David Chapman

Dr. David Chapman


Research Focus & Metrics

Academic Career Length

16Years (2011-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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11 January 2016 in Grass and Forage Science
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DCDavid Chapman
David Chapman
JBJ. R. Bryant
J. R. Bryant
MOM. E. Olayemi
M. E. Olayemi
GEGrant Edwards
Grant Edwards
BTB. S. Thorrold
B. S. Thorrold
MNM. Norriss
M. Norriss

3 November 2011 in Grass and Forage Science
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DCDavid Chapman
David Chapman
JTJ. Tharmaraj
J. Tharmaraj
MAM. Agnusdei
M. Agnusdei
JHJ. Hill
J. Hill

1 August 2014 in Crop & Pasture Science
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DCDavid Chapman
David Chapman
JLJ. M. Lee
J. M. Lee
GWG. C. Waghorn
G. C. Waghorn
Plant–animal interactions impact on all elements of pasture and animal performance in grazing systems. The quality of pastures for animals can be described in terms of feeding value (FV), which is a combination of feed nutritive value (NV) and voluntary intake. There are numerous complex interactions between plant physiology and pasture FV and NV. This review focuses on these interactions in four key areas (plant growth strategies, phenological development, pasture regrowth, and response to environmental stress), extracting key principles and illustrating how plant breeding or management may be used to manipulate such interactions to improve FV. The FV is low in pastures with native species that have evolved in nutrient-poor environments, especially if there are greater proportions of C4 than C3 species in the sward. Reproductive development of grasses and long grazing intervals (which affect stage of regrowth) reduce the proportion of leaf and increase stem or dead matter content in the sward. This is exacerbated by environmental stresses such as warmer temperatures and water deficit. Management decisions provide a means of manipulating many of these interactions to improve the FV of pasture, especially by improving soil nutrient status, using irrigation where possible, introducing exotic perennial pasture species such as perennial ryegrass, phalaris and tall fescue, linking the timing of grazing to stage of regrowth, and carefully managing post-grazing residual sward state. Likewise, plant breeding has focused on altering the flowering date of grasses, reducing aftermath heading, and reducing lignification within the plant to improve the FV of pasture for livestock.

11 June 2015 in Animal Production Science
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DCDavid Chapman
David Chapman
GEGrant Edwards
Grant Edwards
ASA. V. Stewart
A. V. Stewart
MMM. McEvoy
M. McEvoy
MOM. O’dOnovan
M. O’dOnovan
GWG. C. Waghorn
G. C. Waghorn
Failure over the past two to three decades to implement industry-led, systematic forage evaluation systems that translate forage performance data to animal production and economics means that the livestock industries are poorly positioned to judge how much economic benefit they are gaining from forage plant improvement and to propose future priorities and targets. The present paper identifies several knowledge gaps that must be filled to enable the value being delivered to pasture-based livestock industries by forage improvement to be determined, demonstrated to farmers and increased in the future. Seasonal yield, total annual yield, nutritive value and feeding value of pasture are all important traits for driving the productivity of pasture-based livestock production systems. From a farm systems perspective, persistence of the yield or quality advantage of new cultivars is also economically important. However, this is the least well defined of the productivity traits considered in the paper. Contrary to anecdotal reports, evidence indicates that the genetic potential of modern ryegrass cultivars to survive in grazed pastures is at least equivalent to that of older cultivars. Plant breeding in Europe and New Zealand has changed the seasonal yield, quality and intake potential of perennial ryegrass. On the basis of dry matter (DM) yield data from small-plot evaluation trials, the New Zealand forage value index indicates that the top-ranked perennial ryegrass cultivars offer between NZ$280 and NZ $650/ha per year potential additional operating profit to dairy businesses (depending on region), compared with a historical genetic base of cultivars that were first entered into yield testing programs between 1991 and 1996. The equivalent figure in Ireland (including nutritive value effects) is about €325/ha per year. These estimates are yet to be confirmed in animal production studies. In intensive dairy systems, current rates of genetic gain in DM yield lag well behind realised rates of gain in animal genetics and associated increases in feed demand per animal. Genetic gains in yield need to double from current rates (estimated at 0.5% per year); but, it is not known whether this is possible in an outcrossing species such as perennial ryegrass, which is normally grown in a mixture with other species, especially white clover. Improvements in DM yield in seasons where extra DM has greatest economic value in grazing systems should dominate breeding objectives, but this must now be augmented by consideration of the environmental impacts of intensive pasture-based livestock production systems and opportunities to mitigate this through germplasm selection. There is less evidence that nutritive or feeding value of ryegrass cultivars significantly limits animal production and profitability and useful improvements have already been made using tetraploids and later heading material.

18 April 2016 in Agriculture
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DCDavid Chapman
David Chapman
Information on the physiological ecology of grass-dominant pastures has made a substantial contribution to the development of practices that optimise the amount of feed harvested by grazing animals in temperate livestock systems. However, the contribution of ecophysiology is often under-stated, and the need for further research in this field is sometimes questioned. The challenge for ecophysiolgists, therefore, is to demonstrate how ecophysiological knowledge can help solve significant problems looming for grassland farming in temperate regions while also removing constraints to improved productivity from grazed pastures. To do this, ecophysiological research needs to align more closely with related disciplines, particularly genetics/genomics, agronomy, and farming systems, including systems modelling. This review considers how ecophysiological information has contributed to the development of grazing management practices in the New Zealand dairy industry, an industry that is generally regarded as a world leader in the efficiency with which pasture is grown and utilised for animal production. Even so, there are clear opportunities for further gains in pasture utilisation through the refinement of grazing management practices and the harnessing of those practices to improved pasture plant cultivars with phenotypes that facilitate greater grazing efficiency. Meanwhile, sub-optimal persistence of new pastures continues to constrain productivity in some environments. The underlying plant and population processes associated with this have not been clearly defined. Ecophysiological information, placed in the context of trait identification, grounded in well-designed agronomic studies and linked to plant improvements programmes, is required to address this.

1 December 2025 in New Zealand Journal of Agricultural Research
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Journal Article
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DCDavid Chapman
David Chapman
AMAlec Mackay
Alec Mackay
Caradus JohnCaradus John
Caradus John
DCDavid A. Clark
David A. Clark
SGStephen L. Goldson
Stephen L. Goldson
Pasture productivity gains are critical for maintaining global competitiveness of New Zealand’s $38 billion p.a. animal product export industries. This review reveals that gains in pasture eaten on dairy farms declined sharply after ∼ 2001/02, from +1.48% yr −1 to +0.26% yr −1 despite continued increases in nitrogen (N) fertiliser use, stocking rate, irrigation, atmospheric carbon dioxide (CO 2 ) concentrations and products from plant breeding programmes. Thus, gains in pasture productivity (outputs relative to inputs) have also declined. Almost all of the increase in dairy pasture eaten since 1990 can be explained by increases in N fertiliser and stocking rate. Many farms may have reached the peak pasture yields possible within the climatic environment of the late twentieth century. Meanwhile, climate change in northern regions is placing downward pressure on pasture growth and persistence. Climate change also emerges as a key cause of declining production on sheep/beef farms in some regions, while elsewhere predicted increases in growth under climate warming and elevated CO 2 have not materialised. There is a major strategic knowledge gap regarding the state and resilience of the national pasture resource which potentially constrains the optimal allocation of scarce research resources to the key issues affecting future financial and environmental sustainability.