Advertisement
Advertisement

More Related Content

Similar to Opportunities for improving phosphorus-use efficiency in crop plants(20)

Advertisement

More from CIAT(20)

Advertisement

Opportunities for improving phosphorus-use efficiency in crop plants

  1. FACULTY OF SCIENCE Opportunities for improving phosphorus-use efficiency in crop plants Erik Veneklaas School of Plant Biology - UWA
  2. Perth
  3. UWA • 20000 Undergraduate students • 2000 PhD (Research) students • 1500 academic staff • Ranked 88 on the Academic Ranking of World Universities • Ranked 24 for Life and Agricultural Sciences • International collaboration School of Plant Biology • 20-25 academic staff • 110 PhD (Research) students • research strengths in terrestrial ecology, agriculture and marine science
  4. New Phytologist 195:306-320
  5. Phosphorus is an essential mineral nutrient for plants Plants contain approximately 0.1% of P 1/100 1/1000 1/1000 – 1/100,000 P cannot be substituted by any other element www.soil-net.com
  6. P in agriculture: open systems requiring large P inputs CROP residues uptake SOIL fertilizer product runoff drainage unavailable P Can we have more product with less P? Losses to the environment need to be minimized! P needs to be used more efficiently: better yield, more recycling
  7. Mohr & Evans (2013) http://www.philica.com We are running out of P reserves “Peak P” 1900 2000 2100 2200 Supply, Demand (Mt P per year) Projected P supply, using optimistic estimates of P reserves and assuming a stabilizing demand. P cannot be “produced” like N (industrially or plant-mediated).
  8. Fertilizer phosphorus will become scarce and expensive Environmental impact of P is undesirable Aim: produce more food with less P = increase P use efficiency Most food contains more P than we need. • Most P in cereal and legume grains is phytate. • Phytate cannot be used by humans and most animals, and restricts the bioavailability of Fe and Zn.
  9. PUE definitions P acquisition efficiency (= P uptake efficiency): P taken up by plant / P in soil P use efficiency (= P utilization efficiency) = PUE: dry mass production (or yield) / P taken up by the plant
  10. Crops have high P (but higher N) compared to other plants Crops are high in leaf N and P compared to non-crops Crops are high in N/P compared to non-crops with high N and P Presumably due to selection for fast growth and high N
  11. What are the main P pools? 10 8 5 3 0 0 5 10 15 P fractions concentrations (mg g-1 DW) Sum of P fractions (mg g-1 DW) Pi Nucleic acids Lipid P Ester P 1.0 0.8 0.6 0.4 0.2 0.0 <1 1-2 2-4 4-8 >8 Total P (mg g-1) fractions At high tissue P concentrations, much P is inorganic. This 5 Pi is located in 10 vacuoles and is 15 not engaged in metabolism. Sum of P fractions (mg g-1 DW) Pi Nucleic acids Lipid P Ester P Sum of P fractions (mg g-1 DW) P fraction concentration (mg g-1 DW)
  12. Where is P in plants? Inorganic phosphate (Pi) • low and well-regulated concentrations in cytoplasm • vacuole stores excess Pi, should be minimized “Ester P” •Water-soluble small molecules, e.g. sugar phosphates, ATP • Small pool, can probably not be reduced Nucleic acids • DNA and RNA Phospholipids • membranes
  13. Nucleic acid P • represents ~40% of all organic P • 85% is RNA • RNA: ~90% is ribosomal (rRNA) • Ribosomal RNA important for protein synthesis and thus growth • But rRNA and protein synthesis capacity stay very high in fully developed tissue • Functions include turnover, repair, senescence processes • Reduction of rRNA may reduce adaptability and stress tolerance?
  14. Can rRNA levels be reduced? Crops use a lot of RNA to produce proteins (more than trees) Reduction of excess protein synthesis capacity may be possible in well-managed crops Protein / RNA Algae Crops Trees
  15. Lambers et al. (2012) New Phytologist 196:1098-1108 Lipid P is mainly found in membranes Phospholipids may be substituted by sulfolipids and galactolipids (as in chloroplasts) galactolipids sulfolipids phospholipids This substitution is often found in P-starved plants Implications for membrane properties are not fully known
  16. Effects of low P are partly due to signalling, not just P deficiency Rouached et al. (2011) Plant J. 65:557-570 Lower P status without a decrease of growth rate, presumably due to lack of signalling Unlinking Pi status and signalling may enable better growth at low P
  17. Dissecting PUE PUE = biomass production per unit P per unit time X P residence time Carbon balance and the role of P in it Tissue longevity Internal recycling of P photosynthesis high P fast growth time low P slow growth
  18. Photosynthetic P-use efficiency = net photosynthesis per P present Global patterns using the “leaf economics spectrum” dataset (Wright et al. (2004) Nature 428:821-827) 1.0 0.5 0.0 -0.5 -1.0 -1.5 1.0 1.5 2.0 2.5 3.0 3.5 log [P] (mg g-1) log LMA (g m-2) 3.0 2.5 2.0 1.5 1.0 0.5 0.0 1.0 1.5 2.0 2.5 3.0 log Amass (nmol g-1 s-1) Higher Leaf Dry Mass per Area (LMA): thicker, denser leaves Longer leaf lifespan log LMA (g m-2) P concentration Photosynthesis
  19. Photosynthetic P-use efficiency: net photosynthesis per P present 3.0 2.5 2.0 1.5 1.0 0.5 0.0 1.0 1.5 2.0 2.5 3.0 log A/P (μmol g-1 s-1) log LMA (g m-2) PPUE = A / P There is no clear trend with increasing LMA There is an order-of-magnitude range at any LMA
  20. Some of the variation in A/P at a given LMA is related with [N] A/P (μmol g-1 s-1) Leaf N/P > 15 “P-limited” 129.4 Leaf N/P < 15 “N-limited” 59.3 3.0 2.5 2.0 1.5 1.0 0.5 0.0 N/P < 15 N/P > 15 1.0 1.5 2.0 2.5 3.0 log A/P (μmol g-1 s-1) log LMA (g m-2) Much higher Photosynthetic P-use Efficiency in “P-limited” than “N-limited” plants Implication for agronomy: plant production is most efficient when all resources are used optimally at all times
  21. How does this work out over the life-time of a leaf? Photosynthetic P use efficiency: Rate of (maximum) net photosynthesis per amount of P present Lifetime leaf PUE: Amount of C (or dry matter) gained per amount of P used (= P lost upon senescence) photosynthesis high P fast growth time low P slow growth
  22. Modelling of leaf lifetime PUE based on: • photosynthesis and respiration • leaf construction cost 0.12 • leaf lifespan • leaf P concentration 0.08 • P remobilization 0.04 0.00 40, 60 or 80% P remobilization 80% 40% 60% 0 200 400 600 A/P (g C mg-1 P) LMA (g m-2) Conclusions: • Lifetime leaf PUE is very similar for leaves with very different physiology and morphology • Long lifespans compensate for low photosynthetic rates • Fast growth is not incompatible with efficient P use • P remobilization is vital for high lifetime leaf PUE
  23. How do roots compare in terms of P economy? Fine root P concentrations are high, like in leaves. Fine roots have high turnover rates, like leaves. Remobilization of P in roots is similar to that in leaves (?) Variation in these traits is largely unexplored. Temperate angiosperms Temperate gymnosperms Subtropical-tropical Li et al. (2010) Funct. Ecol. 24:224-232 Gill & Jackson (2000) New Phytol. 147:13-31 Turnover (yr-1) Root diameter (mm)
  24. An extreme leaf-root contrast in PUE in a low-P environment Trait Banksia leaf Banksia cluster root [P], mg g-1 0.2 1 Life span, yr 3 0.1 P remobilisation, % 80 90 P cost, mg g-1 yr-1 0.01 1.0 P cost per unit standing crop per year may be 100X more for cluster roots than leaves
  25. From leaf to plant scale – P remobilization in growing plants Remobilization from a senescing leaf can potentially supply P for a growing leaf Relative growth rate (g g-1 d-1) is proportional to leaf replacement rate (d-1) = 1/(leaf lifespan) P P
  26. P recycling in the vegetative plant 60 50 40 30 20 10 0 remobilisation = 80% 0 10 20 30 % P from remobilisation time current cumulative Remobilization only starts contributing to P economy when there is senescing tissue Even with constant growth rate, senescence, [P] and remobilization: • % P derived from remobilization increases only slowly over time • total % P derived from remobilization for vegetative growth is considerably less than the % P remobilized from senescing biomass
  27. P recycling becomes important for later vegetative growth and grain filling Shortlived species; exponential growth followed soon by senescence Conclusions: • P remobilization can reduce dependency on soil P during later stages of crop • P remobilization during vegetative growth is more important in crops with long growing seasons and short leaf life-spans, forming dense stands 100 80 60 40 20 0 biomass produced biomass shed live biomass senesced 0 10 20 30 40 50 biomass time live total biomass time 1500 1000 500 0 P taken up P remobilised total taken up total remobilized 0 10 20 30 40 50 P time P time
  28. Transition to reproductive growth In this period 30-90% of plant P is remobilized 100 50 0 into the grain whole plant vegetative plant 0 20 40 60 80 100 P content (mg) Time after sowing (d) Plant P content (mg) Time after sowing (d) rice wheat lupin canola sunflower
  29. Redistribution of P in the plant, from germination to maturity Reducing the P flux to grain • may allow for longer use of P for photosynthesis • would help reduce P export from the field
  30. P is very efficiently remobilized from plant to grain PHI = Grain P Total P ? Grain mass Total mass N/P = 6 N/P = 12 HI = Grain is relatively enriched in P (compared to plant P and grain N). Can this be reduced, for the benefit of PUE and nutrition?
  31. [P] in grain has already been reduced through selection 0.6 0.4 0.2 0 Domestication of wheat Historic wheat cultivars diploid tetraploid hexaploid P concentration in grain (%) high P low P Calderini et al. (1995) Ann. Bot. 76:315-322 Batten et al. (1986) Ann. Bot. 58:49-59 Mainly due to ‘dilution’ (more starch). Further progress may be possible; physiological limits are unknown but links with N and C are likely.
  32. “Ideotype” for efficient use of P Fast and early P uptake and efficient internal recycling of P • P will be in plant for a longer time to be used productively High photosynthesis at low P • No excess P in tissues (including roots and stems) • More productive use of P Low grain P • More P returns to the soil • Less P is lost to the environment • Improved nutritional value [Need to watch possible early vigour penalty]
  33. Where to invest scarce P? Soil P banks and P debts ... yield increased PUE soil P Yield benefit of high PUE will probably be highest in low-P soils
  34. Where to invest scarce P? Soil P banks and P debts ... yield increased PUE soil P Fertilizer savings in high-P soils should be invested in low-P soils (but only if there are no other major limitations to yield?)
  35. CONCLUSIONS Increased PUE and wiser use of P fertilizer is desirable and probably vital to ensure P fertilizer availability for future generations P is fundamentally different to N in its physiology, agroecology, fertilizer management and environmental implications PUE may be increased by decreasing certain P pools and by improving remobilization to where it is used most productively Use of all resources (P, N, water) is most efficient when they are all balanced; Decisions about the distribution of these resources have large agronomical but also large socio-economical and political implications
  36. Acknowledgements Hans Lambers, John Raven and other co-authors of the review Ian Wright/Peter Reich/Glopnet and many others … The University of Western Australia Contact: Erik.Veneklaas@uwa.edu.au
  37. The University of Western Australia P in ecosystems: tight cycling VEGETATION litter uptake SOIL weathering + atmosphere runoff drainage unavailable P Nevertheless: old weathered soils are very low in soil P
  38. The University of Western Australia Sclerophyllous Banksia leaves have quite high Photosynthetic P-use Efficiency 3.0 2.5 2.0 1.5 1.0 0.5 0.0 N/P < 15 N/P > 15 1.0 1.5 2.0 2.5 3.0 log A/P (μmol g-1 s-1) log LMA (g m-2) In blue: Banksia spp. Foteini Hassiotou Banksia victoriae Banksia Patrick Mitchell
  39. PUE over the life-time of a leaf (in the context of the Leaf Economic Spectrum) C balance: High-LMA leaves live longer but have lower rates of photosynthesis … P balance: High-LMA leaves have lower [P] and may have higher remobilisation … The University of Western Australia 150 100 50 0 0 100 200 300 400 LL (mo) LMA (g m-2) 500 400 300 200 100 0 0 100 200 300 400 Amass (nmol g-1 s-1) LMA (g m-2) 5 4 3 2 1 0 0 100 200 300 400 [P] (mg g-1) LMA (g m-2) Data: glopnet database – Wright et al. (2004) Nature 428:821-827
  40. The University of Western Australia Assumptions for life-time C and P balance: C balance = (mean daily net photosynthesis – respiration) X lifespan – leaf C cost Photosynthetic capacity (Amass) scales with mean net photosynthesis (daily basis): • Daily C balance accounts for suboptimal light conditions, respiration. • Amass declines over lifetime of leaf. Reich et al. (2009) New Phytol. 183:153–166 P balance = (1-remobilised fraction) X leaf P content Remobilisation is typically 40 to 80%, not strongly correlated with LMA
  41. Leaf photosynthetic capacity scales with daily C balance Zotz & Winter (1993) Planta 191:409- 412 Gottsberger (2002) PhD thesis Universität Wien The University of Western Australia Reich et al. (2009) 300 200 100 Tropical rainforest Mediterranean sclerophyllous woodland 0 New Phytol. 183:153-166 0 5 10 15 20 Daily C balance (mmol m-2 d-1) Amax (μmol m-2 s-1) Cloud forest
  42. Lifetime PUE does not correlate strongly with LMA but percentage remobilization has a large impact 80 % 40% 60 % The University of Western Australia 0.2 0.1 0.0 remobilization=60 % 0 200 400 600 lifetime PUE (g C mg-1 P) LMA (g m-2) 0.12 0.08 0.04 0.00 0 200 400 600 A/P (g C mg-1 P) LMA (g m-2) Conclusion: There is large variation in PPUE and lifetime leaf PUE, which doesn’t scale clearly with the Leaf Economics Spectrum; P remobilization is vital for high lifetime leaf PUE.
  43. Summary lifetime leaf PUE: comparing leaves with LMA 100 and 200 g m-2 (P remobilisation 60%) [P] X 0.57 lifetime P balance X 1.85 LMA 100 LMA 200 The University of Western Australia 30 20 10 0 LL X 3.3 LMA 100 LMA 200 100 50 0 Amax X 0.59 LMA 100 LMA 200 15 10 5 0 lifetime C balance X 2.01 LMA 100 LMA 200 1.5 1.0 0.5 0.0 LMA 100 LMA 200 200 150 100 50 0 0.06 0.04 0.02 0.00 lifetime PUE X 1.09 LMA 100 LMA 200 Despite large differences in morphology and physiology, PUE differs by less than 10%
  44. Remobilisation of P from senescing fine roots is significant Species from subarctic communities, Sweden Freschet et al. (2010) New Phytol. 186:879- 889 Remobilisation of P from senescing roots has often been claimed to be very small Root N and P remobilisation rates and root life spans are very poorly known but potentially very important The University of Western Australia Leaves (n=40) Stems (n=38) Roots (n=11)
  45. Banksia attenuata, observed at weekly intervals in a minirhizotron The University of Western Australia Banksia root turnover and P remobilization data are being quantified
  46. P required to maintain biomass (e.g. mature perennial plants) The University of Western Australia 1000 800 600 400 200 0 P remobilisation 20% 40% 60% 80% 0 10 20 30 Annual P cost (% of P content) Tissue lifespan (months) No net growth – maintenance only; P uptake required to maintain same amount of tissue with same [P]
  47. Reduction of rRNA levels in Arabidopsis Sulpice et al (2014) PCE
  48. Lessons from Nature? Many of the traits identified are present in undomesticated plants Plants on low-P soils have: -Low tissue P concentrations -Replace phospholipids by sulfo- and galactolipids -Low levels of RNA -Efficient internal P recycling -Long tissue lifespans (often perennial plants)
Advertisement