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Soil	nitrogen	fluxes	and	root	uptake	in	the	boreal	
forest:	key	processes	to	plant	nitrogen	nutri9on	
Olusegun	Ayodeji	Oyewole	
December	11,	2015
Introduction P. I P. III P. IV ConclusionsP. II
N2 , Nox, N2ONH3
Dissolved
organic N
NH4
+ NO3
-
Nitrification
Denitrification
Immobilization
Volatilization
Complex
Organic N
Leaching
Leaching
Leaching
Immobilization
Dead
Microbes & exoenzymes
N deposition
N fixation
Ammonification
Litter
inputs
Microbes &
exoenzymes
Microbes
The soil nitrogen Cycle
Introduction P. I P. III P. IV ConclusionsP. II
Transport	of	soil	nutrients	to	the	roots	
High	concentra>on Low	concentra>on	
Diffusion	
Mass	flow
Introduction P. I P. III P. IV ConclusionsP. II
Transpira>on	
Diffusion	
Mass	flow	
Transport	of	soil	nutrients	to	the	roots	
Mass	flow	+	Diffusion	Diffusion
Importance	of	diffusion	and	mass	flow	to	plant	N	
nutri9on?	
§ 	Roles	of	diffusion	and	mass	flow	in	plant	nutri>on	is	controversial	
Introduction P. I P. III P. IV ConclusionsP. II
Transpira>on	
Diffusion	
Mass	flow
§ 	Disturbance	to	soil	system	
	
§ Methodological	challenges	
	
Tradi9onal	methods	for	es9ma9ng	soil	N
Lysimeter	 Soil	extrac>on	
Introduction P. I P. III P. IV ConclusionsP. II
Microdialysis	technique	
Probe	
Microdialysis	set	up	
Introduction P. I P. III P. IV ConclusionsP. II
Introduction P. I P. III P. IV ConclusionsP. II
Limita9ons	of	microdialysis	technique	
§ 	Microdialysis	probe	lacks	most	func>ons	of	plant	root	
	
§ 	Underes>ma>on	of	the	availability	of	some	amino	acids	
	
§ 	Less	suitable	for	determining	soil	N	concentra>ons
P. IIntroduction P. III P. IV ConclusionsP. II
N	fluxes	in	fer9lized	and	unfer9lized	forest	soils	at	
the	onset	of	the	growing	season
P. IIntroduction P. III P. IV ConclusionsP. II
Induced	diffusive	flux	of	N	in	boreal	forest	soils
P. IIntroduction P. III P. IV ConclusionsP. II
Effect	of	forest	fer9liza9on	on	soil	N	flux	
Control	plot	 Control	plot	
Fer>lized	plot	 Fer>lized	plot	
Addi>on	of	10	l	
m-2	water	
Addi>on	of	1	g			
N	l-1	KNO3	
Addi>on	of	10	l	
m-2	water	
Addi>on	of	1	g			
N	l-1	KNO3
P. IIntroduction P. III P. IV ConclusionsP. II
Nitrate application
Dynamics	of	added	NO3
-	in	control	and	fer9lized	
forest	soils
P. IIntroduction P. III P. IV ConclusionsP. II
Conclusions	
§ 	Amino	acids	dominated	N	fluxes	in	the	boreal	forest	soil	
	
§ 	Nitrate	addi>on	increases	NO3
-	flux,	but	more	pronounced	in	
the	fer>lized	soil
Introduction P. I P. III P. IV ConclusionsP. II
The	limi9ng	step	for	plant	soil	N	acquisi9on?	
Diffusive	flux	to	the	roots	 Root	uptake	rate
Introduction P. I P. III P. IV ConclusionsP. II
Diffusive	flux	and	root	uptake	rates
Introduction P. I P. III P. IV ConclusionsP. II
Conclusions	
§ 	Plant	capacity	for	N	uptake	greater	than	diffusive		flux	in	the	
range	of	6	–	27	
		
§ Diffusive	flux	is	the	rate	limi>ng	step	to	plant	N	acquisi>on
Introduction P. I P. III P. IV ConclusionsP. II
Can	microdialysis	be	use	to	es9mate	mass	flow	of	N?
Mass	flow
Introduction P. I P. III P. IV ConclusionsP. II
Dextran	40	caused	mass	flow	of	water	into	the	
microdialysis	system
Introduction P. I P. III P. IV ConclusionsP. II
Soil	par>cles	
Soil	water	
Dissolved	
compounds	
Microdialysis	
membrane	
Dextran	
+	soil	water	
+	compounds	
20	%	(w/v)	
Dextran	40	
solu>on	
Diffusion	
Mass	flow	
Es9ma9on	of	diffusion	and	mass	flow	of	soil	N
Mass	flow	+	Diffusion
Introduction P. I P. III P. IV ConclusionsP. II
Mass	flow	increased	N	fluxes	in	standard	solu9on	
and	soil	
Solu>on	 Soil
Conclusions	
Mass	flow	+	Diffusion	Diffusion
§ 	 Using	 various	 osmo>c	 poten>als	 induced	 mass	 flow	 could	 be	
achieved	
§ 	Mass	flow	has	direct	and	indirect	effects	on	plant	N	nutri>on	
§ 	Transpira>on-induced	mass	flow	
may	be	a	driver	for	N	acquisi>on	
Introduction P. I P. III P. IV ConclusionsP. II
Transpiration
Introduction P. I P. III P. IV ConclusionsP. II
Field	es9ma9on	of	mass	flow	and	diffusion
• 	Microdialysis	was	used	to	es>mate	fluxes	of	organic	and	
inorganic	N
	Nutrient-poor	Pine	forest	 Nutrient-rich	Spruce	forest
Introduction P. I P. III P. IV ConclusionsP. II
Mass	flow	increased	flux	rates	of	inorganic	and	total	
amino	acids	
	Nutrient-poor	Pine	forest	soil	
Diffusion	Diffusion	+	Mass	flow	
Nutrient-rich	Spruce	forest	soil	
Diffusion	 Diffusion	+	Mass	flow
Introduction P. I P. III P. IV ConclusionsP. II
Mass	flow	changes	the	composi9on	of	the	N	fluxes	
Scots pine forest soil
Diffusion Diffusion + Mass flow
NO3
-
TotAA TotAA
NO3
-
NO3
-
TotAA
NO3
-
TotAA
Norway spruce forest soil
Diffusion Diffusion + Mass flow
Introduction P. I P. III P. IV ConclusionsP. II
Conclusions	
Results	from	microdialysis	suggest	that:	
• Mass	flow	increases	total	N	flux	and	may	play	an	important	
role	in	plant	N	acquisi>on	
• N	flux	composi>on	changes	with	high	propor>on	of	NO3
-	
Mass	flow	+	Diffusion	Diffusion
Transpira>on
Introduction P. I P. III P. IV ConclusionsP. II
Take	Home	Message	
§ 	Microdialysis	technique	provides	new	insights	to	understanding	
intrinsic	processes	in	plant	N	nutri>on	
	
§ 	The	induced	diffusive	flux	of	N	could	be	the	rate	limi>ng	step	in	
plant	N	acquisi>on	
	
§ 	Transpira>onally-induced	mass	flow	may	play	an	important	role	
in	plant	N	nutri>on
Introduction P. I P. III P. IV ConclusionsP. II
50	µM	
June	 September	
N-forms	 Control	 Fer>lized	 Control	 Fer>lized	
Arginine	 ∞	 ∞	 ∞	 ∞	
Glycine	 14	 12	 63	 31	
NH4
+	 27	 6	 290	 40	
NO3
-	 16	 6	 16	 0.3	
Root	uptake	rates	exceed	induce	diffusive	flux	rates
Introduction P. I P. III P. IV ConclusionsP. II
Mass	flow	increased	N	supply	to	Dialysis	probe	in	soil
Mass	flow	increased	N	supply	to	Dialysis	probe	
in	standard	solu9on

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Olusegun_Presentation

  • 2. Introduction P. I P. III P. IV ConclusionsP. II N2 , Nox, N2ONH3 Dissolved organic N NH4 + NO3 - Nitrification Denitrification Immobilization Volatilization Complex Organic N Leaching Leaching Leaching Immobilization Dead Microbes & exoenzymes N deposition N fixation Ammonification Litter inputs Microbes & exoenzymes Microbes The soil nitrogen Cycle
  • 3. Introduction P. I P. III P. IV ConclusionsP. II Transport of soil nutrients to the roots High concentra>on Low concentra>on Diffusion Mass flow
  • 4. Introduction P. I P. III P. IV ConclusionsP. II Transpira>on Diffusion Mass flow Transport of soil nutrients to the roots Mass flow + Diffusion Diffusion
  • 8. Introduction P. I P. III P. IV ConclusionsP. II Limita9ons of microdialysis technique §  Microdialysis probe lacks most func>ons of plant root §  Underes>ma>on of the availability of some amino acids §  Less suitable for determining soil N concentra>ons
  • 9. P. IIntroduction P. III P. IV ConclusionsP. II N fluxes in fer9lized and unfer9lized forest soils at the onset of the growing season
  • 10. P. IIntroduction P. III P. IV ConclusionsP. II Induced diffusive flux of N in boreal forest soils
  • 11. P. IIntroduction P. III P. IV ConclusionsP. II Effect of forest fer9liza9on on soil N flux Control plot Control plot Fer>lized plot Fer>lized plot Addi>on of 10 l m-2 water Addi>on of 1 g N l-1 KNO3 Addi>on of 10 l m-2 water Addi>on of 1 g N l-1 KNO3
  • 12. P. IIntroduction P. III P. IV ConclusionsP. II Nitrate application Dynamics of added NO3 - in control and fer9lized forest soils
  • 13. P. IIntroduction P. III P. IV ConclusionsP. II Conclusions §  Amino acids dominated N fluxes in the boreal forest soil §  Nitrate addi>on increases NO3 - flux, but more pronounced in the fer>lized soil
  • 14. Introduction P. I P. III P. IV ConclusionsP. II The limi9ng step for plant soil N acquisi9on? Diffusive flux to the roots Root uptake rate
  • 15. Introduction P. I P. III P. IV ConclusionsP. II Diffusive flux and root uptake rates
  • 16. Introduction P. I P. III P. IV ConclusionsP. II Conclusions §  Plant capacity for N uptake greater than diffusive flux in the range of 6 – 27 § Diffusive flux is the rate limi>ng step to plant N acquisi>on
  • 17. Introduction P. I P. III P. IV ConclusionsP. II Can microdialysis be use to es9mate mass flow of N? Mass flow
  • 18. Introduction P. I P. III P. IV ConclusionsP. II Dextran 40 caused mass flow of water into the microdialysis system
  • 19. Introduction P. I P. III P. IV ConclusionsP. II Soil par>cles Soil water Dissolved compounds Microdialysis membrane Dextran + soil water + compounds 20 % (w/v) Dextran 40 solu>on Diffusion Mass flow Es9ma9on of diffusion and mass flow of soil N Mass flow + Diffusion
  • 20. Introduction P. I P. III P. IV ConclusionsP. II Mass flow increased N fluxes in standard solu9on and soil Solu>on Soil
  • 21. Conclusions Mass flow + Diffusion Diffusion §  Using various osmo>c poten>als induced mass flow could be achieved §  Mass flow has direct and indirect effects on plant N nutri>on §  Transpira>on-induced mass flow may be a driver for N acquisi>on Introduction P. I P. III P. IV ConclusionsP. II Transpiration
  • 22. Introduction P. I P. III P. IV ConclusionsP. II Field es9ma9on of mass flow and diffusion •  Microdialysis was used to es>mate fluxes of organic and inorganic N Nutrient-poor Pine forest Nutrient-rich Spruce forest
  • 23. Introduction P. I P. III P. IV ConclusionsP. II Mass flow increased flux rates of inorganic and total amino acids Nutrient-poor Pine forest soil Diffusion Diffusion + Mass flow Nutrient-rich Spruce forest soil Diffusion Diffusion + Mass flow
  • 24. Introduction P. I P. III P. IV ConclusionsP. II Mass flow changes the composi9on of the N fluxes Scots pine forest soil Diffusion Diffusion + Mass flow NO3 - TotAA TotAA NO3 - NO3 - TotAA NO3 - TotAA Norway spruce forest soil Diffusion Diffusion + Mass flow
  • 25. Introduction P. I P. III P. IV ConclusionsP. II Conclusions Results from microdialysis suggest that: • Mass flow increases total N flux and may play an important role in plant N acquisi>on • N flux composi>on changes with high propor>on of NO3 - Mass flow + Diffusion Diffusion Transpira>on
  • 26. Introduction P. I P. III P. IV ConclusionsP. II Take Home Message §  Microdialysis technique provides new insights to understanding intrinsic processes in plant N nutri>on §  The induced diffusive flux of N could be the rate limi>ng step in plant N acquisi>on §  Transpira>onally-induced mass flow may play an important role in plant N nutri>on
  • 27.
  • 28. Introduction P. I P. III P. IV ConclusionsP. II 50 µM June September N-forms Control Fer>lized Control Fer>lized Arginine ∞ ∞ ∞ ∞ Glycine 14 12 63 31 NH4 + 27 6 290 40 NO3 - 16 6 16 0.3 Root uptake rates exceed induce diffusive flux rates
  • 29. Introduction P. I P. III P. IV ConclusionsP. II Mass flow increased N supply to Dialysis probe in soil