experiments

have shown that seed phytate hydrolysis was not a limiting step in seedling P requirements.

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As soon as the seedling radicle was emerged on 2nd day after germination, the seedling P

accumulation was begun. The endogenous seed P reserves or exogenous P availabilities have no

significant effect on seedling radicle emergence. Four day after germination, the maize seedling

roots are able to uptake the exogenous P as shown in both experimental studies. The intensity of

exogenous P uptake by growing seedling roots was mainly determined by the availability of

exogenous P, while it did not depend upon seedling P status or initial endogenous seed P

reserves. Both processes, the exogenous P uptake and endogenous seed P remobilization seem to

be controlled independently during maize germination and early growth stages. A major part of

seedling P, originated from endogenous or exogenous P sources was translocated towards

seedling leaves rather than seedling roots. This suggests a very high seedling leaf P demand

during four weeks of early growth rather than seedling roots. Similarly to C, we can clearly

define the three different stages of P acquisition by newly growing maize seedlings depending

upon the endogenous seed P and exogenous P availabilities. The four day old maize seedlings

are completely made up of endogenous seed P defining it as heterotrophic stages for P

acquisition. Both sources of P including endogenous and exogenous P, provides P to the growing

seedling from 4th to 15th days after germination (transitional stage for P), and from 15 th day after

sowing its only exogenous P which fulfils the seedling P requirements (autotrophic stage for P).

Modelling seed Preserves remobilization and exogenous P uptake under the assumption that P

phytate P hydrolysis and root P uptake are independent process correctly reproduce experimental

data.

From the agronomical point of view, the rapid hydrolysis of phytate in maize seeds

during the first three four days after germination was shown to favour the inorganic P increase in

seed, whereas the four day old seedlings have not much vegetative part during this growth

period. On the whole, these results suggest that although hydrolysis of seed phytate is not a

limiting step for providing P to the growing seedlings, but this rapid hydrolysis may favours the

P losses probably by diffusion during germination. The P losses by efflux were independent of

exogenous P availabilities; therefore the idea of increasing endogenous seed P reserves for better

seedling establishment seems not to be very effective, whereas the study results have shown that

availability of exogenous P in the root zone is very important during germination and early

growth stages. These P losses from germinating maize seeds may explain the early seedling P

deficiencies during germination and early growth.

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Further steps would be to identify external factors (temperature, water content …) which

are likely to affect seed P reserves remobilization during germination and early growth, to

include them in the proposed model and to test this model on independent data set. Because of it

unexpected importance, the mechanism underlying P efflux from the seed and the factors

controlling it also need further studies. We also suggest to test the main findings of this work and

the proposed model on other species. Eventually the proposed model might be included in a

general P uptake model (FUSSIM-P-Maize) to better understand the relationships between early

P nutrition, crop growth and yield.

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Urbano G, Lopez-Jurado M, Aranda P, Vidai-Valverde C, Tenorio E and Porres J 2000 The role of phytic acid in legumes: antinutrient or beneficial function? J Physiol Biochem 56, 283-294.

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APPENDIX

Appendix I: Prélèvement et conservation de grains de maïs avec des teneurs en phosphore différenciées

UMR-TCEM

PROTOCOLE EXPERIMENTAL Réf : PX032Version : 1date : 15 octobre 2008PRÉLÈVEMENT ET CONSERVATION DE GRAINS DE MAIS AVEC DES

TENEURS EN P DIFFÉRENTIEES

Objet et domaine d’application

Récolte d'épi de maïs avec un gradient de teneur en phosphore afin de faire une étude préalable

sur les méthodes de dosage des différentes formes de P contenu dans les graines de maïs et sur la

mise au point d'un dispositif expérimental permettant le suivi de la remobilisation du P de la

graine lors de la germination (Sujet de thèse de Nadeem Muhammad 2008-2011).

Liste de diffusion et si nécessaire niveau de confidentialité

Diffusion interne INRA

Hygiène et sécurité

Précautions habituelles en expérimentation au champ (vêtements sécurité, travail en binôme si

travail en hauteur, etc …)

Principe de la méthode

Récolte d'épis sur les différentes parcelles de l'essai longue durée P au champ sur le site de

Pierroton. Les parcelles sont sélectionnées en fonction des teneurs en P des grains des épis de

façon à disposer d'une gamme de teneur en P. Les semences utilisées en 2005 avaient une teneur

en P moyenne de 3.2 mg P /g. La gamme des teneurs en P des grains produits sur le dispositif

s'étend de 1.3 à 3.2 mg P / g. Pour cette étude, nous souhaitons disposer de trois niveaux de P

dans les graines couvrant cette gamme. A partir des analyses les plus récentes disponibles (2004)

les parcelles suivantes ont été sélectionnées (voir localisation sur le plan ci-dessous):

Low P Intermediate P High PP0.5 Bloc 3 P1 Bloc 1 P4 B11.34 mg P/g 2.2 mg P/g 2.67 mg P/g

Diffusion : Contrôlée Interne TCEMRédacteur : Vérificateur Approbation : Nom : Mollier A Nom : Denoroy P. Nom : PELLERIN S Visa :Fonction : CR Fonction : ingénieur Fonction : Directeur Le : 5/01/09

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Prélever 30 épis par parcelle de façon aléatoire au moment de la récolte (20 octobre 2008) en

dehors des rangs destinés à l'estimation du rendement des parcelles.

Conserver dans une poche en indiquant le nom de la parcelle

Identifier 5 épis par traitement et les peser. Ces épis seront utilisés pour suivre l'évolution du

séchage des épis par des pesées bihebdomadaires.

Enlever les spathes et écarter les épis montrant des attaques d'insectes ou de champignons.

Mettre les épis à sécher à l'air libre jusqu'à un poids constant. Conserver les épis à l'abri de

l'humidité et des ravageurs sans mélanger les traitements (ne pas égrainer les épis).

cases

PLAN ESSAI P PIERROTON lysi-métriques

QuantitéForage P kg/ha

En 2003 P0.5 11.05 cabaneP0.75 16.58

P1 22.10P2 44.20P4 88.40 Nord

piste

Distances 67.20 m

54.40 m6.60 m 12.80 25.60 38.40 51.20 22.50 m

75 m 38 m

P0.75 P4 P1 P0.5 P2

BLOC 4 18 m

1 m allée56 m 19 m

P1 P0.5 P4 P2 P0.75

BLOC 3 18 m

FOS

1 m allée 0 m S37 m E

G PU P2 P1 P0.75 P4 a P0.5 II s ND BLOC 2 s 18 m RA a AG gE e

R 1 m alléeA r 18 mM oP P4 P2 P0.5 P0.75 u P1E BLOC 1 e

18 m

borne 6.60 m12.80 m 12.80 m 12.80 m 12.80 m 3.20 12.80 m 22.91 m

8 rangs 16 rangs 16 rangs 16 rangs 16 rangs 4 r. 16 rangs 28 rangs

18 m surface 1 parcelle = 230.40 m²surface de l'essai = 4608 m²

bornepiste

BOIS de PINS

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Appendix II: Dosage des phytates par chromatographie ionique en milieu HCl 0.65M. Mode opératoire MO-ANA-65

TCEM

MODE OPÉRATOIRE Réf : MO-ANA-065

Version : 0

Date : 30/11/2010DOSAGE DES PHYTATES PAR CHROMATOGRAPHIE IONIQUE EN MILIEU

HCL 0.65M

Objet et domaine d’application

Le présent mode opératoire a pour but de décrire le processus de dosage des phytates (myo-

inositol 1-, 2-, 3-, 4-, 5-, 6-hexakisphosphate) par la technique de séparation des pics en

chromatographie ionique. Ce dosage est réalisé sur des compartiments de grains de mais après

une extraction par le réactif de Wade (modification de la couleur du complexe Fe- acide

sulfosalicylique en présence de phytates).

Hygiène et sécurité

Pas de mesures particulières

Principe de la méthode

La mesure des phytates est déterminée par chromatographie ionique (IC). Le principe est basé

sur un échange d’ions sur une colonne composée d’une résine chargée soit positivement (pour

séparer des anions), soit négativement (pour séparer des cations). Les ions sont entrainés par une

phase mobile (éluent) et séparés par l’action de la phase stationnaire (colonne). La détection est

réalisée par une cellule de conductivité.

Figure 1. Principe de la chromatographie ionique

Diffusion : Contrôlée Interne TCEMRédacteur Vérificateur Approbation : Nom : VIVES.A Nom : MOLLIER.A – MOREL.C Nom : PELLERIN. S Visa :Fonction: Technicien Fonction : Chercheurs Fonction : Directeur Le :17/12/2010

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Matériels nécessaires

- Chromatographie ionique Dionex modèle ICS 2000

- Passeur d’échantillon Dionex modèle AS50

- Système d’eau ultra pure Elga

- Vial 2 ml de type 2-SV

Réactifs (chimiques et biologiques)

- Cartouche d’éluent d’hydroxyde de potassium EGC III KOH P/N 074532

- HCl : préparer 200 ml HCl à 0.65 N (2.4%) soit 10,8 ml dans 200 ml

- Acide phytique dodecasodium salt (PADDSS ; Sigma P-8810)

- Eau ultra-pure

Contraintes de la méthode

- Pas de contraintes particulières

Contenu du mode opératoire

Préparation des réactifs

Solution Standard de Phytates (maïs):

- Dissoudre 100 mg de PADDSS (Sigma P-8810) dans 10 ml d’HCL 0.65N.

- Préparer la gamme de standard Phytates d’après le tableau ci-dessous.

- Disposer ces solutions dans des vials de 2 ml de type 2-SV

Dosage en chromatographie ionique.

L'échantillon à analyser (volume de 20 µL) est injecté, par l’intermédiaire du passeur

d’échantillon AS50, en tête de la pré-colonne AG11- 4mm P/N 044078 dont le rôle est de

préserver la colonne de séparation de tout contaminant provenant des échantillons. La migration

des espèces se fait selon leur affinité (capacité de l'ion à être plus ou moins retenu) pour la résine.

PhytatesStandard HCl 0.65N Stock (10 mg / ml) Concentration.

―――μl――― μg ml

1 1000 0 02 980 20 2003 960 40 4004 920 80 8005 900 100 10006 800 200 2000

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La migration est assurée par l'éluant (EGC III KOH P/N 074532) injecté par la pompe (à un débit

variant de 0.8 ml/min).

Figure 2. Injection de l’échantillon

Création du gradient d’éluent: démarrer à moins trois minutes à 12 mM de KOH pour arriver à

90 mM au bout de quarante cinq minutes.

Ensuite, stabiliser à 12 mM pendant deux minutes avant de passer à l’échantillon suivant :

Figure 3. Analyse de l’échantillon

La séparation est effectuée sur la colonne échangeuse d’ions AS11- 4 mm P/N 044076. Pour ce

dosage, la température de la colonne doit être de 30°C. Pour augmenter la sensibilité et abaisser

le seuil de détection des éléments, un système de suppression est utilisé. Son rôle est de

supprimer la conductivité de l'éluant, afin que le pic de conductivité de l'élément à analyser soit

le plus net possible. Le suppresseur utilisé est le modèle Dionex ASRS 300 – 4mm P/N 064554

avec une intensité réglée à 179 mA.

La détection est assurée par la cellule de conductivité DS6 P/N 057985 à une température de

30°C.

Pour le dosage des phytates en milieu HCl 0.65N, le seuil de détection est de 0.116 mg/L et le

seuil de quantification 0.262 mg/L

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0.0 5.0 10.0 15.0 20.0 25.0 30.0 35.0 40.0 47.0-5.0

0.0

5.0

10.0

15.0

20.0

25.0 1Phytate_08_06_10 #5 [modified by User] ST 1000 ECD_1µS

min

1 - 0.4842 - 2.0873 - 2.2444 - 2.5975 - 2.7446 - 3.4607 - 3.894

8 - 6.777

9 - 8.534 10 - 13.28711 - 13.650 12 - 20.66413 - 23.09014 - 23.69015 - 24.264

16 - Phytates - 26.710

17 - 32.19418 - 35.28019 - 37.744

Figure 4. Séparation des pics des phytates avec la colonne AS-11

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Programme phytates chroméléon

Sampler.AcquireExclusiveAccessPressure.LowerLimit = 200 [psi]Pressure.UpperLimit = 3000 [psi]%A.Equate = « KOH »CR_TC= OnFlush Volume = 100Wait FlushStateNeedleHeight 1 [mm]CutSegmentVolume 10 [µl]SyringeSpeed = 4CycleTime = 0 [mn]WaitForTemperature= 30.0 [°C]Pump-ECD.Data_Collection_Rate 5.0 [hz]CellTemperature.Nominale= 30 [°C]ColumnTemperature.Nominale= 30 [°C]Suppressor_Type= ASRS_4mm; Pump_ECD.Carbonate = 0.0; Pump_ECD.Bicarbonate = 0.0; Pump_ECD.Hydroxyde = 90.0; Pump_ECD.Tetraborate = 0.0; Pump_ECD.Other eluent = 0.0; Pump_ECD.Recommanded Current 179Suppressor_Current 179 [mA]ECD_Total.Step = 0.20 [s]ECD_Total.Average off

Wait SampleReadyFlow 0.80 [ml/mn]

-3.000 Concentration 12.00 [mM]Curve 50.000 Pump_ECD.AutozeoConcentration 12.00 [mM]Curve 5LoadWait CycleTimeStateInjectWait InjectStateECD_1.AcqOnECD_Total.AcqOnSampler.ReleaseExclusive.AccessConcentration 12.00 [mM]Curve 545.000 Concentration 90.00 [mM]Curve 547.000 ECD_1.AcqOnECD_Total.AcqOnSampler.ReleaseExclusive.AccessConcentration 12.00 [mM]Curve 5End

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Appendix III: Nadeem M, Mollier A, Morel C, Vives A, Prud’homme L, Pellerin S (2011) Relative contribution of seed phosphorus reserves and exogenous phosphorus uptake to maize (Zea mays L.) nutrition during early growth stages. Plant Soil 346 (1-2):231-244. doi:10.1007/s11104-011-0814-y

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REMOBILIZATION OF SEED PHOSPHORUS RESERVES AND EXOGENOUS

PHOSPHORUS UPTAKE DURING GERMINATION AND EARLY GROWTH STAGES

OF MAIZE (Zea mays L.)

Key-words: maize, germination, phosphorus, phytate, remobilization, P-uptake, isotope, ecophysiology, mineral nutrition.

REMOBILISATION DES RESERVES EN PHOSPHORE DU GRAIN ET

PRELEVEMENT EXOGENE PENDANT LE GERMINATION ET GERMINATION ET

LA CROISSANCE JUVENILE DU MAIS (Zea mays L.)

Mots-clés: maïs, germination, phosphore, phytate, remobilisation, prélèvement de P, isotope, écophysiologie, nutrition minérale.

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