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	<title>Cover Crops | Promoting Plant Diversity</title>
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	<link>https://covercrops.co.nz</link>
	<description>green manure, seed mixes, soil health</description>
	<lastBuildDate>Sat, 27 Apr 2019 02:33:39 +0000</lastBuildDate>
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		<title>RSWD Gabe Brown 2018</title>
		<link>https://covercrops.co.nz/2019/04/27/rswd-gabe-brown-2018/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Sat, 27 Apr 2019 02:33:39 +0000</pubDate>
				<category><![CDATA[Uncategorized]]></category>
		<guid isPermaLink="false">https://covercrops.co.nz/?p=4676</guid>

					<description><![CDATA[<p>Click here to watch the full video</p>
The post <a href="https://covercrops.co.nz/2019/04/27/rswd-gabe-brown-2018/">RSWD Gabe Brown 2018</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<p>Click here to watch the full video</p>The post <a href="https://covercrops.co.nz/2019/04/27/rswd-gabe-brown-2018/">RSWD Gabe Brown 2018</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<title>Gabe Brown: Keys To Building a Healthy Soil</title>
		<link>https://covercrops.co.nz/2019/01/07/gabe-brown-keys-to-building-a-healthy-soil/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 05:54:00 +0000</pubDate>
				<category><![CDATA[Uncategorized]]></category>
		<guid isPermaLink="false">https://covercrops.co.nz/?p=3029</guid>

					<description><![CDATA[<p>This video features Gabe Brown and his Keys To Building a Healthy Soil, filmed on Nov. 18th 2014 at the Idaho Center for Sustainable Agriculture&#8217;s annual symposium. Watch the video&#8230;</p>
The post <a href="https://covercrops.co.nz/2019/01/07/gabe-brown-keys-to-building-a-healthy-soil/">Gabe Brown: Keys To Building a Healthy Soil</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<p>This video features Gabe Brown and his Keys To Building a Healthy Soil, filmed on Nov. 18th 2014 at the Idaho Center for Sustainable Agriculture&#8217;s annual symposium.</p>
<p><a href="https://www.youtube.com/watch?v=9yPjoh9YJMk">Watch the video&#8230;</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/gabe-brown-keys-to-building-a-healthy-soil/">Gabe Brown: Keys To Building a Healthy Soil</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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			</item>
		<item>
		<title>Pasture Cropping and Grazing</title>
		<link>https://covercrops.co.nz/2019/01/07/pasture-cropping-and-grazing/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 05:50:39 +0000</pubDate>
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		<guid isPermaLink="false">https://covercrops.co.nz/?p=3027</guid>

					<description><![CDATA[<p>Colin Seis, this year’s winner of the national Bob Hawke Landcare Award, shares his extensive knowledge of Pasture Cropping, a regenerative agriculture concept that he and Darryl Clough came up with in the 1990’s. Colin has since refined Pasture Cropping and is having outstanding success on not only his own property, but on over 2000 [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/pasture-cropping-and-grazing/">Pasture Cropping and Grazing</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<p>Colin Seis, this year’s winner of the national Bob Hawke Landcare Award, shares his extensive knowledge of Pasture Cropping, a regenerative agriculture concept that he and Darryl Clough came up with in the 1990’s. Colin has since refined Pasture Cropping and is having outstanding success on not only his own property, but on over 2000 properties throughout the world. This presentation was a part of a workshop held in Central Victoria earlier this year, hosted by the North Central Catchment Management Authority.</p>
<p><a href="https://www.youtube.com/watch?v=AAei0NBVBIM">Watch the video&#8230;</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/pasture-cropping-and-grazing/">Pasture Cropping and Grazing</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<item>
		<title>Biodiversity effects on ecosystem functioning in a 15-year grassland experiment</title>
		<link>https://covercrops.co.nz/2019/01/07/biodiversity-effects-on-ecosystem-functioning-in-a-15-year-grassland-experiment/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 05:48:43 +0000</pubDate>
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		<guid isPermaLink="false">https://covercrops.co.nz/?p=3025</guid>

					<description><![CDATA[<p>Abstract In the past two decades, a large number of studies have investigated the relationship between biodiversity and ecosystem functioning, most of which focussed on a limited set of ecosystem variables. The Jena Experiment was set up in 2002 to investigate the effects of plant diversity on element cycling and trophic interactions, using a multi-disciplinary approach. Here, [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/biodiversity-effects-on-ecosystem-functioning-in-a-15-year-grassland-experiment/">Biodiversity effects on ecosystem functioning in a 15-year grassland experiment</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<h2 class="section-title">Abstract</h2>
<div id="abst0005">
<p id="spar0195">In the past two decades, a large number of studies have investigated the relationship between biodiversity and <a title="Learn more about Ecosystem Functioning" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/ecosystem-functioning">ecosystem functioning</a>, most of which focussed on a limited set of ecosystem variables. The Jena Experiment was set up in 2002 to investigate the effects of plant diversity on element cycling and <a title="Learn more about Trophic Interaction" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/trophic-interaction">trophic interactions</a>, using a multi-disciplinary approach. Here, we review the results of 15 years of research in the Jena Experiment, focussing on the effects of manipulating plant <a title="Learn more about Species Richness" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/species-richness">species richness</a> and plant functional richness. With more than 85,000 measures taken from the plant diversity plots, the Jena Experiment has allowed answering fundamental questions important for functional biodiversity research.</p>
<p id="spar0200">First, the question was how general the effect of plant species richness is, regarding the many different processes that take place in an ecosystem. About 45% of different types of <a title="Learn more about Ecosystem Processes" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/ecosystem-processes">ecosystem processes</a> measured in the ‘main experiment’, where plant species richness ranged from 1 to 60 species, were significantly affected by plant species richness, providing strong support for the view that biodiversity is a significant driver of ecosystem functioning. Many measures were not saturating at the 60-species level, but increased linearly with the <a title="Learn more about Logarithms" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/logarithms">logarithm</a> of species richness. There was, however, great variability in the strength of response among different processes. One striking pattern was that many processes, in particular belowground processes, took several years to respond to the manipulation of plant species richness, showing that biodiversity experiments have to be long-term, to distinguish trends from transitory patterns. In addition, the results from the Jena Experiment provide further evidence that diversity begets stability, for example stability against invasion of plant species, but unexpectedly some results also suggested the opposite, e.g. when plant communities experience severe perturbations or elevated resource availability. This highlights the need to revisit diversity–stability theory.</p>
<p id="spar0205">Second, we explored whether individual plant species or individual plant functional groups, or biodiversity itself is more important for ecosystem functioning, in particular <a title="Learn more about Biomass Production" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/biomass-production">biomass production</a>. We found strong effects of individual species and plant functional groups on <a title="Learn more about Biomass" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/biomass">biomass</a> production, yet these effects mostly occurred in addition to, but not instead of, effects of plant species richness.</p>
<p id="spar0210">Third, the Jena Experiment assessed the effect of diversity on multitrophic interactions. The diversity of most organisms responded positively to increases in plant species richness, and the effect was stronger for above- than for belowground organisms, and stronger for <a title="Learn more about Herbivore" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/herbivore">herbivores</a> than for <a title="Learn more about Carnivores" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/carnivores">carnivores</a> or <a title="Learn more about Detritivores" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/detritivores">detritivores</a>. Thus, diversity begets diversity. In addition, the effect on organismic diversity was stronger than the effect on species abundances.</p>
<p id="spar0215">Fourth, the Jena Experiment aimed to assess the effect of diversity on N, P and C cycling and the <a title="Learn more about Water Balance" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/water-balance">water balance</a> of the plots, separating between element input into the ecosystem, element turnover, element stocks, and output from the ecosystem. While inputs were generally less affected by plant species richness, measures of element stocks, turnover and output were often positively affected by plant diversity, e.g. <a title="Learn more about Carbon Sequestration" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/carbon-sequestration">carbon storage</a> strongly increased with increasing plant species richness. Variables of the N cycle responded less strongly to plant species richness than variables of the C cycle.</p>
<p id="spar0220">Fifth, plant traits are often used to unravel mechanisms underlying the biodiversity–ecosystem functioning relationship. In the Jena Experiment, most investigated plant traits, both above- and belowground, were plastic and trait expression depended on plant diversity in a complex way, suggesting limitation to using database traits for linking plant traits to particular functions.</p>
<p id="spar0225">Sixth, plant diversity effects on ecosystem processes are often caused by plant diversity effects on species interactions. Analyses in the Jena Experiment including <a title="Learn more about Structural Equation Modeling" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/structural-equation-modeling">structural equation modelling</a> suggest complex interactions that changed with diversity, e.g. soil carbon storage and <a title="Learn more about Greenhouse Gas Emission" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/greenhouse-gas-emission">greenhouse gas emission</a> were affected by changes in the composition and activity of the belowground <a title="Learn more about Microbial Community" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/microbial-community">microbial community</a>. Manipulation experiments, in which particular organisms, e.g. belowground <a title="Learn more about Invertebrate" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/invertebrate">invertebrates</a>, were excluded from plots in split-plot experiments, supported the important role of the biotic component for element and <a title="Learn more about Water Flux" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/water-flux">water fluxes</a>.</p>
<p id="spar0230">Seventh, the Jena Experiment aimed to put the results into the context of agricultural practices in managed <a title="Learn more about Grasslands" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/grasslands">grasslands</a>. The effect of increasing plant species richness from 1 to 16 species on plant biomass was, in absolute terms, as strong as the effect of a more intensive grassland management, using fertiliser and increasing mowing frequency. Potential <a title="Learn more about Bioenergy" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/bioenergy">bioenergy</a> production from high-diversity plots was similar to that of conventionally used <a title="Learn more about Energy Crop" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/energy-crop">energy crops</a>. These results suggest that diverse ‘High Nature Value Grasslands’ are multifunctional and can deliver a range of ecosystem services including production-related services.</p>
<p id="spar0235">A final task was to assess the importance of potential artefacts in biodiversity–ecosystem functioning relationships, caused by the weeding of the plant community to maintain plant species composition. While the effort (in hours) needed to weed a plot was often negatively related to plant species richness, species richness still affected the majority of ecosystem variables. Weeding also did not negatively affect <a title="Learn more about Monoculture" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/monoculture">monoculture</a> performance; rather, monocultures deteriorated over time for a number of biological reasons, as shown in plant-soil feedback experiments.</p>
<p id="spar0240">To summarize, the Jena Experiment has allowed for a comprehensive analysis of the <a title="Learn more about Functional Role" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/functional-role">functional role</a> of biodiversity in an ecosystem. A main challenge for future biodiversity research is to increase our mechanistic understanding of why the magnitude of biodiversity effects differs among processes and contexts. It is likely that there will be no simple answer. For example, among the multitude of mechanisms suggested to underlie the positive plant species richness effect on biomass, some have received limited support in the Jena Experiment, such as vertical root <a title="Learn more about Niche Partitioning" href="https://www.sciencedirect.com/topics/earth-and-planetary-sciences/niche-partitioning">niche partitioning</a>. However, others could not be rejected in targeted analyses. Thus, from the current results in the Jena Experiment, it seems likely that the positive biodiversity effect results from several mechanisms acting simultaneously in more diverse communities, such as reduced pathogen attack, the presence of more <a title="Learn more about Plant Growth" href="https://www.sciencedirect.com/topics/agricultural-and-biological-sciences/plant-growth">plant growth</a> promoting organisms, less seed limitation, and increased trait differences leading to complementarity in resource uptake. Distinguishing between different mechanisms requires careful testing of competing hypotheses. Biodiversity research has matured such that predictive approaches testing particular mechanisms are now possible.</p>
</div>
<p>&nbsp;</p>
<p><a href="https://www.sciencedirect.com/science/article/pii/S1439179116300913">Read full article</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/biodiversity-effects-on-ecosystem-functioning-in-a-15-year-grassland-experiment/">Biodiversity effects on ecosystem functioning in a 15-year grassland experiment</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<title>Biodiversity for multifunctional grasslands</title>
		<link>https://covercrops.co.nz/2019/01/07/biodiversity-for-multifunctional-grasslands/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 04:08:15 +0000</pubDate>
				<category><![CDATA[Uncategorized]]></category>
		<guid isPermaLink="false">https://covercrops.co.nz/?p=3003</guid>

					<description><![CDATA[<p>Abstract. Modern grassland management seeks to provide many ecosystem services and experimental studies in resource-poor grasslands have shown a positive relationship between plant species richness and a variety of ecosystem functions. Thus, increasing species richness might help to enhance multifunctionality in managed grasslands if the relationship between species richness and ecosystem functioning is equally valid in [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/biodiversity-for-multifunctional-grasslands/">Biodiversity for multifunctional grasslands</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<div class="abstract">
<p><strong>Abstract.</strong> Modern grassland management seeks to provide many ecosystem services and experimental studies in resource-poor grasslands have shown a positive relationship between plant species richness and a variety of ecosystem functions. Thus, increasing species richness might help to enhance multifunctionality in managed grasslands if the relationship between species richness and ecosystem functioning is equally valid in high-input grassland systems.</p>
<p>We tested the relative effects of low-input to high-input management intensities and low to high plant species richness. Using a combination of mowing frequencies (1, 2 or 4 cuts per season) and fertilisation levels (0, 100 and 200 kg N ha<sup>−1</sup> a<sup>−1</sup>), we studied the productivity of 78 experimental grassland communities of increasing plant species richness (1, 2, 4, 8 or 16 species with 1 to 4 functional groups) in two successive years.</p>
<p>Our results showed that in both years higher diversity was more effective in increasing productivity than higher management intensity: the 16-species mixtures had a surplus of 449 g m<sup>−2</sup> y<sup>−1</sup> in 2006 and 492 g m<sup>−2</sup> y<sup>−1</sup> in 2007 over the monoculture yields whereas the high-input management resulted in only 315 g m<sup>−2</sup> y<sup>−1</sup> higher productivity in 2006 and 440 g m<sup>−2</sup> y<sup>−1</sup> in 2007 than the low-input management. In addition, high-diversity low-input grassland communities had similar productivity as low-diversity high-input communities. The slopes of the biodiversity – productivity relationships significantly increased with increasing levels of management intensity in both years.</p>
<p>We conclude that the biological mechanisms leading to enhanced biomass production in diverse grassland communities are as effective for productivity as a combination of several agricultural measures. Our results demonstrate that high-diversity low-input grassland communities provide not only a high diversity of plants and other organisms, but also ensure high forage yields, thus granting the basis for multifunctional managed grasslands.</p>
</div>
<div class="grid-container citation-footer "><strong>How to cite: </strong>Weigelt, A., Weisser, W. W., Buchmann, N., and Scherer-Lorenzen, M.: Biodiversity for multifunctional grasslands: equal productivity in high-diversity low-input and low-diversity high-input systems, Biogeosciences, 6, 1695-1706, https://doi.org/10.5194/bg-6-1695-2009, 2009.</div>
<p><strong>source: </strong><a href="https://www.biogeosciences.net/6/1695/2009/">https://www.biogeosciences.net/6/1695/2009/</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/biodiversity-for-multifunctional-grasslands/">Biodiversity for multifunctional grasslands</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<title>Regenerative agriculture</title>
		<link>https://covercrops.co.nz/2019/01/07/regenerative-agriculture/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 04:05:57 +0000</pubDate>
				<category><![CDATA[Uncategorized]]></category>
		<guid isPermaLink="false">https://covercrops.co.nz/?p=3001</guid>

					<description><![CDATA[<p>Introduction Development of synthetic fertilizers, hybrid crops, genetically modified crops, and policies that decouple farmer decisions from market demands all helped create a modern food production system which reduces the diversity of foods that are produced (Fausti &#38; Lundgren, 2015; Pretty, 1995). This simplification of our food system contributes to climate change (Carlsson-Kanyama &#38; Gonzalez, 2009), [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/regenerative-agriculture/">Regenerative agriculture</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<div>
<div class="row-fluid row-article-item-section">
<div class="span11 article-item-section-content">
<div id="article-item-main-sections">
<section id="intro" class="sec">
<h2 class="heading">Introduction</h2>
<p id="p-1" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>Development of synthetic fertilizers, hybrid crops, genetically modified crops, and policies that decouple farmer decisions from market demands all helped create a modern food production system which reduces the diversity of foods that are produced (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.envsci.2015.04.017" data-jats-ref-type="bibr" data-jats-rid="ref-12" data-original-title="The causes and unintended consequences of a paradigm shift in corn production practices">Fausti &amp; Lundgren, 2015</a>; <a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Regenerating%20agriculture:%20policies%20and%20practice%20for%20sustainability%20and%20self-reliance&amp;author=Pretty&amp;publication_year=1995" data-jats-ref-type="bibr" data-jats-rid="ref-34" data-original-title="Regenerating agriculture: policies and practice for sustainability and self-reliance">Pretty, 1995</a>). This simplification of our food system contributes to climate change (<a class="xref xref-bibr" title="" href="https://doi.org/10.3945%2Fajcn.2009.26736AA" data-jats-ref-type="bibr" data-jats-rid="ref-7" data-original-title="Potential contributions of food consumption patterns to climate change">Carlsson-Kanyama &amp; Gonzalez, 2009</a>), rising pollution (<a class="xref xref-bibr" title="" href="https://doi.org/10.1073%2Fpnas.1011053108" data-jats-ref-type="bibr" data-jats-rid="ref-3" data-original-title="Global declines in oceanic nitrification rates as a consequence of ocean acidification">Beman et al., 2011</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.envint.2014.10.024" data-jats-ref-type="bibr" data-jats-rid="ref-30" data-original-title="Neonicotinoid contamination of global surface waters and associated risk to aquatic invertebrates: a review">Morrissey et al., 2015</a>), biodiversity loss (<a class="xref xref-bibr" title="" href="https://doi.org/10.1126%2Fscience.1136607" data-jats-ref-type="bibr" data-jats-rid="ref-5" data-original-title="Farmland biodiversity and the footprint of agriculture">Butler, Vickery &amp; Norris, 2007</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1073%2Fpnas.0804951106" data-jats-ref-type="bibr" data-jats-rid="ref-23" data-original-title="Increasing corn for biofuel production reduces biocontrol services in agricultural landscapes">Landis et al., 2008</a>), and damaging land use changes (<a class="xref xref-bibr" title="" href="https://doi.org/10.1007%2Fs10980-013-9947-0" data-jats-ref-type="bibr" data-jats-rid="ref-16" data-original-title="Agricultural expansion: land use shell game in the US Northern Plains">Johnston, 2014</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1073%2Fpnas.1215404110" data-jats-ref-type="bibr" data-jats-rid="ref-46" data-original-title="Recent land use change in the Western Corn Belt threatens grasslands and wetlands">Wright &amp; Wimberly, 2013</a>) that affect the sustainability, profitability and resilience of farms (<a class="xref xref-bibr" title="" href="https://doi.org/10.1093%2Fbiosci%2Fbiw052" data-jats-ref-type="bibr" data-jats-rid="ref-37" data-original-title="Realizing resilient food systems">Schipanski et al., 2016</a>). Farmers experience the highest suicide rate of any profession in the United States, a rate nearly five-fold higher than the general public (<a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Suicide%20rates%20by%20occupational%20group%E2%80%9417%20states,%202012&amp;author=McIntosh&amp;publication_year=2016" data-jats-ref-type="bibr" data-jats-rid="ref-29" data-original-title="Suicide rates by occupational group—17 states, 2012">McIntosh et al., 2016</a>); the driving depression rates are related to conventional production practices (<a class="xref xref-bibr" title="" href="https://doi.org/10.1289%2Fehp.1307450" data-jats-ref-type="bibr" data-jats-rid="ref-2" data-original-title="Pesticide exposure and depression among male private pesticide applicators in the agricultural health study">Beard et al., 2014</a>). The scale of our food production system provides opportunities for solving some of these planetary scale problems (<a class="xref xref-bibr" title="" href="https://doi.org/10.1126%2Fscience.1097396" data-jats-ref-type="bibr" data-jats-rid="ref-21" data-original-title="Soil carbon sequestration impacts on global climate change and food security">Lal, 2004</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.2489%2Fjswc.71.2.156" data-jats-ref-type="bibr" data-jats-rid="ref-41" data-original-title="The role of ruminants in reducing agriculture’s carbon footprint in North America">Teague et al., 2016</a>), but requires a systems-level shift in the values and goals of our food production system that de-prioritizes solely generating high yields toward one that produces higher quality food while conserving our natural resource base.</p>
<p id="p-2" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>The goal of regenerative farming systems (<a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Breaking%20new%20ground:%20the%20search%20for%20a%20sustainable%20agriculture&amp;author=Rodale&amp;publication_year=1983" data-jats-ref-type="bibr" data-jats-rid="ref-35" data-original-title="Breaking new ground: the search for a sustainable agriculture">Rodale, 1983</a>) is to increase soil quality and biodiversity in farmland while producing nourishing farm products profitably. Unifying principles consistent across regenerative farming systems include (1) abandoning tillage (or actively rebuilding soil communities following a tillage event), (2) eliminating spatio-temporal events of bare soil, (3) fostering plant diversity on the farm, and (4) integrating livestock and cropping operations on the land. Further characterization of a regenerative system is problematic because of the myriad combinations of farming practices that comprise a system targeting the regenerative goal. Other comparisons of conventional agriculture with alternative agriculture schemes do not compare <i>in situ</i> best management practices developed by farmers, and frequently ignore a key driver to decision making on farming operations: the examined systems’ relative net profit to the farmer (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.agsy.2011.12.004" data-jats-ref-type="bibr" data-jats-rid="ref-9" data-original-title="The crop yield gap between organic and conventional agriculture">De Ponti, Rijk &amp; Van Ittersum, 2012</a>).</p>
</section>
<section id="materials|methods" class="sec">
<h2 class="heading">Materials and Methods</h2>
<p id="p-3" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>Corn (<i>Zea mays</i> L.) was selected for our study due to its pre-eminence as a food crop in North America and globally. Corn is planted on 39.9% of all crop acres (<a class="xref xref-bibr" title="" href="http://www.nass.usda.gov/" data-jats-ref-type="bibr" data-jats-rid="ref-31" data-original-title="National Agriculture Statistics Service">NASS, 2017</a>), or 4.8% (37.1 million ha) of the terrestrial land surface of the contiguous 48 states. In 2012, it generated 30.3% ($64,319 billion) of all gross crop value in the US (<a class="xref xref-bibr" title="" href="http://www.nass.usda.gov/" data-jats-ref-type="bibr" data-jats-rid="ref-31" data-original-title="National Agriculture Statistics Service">NASS, 2017</a>). Nearly 100% of cornfields are treated annually with insecticides (<a class="xref xref-bibr" title="" href="http://www.nass.usda.gov/" data-jats-ref-type="bibr" data-jats-rid="ref-31" data-original-title="National Agriculture Statistics Service">NASS, 2017</a>). We used a matrix of specific production practices (<a class="xref xref-table" href="https://peerj.com/articles/4428/#table-1" data-jats-ref-type="table" data-jats-rid="table-1">Table 1</a>) to define each farm into one of two systems (regenerative or conventional). The most regenerative systems (<i>n</i> = 40 fields on 10 farms) used mixed multispecies cover crops (ranging from 2–40 plant species), were never-till, used no insecticides, and grazed livestock on their cropland. The most conventional farms practiced tillage at least annually (36 fields on eight farms), applied insecticides (as GM insect-resistant varieties and neonicotinoid seed treatments), and left their soil bare aside from the cash crop.</p>
<figure id="table-1" class="table-wrap has-plink"><i class="icon-comment icon-flip-horizontal"></i></p>
<div class="caption"><span class="caption-label">Table 1:</span></p>
<div class="title">Trait matrix used to assign farms to regenerative or conventional corn production systems.</div>
<p><span class="p">The composite rank scores are based on the number of regenerative practices used on a particular farm. Farms whose rank scores are in the top 50% of farms are considered regenerative (shaded rows); those with rank scores in the lower half are conventional (white rows). To aid interpretation, additional traits of each system could be included in enhanced trait matrices. Organic operations are indicated by an asterisk in the “Reference town” column.</span></div>
<div class="table-container">
<table class="table table-bordered table-condensed table-hover">
<colgroup>
<col />
<col />
<col />
<col />
<col />
<col />
<col />
<col /></colgroup>
<thead>
<tr>
<th>Reference town</th>
<th>Farm locations (latitude, longitude)</th>
<th>Cover crop (yes: 1; no: 0)</th>
<th>Insecticide (no: 1; yes: 0)</th>
<th>Other pesticides (no: 1; yes: 0)</th>
<th>Tillage (yes: 0; no: 1)</th>
<th>Grazed corn field (yes: 1; no: 0)</th>
<th>Composite rank score</th>
</tr>
</thead>
<tbody>
<tr>
<td>Bladen, NE</td>
<td>40.31971, −98.57358</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>3</td>
</tr>
<tr>
<td>Bladen, NE</td>
<td>40.33703, −98.56301</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>York, NE</td>
<td>40.63054, −97.66534</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>3</td>
</tr>
<tr>
<td>York, NE</td>
<td>40.97390, −97.49031</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.85280, −100.60131</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>no</td>
<td>yes</td>
<td>5</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.85280, −100.35145</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>1</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.81734, −100.51257</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>4</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>47.14250, −100.19720</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>1</td>
</tr>
<tr>
<td>White, SD*</td>
<td>44.42572, −96.58806</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>3</td>
</tr>
<tr>
<td>White, SD</td>
<td>44.41155, −96.60008</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Pipestone, MN*</td>
<td>44.11446, −96.32468</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>3</td>
</tr>
<tr>
<td>Pipestone, MN</td>
<td>44.12416, −96.36422</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Toronto, SD</td>
<td>44.59248, −96.57923</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>3</td>
</tr>
<tr>
<td>Toronto, SD</td>
<td>44.57960, −96.58367</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Gary, SD*</td>
<td>44.80565, −96.34708</td>
<td>yes</td>
<td>no</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>4</td>
</tr>
<tr>
<td>Gary, SD</td>
<td>44.80689, −96.35465</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Arlington, SD</td>
<td>44.41566, −97.18795</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>4</td>
</tr>
<tr>
<td>Arlington, SD</td>
<td>44.42644, −97.25077</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
<tr>
<td>Lake Norden, SD</td>
<td>44.58976, −97.08649</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>yes</td>
<td>3</td>
</tr>
<tr>
<td>Lake Norden, SD</td>
<td>44.55.6839, −97.243820</td>
<td>no</td>
<td>yes</td>
<td>yes</td>
<td>yes</td>
<td>no</td>
<td>0</td>
</tr>
</tbody>
</table>
</div>
<div class="object-id article-component-doi">DOI: <a title="" href="https://doi.org/10.7717/peerj.4428/table-1" data-toggle="tooltip" data-original-title="Cite this object using this DOI">10.7717/peerj.4428/table-1</a></div>
</figure>
<p id="p-5" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>Soil organic matter, insect pest populations, and corn yield and profit were assessed for each field. Soil cores (8.5 cm deep, 5 cm in diameter; 30 g of soil each; <i>n</i> = 4 samples per field that were made a composite sample; only one field was sampled per farm- selected by the producer- and two farms were omitted due to adverse weather during the sampling event) were collected at least 10 m from one another during anthesis. Samples were cleaned of plant residue, ground, and dried to constant weight at 105 °C. Particulate soil organic matter (POM) was determined by screening each sample (soaked in 5 g L<sup>−1</sup> aqueous hexametaphosphate) through 500 um (course POM) and 53 um (fine POM) sieves and then applying the loss on ignition (LOI) technique (<a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj1974.03615995003800010046x" data-jats-ref-type="bibr" data-jats-rid="ref-8" data-original-title="Loss-on-ignition as an estimate of soil organic matter">Davies, 1974</a>). Insect pests were enumerated through dissections of all aboveground plant tissues (25 plants per field). Major pests of corn (rootworm adults, caterpillar pests, and aphids) are all present in cornfields at this crop developmental stage (<a class="xref xref-bibr" title="" href="https://doi.org/10.1111%2Fjen.12215" data-jats-ref-type="bibr" data-jats-rid="ref-28" data-original-title="Spatial and numerical relationships of arthropod communities associated with key pests of maize">Lundgren et al., 2015</a>), and this was substantiated in the observations in this study as well. Yields were gathered from three randomly selected 3.5 m sections of row from each field. Gross revenue for each field were considered as yield and return on grain, and additional revenue streams (e.g., animal weight gain resulting from grazing). Total direct costs for each field were calculated based on the costs of corn seed, cover crop seed, drying/cleaning grain, crop insurance, tillage, planting, fertilizers, pesticides, and irrigation.</p>
</section>
<section id="results-and-discussion" class="sec">
<h2 class="heading">Results and Discussion</h2>
<p id="p-6" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>Insect pest populations were more than 10 fold higher on the insecticide-treated farms than on the insecticide-free regenerative farms (ANOVA; <i>F</i><sub>1,77</sub> = 13.52, <i>P</i> &lt;0.001; <a class="xref xref-fig" title="" href="https://peerj.com/articles/4428/#fig-1" data-jats-ref-type="fig" data-jats-rid="fig-1" data-original-title="">Fig. 1</a>). Pest populations were numerically dominated by aphids, but each of the individual pest species followed the same pattern of the aggregated data; none of these pests were at economically damaging levels, as observed in other work in the region (<a class="xref xref-bibr" title="" href="https://doi.org/10.1126%2Fscience.1190242" data-jats-ref-type="bibr" data-jats-rid="ref-14" data-original-title="Areawide suppression of European corn borer with Bt maize reaps savings to non-Bt maize grower">Hutchison et al., 2010</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1111%2Fjen.12215" data-jats-ref-type="bibr" data-jats-rid="ref-28" data-original-title="Spatial and numerical relationships of arthropod communities associated with key pests of maize">Lundgren et al., 2015</a>). Pest problems in agriculture are often the product of low biodiversity and simple community structure on numerous spatial scales (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.biocon.2012.01.068" data-jats-ref-type="bibr" data-jats-rid="ref-44" data-original-title="Global food security, biodiversity conservation and the future of agricultural intensification">Tscharntke et al., 2012</a>). Hundreds of invertebrate species have been inventoried from cornfields of the Northern Plains of the US (<a class="xref xref-bibr" title="" href="https://doi.org/10.1111%2Fjen.12215" data-jats-ref-type="bibr" data-jats-rid="ref-28" data-original-title="Spatial and numerical relationships of arthropod communities associated with key pests of maize">Lundgren et al., 2015</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.fooweb.2016.02.004" data-jats-ref-type="bibr" data-jats-rid="ref-45" data-original-title="An exposure-based, ecology-driven framework for selection of indicator species for insecticide risk assessment">Welch &amp; Lundgren, 2016</a>), but these communities represent only 25% of the insect species that lived in ancestral habitats (e.g., prairie) that cornfields replaced in this region (<a class="xref xref-bibr" title="" href="https://doi.org/10.1093%2Faesa%2Fsav081" data-jats-ref-type="bibr" data-jats-rid="ref-38" data-original-title="Gut bacterial symbiont diversity within beneficial insects linked to reductions in local biodiversity">Schmid et al., 2015</a>). Pest abundance is lower in cornfields that have greater insect diversity, enhanced biological network strength and greater community evenness (<a class="xref xref-bibr" title="" href="https://doi.org/10.1126%2Fsciadv.1500558" data-jats-ref-type="bibr" data-jats-rid="ref-26" data-original-title="Trading biodiversity for pest problems">Lundgren &amp; Fausti, 2015</a>). Suggested mechanisms to explain how invertebrate diversity and network interactions reduce pests include predation (<a class="xref xref-bibr" title="" href="https://doi.org/10.1146%2Fannurev.ecolsys.110308.120320" data-jats-ref-type="bibr" data-jats-rid="ref-25" data-original-title="Effects of natural enemy biodiversity on the suppression of arthropod herbivores in terrestrial ecosystems">Letourneau et al., 2009</a>), competition (<a class="xref xref-bibr" title="" href="https://doi.org/10.1146%2Fannurev.ecolsys.110308.120242" data-jats-ref-type="bibr" data-jats-rid="ref-1" data-original-title="Associational resistance and susceptibility: having right or wrong neighbors">Barbosa et al., 2009</a>), and other processes that may not be easily predicted. What practices foster diversity in agroecosystems? In our studies, farmers that replaced insecticide use with agronomic forms of plant diversity invariably had fewer pest problems than those with strict monocultures. Reducing insect diversity and relying solely on insecticide use establishes a scenario whereby pests persist and resurge through adaptation, as was observed by our forebears (<a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Insects,%20experts,%20and%20the%20insecticide%20crisis&amp;author=Perkins&amp;publication_year=1982" data-jats-ref-type="bibr" data-jats-rid="ref-32" data-original-title="Insects, experts, and the insecticide crisis">Perkins, 1982</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.3733%2Fhilg.v29n02p081" data-jats-ref-type="bibr" data-jats-rid="ref-40" data-original-title="The integrated control concept">Stern et al., 1959</a>). Applying winter cover crops (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.apsoil.2011.08.005" data-jats-ref-type="bibr" data-jats-rid="ref-27" data-original-title="Enhancing predation of a subterranean insect pest: a conservation benefit of winter vegetation in agroecosystems">Lundgren &amp; Fergen, 2011</a>), lengthening crop rotations (<a class="xref xref-bibr" title="" href="https://doi.org/10.1080%2F07352689209382349" data-jats-ref-type="bibr" data-jats-rid="ref-4" data-original-title="Crop rotation">Bullock, 1992</a>), diversifying field margins using conservation mixes (<a class="xref xref-bibr" title="" href="https://doi.org/10.1111%2Fj.1752-4598.2010.00098.x" data-jats-ref-type="bibr" data-jats-rid="ref-13" data-original-title="Sown wildflower strips for insect conservation: a review">Haaland, Naisbit &amp; Bersier, 2011</a>), and allowing or promoting non-crop plants between crop rows (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.cropro.2006.01.008" data-jats-ref-type="bibr" data-jats-rid="ref-18" data-original-title="Combined control of Striga hermonthica and stemborers by maize-Desmodium spp. intercrops">Khan et al., 2006</a>) are other agronomically sound practices that regenerative farmers successfully apply to improve the resilience of their system to pest proliferation.</p>
<figure id="fig-1" class="fig has-plink"><i class="icon-comment icon-flip-horizontal"></i></p>
<div class="image-container"><a class="fresco" title="View the full image" href="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-2x.jpg" data-fresco-caption="Figure 1: Insecticide-treated cornfields had higher pest abundance than untreated, regenerative cornfields." data-fresco-group="figure" data-fresco-options="fit: 'width', ui: 'outside', thumbnails: false, loop: true, position: true, overflow: true, preload: false"><img loading="lazy" decoding="async" class="graphic" src="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-1x.jpg" sizes="auto, (min-width: 1200px) 581px, (max-width: 1199px) and (min-width: 980px) 462px, (max-width: 979px) and (min-width: 768px) 347px, (max-width: 767px) calc(100vw - 50px)" srcset="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-2x.jpg 1200w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-1x.jpg 600w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-small.jpg 355w" alt="Insecticide-treated cornfields had higher pest abundance than untreated, regenerative cornfields." width="600" height="410" data-image-id="fig-1" data-full="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-full.png" data-thumb="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1-thumb.jpg" data-original="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-1.png" data-image-type="figure" data-jats-mimetype="image" data-jats-mime-subtype="png" /></a></div><figcaption>
<h3 class="heading"><span class="caption-label">Figure 1: </span>Insecticide-treated cornfields had higher pest abundance than untreated, regenerative cornfields.</h3>
<p><span class="p">Values presented are mean ± SEM total pests (corn rootworm adults, European corn borers, Western bean cutworm, other caterpillars, and aphids) per m<sup>2</sup>, and were assessed during corn anthesis. The systems were regarded as best-management practices for the sampled region by the farmers themselves. All conventional farms planted neonicotinoid-treated, Bt corn seed to prophylactically reduce pests, and some cornfields were also sprayed with insecticides. Regenerative farms included &gt;3 of the following practices: use of a multispecies cover crop, abandonment of insecticide, abandonment of tillage, and the cropland was grazed, etc. Pest abundance was significantly different in the two systems (<i>α</i> = 0.05; <i>n</i> = 39 regenerative cornfields and 40 conventional cornfields).</span></p>
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<figure id="fig-2" class="fig has-plink"><i class="icon-comment icon-flip-horizontal"></i></p>
<div class="image-container"><a class="fresco" title="View the full image" href="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-2x.jpg" data-fresco-caption="Figure 2: Regenerative corn fields generate nearly twice the profit of conventionally managed corn fields." data-fresco-group="figure" data-fresco-options="fit: 'width', ui: 'outside', thumbnails: false, loop: true, position: true, overflow: true, preload: false"><img loading="lazy" decoding="async" class="graphic" src="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-1x.jpg" sizes="auto, (min-width: 1200px) 581px, (max-width: 1199px) and (min-width: 980px) 462px, (max-width: 979px) and (min-width: 768px) 347px, (max-width: 767px) calc(100vw - 50px)" srcset="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-2x.jpg 1200w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-1x.jpg 600w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-small.jpg 355w" alt="Regenerative corn fields generate nearly twice the profit of conventionally managed corn fields." width="600" height="340" data-image-id="fig-2" data-full="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-full.png" data-thumb="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2-thumb.jpg" data-original="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-2.png" data-image-type="figure" data-jats-mimetype="image" data-jats-mime-subtype="png" /></a></div><figcaption>
<h3 class="heading"><span class="caption-label">Figure 2: </span>Regenerative corn fields generate nearly twice the profit of conventionally managed corn fields.</h3>
<p><span class="p">The heights of the bars represent average gross profits across all 40 fields (in each treatment). Profit was calculated using direct costs and revenues for each field and excludes any overhead and indirect expenses. Regenerative cornfields implemented three or more practices such as planting a multispecies cover mix, eliminating pesticide use, abandoning tillage, and integrating livestock onto the crop ground. Conventional cornfields used fewer than two of these practices. The regenerative systems had 70% higher profit than conventional cornfields (<i>α</i> = 0.05; <i>n</i> = 36 fields in each system). Seed drying, corn planting, and cover crop planting are present on the graphs, but were negligible costs.</span></p>
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<p id="p-9" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>Despite having lower grain yields, the regenerative system was nearly twice as profitable as the conventional corn farms (ANOVA; <i>F</i><sub>1,70</sub> = 14.35, <i>P</i> &lt;  0.001; <a class="xref xref-fig" title="" href="https://peerj.com/articles/4428/#fig-2" data-jats-ref-type="fig" data-jats-rid="fig-2" data-original-title="">Fig. 2</a>). Regenerative farms produced 29% less corn grain than conventional operations (8,481 ± 684 kg/ha vs. 11,884 ±  648 kg/ha; ANOVA; <i>F</i><sub>1,70</sub> = 8.39, <i>P</i> = 0.01). Yield reductions are commonly reported in more ecologically based food production systems relative to conventional systems (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.agsy.2011.12.004" data-jats-ref-type="bibr" data-jats-rid="ref-9" data-original-title="The crop yield gap between organic and conventional agriculture">De Ponti, Rijk &amp; Van Ittersum, 2012</a>). However, only 4% of calories produced as corn grain is eaten directly by humans, and almost none is consumed as grain. Thirty-six percent of grain is fed to livestock (<a class="xref xref-bibr" title="" href="http://www.nass.usda.gov/" data-jats-ref-type="bibr" data-jats-rid="ref-31" data-original-title="National Agriculture Statistics Service">NASS, 2017</a>), and corn-fed beef contains only 13% of the total calories produced by corn grain. Two ways that regenerative systems could increase the human food produced per ha in cornfields would be to increase the diversity of livestock on the field, or increasing the duration of grazing current stock. The relative profitability in the two systems was driven by the high seed and fertilizer costs that conventional farms incurred (32% of the gross income went into these inputs on conventional fields, versus only 12% in regenerative fields), and the higher revenue generated from grain and other products produced (e.g., meat production) on the regenerative corn fields (<a class="xref xref-fig" title="" href="https://peerj.com/articles/4428/#fig-2" data-jats-ref-type="fig" data-jats-rid="fig-2" data-original-title="">Fig. 2</a>). The high seed costs on conventional farms are largely attributable to premiums paid by farmers for prophylactic insecticide traits (no insecticide was applied as spray on these fields), whose value is questionable due to pest resistance and persistent low abundance for some targeted pests in the Northern Plains (<a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Evidence%20for%20regional%20suppression%20of%20European%20corn%20borer%20populations%20in%20Bt%20maize%20in%20the%20midwestern%20US:%20analysis%20of%20long-term%20time%20series%E2%80%99%20from%20three%20states&amp;author=Hutchison&amp;publication_year=2007" data-jats-ref-type="bibr" data-jats-rid="ref-15" data-original-title="Evidence for regional suppression of European corn borer populations in Bt maize in the midwestern US: analysis of long-term time series’ from three states">Hutchison et al., 2007</a>; <a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Planting%20of%20neonicotinoid-treated%20maize%20poses%20risks%20for%20honey%20bees%20and%20other%20non-target%20organisms%20over%20a%20wide%20area%20without%20consistent%20crop%20yield%20benefit&amp;author=Krupke&amp;publication_year=2017" data-jats-ref-type="bibr" data-jats-rid="ref-19" data-original-title="Planting of neonicotinoid-treated maize poses risks for honey bees and other non-target organisms over a wide area without consistent crop yield benefit">Krupke et al., 2017</a>). Regenerative farmers reduced their fertilizer costs by including legume-based cover crops on their fields during the fallow period (<a class="xref xref-bibr" title="" href="https://doi.org/10.2134%2Fagronj1984.00021962007600010014x" data-jats-ref-type="bibr" data-jats-rid="ref-11" data-original-title="Nitrogen from legume cover crops for no-tillage corn">Ebelhar, Frye &amp; Blevins, 1984</a>), adopting no-till practices (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.still.2006.11.004" data-jats-ref-type="bibr" data-jats-rid="ref-22" data-original-title="Evolution of the plow over 10,000 years and the rationale for no-till farming">Lal, Reicosky &amp; Hanson, 2007</a>), and grazing the crop field with livestock (<a class="xref xref-bibr" title="" href="https://scholar.google.com/scholar_lookup?title=Reconsidering%20integrated%20crop-livestock%20systems%20in%20North%20America&amp;author=Russelle&amp;publication_year=2010" data-jats-ref-type="bibr" data-jats-rid="ref-36" data-original-title="Reconsidering integrated crop-livestock systems in North America">Russelle, Entz &amp; Franzluebbers, 2010</a>). They also received higher value for their crop by receiving an organic premium, by selling their grain directly to consumers as seed or feed, and by extracting more than just corn revenue from their field (e.g., by grazing cover mixes with livestock).</p>
<p id="p-10" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>The profitability of a corn field was not related to grain yields (<i>F</i><sub>1,70</sub> &lt; 0.001; <i>P</i> = 0.98; <i>r</i><sup>2</sup> &lt; 0.01; profit = −0.0006[yield] + 1,274), but was positively correlated with the level of POM in the soil, and inversely related to the bulk density of the soil (<a class="xref xref-fig" title="" href="https://peerj.com/articles/4428/#fig-3" data-jats-ref-type="fig" data-jats-rid="fig-3" data-original-title="">Fig. 3</a>; the SOM quantities upon which %POM are presented here are reported in <a class="xref xref-table" href="https://peerj.com/articles/4428/#table-2" data-jats-ref-type="table" data-jats-rid="table-2">Table 2</a>). Organic matter is considered by some as the basis for productivity in the soil (<a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj1997.03615995006100010001x" data-jats-ref-type="bibr" data-jats-rid="ref-17" data-original-title="Soil quality: a concept, definition, and framework for evaluation">Karlen et al., 1997</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.1038%2F371783a0" data-jats-ref-type="bibr" data-jats-rid="ref-42" data-original-title="The role of soil organic matter in sustaining soil fertility">Tiessen, Cuevas &amp; Chacon, 1994</a>), and soils with high SOM typically have lower bulk density. SOM increases water infiltration rates, and supports greater microbial and animal abundance and diversity (<a class="xref xref-bibr" title="" href="https://doi.org/10.3390%2Fsu7010988" data-jats-ref-type="bibr" data-jats-rid="ref-24" data-original-title="Understanding and enhancing soil biological health: the solution for reversing soil degradation">Lehman et al., 2015</a>). The components of POM are the labile portion of this SOM, and are frequently used to study the effects of management-based differences in SOM (<a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj1992.03615995005600030017x" data-jats-ref-type="bibr" data-jats-rid="ref-6" data-original-title="Particulate soil organic-matter changes across a grassland cultivation sequence">Cambardella &amp; Elliott, 1992</a>). The only way to generate SOM <i>in situ</i> in cropland is through fostering biology, which inherently is driven by plant communities through sequestration of CO<sub>2</sub> from the atmosphere. Eliminating tillage (<a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj2005.0334" data-jats-ref-type="bibr" data-jats-rid="ref-33" data-original-title="Particulate organic matter and water-stable aggregation of soil under contrasting management">Pikul Jr et al., 2007</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj1999.6351350x" data-jats-ref-type="bibr" data-jats-rid="ref-39" data-original-title="Aggregate and soil organic matter dynamics under conventional and no-tillage systems">Six, Elliott &amp; Paustian, 1999</a>), implementing cover crops (<a class="xref xref-bibr" title="" href="https://doi.org/10.1016%2Fj.geoderma.2005.01.019" data-jats-ref-type="bibr" data-jats-rid="ref-10" data-original-title="Effect of cover crop management on soil organic matter">Ding et al., 2006</a>; <a class="xref xref-bibr" title="" href="https://doi.org/10.2136%2Fsssaj1997.03615995006100010022x" data-jats-ref-type="bibr" data-jats-rid="ref-20" data-original-title="Winter cover crop effects on soil organic carbon and carbohydrate in soil">Kuo, Sainju &amp; Jellum, 1997</a>), and cycling plant residue through livestock (<a class="xref xref-bibr" title="" href="https://doi.org/10.2135%2Fcropsci2007.07.0390" data-jats-ref-type="bibr" data-jats-rid="ref-43" data-original-title="Soil compaction, corn yield response, and soil nutrient pool dynamics within an integrated crop-livestock system in Illinois">Tracy &amp; Zhang, 2008</a>) all enhance this process, and all are important practices used in regenerative food systems that raise POM in the soil.</p>
<figure id="fig-3" class="fig has-plink"><i class="icon-comment icon-flip-horizontal"></i></p>
<div class="image-container"><a class="fresco" title="View the full image" href="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-2x.jpg" data-fresco-caption="Figure 3: Corn fields with high particulate organic matter and low bulk density in the soil have greater profits." data-fresco-group="figure" data-fresco-options="fit: 'width', ui: 'outside', thumbnails: false, loop: true, position: true, overflow: true, preload: false"><img loading="lazy" decoding="async" class="graphic" src="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-1x.jpg" sizes="auto, (min-width: 1200px) 581px, (max-width: 1199px) and (min-width: 980px) 462px, (max-width: 979px) and (min-width: 768px) 347px, (max-width: 767px) calc(100vw - 50px)" srcset="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-2x.jpg 1200w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-1x.jpg 600w, https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-small.jpg 355w" alt="Corn fields with high particulate organic matter and low bulk density in the soil have greater profits." width="600" height="507" data-image-id="fig-3" data-full="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-full.png" data-thumb="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3-thumb.jpg" data-original="https://dfzljdn9uc3pi.cloudfront.net/2018/4428/1/fig-3.png" data-image-type="figure" data-jats-mimetype="image" data-jats-mime-subtype="png" /></a></div><figcaption>
<h3 class="heading"><span class="caption-label">Figure 3: </span>Corn fields with high particulate organic matter and low bulk density in the soil have greater profits.</h3>
<p><span class="p">Corn fields were managed under either conventional or regenerative systems, and profit was calculated using direct costs and revenues for each field and excludes any overhead and indirect expenses. (general linear regression model; <i>F</i><sub>1,16</sub> = 7.84; <i>P</i> = 0.01; <i>r</i><sup>2</sup> = 0.34; profit = 29.68[POM]–66.94; bulk density; <i>F</i><sub>1,19</sub> = 5.23; <i>P</i> = 0.03; <i>r</i><sup>2</sup> = 0.24; profit = −975 [POM] + 1,593).</span></p>
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</div>
</figcaption></figure>
<figure id="table-2" class="table-wrap has-plink"><i class="icon-comment icon-flip-horizontal"></i></p>
<div class="caption"><span class="caption-label">Table 2:</span></p>
<div class="title">Soil organic matter on regenerative and conventional corn farms.</div>
<p><span class="p">Shaded rows represent regenerative corn farms.</span></div>
<div class="table-container">
<table class="table table-bordered table-condensed table-hover">
<colgroup>
<col />
<col />
<col /></colgroup>
<thead>
<tr>
<th>Reference town</th>
<th>Farm locations (latitude, longitude)</th>
<th>SOM (%)</th>
</tr>
</thead>
<tbody>
<tr>
<td>Bladen, NE</td>
<td>40.31971, −98.57358</td>
<td>6.23</td>
</tr>
<tr>
<td>Bladen, NE</td>
<td>40.33703, −98.56301</td>
<td>4.52</td>
</tr>
<tr>
<td>York, NE</td>
<td>40.63054, −97.66534</td>
<td>6.21</td>
</tr>
<tr>
<td>York, NE</td>
<td>40.97390, −97.49031</td>
<td>5.55</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.85280, −100.60131</td>
<td>4.19</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.85280, −100.35145</td>
<td>N/A</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>46.81734, −100.51257</td>
<td>5.82</td>
</tr>
<tr>
<td>Bismarck, ND</td>
<td>47.14250, −100.19720</td>
<td>3.85</td>
</tr>
<tr>
<td>White, SD</td>
<td>44.42572, −96.58806</td>
<td>N/A</td>
</tr>
<tr>
<td>White, SD</td>
<td>44.41155, −96.60008</td>
<td>5.52</td>
</tr>
<tr>
<td>Pipestone, MN</td>
<td>44.11446, −96.32468</td>
<td>N/A</td>
</tr>
<tr>
<td>Pipestone, MN</td>
<td>44.12416, −96.36422</td>
<td>4.75</td>
</tr>
<tr>
<td>Toronto, SD</td>
<td>44.59248, −96.57923</td>
<td>7.60</td>
</tr>
<tr>
<td>Toronto, SD</td>
<td>44.57960, −96.58367</td>
<td>6.38</td>
</tr>
<tr>
<td>Gary, SD</td>
<td>44.80565, −96.34708</td>
<td>7.53</td>
</tr>
<tr>
<td>Gary, SD</td>
<td>44.80689, −96.35465</td>
<td>7.36</td>
</tr>
<tr>
<td>Arlington, SD</td>
<td>44.41566, −97.18795</td>
<td>8.17</td>
</tr>
<tr>
<td>Arlington, SD</td>
<td>44.42644, −97.25077</td>
<td>8.18</td>
</tr>
<tr>
<td>Lake Norden, SD</td>
<td>44.58976, −97.08649</td>
<td>4.56</td>
</tr>
<tr>
<td>Lake Norden, SD</td>
<td>44.55.6839, −97.243820</td>
<td>6.26</td>
</tr>
</tbody>
</table>
</div>
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</figure>
</section>
<section id="conclusions" class="sec">
<h2 class="heading">Conclusions</h2>
<p id="p-13" class="has-plink"><i class="icon-comment icon-flip-horizontal"></i>The farmers themselves have devised an ecologically based production system comprised of multiple practices that are woven into a profitable farm that promotes ecosystem services. Regenerative farms fundamentally challenge the current food production paradigm that maximizes gross profits at the expense of net gains for the farmer. Key elements of this successful approach to farming include</p>
<ol id="list-1" class="list" data-jats-list-type="order">
<li class="list-item">
<p id="p-14">By promoting soil biology and organic matter and biodiversity on their farms, regenerative farmers required fewer costly inputs like insecticides and fertilizers, and managed their pest populations more effectively.</p>
</li>
<li class="list-item">
<p id="p-15">Soil organic matter was a more important driver of proximate farm profitability than yields were, in part because the regenerative farms marketed their products differently or had a diversified income stream from a single field.</p>
</li>
</ol>
</section>
<section id="supplemental-information" class="sec">
<h2 class="heading">Supplemental Information</h2>
<div id="supp-1" class="supplementary-material well well-small" data-jats-mimetype="application" data-jats-mime-subtype="vnd.openxmlformats-officedocument.spreadsheetml.sheet">
<h3 class="heading">Raw data</h3>
<p id="p-16">The raw data used to generate the published results.</p>
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</section>
<div id="additional-information" class="sec">
<h2 class="heading">Additional Information and Declarations</h2>
<div class="fn-group" data-jats-content-type="competing-interests">
<h3 class="heading">Competing Interests</h3>
<div id="conflict-1" class="fn" data-jats-fn-type="conflict">
<p>Jonathan G. Lundgren is the CEO for Blue Dasher Farm and director of the Ecdysis Foundation. Claire E. LaCanne is an employee of the University of Minnesota, and was a graduate student for South Dakota State University during her thesis program (this work is part of that thesis).</p>
</div>
</div>
<div class="fn-group" data-jats-content-type="author-contributions">
<h3 class="heading">Author Contributions</h3>
<div id="contribution-1" class="fn" data-jats-fn-type="con">
<p><a class="xref xref-contrib" href="https://peerj.com/articles/4428/#author-1" data-jats-ref-type="contrib" data-jats-rid="author-1">Claire E. LaCanne</a> conceived and designed the experiments, performed the experiments, analyzed the data, prepared figures and/or tables, authored or reviewed drafts of the paper, approved the final draft.</p>
</div>
<div id="contribution-2" class="fn" data-jats-fn-type="con">
<p><a class="xref xref-contrib" href="https://peerj.com/articles/4428/#author-2" data-jats-ref-type="contrib" data-jats-rid="author-2">Jonathan G. Lundgren</a> conceived and designed the experiments, analyzed the data, contributed reagents/materials/analysis tools, prepared figures and/or tables, authored or reviewed drafts of the paper, approved the final draft.</p>
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<h3 class="heading">Data Availability</h3>
<div id="addinfo-1" class="fn">
<p>The following information was supplied regarding data availability:</p>
<p>The raw data is provided as a <a class="xref xref-supplementary-material" href="https://peerj.com/articles/4428/#supplemental-information" data-jats-ref-type="supplementary-material" data-jats-rid="supplemental-information">Supplemental File</a>.</p>
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<h3 class="heading">Funding</h3>
<p>The project was supported by USDA PMAP Award # 2013-34381-21245, a NC-SARE graduate student fellowship GNC16-227, and donations of farmers and beekeepers to Ecdysis Foundation. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.</p>
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<h2>Acknowledgements</h2>
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<section id="acknowledgements" class="ack">We thank our 20 farmers throughout the Northern Plains for providing us with study sites and management information. E Adee, M Bredeson, J Fergen, D Grosz, K Januschka, N Koens, R LaCanne, M La Vallie, A Leiferman, J Lundgren, A Martens, C Mogren, K Nemec, A Nikolas, J Pecenka, G Schen, C Snyder, &amp; K Weathers assisted field work. R Conser, M Entz, C Morrissey, &amp; R Teague provided comments on earlier drafts. M Longfellow and L Hesler identified invertebrates. Mention of trade names or commercial products in this publication does not imply recommendation or endorsement by South Dakota State University or Ecdysis Foundation.</p>
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<p><strong>source: </strong><a href="https://landstewardshipproject.org/posts/360">https://landstewardshipproject.org/posts/360</a></p>
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		<title>Healthy Soil, Healthy Farms, Healthy Communities</title>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 03:55:09 +0000</pubDate>
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					<description><![CDATA[<p>On a crisp morning in September, North Dakota farmer Gabe Brown held two handfuls of soil and searched for signs of life—theoretically not a difficult task considering one teaspoon of humus contains more organisms than there are humans in the world. But many of the bacteria and invertebrates that lurk in the dark basement of [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/healthy-soil-healthy-farms-healthy-communities/">Healthy Soil, Healthy Farms, Healthy Communities</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<p>On a crisp morning in September, North Dakota farmer Gabe Brown held two handfuls of soil and searched for signs of life—theoretically not a difficult task considering one teaspoon of humus contains more organisms than there are humans in the world. But many of the bacteria and invertebrates that lurk in the dark basement of our farm fields exist visually only in the world of high-powered microscopes. So Brown, a compact ball of energy who can somehow combine references to soil biology, farm policy and animal husbandry in the same sentence, uses a less scientific assessment method to compare and contrast the two handfuls—one from his field, the other from a neighbor’s.</p>
<p>“When you grab this soil there is no structure,” says Brown, referring to his neighbor’s soil. Indeed, it has a slabbed, compacted look to it, indicating there isn’t much room for worms and roots to facilitate transfer of water and nutrients. It’s also a lighter color than Brown’s darker soil, which is the consistency of cottage cheese. “If you have this dark color, you know you have organic matter. I look at it as an investment.”</p>
<p>It’s an investment in a good crop—just a few feet away stands a field of corn that’s emerged<img decoding="async" src="https://landstewardshipproject.org/cmsimage/685/medium" /> from Brown’s rich soil, and it’s thriving, a rarity this year in a part of North Dakota that has been hit especially hard by drought. But to Brown, that healthy soil represents more than more bushels in the bin. It’s also an investment in his farm’s long-term viability and the future of his entire community—human and natural.</p>
<p>The idea that <a href="http://soils.usda.gov/sqi/" target="_blank" rel="noopener">healthy soil</a> is an investment, not just one of many tools, has led Brown and his neighbors to develop a farming system that combines some of the most exciting advances in sustainable production systems—conservation tillage, multi-species cover cropping, mob grazing and frequent rotations. This system, which is evolving, combines cutting-edge soil science with the desire on the part of natural resource professionals to no longer accept a Band Aid approach to conservation. It also shows how teamwork fueled by a holistic, big picture view of agriculture can produce a farming system that benefits land, farmers and communities.</p>
<p>“What Brown and the others he is working with are doing is one of the most exciting and revolutionary in-the-field developments in agriculture today,” says Richard Ness, a Land Stewardship Project staff member who has worked with sustainable farmers throughout the Midwest and who has spent time in south-central North Dakota, where Brown farms. “They’re pushing scientists, conservationists and sustainable agriculture in general to a new level.”</p>
<h3>Getting at the root of the matter</h3>
<p>At the core of this story is a change in attitude toward soil—perhaps one of the most taken-for-granted resources around. Consider, for example, how Jay Fuhrer used to do his job. Fuhrer is the <a href="http://www.bcscd.com/" target="_blank" rel="noopener">Burleigh County district conservationist</a> for the USDA’s Natural Resources Conservation Service (NRCS). Burleigh County lies near the section of the Missouri River where it passes through the south-central part of North Dakota. Here the flatness of the state gives way to a more rolling landscape—a landscape known for wheat, “wild” pastures that contain native species such as big bluestem, hay ground and, in the past decade or so, corn. This part of the state receives on-average 16 inches of rain a year, making water a dear resource. So for many years Fuhrer and other resource professionals focused on short-term efforts to get more water into the soil profile and keep it where plants could use it.</p>
<p><img decoding="async" class="alignright" src="https://landstewardshipproject.org/cmsimage/546/small" alt="Image" />“We had accepted a degraded resource,” Fuhrer recalls as he sits in his office in Bismarck, just a few miles from Brown’s farm. “And when you accept a degraded resource you generally work from the viewpoint of minimizing the loss. And so we would apply a lot of practices.”</p>
<p>Fuhrer’s specialty during the 1980s and early 1990s was putting in <a href="http://en.wikipedia.org/wiki/Grassed_waterway" target="_blank" rel="noopener">grassed waterways</a> in an attempt to keep water from running off so quickly. It helped, but didn’t get at the core of the issue: why was that water not infiltrating the soil in the first place?</p>
<p>“In retrospect very few of those waterways were actually needed,” he concedes.</p>
<p>What farmers like Brown and soil scientists in the area were starting to figure out was that the production system that had come to predominate—extensive tillage, low crop diversity, no cover crops, livestock kept out all-season long on overgrazed pastures—was compacting the soil to the point where little water could make its way beneath the surface. It was also sharply reducing the amount of soil organic matter, which drives the entire soil food web. Unbroken prairie soils can have as much as 10 percent to 15 percent organic matter. But because of intensive tillage, Midwestern soil organic matter levels have plummeted to below 1 percent of total soil volume in some cases. This means the soil has little opportunity to cook up its own fertility via the exchange of nutrients, making it increasingly dependent on applications of petroleum-based fertilizers.</p>
<h3>Learning from failure</h3>
<p>There is a <a href="http://landstewardshipproject.org/repository/1/555/managing_soil_biota_nichols.pdf" target="_blank" rel="noopener">photo that has acquired almost legendary status</a> in Burleigh County. It shows one of Gabe Brown’s fields after 13 inches of rain fell in 24 hours. The picture shows no standing water on this low-lying field, even though plots on neighboring land are inundated. Brown has created a soil profile that allows water to infiltrate quite efficiently. And unlike a field that’s been drained through artificial tiling—sending water at rocket speed through the profile and eventually downstream—Brown’s fields retain that moisture in the system, meaning plants can access it during drier periods. Such a healthy water cycle requires a healthy biological food web.</p>
<p><a href="http://www.ars.usda.gov/pandp/people/people.htm?personid=35170" target="_blank" rel="noopener">Kristine Nichols</a>, a soil microbiologist at the USDA’s <a href="http://www.ars.usda.gov/Main/docs.htm?docid=17646" target="_blank" rel="noopener">Northern Great Plains Research Laboratory</a> in Mandan, N. Dak., says this photo is a prime indicator that farmers like Brown are able to increase their organic matter to the point where it is able to, for example, make better use of water. As soil organic matter increases from 1 percent to 3 percent, soil’s water holding capacity doubles. During the past decade or so, Brown has more than doubled the organic matter in some of his fields, raising it from less than 2 percent to nearly 5 percent.</p>
<p>Nichols says that as a soil scientist she was taught that a farmer couldn’t have a positive impact on soil organic matter in a typical lifetime.</p>
<p>“We were told this was something we couldn’t change, except in a negative way. Now we realize we can change organic matter,” she says while sitting in her office across the Missouri River from Bismarck. That’s important, Nichols adds, because in the case of organic matter, “You have something that’s less than 5 percent of the soil, but it controls 90 percent of the functions.”</p>
<p>Brown came to his own realization that he could have a positive impact on organic matter somewhat by accident. He and his wife Shelly bought their <a href="http://www.brownsranch.us/" target="_blank" rel="noopener">farm</a> from her parents in 1991, and in 1994 they went 100 percent no-till as a way to save moisture in their cropping system, which produced mostly small grains like wheat. Brown liked the no-till system, but bad weather produced a string of crop failures during the late 1990s.</p>
<p>It made things extremely difficult financially, to the point where the Browns were having a hard time borrowing enough money to purchase fertilizer. This forced them to start planting more legumes such as field peas, triticale and hairy vetch that could fix nitrogen and provide more homegrown fertility while feeding their cattle herd.</p>
<p>“I was using cover crops but I didn’t really grasp soil health,” recalls Brown. What he did grasp was that his wheat often did better when planted into ground that had just produced a cover crop. His soil color and texture was improving, organic matter levels were rising and water seemed to infiltrate the soil profile, rather than simply running off.</p>
<p>“So we had four crop failures in a row, and I tell people today that was absolutely the best thing that could have happened to me and my family, although we didn’t think that at the time,” Brown says with a laugh as he guides his pickup past beef cattle grazing a cocktail mix of warm season cover crops.</p>
<p>Fuhrer and other soil conservation experts in the region were impressed with Brown’s results and began talking about ways of combining cover cropping, livestock impact and no-till agriculture in a way that soil quality could actually be improved, not just maintained at a high enough level to grow a stand of wheat. For Fuhrer, taking such proactive steps couldn’t have come at a better time—he had grown frustrated with applying practices that simply maintained the status quo, if that.</p>
<h3>Diversity is strength</h3>
<p>Frankly, cover crops are nothing new. Natural resource professionals <a href="http://www.sare.org/Learning-Center/Books/Managing-Cover-Crops-Profitably-3rd-Edition" target="_blank" rel="noopener">have long promoted</a> planting a soil-friendly crop like rye in the fall after corn or soybeans are harvested as a way to reduce erosion. Such cover crops are often seen as having no immediate economic value, making them a tough sell in row crop country.</p>
<p>But in <a href="http://www.bcscd.com/" target="_blank" rel="noopener">Burleigh County</a>, the cover cropping concept has been taken to whole new level, and farmers have begun to see them as an integral part of their long-term financial viability, as well as the land’s ecological health. Again, this breakthrough on cover crops came at failure’s doorstep.</p>
<p>In 2006 Fuhrer was examining eight different species of cover crops planted on <a href="http://www.bcscd.com/" target="_blank" rel="noopener">test plots</a>. In one plot each species had been planted as a monoculture, and the other plots contained various combinations: two-way mix, three-way, etc., all the way up to where all eight species were planted together.</p>
<p>“And then we had one of the driest years on record,” recalls Fuhrer. “And then I just thought, oh, everything’s failed and we’re just not going to learn anything this year. And I was so wrong.”</p>
<p>What Fuhrer and his colleagues learned was that the monocultures failed, and the mixes involving just a few species didn’t fare much better. But the eight-way mixture didn’t seem drought stressed at all, and in fact yielded quite well.</p>
<p>“It really taught us a lot from the viewpoint of how plants won’t necessarily compete with each other—they can actually help each other,” says Fuhrer.</p>
<p>Minnesota <a href="http://www.nsf.gov/news/news_summ.jsp?cntn_id=107018&amp;org=NSF" target="_blank" rel="noopener">ecologists have found that in planted prairies</a>, greater diversity resulted in a similar synergistic effect—making the entire system more resilient. Fuhrer and his colleagues started thinking that maybe it was a lack of carbon below the soil that was the problem. The difference between soil and dirt is soil produces life, and it can do that because it contains carbon. And socking away that carbon for a rainy day (or a very dry one) pays big dividends.</p>
<p>Those eight species of plants growing above ground may appear to be in competition, but all the while they are creating an incredibly diverse subterranean ecosystem. Soil scientists say a diverse root system can create a soil that is resilient, less erosion prone and able to develop its own fertility.</p>
<p>“We figured out we wanted to stimulate soil biology through nutrient cycling and through roots,” says Brown. “Well, let’s have something really diverse and try it.”</p>
<p>These days most of Brown’s <a href="http://www.brownsranch.us/?id=13" target="_blank" rel="noopener">cover crop mixes contain as many as 20 species</a>. The goal is to keep the soil covered and spider-webbed with roots year-round, and to extend the subsoil’s active biological season as long as possible—the greater variety of species above ground, the greater diversity of species below ground. In a typical year, Brown will do this by planting four crop types: warm season broadleafs such as alfalfa, buckwheat, chick pea, cowpea and sunflower; warm season grasses such as corn, millet, sorghum and Sudan; cool season grasses such as barley, oats and triticale; and cool season broadleafs such as canola, flax, vetch and sweet clover.</p>
<p>A growing season may consist of Brown planting winter wheat, harvesting it in June or July and planting a cocktail mix of warm season crops. Once they’ve grown up by late summer, these crops can be grazed well into the fall and even into early winter, producing good cash flow through the animals. The manure and urine deposited by the cattle, plus the trampling they execute while browsing, builds nutrients and carbon in the soil while supercharging biological activity, providing the basis for planting another cash crop like corn the following spring.</p>
<p>What must be kept in mind is that this isn’t strictly a no-till system, or strictly a grazing system. No-till—planting crops in ground that’s been disturbed as little as possible—is better for the soil than heavy tillage, but it doesn’t take full advantage of the nutrients and biological activity present deep in the soil profile, says Brown. He points out that the neighbor’s soil that’s lower in organic matter than his has actually been under a no-till regime since the late 1990s.</p>
<p>And grazing perennial grasses, again a more soil-friendly system when compared to tillage, isn’t the final word. Hal Weiser, a soil health specialist with the North Dakota NRCS, estimates that some of the season-long grazed land in the area has water infiltration rates of only a quarter inch. “Which is simply unacceptable,” he says.</p>
<p>Several years ago farmers in the region began switching from simply turning cattle out into large pastures for the entire season, to breaking them up into rotated paddocks. This provided extended rest periods for grass, and pastures responded with healthier stands that provided forage longer.</p>
<p>But more recently livestock producers have taken that rotational grazing concept one step further by utilizing mob grazing—a system where a lot of animals are placed in a paddock for sometimes only a few hours. The animals browse the most palatable part of the plants and generate a lot of biological activity, but don’t compact the soil. This system comes with the assumption that the cattle won’t make the most efficient use of all the forage—in fact they may trample a good amount of it, which is not only acceptable, but may be preferable in some cases. All that trampling just puts carbon underground and generates biological activity, in effect feeding the soil.</p>
<h3>Making soil the focus</h3>
<p>Nichols says the key to this system is accepting that soil is at the center of one’s farming system—not just another input that can be plugged in. That “dirt” is much more complex than we once thought is becoming increasingly evident as new advances in electron microscopes (thanks to medical technology) and DNA testing offer unprecedented glimpses into this fascinating world. But Nichols points out that in a way soil is a “big black box” that’s just becoming “blacker” as science churns up new information about what goes on beneath our feet.</p>
<p>“The chemistry happens the way the chemistry happens. But when you throw biology into the mix, it gets complicated,” she says while flashing microscopic images of soil organisms on her computer. “In some ways it’s a step backwards—we thought we knew 10 percent of the organisms in soil, now we realize it’s less than 1 percent.”</p>
<p>But that may not necessarily be a bad thing. It’s when farmers begin seeing soil as the heart of an extremely complex, oftentimes mysterious, system that they can start taking steps to get at the problem, rather than just treating the symptoms.</p>
<p>Nichols, who grew up on a southwest Minnesota crop farm, says a prime example of treating symptoms without getting at the core of the problem is what’s happening in the Minnesota River Valley with erosion. There are indications that field-level erosion in the Valley has gone down, thanks to the adoption of conservation farming techniques, among other things. However, studies show that sedimentation of the river continues at an alarming rate.</p>
<p>“What is going on with the soil now where we can’t get the infiltration of water?” Nichols asks. “We addressed some of the symptoms, which was great, but did we address the bottom line?”</p>
<p>An example of the bottom line being addressed is when microorganisms do something called “habitat engineering,” which has huge implications for not only cutting erosion, but also making sure soil can cook up its own fertility while staying in place. When soil does not have good aeration and plenty of pore space, it loses its ability to stick together and form strong aggregates.</p>
<p>“The water coming in can actually cause these aggregates to explode with air pressure,” says Nichols of a typical soil erosion situation in compacted soils.</p>
<p>But soils with more carbon feed themselves, and extra “food” goes into developing a waxy glue that holds aggregates together, creating a habitat where water can’t build up explosive pressure.</p>
<p>“They’ve actually engineered an environment that’s safe, that has food and has the ability to produce carbon to self-perpetuate,” she says. “The more of these aggregates there are, and the larger they are, the less susceptible to erosion the soil is. We’ve found management can impact this.”</p>
<h3>Investing in the soil bank</h3>
<p>Being able to improve soil’s ability to engineer its own healthy environment has huge implications on and off the farm.</p>
<p>Soil provides at least <a href="http://www.nature.com/news/2008/081008/full/455724a.html" target="_blank" rel="noopener">$1.5 trillion in services worldwide</a> annually, according to the journal <em>Nature</em>. For example,<a href="http://www.nature.com/news/2008/081008/full/455724a.html" target="_blank" rel="noopener"> soil stockpiles 1,500 gigatonnes of carbon</a>, more than the Earth’s atmosphere and all the plants on the planet. And it’s the organic matter that does the heavy lifting: it can hold 10 to 1,000 times more water and nutrients than the same amount of soil minerals.</p>
<p>In recent decades, great strides have been made in reducing soil erosion to “T”, or “tolerable” loss rates—that’s the rate at which soil can be lost and still replaced. This is thanks to conservation tillage and structures such as grassed waterways and terraces.</p>
<p>But it’s become clear even bigger strides in conservation could be made by increasing soil carbon content, or managing for “C.” One <a href="http://www.nm.nrcs.usda.gov/technical/tech-notes/soils/soil2.pdf" target="_blank" rel="noopener">NRCS estimate</a> is that if all of our country’s cropland was managed for T, soil erosion would decline by 0.85 billion tons annually. If cropland was managed in such a way that C was increased, erosion levels would drop by 1.29 billion tons per year. In financial terms, managing for T is worth $16.5 billion annually; managing for C almost $25 billion per year.</p>
<p>But the health of soil on an international or even national level means little unless those dollars can come home to roost on the farm.</p>
<p>Brown says in his case, they already have. He <a href="http://www.brownsranch.us/" target="_blank" rel="noopener">farms around 5,400 acres</a>—1,300 of that is cropland and most of the rest is pasture. The Browns own about 1,400 acres and rent the rest, so maintaining a regular cash flow is important. The main cash crops are corn, spring wheat, triticale and vetch. They run 400 cow-calf pairs and anywhere from 300 to 800 yearlings, depending on the year</p>
<p>Increasing organic matter on his farm has allowed Brown to reduce the use of commercial fertilizer by over 90 percent, and herbicides by 75 percent, and that’s paying off big time. Sitting on a four-wheeler near one of his corn fields, Brown shows a printout that outlines the financials for his 2011 crop. At today’s fertilizer prices, each 1 percent of organic matter contains $751 worth of nitrogen, phosphorous, potassium, sulfur and carbon, he estimates. That means Brown’s 5 percent organic matter content is worth $3,755 per acre. When he figures in his expenses for the 2011 corn crop—seed, herbicide, planting, storage, etc.—his 2011 return to labor, management and land was $5.38 per bushel of corn.</p>
<p>A <a href="http://www.leopold.iastate.edu/news/07-09-2012/higher-diversity-fewer-inputs-make-profitable-farms" target="_blank" rel="noopener">long-term study done in</a> Iowa recently showed that increasing diversity in cropping systems significantly reduced a farm&#8217;s reliance on fossil fuels and chemicals without sacrificing profits.</p>
<p>Still, cover crops and grazing aren’t attractive to producers farming high-priced land and gunning for bin-busting yields.</p>
<p>“There’s such an emphasis on yield and unfortunately with a lot of these systems, there is not an increase in yield,” says Nichols of soil building farming techniques. “But if you can afford to buy an input, then you can afford the cover crop seed or the yield drag. You have to look at your goals: yield or long-term viability?”</p>
<p>Brown says he sees planting cover crops and letting cattle graze/trample them as no different than forward-pricing his fertilizer. But he concedes that in these days of record corn prices, planting a cocktail mix of forages, many of which will end up as worm food, may appear financially foolish.</p>
<p>“And now we’re going to mob graze this with cow-calf pairs probably starting next week,” he says while standing in a former Conservation Reserve Program field he is renting. It was planted to some 20 species of warm season plants on July 20; on this day in early September, the crop is up to his chest. “I’ve got to pay cropland rate on it but I’m going to seed it back to native grasses next year. Everybody thinks I’m crazy seeding good cropland back to native grass but that’s what we want to do. To us, the resource comes first. The cattle can still gain on this and we’re still making money.”</p>
<p>Given the great strides he and other farmers have made in building soil health while improving profitability, Brown is a little perplexed that more producers aren’t focusing on treating the problem, rather than the symptoms. Some of the hesitation may be the result of the “inputs in-results out” model of agriculture that predominates.</p>
<p>Invariably, when Nichols talks to farmers about how fungi can improve soil quality, someone will ask, “Where can I buy them?”</p>
<p>“We are in the mindset that we can always go out and buy something to fix a problem, which may not be a problem, but a symptom,” says Nichols.</p>
<p>Brown says government programs like federal crop insurance don’t help matters any, since <img decoding="async" class="alignright" src="https://landstewardshipproject.org/cmsimage/684/small" alt="Image" />in many ways they reward farmers for raising crops in a way that is risky, but not sustainable. Remember: he credits failure for pulling his operation out of its monocultural rut.</p>
<p>“Adversity drives change,” he says.</p>
<p>Without that adversity, farmers aren’t forced to take a closer look at whether their system is just a series of reactions to symptoms, or whether it’s getting at the root of the problem. And without such a reexamination of systems, the true potential of soil, land and farms may never be reached.</p>
<p>“Gabe did something I thought was impossible and instead of telling him, ‘Good job,’ I said, ‘What more can you do?’ ” Nichols says. “I don’t know how far we can take it, but I like the idea of not putting limitations or constraints on a system. Can we take it a little further?”</p>
<p><strong>source: </strong><a href="https://www.google.com/url?q=https://landstewardshipproject.org/posts/360&amp;source=gmail&amp;ust=1546919574596000&amp;usg=AFQjCNEKg5WmPtsZbjiHsNZ-mDcD8TE0YA">https://www.google.com/url?q=https://landstewardshipproject.org/posts/360&amp;source=gmail&amp;ust=1546919574596000&amp;usg=AFQjCNEKg5WmPtsZbjiHsNZ-mDcD8TE0YA</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/healthy-soil-healthy-farms-healthy-communities/">Healthy Soil, Healthy Farms, Healthy Communities</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<title>Can Responsible Grazing Make Beef Climate-Neutral?</title>
		<link>https://covercrops.co.nz/2019/01/07/can-responsible-grazing-make-beef-climate-neutral/</link>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 02:20:12 +0000</pubDate>
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					<description><![CDATA[<p>There’s no denying Americans eat a lot of meat. In fact, the average U.S. citizen eats about 55 pounds of beef a year, including an estimated three hamburgers a week, and the United States Department of Agriculture (USDA) expects that amount to increase by about 3 percent by 2025. This heavy reliance on animal protein carries a [&#8230;]</p>
The post <a href="https://covercrops.co.nz/2019/01/07/can-responsible-grazing-make-beef-climate-neutral/">Can Responsible Grazing Make Beef Climate-Neutral?</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></description>
										<content:encoded><![CDATA[<p>There’s no denying Americans eat a lot of meat. In fact, the average U.S. citizen eats about <a href="https://data.oecd.org/agroutput/meat-consumption.htm">55 pounds of beef a year</a>, including an estimated three hamburgers a week, and the United States Department of Agriculture (USDA) expects that amount to <a href="https://www.ers.usda.gov/amber-waves/2016/september/us-beef-and-pork-consumption-projected-to-rebound/">increase by about 3 percent by 2025</a>. This heavy reliance on animal protein carries a big environmental footprint—livestock production contributes <a href="http://www.fao.org/3/a-i3437e.pdf">about 14.5 percent</a> of global greenhouse gas (GHG) emissions, with <a href="http://www.fao.org/3/a-i3437e.pdf">beef constituting 41 percent of that figure</a>, thanks to the methane cattle produce in the digestion process and the fact that overgrazing can release carbon stored in soils.</p>
<p>Though most livestock production impacts the climate, the <a href="http://www.regenerationinternational.org/why-regenerative-agriculture/">regenerative agriculture movement</a> recognizes many benefits to <a href="https://civileats.com/2014/12/01/nicolette-niman-our-beef-shouldnt-be-with-cows/">properly managed livestock grazing</a>, including carbon sequestration, restoring topsoil, improving ecosystem biodiversity, reducing pesticide and fertilizer inputs, and producing more nutritious food.</p>
<p>Yet despite the benefits of careful grazing, the question remains: Can cattle be raised, fed, and slaughtered in a way that reduces their greenhouse gas emissions to a tolerable level?</p>
<p>A new five-year <a href="https://www.sciencedirect.com/science/article/pii/S0308521X17310338" rel="noopener" data-saferedirecturl="https://www.google.com/url?hl=en&amp;q=https://www.sciencedirect.com/science/article/pii/S0308521X17310338&amp;source=gmail&amp;ust=1523485347520000&amp;usg=AFQjCNFG_g7l8jYUVuO8xCCjPeF3Uqfirg">study</a> that will be published in the May 2018 issue of the journal <em>Agricultural Systems</em> suggests that they can. Conducted by a team of researchers from Michigan State University (MSU) and the <a href="https://www.ucsusa.org/" rel="noopener" data-saferedirecturl="https://www.google.com/url?hl=en&amp;q=https://www.ucsusa.org/&amp;source=gmail&amp;ust=1523485347520000&amp;usg=AFQjCNGB0SRzckQGxtbS_M3BfPSY6iHBuw">Union of Concerned Scientists</a> (UCS), the study suggests that if cattle are managed in a certain way during the finishing phase, grassfed beef can be carbon-negative in the short term and carbon-neutral in the long term.</p>
<p>The research, led by <a href="https://ourenvironment.berkeley.edu/people/paige-stanley" rel="noopener" data-saferedirecturl="https://www.google.com/url?hl=en&amp;q=https://ourenvironment.berkeley.edu/people/paige-stanley&amp;source=gmail&amp;ust=1523485347520000&amp;usg=AFQjCNGqGN8xENo5ANg2SYFf2cuVrby6LQ">Paige Stanley</a>, who earned a Master’s degree in 2017 from MSU and is now a doctoral student at the University of California, Berkeley, states, “it is possible that long-term [adaptive multi-paddock grazing] AMP grazing finishing in the Upper Midwest could contribute considerably more to climate change mitigation and adaptation than previously thought.”</p>
<p>Rather than using the common method of continuous grazing, in which cattle remain on the same pasture for an entire grazing season, the researchers used the more labor-intensive method of AMP, which entails moving the cattle <a href="https://www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/stelprdb1097378.pdf">at intervals ranging from days to months</a>, depending on the type of forage, weather, time of year, and other considerations. A herd of adult cattle on MSU grazing land served as their test population.</p>
<p>Though the study’s finding that strategic grazing can make a dent in the overall environmental impact of cattle runs counter to the widespread opinion among other researchers and climate activists, it is welcome news for advocates of regenerative agriculture.</p>
<p>Christine Jones, an Australian soil ecologist, believes the MSU paper makes an invaluable contribution to the ongoing discussion on the role livestock can play in mitigating climate change. “The research clearly demonstrates there are no net emissions of greenhouse gas with well-planned AMP grazing, due to the sequestration of soil carbon,” Jones said. AMP grazing provides “countless other ecosystem services,” she added, “including improved biodiversity, erosion control (soil is by far America’s largest export), increased soil water-holding capacity, and greater drought resilience.”</p>
<h4><strong>Managed Grazing in the Finishing Phase</strong></h4>
<p>Beef cattle’s lives are divided into <a href="http://www.sites.ext.vt.edu/virtualfarm/beef/beef_va.html">three phases</a>: the cow-calf phase from birth to weaning, which the animals generally spend in pastures, paddocks, or rangeland; the growth phase, which they often pass in open grazing areas; and the “finishing” phase in the three months prior to slaughter, during which <a href="https://www.stonebarnscenter.org/wp-content/uploads/2017/10/Grassfed_Full_v2.pdf">97 percent are fattened up with grain</a> in feedlots of confined animal feeding operations.</p>
<p>While currently only 3 percent of cattle continue to graze during the finishing phase, earning the title of grass-fed beef, this sector is growing: <a href="https://www.stonebarnscenter.org/wp-content/uploads/2017/10/Grassfed_Full_v2.pdf">Retail sales of organic, fresh grass-fed beef</a> grew from $6 million in 2012 to $89 million in 2016, driven by consumers concerned about sustainability, health, and animal welfare.</p>
<p>The study authors chose to focus on the finishing phase because it represents the largest contrast between two livestock production methods, as the first two phases are broadly similar. To conduct their research, they measured methane emitted from the cattle’s digestive tracts and manure and added it to existing lifecycle data on the amount of carbon dioxide emitted during the production of cattle feed and mineral supplements and the amount of energy consumed on the farm and in transporting the animals.</p>
<p>Applying the manure to the pastures, adding no pesticides or soil amendments, they also tracked soil organic carbon and nitrogen levels. To see how their grazing method contrasted with feedlot finishing, they compared their data to the same parameters from a previously conducted two-year MSU feedlot study.</p>
<p>The extensive analysis showed a significant reduction in GHG emissions under the AMP grazing system, because the soil absorbed enough carbon to cancel out the methane emissions. (By contrast, the calculated carbon loss from soil erosion during feed crop production made for slightly higher feedlot emissions.)</p>
<p>“This carbon sequestration rate allowed us to turn a carbon positive into a carbon negative compared to the most common management system in the finishing phase,” explained Stanley.</p>
<p>The reason for the decreased GHG emission is this: soils tend to sequester more carbon <a href="https://www.nature.com/scitable/knowledge/library/soil-carbon-storage-84223790">when their microbiota and root systems remain intact;</a> at the same time, manure left on the ground, rather than sluiced out of a feedlot and sprayed on a pasture, releases less nitrogen. (In addition to methane and<sub> </sub>carbon dioxide, nitrous oxide is a potent greenhouse gas, comprising <a href="http://www.fao.org/3/a-i3437e.pdf">about 18 percent of total beef cattle emissions</a>.)</p>
<p>Overgrazing has long been observed to severely damage soils, with the implication being that the damage is caused by too many animals in an area. But, said Jason Rowntree, a study co-author and animal science professor at MSU, “It isn’t the amount of animals [that should determine grazing patterns], it’s the amount of time the animals spend in a certain spot.” Moving the cattle when they have eaten just enough forage to stimulate grass regrowth and prevent the incursion of woody plants and trees preserves the soil structure and doesn’t liberate the carbon already stored in the soil.</p>
<p>The study’s results apply only to the last part of the animals’ lives, Rowntree said—but, since nearly all cattle are raised on pasture in their first six months, implementing AMP in that phase could also offer significant results, even if feedlots don’t switch to grazing.</p>
<h4><strong>The Latest in a Long Tradition</strong></h4>
<p>The researchers’ insight is not completely new: it first arose in the early 20<sup>th</sup>century when the visionary French farmer <a href="https://en.wikipedia.org/wiki/Andr%C3%A9_Voisin#Return_to_farming">André Voisin</a> observed his cattle’s eating habits and concluded that overgrazing could be prevented by allowing more animals in a pasture for a shorter period of time than conventional grazing theories prescribed; Voisin published <a href="https://www.amazon.com/Grass-Productivity-Introduction-Rational-Grazing-ebook/dp/B00U22PXQW">a book on “rational grazing”</a> in 1959.</p>
<p>More recently, Allan Savory, a Zimbabwean cattle rancher and founder of the Boulder, Colorado-based <a href="https://www.savory.global/">Savory Institute</a>, has become an evangelist for “holistic planned grazing,” a <a href="https://www.savory.global/wp-content/uploads/2017/02/about-holistic-planned-grazing.pdf">complex method</a> for managing grazing to provide healthy livestock feed, prevent erosion, integrate wildlife, improve the soil, and plan for drought and fire.</p>
<p>According to a 2013 <a href="http://www.savory.global/wp-content/uploads/2017/02/restoring-the-climate.pdf">Savory Institute report</a>, if the method were used on “up to 5 billion hectares of degraded grassland soils,” it could sequester at least 10 billion tons of atmospheric carbon in soils—the approximate equivalent of five times the area of Europe taking up a year’s worth of global carbon emissions. The report further claims that this would lower “greenhouse gas concentrations to pre-industrial levels in a matter of decades.” Savory has been <a href="https://www.sierraclub.org/sierra/2017-2-march-april/feature/allan-savory-says-more-cows-land-will-reverse-climate-change">heavily criticized</a> for lack of scientific rigor in these and other claims.</p>
<p>While the MSU–UCS study doesn’t go as far as the Savory Institute report, it does present a comprehensive analysis of the factors influencing net greenhouse emissions from livestock.</p>
<h4><strong>Skeptics and Believers</strong></h4>
<p>While some see numerous climate-related benefits to AMP grazing, daunting limitations still exist. Several factors drive many analysts to be skeptical that any cattle production can ever pare down net GHG emissions.</p>
<p>Tara Garnett, a food systems analyst and the founder of the <a href="https://www.fcrn.org.uk/">Food Climate Research Network</a> (FCRN) at the University of Oxford in England, calls the MSU work “a really useful study,” but also <a href="https://fcrn.org.uk/research-library/impacts-soil-carbon-sequestration-life-cycle-greenhouse-gas-emissions-midwestern">observes</a> that it is “unclear how far this approach will lead to the same results elsewhere.” The study authors, too, are careful to stress that their results apply to Upper Midwestern conditions, and using a similar method in other ecosystem types will require further tailored study. They also acknowledge that while degraded land properly managed can take up large amounts of carbon, the soil will eventually reach equilibrium (meaning it will reach its carbon limit), and estimates of how long that takes vary widely.</p>
<p>In addition, soil types and the many other aspects of climate and ecosystems in different regions require detailed understanding and granular management of grazing—something many beef producers may be unwilling to undertake. And grazing requires twice as much land as feedlots.</p>
<p>As a result, reducing beef consumption is still the best use of energy, according to Janet Ranganathan, vice president for science and research at the <a href="http://www.wri.org/">World Resources Institute</a>. “Beef is one of the least efficient foods to produce when considered from a ‘feed input to food output’ perspective,” she said. “Only about 1 percent of cattle feed calories and 4 percent of ingested protein are converted to human-edible calories and protein, respectively.”</p>
<p>David Briske, a rangeland ecologist at Texas A&amp;M University, who declined to speak with Civil Eats about the study, echoed the skeptics’ sentiments, writing in an email that “the quest for a superior grazing system is a fool’s errand.”</p>
<p>Still, a growing number of cattle producers disagree with the doubters. <a href="https://carmanranch.com/carman-ranch">Cory Carman</a>, whose family’s 100-year-old ranch in northeastern Oregon produces range- and pasture-fed cattle, has seen numerous benefits from careful grazing practices. She works with about 10 other ranchers to market grass-fed beef directly to consumers, grocery stores, and restaurants.</p>
<p>One very promising practice, she said, is for ranchers to enlist farmers in the beef finishing phase. One farmer was initially very skeptical, but after he had grown a series of cover crops to rest his wheat fields and used cattle to “harvest” them, leaving the residue on the fields, he discovered that the soil was improving rapidly, Carman said. Reduced fertilizer and pesticide inputs, together with the income from the pasturage fees, makes the next wheat crop less expensive to grow.</p>
<p>“In the beginning, he took a lot of soil tests that now he says he doesn’t need,” Carman said. “The impacts that he’s seeing in his soil health are largely related to soil carbon sequestration and the microbiology that’s going on in the soil that none of us really understand.”</p>
<p>Thus, the path to a climate-friendly, science-based, ethically consistent, and practically achievable decision on beef production and consumption remains about as clear as the mud in a herd-trampled pasture. Still, said Rowntree, “I hope our paper can give our industry, combined with policymakers, a lens that can potentially help. We’re not trying to pit one group against another.”</p>
<p>Carman also acknowledges the complexity at hand, but feels the benefits to the soil she has seen are important to take into account. “Livestock are partly to blame for a lot of ecological problems we’ve got,” she said. “But we couldn’t repair these problems without livestock.”</p>
<p><em>Editor’s note: This article has been updated to reflect the research’s findings that this type of grazing can be carbon-negative in the short-term and carbon-neutral over the longer term.</em></p>
<p><strong>Source:</strong> <a href="https://civileats.com/2018/04/10/can-responsible-grazing-make-beef-climate-neutral/">https://civileats.com/2018/04/10/can-responsible-grazing-make-beef-climate-neutral/</a></p>The post <a href="https://covercrops.co.nz/2019/01/07/can-responsible-grazing-make-beef-climate-neutral/">Can Responsible Grazing Make Beef Climate-Neutral?</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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		<title>Plants Really Do Feed Their Friends</title>
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		<dc:creator><![CDATA[Artur]]></dc:creator>
		<pubDate>Mon, 07 Jan 2019 02:12:20 +0000</pubDate>
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				<div class="et_pb_text_inner"><p>Researchers at the Department of Energy’s Lawrence Berkeley National Laboratory (Berkeley Lab) and UC Berkeley have discovered that as plants develop they craft their root microbiome, <g class="gr_ gr_92 gr-alert gr_spell gr_inline_cards gr_run_anim ContextualSpelling multiReplace" id="92" data-gr-id="92">favoring</g> microbes that consume very specific metabolites. Their study could help scientists identify ways to enhance the soil microbiome for improved carbon storage and plant productivity.</p>
<p> <span style="font-size: 14px;">“For more than a century, it’s been known that plants influence the makeup of their soil microbiome, in part through the release of metabolites into the soil surrounding their roots,” said Berkeley Lab postdoctoral researcher Kateryna Zhalnina, the study’s lead author. “Until now, however, it was not understood whether the contents of this cocktail released by plants was matched by the feeding preferences of soil microbes in a way that would allow plants to guide the development of their external microbiome.”</span></p>
<p> <span style="font-size: 14px;">The study,</span><span style="font-size: 14px;"> </span><a href="https://www.nature.com/articles/s41564-018-0129-3.epdf?author_access_token=9hnNOZwRBw82E92mF4FyGdRgN0jAjWel9jnR3ZoTv0O5nbnVk_NkLkKSgPTNcIsRy1D1GEfBoMPGl-DuC4Qhg0RFjKAq0eUAdIBMlUKzUZZPRI7Kp7RdpdsEwzPMqANRgANEz7QByxRw31gUJQNFzg%3D%3D" target="_blank" rel="noopener" style="font-size: 14px;">“Dynamic root exudate chemistry and microbial substrate preferences drive patterns in rhizosphere microbial community assembly,”</a><span style="font-size: 14px;"> </span><span style="font-size: 14px;">has just been published in the journal</span><span style="font-size: 14px;"> </span><em style="font-size: 14px;">Nature Microbiology</em><span style="font-size: 14px;">. The corresponding authors were Berkeley Lab scientists</span><span style="font-size: 14px;"> </span><a href="http://biosciences.lbl.gov/profiles/trent-r-northen/" style="font-size: 14px;">Trent Northen</a><span style="font-size: 14px;"> </span><span style="font-size: 14px;">and</span><span style="font-size: 14px;"> </span><a href="https://eesa.lbl.gov/profiles/eoin-brodie/" style="font-size: 14px;">Eoin Brodie</a><span style="font-size: 14px;">.</span></p>
<p> <span style="font-size: 14px;">Microbes within soil improve the ability of plants to absorb nutrients and resist drought, disease, and pests. They mediate soil carbon conversion, affecting the amount of carbon stored in soil or released into the atmosphere as carbon dioxide. The relevance of these functions to agriculture and climate are being observed like never before.</span></p>
<p> <span style="font-size: 14px;">Just one gram of soil contains tens of thousands of microbial species. Scientists have long known that plants impact the composition of the soil microbiome in the area surrounding their roots by sending out chemicals (metabolites). Prior work by Mary Firestone, Berkeley Lab faculty scientist and a professor of microbiology at UC Berkeley, had shown that plants were consistently selecting or suppressing the same types of microbes over time in the root zone, suggesting some form of synchronization between plant and microbiome development.</span></p>
<p> <span style="font-size: 14px;">Yet, little research had gone into the relationship between specific metabolites that plants release and the microbes consuming them. The new study brought together experts in soil science, microbial and plant genomics, and metabolomics to explore these potential metabolic connections. Their study took a close look at the rhizosphere of an annual grass (</span><em style="font-size: 14px;">Avena barbata</em><span style="font-size: 14px;">) common in California and other Mediterranean ecosystems.</span></p>
<p> <span style="font-size: 14px;">The Berkeley Lab team felt the time was ripe for doing so. As pressure mounts for farmers to grow enough healthy crops to meet a burgeoning population’s needs, and for new land management strategies that improve soil carbon storage to reduce atmospheric CO</span><sub>2</sub><span style="font-size: 14px;"> </span><span style="font-size: 14px;">and produce healthy soils, the soil microbiome is the subject of more in-depth scientific research than ever before.</span></p>
<p> <span style="font-size: 14px;">The researchers set out to determine the relationship between microbes that consistently bloomed near the </span><g class="gr_ gr_78 gr-alert gr_spell gr_inline_cards gr_run_anim ContextualSpelling ins-del" id="78" data-gr-id="78" style="background-color: initial; font-size: 14px; color: #666666;">grass roots</g><span style="font-size: 14px;"> and the metabolites released by the plant. Their first step was to collect soil from the University of California’s Hopland Research and Extension Center in northern California. Brodie, deputy director of Berkeley Lab’s Climate and Ecosystem Sciences Division, and his group used what they knew about the lifestyles of these soil bacteria to develop specialized microbial growth media to cultivate hundreds of different bacterial species. They then selected a subset that either flourished or declined as roots grew through the soil.</span></p>
<p> <span style="font-size: 14px;">This collection of microbes was then sent to the</span><span style="font-size: 14px;"> </span><a href="https://jgi.doe.gov/" target="_blank" rel="noopener" style="font-size: 14px;">Joint Genome Institute (JGI)</a><span style="font-size: 14px;">, a DOE Office of Science User Facility, where their genomes were sequenced to provide clues as to why their responses to roots differed. This analysis suggested that the key to success for microbes that thrived in the rhizosphere was their diet.</span></p>
<p> <span style="font-size: 14px;">Northen, </span><g class="gr_ gr_90 gr-alert gr_gramm gr_inline_cards gr_run_anim Grammar only-ins doubleReplace replaceWithoutSep" id="90" data-gr-id="90" style="background-color: initial; font-size: 14px; color: #666666;">senior</g><span style="font-size: 14px;"> scientist in Berkeley Lab’s Environmental Genomics and System Biology Division, is fascinated by the chemistry of microbiomes, and his group has developed advanced mass spectrometry-based </span><g class="gr_ gr_79 gr-alert gr_spell gr_inline_cards gr_run_anim ContextualSpelling" id="79" data-gr-id="79" style="background-color: initial; font-size: 14px; color: #666666;">exometabolomic</g><span style="font-size: 14px;"> approaches to elucidate metabolic interactions between organisms. Zhalnina and Northen combined their expertise to identify what the more successful microbes surrounding the roots of the Avena grasses preferred to eat.</span></p>
<p> <span style="font-size: 14px;">Using a hydroponic setup at the</span><span style="font-size: 14px;"> </span><a href="https://www.jbei.org/" target="_blank" rel="noopener" style="font-size: 14px;">Joint BioEnergy Institute</a><span style="font-size: 14px;">, a DOE Bioenergy Research Center, they immersed plants at different developmental stages in water to stimulate them to exude their metabolites, then measured the metabolites being released by the plants using mass spectrometry. Subsequently, the cultivated soil microbes were fed a cocktail of root metabolites, and the researchers used mass spectrometry to determine which microbes preferred which metabolites.</span></p>
<p> <span style="font-size: 14px;">They found that the microbes that flourished in the area around plant roots preferred a diet more rich in organic acids than the less successful microbes in the community.</span></p>
<p> <span style="font-size: 14px;">“Early in its growth cycle, the plant is putting out a lot of sugars, ‘candy’, which we find many of the microbes like,” Northen said. “As the plant matures, it releases a more diverse mixture of metabolites, including phenolic acids. What we discovered is that the microbes that become more abundant in the rhizosphere are those that can use these aromatic metabolites.”</span></p>
<p> <span style="font-size: 14px;">Brodie describes these phenolic acids as very specific compounds released by plants throughout their development. Phenolic acids are often associated with plant </span><g class="gr_ gr_98 gr-alert gr_spell gr_inline_cards gr_run_anim ContextualSpelling multiReplace" id="98" data-gr-id="98" style="background-color: initial; font-size: 14px; color: #666666;">defenses</g><span style="font-size: 14px;"> or plant-microbe communication. This indicates to Brodie that as they establish the microbial community within the rhizosphere, plants could be exuding metabolites like phenolic acids to help them control the types of microbes thriving around their roots.</span></p>
<p> <span style="font-size: 14px;">“We’ve thought for a long time that plants are establishing the rhizosphere best suited to their growth and development,” said Brodie. “Because there are so many different types of microbes in </span><g class="gr_ gr_88 gr-alert gr_gramm gr_inline_cards gr_run_anim Grammar only-ins replaceWithoutSep" id="88" data-gr-id="88" style="background-color: initial; font-size: 14px; color: #666666;">soil</g><span style="font-size: 14px;">, if the plants release just any chemical it could be detrimental to their health.</span></p>
<p> <span style="font-size: 14px;">“By controlling the types of microbes that thrive around their roots, plants could be trying to protect themselves from less friendly pathogens while promoting other microbes that stimulate nutrient supply.</span></p>
<p> <span style="font-size: 14px;">Zhalnina, Firestone, Northen, and Brodie believe their findings have great potential to influence additional scientific and applied research. Zhalnina points out that a lot of research and development is currently underway by government and industry to harness the power of microbes that improve plant yield and quality of soil to help meet society’s growing demands for a sustainable food supply.</span></p>
<p> <span style="font-size: 14px;">She said, “It’s exciting that we can potentially use the plant’s own chemistry to help nourish beneficial microbes within </span><g class="gr_ gr_94 gr-alert gr_gramm gr_inline_cards gr_run_anim Grammar only-ins doubleReplace replaceWithoutSep" id="94" data-gr-id="94" style="background-color: initial; font-size: 14px; color: #666666;">soil</g><span style="font-size: 14px;">. Population growth, especially, has created a demand for identifying more reliable ways to manipulate the soil microbiome for </span><g class="gr_ gr_95 gr-alert gr_gramm gr_inline_cards gr_run_anim Grammar only-ins replaceWithoutSep" id="95" data-gr-id="95" style="background-color: initial; font-size: 14px; color: #666666;">beneficial</g><span style="font-size: 14px;"> outcome.”</span></p>
<p> <span style="font-size: 14px;">Other current or former Berkeley Lab scientists contributing to this studying were: Katherine Louie, Nasim Mansoori, Dominique Loqué, Benjamin Bowen, Zhao Hao, Ulisses Nunes da Rocha, and Ulas Karaoz; Shengjing Shi and Heejung Cho of UC Berkeley were also co-authors</span><strong style="font-size: 14px;">. </strong><span style="font-size: 14px;">The DOE Office of Science supported the research. This work was </span><a href="https://jgi.doe.gov/mediterranean-grassland-soil-metagenome/" style="font-size: 14px;">done in part</a><span style="font-size: 14px;"> through the </span><a href="https://jgi.doe.gov/user-program-info/community-science-program/" style="font-size: 14px;">JGI Community Science Program</a><span style="font-size: 14px;">.</span></p>
<p> <span style="font-size: 14px;"># # #</span></p>
<p> <span style="font-size: 14px;">Lawrence Berkeley National Laboratory addresses the world’s most urgent scientific challenges by advancing sustainable energy, protecting human health, creating new materials, and revealing the origin and fate of the universe. Founded in 1931, Berkeley Lab’s scientific expertise has been recognized with 13 Nobel Prizes. The University of California manages Berkeley Lab for the U.S. Department of Energy’s Office of Science. For more, visit</span><span style="font-size: 14px;"> </span><a href="https://www.lbl.gov/" style="font-size: 14px;">www.lbl.gov</a><span style="font-size: 14px;">.</span></p>
<p> <span style="font-size: 14px;">DOE’s Office of Science is the single largest supporter of basic research in the physical sciences in the United </span><g class="gr_ gr_87 gr-alert gr_gramm gr_inline_cards gr_run_anim Punctuation only-del replaceWithoutSep" id="87" data-gr-id="87" style="background-color: initial; font-size: 14px; color: #666666;">States,</g><span style="font-size: 14px;"> and is working to address some of the most pressing challenges of our time. For more information, please visit</span><span style="font-size: 14px;"> </span><a href="http://science.energy.gov/" style="font-size: 14px;">science.energy.gov</a><span style="font-size: 14px;">.</span></p>
<p><strong>source: </strong><a href="https://newscenter.lbl.gov/2018/03/22/plants-really-do-feed-their-friends/">https://newscenter.lbl.gov/2018/03/22/plants-really-do-feed-their-friends/</a><strong> </strong></p></div>
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			</div> <!-- .et_pb_section -->The post <a href="https://covercrops.co.nz/2019/01/07/plants-really-do-feed-their-friends/">Plants Really Do Feed Their Friends</a> first appeared on <a href="https://covercrops.co.nz">Cover Crops | Promoting Plant Diversity</a>.]]></content:encoded>
					
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