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PHOSPHORUS CYCLING IN
GRAZED , STEEP HILL COUNTRY
A thesis presented in par tial fulfilment of the requirements for the degree o f Doc tor o f P hilosophy in So il Science
a t Massey University
Allan Gilber t Gillingham 1 9 78
( i )
MS TRACT
Measurements of P uptake by pas ture and P return in pas ture l i tt er and dung \\rere made on two intensively gra zed , nor th- and south-facing
paddocks in steep hil l country with soils of moderate to high P s ta tus . Both P uptake and mor e particularly the return of P in dung by grazing sheep , was high on the rela tively level campsite areas but decreased
sharply as ground surface slope increased . A high graz ing pressure ens ur ed that P return via l itter was low relative to plant up take .
A net P balance d erived for d iffering paddock s trata showed a large net annual gain of P on c amps ites ( 50 . 1 and 1 1 9 . 8 kg ha -1 on north and south aspec ts , respec tively) but a cons id erab l e net P lo ss from bo th 25 s lopes 0
( 19 . 5 and 10 . 0 kg ha- 1on nor th and south aspec ts , respec tively) a nd 4 5°
- 1
slopes ( 1 5 . 3 and 1 3 . 8 kg ha o n nor th and south aspec ts , r espec tively) . Dif f erences bet\veen aspects in the net P balanc e could b e expla ined by the overall differenc e in the topography of the two paddocks as it a f f ec ted relative ca mping and graz ing pressure on each s tratum .
Sub s equ ent simula tion s tudies \vere conduc ted using a ma thema tical mod el based on f ield da ta f rom the nor th-aspec t paddock and val ida ted agains t resul ts from the south-aspec t paddock . Resul ts o btained f rom the mod el indica ted that the quantity of P transf er f rom slopes inc r ea s ed at a
grea ter than direc tly propor t ionate rate a s s tocking rate increas ed and was a:ls o d irec tly related to pas ture P content .
Determina tion o f relative roo t ac tivity using 32 P sho wed tha t
approximately 90% o f P up take by pas ture in spring occurred from wi thin 7cm of the soil surface . The greater proportion of this o ccurred within the 0-3cm s oil dep th . No s ignificant P uptake occurred from depths grea t er than 30cm . Al though the extent of P uptake from 0-3cm depth soil was
(ii)
similar both upslope and dmvnslope from. a P sourc e , the d ir ec tion o f
predominant root activity a t grea ter dep ths was affec ted by the s teepness of s lope, tending to b e a t an angle between ver tical and that normal to the soil surface .
A technique was developed to charac terize shor t term plant-available P ,
. 32 33
using bo th P and P . Resul ts indicated tha t the 32P!33P ra tio o f the wat er-extrac table P f raction more closely res embl ed tha t in the plant than was the case for the O l s en P extrac t . Both ryegrass (Lolium perenne) and white clover ( Trifoliu� repens) apparently u tilized P from the same soi l pool , the measured higher'P content of ryegrass in this s tudy being due only to a more extensive· and rapidly developing roo t sys tem than that o f c lover .
The addition to soil of P extracted by wat er from l i tter , dung , and superphosphate sources showed that all forms had similar effec ts in
inc r easing the wa ter-ex trac table and Olsen P l evels in the soil . Thus i t could b e expec ted that P from these three sour c es would have a s imilar ava i lability to plants . The results of these and also P desorpt ion experiments were qualitatively similar to tho s e derived f rom a s imp l e
Langmuir model , sugges t ing that sorption and d esorption o f P in the s o il from the f ield area o c curred a t s ites on the solid phas e with predominantly uniform sorption charac t eris tic s .
Marked and largely unexplained varia tions. in s everal soil parameters monitored over a year obscured the eff ec ts of P addition as a maintenance
fer til izer applica tion and also the net P transfer by grazing animals . In this and related s i tua tions, so il P analysis may no t provide a s ensitive measure of P s tatus, excep t in the longer term . A mor e detailed examina tion
is r equired to assess the usefulness of 'routine soil P analysis of hill
(iii)
so ils for advisory purpo s es . The signif icant net P traps fer from
slopes by graz1ng animals suggests tha t the complementary roles of gra zing manag ement and fer tilizer r equirements in hill country should also b e
examined further .
ACKNOWLEDGEMENTS
I wish to express my gra ti tude to the following people :
Professor J . K . Syers for guidance, direction� and s timula tion throughout all s tages of this s tudy .
Dr . P . E . H . Gregg for many helpful discussions and comments .
Mr . R .W . Tillman for the d evelopment of computer programmes and for many valuable d iscus sions .
The several s taff from the Hill Country Sec t ion , S o il and Field Research Division, Ministry of Agriculture and Fisher ies and Wha tawhata Hill Country Research·S ta tion who assis ted with the f i eld work .
(iv)
Jan , (my wifeL for her encouragement, und ers tanding , and assistance d uring the term of this s tudy .
D ianne Syers for the excell ent and patient typing o f this thesis . F inally , I w ish to express my thanks to the New Zealand Minis try o f Agricul ture and Fisheries vTho granted m e leave to und er take this study .
(v)
TABLE OF CONTENTS
Page ABSTRACT • . . .
AC KNOWLEDGEMENTS iv
TABL E OF CONTENTS V
LIST OF FIGURES xi
LIST OF PLATES xiii
LIST O F TABLES
S ECTION 1 INTRODUCTION
S ECTION 2 REVIill� OF LITE��TURE
2 . 1
2 . 2
Soil P
2 . 1 . 1 Forms of soil P . 2 . 1 . 2 The P sorption proc ess 2 . 1 . 3 Exchangeab le P
2 . 1 . 4 Assessment of plant-availabl e P . 2 . 1 . 4 . 1 Iso tope methods
2 . 1 . 4 . 2 Non-iso tope methods Plant p . . . . .
2 . 2 . 1 Fac tors affecting plant intake of p
2 . 2 . 2 Fac tors affec t ing the rate of p uptake ---
2 . 3 2 . 4
2 . 2 . 3 Plant P content . . . .
2 . 2 .lf Interspec ies competitibn for Animal P Intake
P Return to Soil
2 . 4 . 1 P return via animal dung
. . . . . p
.
. .
. . .
2 . 4 . 1 . 1 Dung d is tribu tion by grazing stock 2 . 4 . 1 . 2 Dung excr eted and area covered
. . . . .
xiv
1
4 4 7 1 1 1 3 14 17 1 9 1 9 2 1 22 23 25
28 29 29
�excreti�� . • . • . • . . . • . • . . • 3 1
2 . 5
2 . 6
2 , 7
2 . 4 . 1 . 3 Dung P content . . • . 2 . 4 . 1 . 4 Rel eas e of P from dung 2 . 4 . 2 P r eturn via pas ture litter
2 . 4 . 2 . 1 Types o f lit ter 2 . 4 . 2 . 2 Plant s enesc ence
2 . 4 . 2 . 3 Release of P from l i tter Availab ility of Returned and Applied P . •
2 . 5 . 1 P f rom organic residues 2 . 5 . 2 P from fertil izer
Above Ground P Loss es
2 . 6 . 1 p los ses in animal produc ts 2 . 6 . 2 p losses by animal transfer 2 . 6 . 3 p losses in surface runoff General Conclusions . . . .
SECTION 3 .
\vater . . . .
PHOSPHORUS UPTAKE �� RETURN IN GRAZED , STEEP HILL PASTURES 3 . 1
3 . 2
Introduction . • . . . Ma terials and Methods 3 . 2 . 1 Trial site 3 . 2 . 2
3 . 2 . 3 3 . 2 . 4
3 . 2 . 5
Gra z ing management Sampling procedure Phosphorus up take .
. . . . .
3 . 2 . 4 . 1 Pas ture dry matter production 3 . 2 . 4 . 2
3 . 2 . 4 . 3
Assessment of P l imita tion to .E_?s ture dry mat ter produc tion
Pas ture P conc entration Phosphorus return .
3 . 2 . 5 . 1 To tal dung dry weight 3 . 2 . 5 . 2
3 . 2 . 5 . 3 3 . 2 . 5 . 4
Field trial dung for P analysis Dung P concentration
Total lit ter d ry weigh t 3 . 2 . 5. 5 Litter P concentra tion 3 . 2 . 6 S o il phosphorus
Page 32 34 35 36 3 7 38
42 4 3 4 6
4 9 50 5 1 5 1 5 3
55
57 57 6 1 6 1 6 1 6 1
6 2 6 3 63 64 64 65 66 6 6 6 8
(vi)
3 . 3 Results and D iscussion • . � . . . . . . . .
3 . 4
3 . 3 . 1 Phosphorus �p�ak
;
.3 . 3 . 1 . 1 Pas ture dry matter produc tion =---
3 . 3 . 1 . 2 As s essment of P l imi ta tion to pas ture growth . . . . . . •
3 . 3 . 1 . 3 Pas ture species compo s ition 3 . 3 . 1 . 4 Pas ture P conc entrat ion 3 . 3� 1 . 5 To tal P uptake by pas ture 3 . 3 . 2 Phosphorus return via dung
3 . 3 . 3
3 . 3 . 2 . 1 To tal dung dry �oJe:lgh t
3 . 3 . 2 . 2 Estimated dung dis tribution pattern 3 . 3 . 2 . 3 Dung P content . . . . •
3 . 3 . 2 . 4 To tal P return in dung Phosphorus return via pasture litter 3 . 3 . 3 . 1 To tal l i t ter dry weight 3 . 3 . 3 . 2 Litter P content
3 . 3 . 3 . 3 Total P return in l i tter 3 . 3 . 3 . 4 Es tima ted pas ture u tilization
by sheep . . . . • . 3 . 3 . 4 The phosphorus cycle
3 . 3 . 4 . 1 Annual uptake and r eturn of P 3 . 3 . 4 . 2 Seasonal uptake and return o f P 3 . 3 . 4. 3
3 . 3 . 4 . 4
Dung P and litter P rela tionships Dung P return and net P balance rela tionships . . . . • . . . • 3 . 3 . 5 Soil phosphorus . • • .
3 . 3 . 5 . 1 To tal phosphorus 3 . 3 . 5 . 2 Soil DIP
3 . 3 . 5 . 3 Soil DOP .
3 . 3 . 5 . 4 Bicarbona te-extrac table P General Discussion . • . . • • . • . • . .
SECTION 4
UPTAKE ZONES FOR PHOSPHORUS BY PASTURE ON DIFFERING S TRATA WITHIN A HILL PADDOCK
4 . 1 Introduc tion . . . . .
. . .
Page 68 68 68
7 0 7 1 7 4 7 8 7 8 78 82 8 5 94 9 6 9 6 9 8 1 0 2
104 107 107 1 10 1 1 3
1 1 6 1 2 1 1 2 1 1 2 7 1 30 1 3 0 1 34
(vii )
4 . 2
4 . 3
4 . 4
Mater ials and Methods 4 . 2 . 1 Treatmen ts . . . . 4 . 2 . 2 Isotope preparation 4 . 2 . 3 Isotope placement 4 . 2 . 4
4 . 2 . 5 4 . 2 . 6 4 . 2 . 7
Soil measurements Pas ture harves ting
3 2
Measurement of P activity Processing of results
Resul ts and Discussion
4 . 3 . 1 Sample prepara tion comparison 4 . 3 . 2 Field resul ts
4 . 3 . 2 . 1 P uptake a fter 2 da�
4 . 3 . 2 . 2 P uptake af ter 29 days General Discussion . .
SECTION 5
(viii)
Page 144 144 1 4 5 1 4 7 148 148 150 1 5 1 152 1 5 2 ;
1 54 1 56 1 56 1 6 9
THE ASS ES SMENT OF SOME P SORPTION CHARACTERISTICS OF SOILS FROM THE FIELD TRIAL AREA
5 . 1 5 . 2
5 . 3
Introduc tion
Ma terials and Methods . . . . • 5 . 2 . 1 Labora tory experiments .
5 . 2 . 2
5 . 2 . 1 . 1 Measurements of P desorption
5 . 2 . 1 . 2 Evaluation of P exchange reac tions 5 . 2 . 1 . 3 Measurements of P sorption
The Langmuir model . • . .
5 . 2 . 2 . 1 Measurements of P desorption (Langmuir
173 1 7 5 1 7 5 1 7 5 1 7 7 1 7 8 1 7 9 model) . • . . • • . . . . . . . • 180 5 . 2 . 2 . 2 Fa te o f an appli ed ' label ' (Langrnuir model) 180 5 . 2 . 2 . 3 Measurements of P sorption .
Results and Dicussion . . . . • . 5 . 3 . 1 Measurements of P desorption
5 . 3 . 1 . 1 Effec t of wa ter : soiL ratio and extrac tion period on desorption of P . • . • . . 5;3 . 1 . 2 Effect o f success ive extrac tions with
wa ter on desorption of P
18 1 1 8 1 18 1
1 8 1
184
5 . 4
5 . 3 . 1 . 3 Effec t o f antecedent .soil mois ture content on desorption of P
5 . 3 . 2 Evaluation o f P exchange reac tions
5 . 3 . 2 . 1 Fa te of appli ed carrier-fr ee 32P . 5 . 3.2 . 2 Effect o f soil P s tatus on net
sorption of appl ied carrier-free 3 2p from soil solution
5 . 3 . 3 Effec ts o f the addition to soil of P from various sources . . .
3 1
5 . 3 . 3 . 1 Changes in extract P content 5 3 3 2 eh . . . anges 1n extrac t . . 32p content General Discussion . . . .
SECTION 6
CHARACTERIZATION OF SHORT-TERM, PLANT-AVAILABLE P USING A DOUBLE LABELLING TECHNIQUE
6 . 3
6 . 4
Introduc tion . • •
Materials and Methods
6 . 2 . 1 Prepara tion of plants 6 . 2 . 2 Preparation of soil • .
6 . 2 . 3 Sampling and analysis proc edures 6 . 2 . 3.. 1
6 . 2 . 3 . 2
Soil analysis
Plant sampling and analysis Results and Discuss ion
6 . 3 . 1 6 . 3 . 2 6 . 3 . 3
3 1
Soil P l evels . . Plant 3 1P levels
32 33 .
So il and plant P : P rat1os • . General Discus s ion . . . • • . . • •
SECTION 7
SIMULATION OF "ABOVE-GROUND" COMPONENTS OF THE P CYCLE IN STEEP , GRAZED PASTURE
7 . 1 I ntroduction . • .
Pag e
1 8 8 19 1 1 9 1
1 9 5
200 200 206 208
2 13 214
216 216 217 218 218 2 2 0 2 2 0 2 2 3
2 2 7 (ix)
7 . 2
7 . 3
7.4
Materials and Method s . •
7 . 2 . 1 Effec t of s tocking ra te on the net P balance on each s tratum
7 . 2 . 2 Effec t of overall pas ture utilization level on the net P balance on each s tra tum . 7 . 2 . 3 Effec t of pas ture produc tion l evel on
the net P balance on each stratum . 7 . 2 . 4 Effec t of pas ture P content on the net P
balance on each stra tum Results and Discus s ion .
7 . 3 . 1 Mod el valida tion 7 . 3 . 2 Model manipulations •
7 . 3 . 2 . 1 Eff ec t o f s tocking ra te on the net P balance on each s tra tum .
7 . 3 . 2 . 2 Eff ec t of overall pas ture utiliza tion l evel on the net P balance on each stra tum .
7 . 3 . 2 . 3 Eff ec t o f pa s ture produc tion and P concentration level on the net P balanc e on each stra tum
General Discussion . . .
SU�1ARY AND CONCLUSIONS • B I BLIOGRAPHY .
APPENDICES . .
Page
2 2 8
2 2 9 2 30 230
23 1 2 3 1 23 1 2 3 3 233
2 3 5
2 37 237 243
2 8 1 (x)
FIGURE A
2 . 1 3 . 1 3 . 2
3 . 3
3 . 4
3.5
3.6 3 . 7
3 . 8 3 . 9 3 . 10 4 . 1 4 . 2
LIST OF FIGURES .
"
Slope : area distribution curves for the total area , for campsites and for tracks in paddocks of b o th north- and south-facing aspects . . •
Components of the P cycle in grazed , fertilized pasture . . . • . . . . • Relationship b e tween the concentration of DIP and TP in pas ture • . • . . . . Annual total P uptake by pas ture and total P return in l i t ter and dung , and net total P balance (kg ha- 1) including S tandard
Errors of es timate for each value • • . • • Rela tionship b e tween tota l P return in litter and to tal P return in dung in each s ea son
(as % of P uptake by pas ture) . . • o • • Rela tionship b ett.:reen net total P balance and total P return in dung in each s eason
(kg ha- 1) • . . . o . • • • • • • • • • o • Relationship b e tween net total P balance and to tal P return in dung in each season
(as % of total P up take by pas ture) • • . - 1
Soil total P content (� g g ) on campsites
' 1 1 p ( - 1 ) 2 5° 1
So1 tota content � g g on s opes . Soil total P content (�g g-l) on 4 5° s lopes • Soil DIP ( as % o f TP)
Ols en P (as % o f TP) •
Effec t of sample s ize on measured 32 P at
Page
285
5
7 7
108
1 1 5
1 1 7
1 20 1 2 2 123 1 2 4
• 1 28 1 3 3
three levels o f a ctivity • • . • . . • • • . . . 1 53 Lateral and vertical dis tribution o f
relative roo t a c t ivity ( % ) (Correc ted for
soil P sta tus at each d epth) • • • • 1 6 1 4.3 Lateral and vertical dis tribution of relative
root activity ( %) adj acent to s tock tracks
(Corrected for soil P s ta tus a t each dep th) • . • • • 1 6 3
(xi)
4 . 4 Relative root ac tivity at each depth for the north campsit e , nor th 25° s lopes , and north 45° slopes , and estima ted integrated relative roo t activity for each soil dep th range on nor th camps ite , north 25° slope and north 4 5°
4 . 5
5 . 1
5 . 2 5 . 3
5 . 4
5 . 5 5 . 6
5 . 7
5 . 8
5 . 9
slope . . . . . . . • .
Calcula ted mid point of la teral roo t activity distribution at each sampling depth and
derivation of the d irec tion of predominant
root ac ti vi ty on each s tra turn . . . . • • • • . . • • Effect of '"a ter : soil ratio ·and extraction
period on desorp tion of P from north 0 25 slope soil • • •
Relationship bet\veen DIP release per
extraction and cumulative total DIP releas e • Rela tionship b etween P release per
extraction at a 40 : 1 wa ter : so il ratio (Langmuir model ) . • • . • . . . • Effec t of antecedent soil mois ture on desorp tion of DIP • • . . . . • . . . Fat e o f carrier-free 32P applied to north 25° s lope soil during subs equent incubation Change in iso tope content during incuba tion of water and Olsen P extrac ts from soils of differing P s ta tus . . . . • • . . . . • . Change in isotope content (Rela tive Specific Ac tivity) during incubation of Hater and O l s en P extracts from soils o f differing P s tatus . Change in 31P content of A wa ter-extrac table P ( 10 : 1 ratio) , B Mater-extrac table P ( 40 : 1 ratio) and C Ols en P a t various t imes following add i t ion to soil of water-extractable P from superphosphate , l i tter , dung and control - nil added P . . . • . . . . . . . . . . . . . • Change in 32P content o f A water-extractabl e P
( 10 : 1 ratio ) , B water-extrac table P ( 40 : 1 ra tio) and C Ols en P at vario us times following
addition to soil of 32P-labelled '"ater
extrac table P from superphosphate , litter, dung and control - carrier. free 32p added • • •
(xii)
Page
165
167
182
185
1 8 6
1 9 0
1 9 3
1 9 6
1 9 9
20 1
207
LIST OF PLATES
PLATE 3 . 1 S tudy area paddock with a north-facing aspect • 3 . 2 S tudy area paddock with a south-facing aspec t • 3 . 3 Dung and l itter collection plo t .
Dung was collec ted from the complete ( 0 . 2 m2) plot and l i tter was collected f rom only the 8 subplo ts occupying the c entral and left side longitudinal thirds .
4 . 1 Equipment used for loading gela tin capsules with 3Zp , showing capsule
holder in posi tion on the mobile p la tform o f the modified b eam balance . .
4 . 2 Wooden template in posit ion above th e
"ho t l ine" with rods us ed to make
isotope placement holes to required dep th 4 . 3 Pasture on a 25° s lope plot prior to
harvest 29 days following isotope p lacement . Perspex sheet in pos i t ion to shield operator from the "ho t l ine" and ba ttery-powered harves t ing shears ready for use . • . •
6 . 1 Ryegrass grown in sand within nes ted pots ( lef t side) and shm.,ring root development (centre) prior to placement in contact with isotope-labelled and incubated soil
( right side) • • • • • • • . . . . . .
(xiii)
Page 58 58
6 7
1 4 6
1 4 6
1 4 9
2 1 5
TABLE 3 . 1
3 . 2
3 . 3
LIST OF TABLES
Paddock slope composition (% of to tal area per s tratum)
S easonal and annual pas ture produc tion (kgDM ha- 1 ) from each s tratum . . . • • S easonal and annual pasture produc tion from topdressed and untopdres s ed s lope s trata (kgDM ha- 1 ) . • • . . . •. •
3 . 4 Pas ture species composi t ion ( % by wt . )
3 . 5 3 . 6
3 . 7 3 . 8
3 . 9
3 . 10
3 . 1 1
in each season
Amounts of P forms in pas ture in each season S easonal and annual up take of P by
pasture on each s tratum (kg ha- l ) . Seasonal and annual deposi t ion of dung on each s tratum (kgDM ha- l)
Estima ted time required for dung f rom grazing sheep to completely cover various proportions of each s tratum . . . . • • • . • • Dry matter , TDP and TP content of who l e , undried sh eep dung from " improved" compared with
"unimproved" pas tu re . . . • • • . . • . . Amounts of P forms (f.lg g ) in var iously -1
prepared forms o f dung as determined by two methods o f analysis . . . • . • . • .
- 1 Amounts o f water-extractab le P (f.lg g )
in variously prepared forms of dung • . 3 . 1 2 Wat er-extractable P removed from oven-dried ,
crushed dung by both rep ea t ed and prolonged extrac tions • . . . .
3 . 1 3 Amounts o f P forms in dung collec ted
3 . 14 3 . 1 5
at each s tratum . . .
Seasonal and annual re turn o f P in dung to each s tratum (kgDM ha-1) . • • . • •
S ea sonal and annual pas ture lit ter accumulation on each s tratum (kgDM ha- 1 ) . • . . . • • . • •
(xiv)
Page
6 0 6 9
7 2
7 3 7 5
7 9 8 0
8 4
8 6
8 7 8 9
9 0 9 3 9 5
9 7
TABLE 3 . 1 6
3 . 1 7
3 . 1 8
3 . 19
3 . 20 3 . 2 1
3 . 22 3 . 23
4 . 1
4 . 2
4 . 3
5 . 1
Amounts of P forms in l i t ter collec ted at each season . •
Eff ec t o f sample condition on amounts of wa ter-extrac tabl e inorganic (DIP ) and organic P (DOP ) in autumn l i tt er . . . • Seasonal and annual return o f total P in litter to each s tratum (kg ha- 1 )
Es timated seasonal and annual utilization of pas ture on each s tratum by grazing sheep Seasonal to tal P net balance on each stra tum Seasonal to tal P net balance on each stratum assuming a 3-month delay in . availability of P from litter and dung (kg ha- 1 ) • . Organic ma tter content of so il on each stra tum at four sampling dates ( % by wt . ) Water-extractable organic P content of
soil on each s tratum (as % of TP) .
Mean 32P levels ( cpm) measured in \..:rhole , undried pas ture two days following iso tope placement in soil at various dep ths • • . . • • •
Relative root activity ( %) a t va rious soil depths on each stra tum es timated both with and without correc t ion for soil Olsen P values Soil charac teristics on each s tratum at trial corr�encement ( 1 3 . 9 . 76) and also soil mois ture content at f inal harves t - Nor th aspec t . . .
Effect of solution soil ra tio on extraction of P (Langmuir model) • • • . • . . • 5 . 2 To tal water extrac table P ( 1TIP) from air-dried
soil from each s tratum of the field trial area and moisture content of each soil during
5 . 3
sub sequent incuba tion .
Effect of soil P status on fate o f applied label and time required to rea ch equilibrium
(Langmuir model) . • • . • • • • • • • • . •
(xv) Page
9 9
1 0 1
1 03
1 0 5 1 1 1
1 1 2
1 26
1 3 1
1 57
1 58
1 59
1 8 3
1 8 9
1 9 7
TABLE 5 . 4
5 . 5
6 . 1
6 . 2
7 . 1
7 . 2
7 . 3
7 . 4
Effect of soil P sta tus on fate of applied P ( Langmuir model) • . . •
S ta tus o f severa l soil P fra c t ions after 53 days incuba tion both with and withou t addition of wa ter-extrac tab le P f rom pasture li tter , dung and superphospha te sources ( �g p g- 1 ) . . • • . . • • .
Soil P levels before plant P up take and so il and plant P levels af ter plant P uptake ( � g g- 1 ) . . . . . . .
32p 33p : ra tlos ln sol . . ' 1 b f e ore p.1 ant . p uptake and in soil and plant ma terial after plant uptake ( 32Pcpm : 33pcpm)
S imulated P uptake and return in paddocks on north- and south-facing aspec t s
(Sec t ion 3 ) incorpo ra ting paramet er values measured in the field . . . .
S imulated P uptake and return in paddocks of differing slope composi tion a t both full and half maximum stocking ra tes . . Simula ted P uptake and return a t maximum pasture grazing utilization l evels 65 , 70 and 55% o f pasture growth on campsites , 25° slopes and 45° slopes resp ec t ively in paddocks o f differing average slope
S imulated P uptake and return at
(i) pasture produc tion levels equivalent to 80% o f those set in Sec tion 7 . 2 . 1 and (ii) at a pasture P content o f 3500�g g- 1
using the same pasture production levels set in Section 7 . 2 . 1 . • • . • . • . . • •
(xvi)
Page
203
205
2 1 9
222
232
2 34
236
2 38