Impacts of soil carbon sequestration on life cycle greenhouse gas emissions in Midwestern USA beef finishing systems
Open accessAbstract
Beef cattle have been identified as the largest livestock-sector contributor to greenhouse gas (GHG) emissions. Using life cycle analysis (LCA), several studies have concluded that grass-finished beef systems have greater GHG intensities than feedlot-finished (FL) beef systems. These studies evaluated only one grazing management system – continuous grazing – and assumed steady-state soil carbon (C), to model the grass-finishing environmental impact. However, by managing for more optimal forage growth and recovery, adaptive multi-paddock (AMP) grazing can improve animal and forage productivity, potentially sequestering more soil organic carbon (SOC) than continuous grazing. To examine impacts of AMP grazing and related SOC sequestration on net GHG emissions, a comparative LCA was performed of two different beef finishing systems in the Upper Midwest, USA: AMP grazing and FL. We used on-farm data collected from the Michigan State University Lake City AgBioResearch Center for AMP grazing. Impact scope included GHG emissions from enteric methane, feed production and mineral supplement manufacture, manure, and on-farm energy use and transportation, as well as the potential C sink arising from SOC sequestration. Across-farm SOC data showed a 4-year C sequestration rate of 3.59 Mg C ha−1 yr−1 in AMP grazed pastures. After including SOC in the GHG footprint estimates, finishing emissions from the AMP system were reduced from 9.62 to −6.65 kg CO2-e kg carcass weight (CW)−1, whereas FL emissions increased slightly from 6.09 to 6.12 kg CO2-e kg CW−1 due to soil erosion. This indicates that AMP grazing has the potential to offset GHG emissions through soil C sequestration, and therefore the finishing phase could be a net C sink. However, FL production required only half as much land as AMP grazing. While the SOC sequestration rates measured here were relatively high, lower rates would still reduce the AMP emissions relative to the FL emissions. This research suggests that AMP grazing can contribute to climate change mitigation through SOC sequestration and challenges existing conclusions that only feedlot-intensification reduces the overall beef GHG footprint through greater productivity.
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Written from the paper’s full text.
TL;DR
This comparative partial LCA found that adaptive multi-paddock (AMP) grazing finishing in the Upper Midwest could be a net GHG sink after including on-farm soil C sequestration, whereas feedlot (FL) finishing remained a net source. AMP required about twice as much land as FL, but its estimated net emissions were −6.65 vs 6.12 kg CO₂-e kg carcass weight (CW)⁻¹.
Key findings
- Across-farm SOC data showed a 4-year C sequestration rate of 3.59 Mg C ha⁻¹ yr⁻¹ in AMP grazed pastures; after including SOC, AMP finishing emissions changed from 9.62 to −6.65 kg CO₂-e kg CW⁻¹, while FL emissions increased slightly from 6.09 to 6.12 kg CO₂-e kg CW⁻¹ due to soil erosion.
- FL required half as much land as AMP: 0.30 vs 0.67 ha to produce 500 kg beef CW, and FL produced 1655 vs AMP 751 kg CW ha feed⁻¹.
- Enteric CH₄ was the largest source for AMP (53%) and intermediate for FL (31%); feed emissions were the largest FL source (37% vs 19% for AMP); manure emissions represented 30% of FL and 26% of AMP emissions.
- Sensitivity analysis: using on-farm SF₆ data instead of IPCC default Yₘ reduced AMP enteric CH₄ footprint by 36% and overall GHG footprint by 1.81 kg CO₂-e kg CW⁻¹ (19% decrease); reducing Yₘ from 6.5 to 5.5 reduced AMP enteric CH₄ by 15%.
Methods
- ISO-compliant partial LCA limited to the finishing phase, comparing FL and AMP grazing in the Upper Midwest; functional unit was 1 kg CW; a deterministic Excel model summed CH₄, CO₂, and N₂O from enteric fermentation, manure, feed production, on-farm energy/transportation, plus soil C sequestration and erosion.
- AMP data: 5 years (2012–2016) of on-farm data at MSU Lake City AgBioResearch Center, Red Angus steers (n = 210), finished at 530 kg live weight in 200 days; FL data: 2 years (2015–2016) at MSU Beef Center, n = 16 steers, with 90-day observed data simulated to 170 days; soil C sampled in 2012 and 2016 at 0–30 cm, with 2016 sampling at nine transects across sandy, sandy loam, and clay loam soils.
- Analysis used IPCC Tier 2 methods for enteric CH₄ and manure CH₄/N₂O, the Farm Energy Analysis Tool for feed production emissions, and soil C stock via elemental combustion and bulk density; net GHG flux summed production emissions, soil erosion, and SOC sequestration.
Limitations
- Stated: locational variation between 2012 and 2016 soil sampling sites could influence results; FL 90-day data were simulated to 170 days because 90 days is not representative, a trade-off lacking complete 170-day field data; uncertainty remains about soil C change over time and how long high sequestration rates continue, so the authors caution against extrapolating rates for extended periods and note different regions likely show different outcomes.
- Stated: enteric CH₄ accounting using IPCC default Yₘ has high uncertainty, motivating the SF₆ and lower-Yₘ sensitivity analyses.
- Evident from the text: system boundaries exclude cow-calf and backgrounding, so results apply only to the finishing phase; on-farm energy use was taken from Ryan and Tiffany (1998) in the absence of current data; land-use change and irrigation were excluded; FL soil erosion relied on literature values and AMP assumed zero soil erosion.
Model-written summary. Check it against the paper before relying on it.
Integrity signals
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Cites
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Claims the paper makes
23 of 84 cited sources checked · 8 supported · 0 flagged · accuracy not yet measured
- Premisecitation
There remains substantial uncertainty about soil carbon change over time in managed grasslands.
“However, there remains substantial uncertainty about soil C change over time in managed grasslands”
Quote in the paperSubstantial claim3 of 3 sources checked- cites Desjardins et al., 2012 source
The Discussion and Conclusions section says uncertainty in soil carbon change remains, estimating it at ±20% nationally and likely higher at smaller spatial scales. But this discussion concerns land management and agricultural soils generally, not specifically managed grasslands; Section 3.1 says the impact of grazing on soil carbon sequestration was not included. (LLM, conf=0.84)
Experimental — accuracy not yet measured - cites Olson et al., 2017 source
The section ‘Management of Intensified Cropping Systems and Soil Organic Carbon Stocks’ describes soil-carbon changes after perennial grassland was converted to cropping, but does not say that change over time in managed grasslands remains substantially uncertain. Searches for uncertainty and long-term soil-carbon change in grasslands found no passage addressing that claim. Page numbers were not available in our copy. (LLM, conf=0.72)
Experimental — accuracy not yet measured - cites Paustian et al., 2016 source
- Premisecitation
Previous beef life cycle assessment studies modeled grass-fed or grass-finished systems using simplified grazing parameters typically representative of continuous grazing and assumed steady-state soil carbon.
“These studies evaluated only one grazing management system continuous grazingand assumed steady-state soil carbon (C), to model the grass-finishing environmental impact.”
- Also stated in: § 1. Introduction · plain
“In previous beef LCA literature, grass-fed (over the entire life cycle) or grass-finished (referring exclusively to the finishing stage) systems are often modeled using simplified grazing parameters typically representative of continuous grazing, a simplistic management strategy in which cattle graze the same pasture continuously through an entire grazing season”
Quote in the paperSubstantial claim1 of 2 sources checked- cites Crosson et al., 2011 source
- cites de Vries et al., 2015 source
The available Abstract (no page given) says the review examined 14 beef life-cycle assessment studies, but cuts off before describing their methods. Searches for continuous grazing, grass-finishing, and steady-state soil carbon found no passage addressing those modeling assumptions; the decisive part of the paper is not present in our copy. (LLM, conf=0.72)
Experimental — accuracy not yet measured
- Also stated in: § 1. Introduction · plain
- Premisecitation
Several life cycle assessment studies have concluded that grass-finished beef systems have greater greenhouse gas intensities than feedlot-finished beef systems.
“Using life cycle analysis (LCA), several studies have concluded that grass-finished beef systems have greater GHG intensities than feedlot-finished (FL) beef systems.”
- Also stated in: § 1. Introduction · hedged
“Many studies indicate that feedlot finishing systems have lower cradle-to-gate GHG emissions per kg of carcass weight because grass-fed systems have greater enteric methane (CH 4 ) emissions (due to microbial ruminal fermentation), attributed to the more fibrous diet and longer finishing times, and lower overall carcass weights”
Quote in the paperSubstantial claim2 of 3 sources checked- cites Capper, 2012 source
The Results and Discussion (page unavailable) report a 67.5% higher carbon footprint per unit of beef for the grass-fed system than for the conventional feedlot-finished system. The same section cites one earlier partial life-cycle assessment with a similar grass-versus-feedlot conclusion. Our copy does not establish that several LCA studies reached that specific GHG-intensity conclusion; the paper describes its own analysis as a deterministic whole-system model. (LLM, conf=0.86)
Experimental — accuracy not yet measured - cites Desjardins et al., 2012 source
Section 2 says grass-finished cattle's lower feed-input footprint is usually offset by slower weight gain and longer methane-producing periods than for feedlot-finished cattle. The Introduction describes carbon-footprint estimation as based on LCA guidelines, but the cited passages do not establish that several comparative LCA studies reached the stated conclusion. (LLM, conf=0.82)
Experimental — accuracy not yet measured - cites Lupo et al., 2013 source
- Also stated in: § 1. Introduction · hedged
- Premisecitation
Studies using adaptive multi-paddock grazing indicate that it can result in more ideal pasture species composition (more digestible forages with greater digestible energy content) due to prevention of consistent species selection and overgrazing, providing pasture recovery, and re-grazing before lignification.
“Studies using AMP grazing indicate that it can result in more ideal pasture species composition (more digestible forages with greater digestible energy content) due to prevention of consistent species selection and overgrazing, providing pasture recovery, and re-grazing before lignification”
Quote in the paperSubstantial claim1 of 3 sources checked - Findingreasoning
The 4-year adaptive multi-paddock animal performance and days to finish were considerably different than previous studies.
“However, our 4-year AMP animal performance and days to finish were considerably different than that of previous studies”
Quote in the paperNot a substantial claim1 of 2 sources checked- cites Nguyen et al., 2010 source
- cites Picasso et al., 2014 source
The available indexed passages contain bibliographic details and keywords for grazing-system sustainability, but no findings about adaptive multi-paddock grazing, animal performance, or days to finish. Searches for those terms and for a four-year comparison with previous studies found no passage addressing the claim. (LLM, conf=0.72)
Experimental — accuracy not yet measured
- Premisecitation
Machmuller et al. (2015) reported mean sequestration values as great as 8.0 ± 0.85 Mg C ha-1 yr-1 in the top 30 cm of soil for a 7-year duration when converting degraded cropland to AMP grazing.
“Finally, when converting degraded cropland to AMP grazing, Machmuller et al. (2015) reported mean sequestration values as great as 8.0 ± 0.85 Mg C ha -1 yr -1 in the top 30 cm of soil for a 7-year duration.”
Quote in the paperSubstantial claim1 of 1 sources checked- cites Machmuller et al. (2015) source
The “Rapid soil C accumulation” section reports a peak gain of 8.0 ± 0.85 Mg C ha⁻¹ yr⁻¹ in the upper 30 cm after conversion to intensively grazed pasture. It places that peak 2–6 years after establishment; the Abstract describes a 7-year chronosequence, not seven years sustained at that rate. The claimed 7-year duration of sequestration at 8.0 ± 0.85 is therefore unsupported. (LLM, conf=0.87)
Experimental — accuracy not yet measured
- Premisecitation
Teague et al. (2016) estimated that AMP grazing could induce SOC sequestration rates 10 times greater than the commonly used default value of 0.41 Mg C ha-1 yr-1 proposed by Conant et al. (2003).
“For instance, Teague et al. (2016) estimated that AMP grazing could induce SOC sequestration rates 10 times greater than the commonly used default value of 0.41 Mg C ha -1 yr -1 proposed by Conant et al. (2003).”
Quote in the paperSubstantial claim1 of 2 sources checked- cites Teague et al. (2016) source
In the discussion accompanying Table 2 (page not available in our copy), Teague et al. estimate that AMP grazing sequestered 3 t C ha⁻¹ yr⁻¹ more than heavy continuous grazing in the comparison they describe. Our copy does not give the claimed Conant et al. default of 0.41 Mg C ha⁻¹ yr⁻¹ or make a tenfold comparison with it; 3 divided by 0.41 is about 7.3, not 10. (LLM, conf=0.88)
Experimental — accuracy not yet measured - cites Conant et al. (2003) source
- Interpretationcitation
Based on the 3.53 Mg C ha-1 yr-1 of C sequestered over a 9-year period in Wang et al. (2015), we expect that our soils could continue to sequester at this rate for several years.
“Based on the 3.53 Mg C ha -1 yr -1 of C sequestered over a 9-year period in Wang et al. (2015), we expect that our soils could continue to sequester at this rate for several years.”
Quote in the paperSubstantial claim1 of 1 sources checked- cites Wang et al. (2015) source
Table 4 reports 3,530 kg C ha⁻¹ yr⁻¹ (3.53 Mg) for a modeled 10-year transition from heavy continuous to multi-paddock grazing. Section 2.3.2 describes 10-, 15-, and 20-year scenarios, not an observed nine-year period. The expectation for the citing authors’ own soils is their inference, not a finding attributed to Wang et al. (LLM, conf=0.91)
Experimental — accuracy not yet measured
- Premisecitation
Wang et al. (2015) demonstrated that AMP grazing lands sequestered 3 Mg C ha-1 yr-1 more than land under continuous grazing.
“This is also demonstrated by Wang et al. (2015) where AMP grazing lands sequestered 3 Mg C ha -1 yr -1 more than land under continuous grazing.”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Wang et al. (2015) source
Section 3.2 reports greater carbon sequestration after conversion from heavy continuous (HC) to multi-paddock (MP) grazing, supporting the comparison in direction. But the rate depends on the assumed transition period: it gives 1.765 Mg C ha⁻¹ yr⁻¹ for the 20-year scenario, not an unqualified 3 Mg C ha⁻¹ yr⁻¹. Section 2.3.2 explains that these rates are estimates calculated from differences in soil-carbon stocks, rather than directly measured annual rates. (LLM, conf=0.84)
Experimental — accuracy not yet measured
- Findingreasoning
After including soil organic carbon in the greenhouse gas footprint estimates, finishing emissions from the adaptive multi-paddock system were reduced from 9.62 to -6.65 kg CO2-e kg carcass weight-1.
“After including SOC in the GHG footprint estimates, finishing emissions from the AMP system were reduced from 9.62 to -6.65 kg CO 2 -e kg carcass weight (CW) -1”
- Also stated in: § 3.5. Net GHG flux · plain
“Combined with 9.62 kg CO 2 -e kg CW -1 in emissions, this resulted in a net GHG sink of -6.65 kg CO 2 -e kg CW -1”
Quote in the paperSubstantial claim- The authors state this as an assumption: Soil carbon sequestration was linear over the 4-year interval.
- The authors state this as an assumption: Carbon sequestration was possible for all the land in the adaptive multi-paddock grazing finishing scenario.
- Also stated in: § 3.5. Net GHG flux · plain
- Findingown data
Feedlot emissions increased slightly from 6.09 to 6.12 kg CO2-e kg carcass weight-1 due to soil erosion.
“FL emissions increased slightly from 6.09 to 6.12 kg CO 2 -e kg CW -1 due to soil erosion.”
- Also stated in: § 3.5. Net GHG flux · plain
“The 6.09 kg CO 2 -e kg CW -1 of FL emissions combined with 0.03 kg CO 2 -e kg CW -1 from erosion resulted in a net emission of 6.12 kg CO 2 -e kg CW -1 for the FL scenario”
Quote in the paperNot a substantial claim- The authors state this as an assumption: For the feedlot scenario, an intensive cropping system with no soil carbon sequestration was assumed.
- Also stated in: § 3.5. Net GHG flux · plain
- Findingown data
Feedlot production required only half as much land as adaptive multi-paddock grazing.
“However, FL production required only half as much land as AMP grazing.”
- Also stated in: § 3.2. Land occupation · plain
“In other words, 0.30 and 0.67 ha was required to produce 500 kg beef CW in the FL and AMP grazing systems, respectively.”
Quote in the paperSubstantial claim - Also stated in: § 3.2. Land occupation · plain
- Findingown data
Across-farm soil organic carbon data showed a 4-year carbon sequestration rate of 3.59 Mg C ha-1 yr-1 in adaptive multi-paddock grazed pastures.
“Across-farm SOC data showed a 4-year C sequestration rate of 3.59 Mg C ha -1 yr -1 in AMP grazed pastures.”
- Also stated in: § 3.4. Soil C sequestration · hedged
“Averaging data for all three soil types (for S, SL and CL) led to an estimated sequestration rate of 3.59 Mg C ha -1 yr -1”
Quote in the paperSubstantial claim- The authors state this as an assumption: Soil carbon sequestration was linear over the 4-year interval.
- Also stated in: § 3.4. Soil C sequestration · hedged
- Findingown data
These data indicate a 4-year sequestration rate of 3.79 Mg C ha-1 yr-1 for the sandy-loam soils.
“These data indicate a 4-year sequestration rate of 3.79 Mg C ha -1 yr -1 for the SL soils.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Soil carbon sequestration was linear over the 4-year interval.
- Findingown data
If Ym had been reduced from the default of 6.5 (±1.0) to 5.5 to reflect improved forage quality, enteric methane emissions from the adaptive multi-paddock grazing scenario would have been reduced by 15%.
“Similarly, if Y m had been reduced from the default of 6.5 ( ± 1.0) to 5.5 to reflect improved forage quality, enteric CH 4 emissions from the AMP grazing scenario would have been reduced by 15%”
Quote in the paperNot a substantial claim - Findingnone given
Soil erosion due to feed production in the feedlot scenario contributed 22.76 kg CO2-e (0.03 kg CO2 kg carcass weight-1).
“Soil erosion due to feed production in the FL scenario contributed 22.76 kg CO 2 -e (0.03 kg CO 2 kg CW -1 ).”
Quote in the paperNot a substantial claim- The authors state this as an assumption: For the feedlot scenario, an intensive cropping system with no soil carbon sequestration was assumed.
- Findingown data
Greenhouse gas emissions from mineral supplement production and on-farm energy and transportation together contributed less than 2.5% to overall emissions in both finishing scenarios.
“GHG emissions from mineral supplement production and on-farm energy and transportation together contributed < 2.5% to overall emissions in both finishing scenarios.”
Quote in the paperNot a substantial claim - Findingown data
For the feedlot, this represents a 120% greater productivity on a carcass weight basis per hectare compared to adaptive multi-paddock.
“For the FL, this represents a 120% greater productivity on a CW basis per ha compared to AMP.”
Quote in the paperNot a substantial claim - Findingown data
On average, adaptive multi-paddock steers finished at 530 kg live weight in 200 days, comprising 180 days of grazing and 20 days of alfalfa hay feeding.
“On average, steers finished at 530 kg (σ = 47 kg) live weight in 200 days (average of 180 days AMP grazing and 20 days of alfalfa hay feeding).”
Quote in the paperSubstantial claim - Findingown data
The carbon contents in the 2016 sandy-loam soils were slightly greater than the mean of those of all three soil types.
“The C contents in the 2016 SL soils were slightly greater than the mean of those of all three soil types.”
Quote in the paperSubstantial claim - Findingreasoning
If the sandy and clay loam soil types had had a similar 2012 baseline, their sequestration rates would have been 2.04 and 4.94 Mg C ha-1 yr-1, respectively.
“If the S and CL soil types had had a similar 2012 baseline, however, their sequestration rates would have been 2.04 and 4.94 Mg C ha -1 yr -1 , respectively.”
Quote in the paperNot a substantial claim - Findingreasoning
Feed conversion ratio was 56% lower for feedlot than for adaptive multi-paddock grazed finishing.
“This resulted in a feed conversion ratio that was 56% lower for FL than for AMP grazed finishing.”
Quote in the paperSubstantial claim - Findingreasoning
Manure-derived nitrogen application was calculated to reduce needed nitrogen inputs by 31.4%.
“According to these calculations and current synthetic N application rates, manure-derived N application was calculated to reduce needed N inputs by 31.4%.”
Quote in the paperNot a substantial claim - Findingown data
Enteric CH4 in this study contributed the most to overall GHG emissions in the AMP grazing system.
“Similar to other studies, enteric CH 4 in our study contributed the most to overall GHG emissions (Fig. 1) in the AMP grazing system.”
Quote in the paperSubstantial claim - Findingcitation
FL requires less than half the agricultural land to produce beef versus grass-fed (AMP).
“The result that FL requires less than half the agricultural land to produce beef versus grass-fed (in this case, AMP) is typical of assumptions or results in other studies”
Quote in the paperNot a substantial claim - Findingnone given
The AMP grazing system produced considerably greater amounts of beef on a land basis compared to continuous grazing.
“While not as productive as FL based on yields, the AMP grazing system produced considerably greater amounts of beef on a land basis as compared to continuous grazing, showing that improved management can increase the output of grassfed beef.”
Quote in the paperNot a substantial claim - Findingreasoning
Manure CH4 and N2O for the FL scenario estimated in this study were greater than those in other studies (Lupo et al., 2013; Pelletier et al., 2010).
“Manure CH 4 and N 2 O for the FL scenario estimated in this study were greater than those in other studies (Lupo et al., 2013;Pelletier et al., 2010).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Findingcitation
GHG emissions (per kg CW) were within the range of those reported in other studies for the Northern Great Plains, Upper Midwest, and California within the U.S.
“Generally, GHG emissions (per kg CW) were within the range of those reported in other studies for the Northern Great Plains (Lupo et al., 2013), Upper Midwest (Pelletier et al., 2010), andCalifornia (Stackhouse-Lawson et al., 2012) within the U.S.”
Quote in the paperNot a substantial claim0 of 3 sources checked - Findingown data
Compared to FL finishing, AMP finishing generated more than twice the enteric CH4 emissions per kg CW.
“Compared to FL finishing, AMP finishing generated more than twice the enteric CH 4 emissions per kg CW (Fig. 1).”
Quote in the paperSubstantial claim - Findingown data
It is likely that the use of IPCC (2006) enteric CH4 accounting methodology overestimates actual enteric CH4 emissions in the AMP grazing system, especially when more digestible, higher quality forages are grazed.
“However, as shown in the sensitivity analysis (Fig. 3), it is likely that the use of IPCC (2006) enteric CH 4 accounting methodology overestimates actual enteric CH 4 emissions in the AMP grazing system, especially when more digestible, higher quality forages are grazed.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites IPCC (2006)
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- Findingown data
Estimated total manure emissions were lower for the AMP grazing scenario than the FL scenario (6.9 vs 7.3 Mg CO2-e).
“Although estimated total manure emissions were lower for the AMP grazing scenario than the FL scenario (6.9 vs 7.3 Mg CO 2 -e, respectively), the opposite was true when reflected on an animal productivity basis (CO 2 -e kg CW -1 ) (2.46 vs. 1.81CO 2 -e kg CW -1 for AMP grazing and FL, respectively; Fig. 1).”
Quote in the paperNot a substantial claim - Findingreasoning
Manure emissions per kg CW were higher for AMP grazing than FL (2.46 vs 1.81 CO2-e kg CW-1).
“Although estimated total manure emissions were lower for the AMP grazing scenario than the FL scenario (6.9 vs 7.3 Mg CO 2 -e, respectively), the opposite was true when reflected on an animal productivity basis (CO 2 -e kg CW -1 ) (2.46 vs. 1.81CO 2 -e kg CW -1 for AMP grazing and FL, respectively; Fig. 1).”
Quote in the paperNot a substantial claim - Findingreasoning
Compared to the grass-finishing model of Pelletier et al. (2010), GHG emissions from finishing with AMP grazing in this study were about 45% lower.
“Compared to results of the grass-finishing model of Pelletier et al. (2010), GHG emissions from finishing with AMP grazing in our study were about 45% lower.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Pelletier et al. (2010) source
- Findingreasoning
Feed production emissions in the FL finishing scenario were slightly greater than those reported by Lupo et al. (2013) and Pelletier et al. (2010).
“Feed production emissions in the FL finishing scenario were slightly greater than those reported by Lupo et al. (2013) and Pelletier et al. (2010), likely because our FL ration included only a small proportion of legume forages and a larger proportion of DDGS and corn grain which have greater emissions per kg than other feedstuffs (Camargo et al., 2013).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Findingcitation
Our estimated sequestration rate (3.59 Mg C ha-1 yr-1) is considerably greater than the mean C sequestration rate of 0.41 Mg C ha-1 yr-1 for 'management intensive grazing' in the Southeastern U.S. cited by Conant et al. (2003).
“Our estimated sequestration rate (3.59 Mg C ha -1 yr -1 ) is considerably greater than the mean C sequestration rate of 0.41 Mg C ha -1 yr -1 for”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Conant et al. (2003) source
- Findingnone given
Soil erosion contributed negligibly (< 0.5%) to net GHG emissions of FL finishing.
“Although soil erosion contributed negligibly (< 0.5%) to net GHG emissions of FL finishing, soil erosion magnified by intensive cropping systems, such as under conventional feed production in the FL scenario, has important negative impacts on other ecosystem services that are vital to food production, water quality, nutrient cycling and habitat support (Olson et al., 2017).”
Quote in the paperNot a substantial claim - Findingown data
The finishing phase of the beef production system may serve as an overall GHG sink.
“In doing so, our results show that not only can adoption of improved grazing management facilitate soil C sequestration, but that the finishing phase of the beef production system may serve as an overall GHG sink.”
Quote in the paperSubstantial claim - Findingnone given
AMP grazing requires twice as much land than FL.
“While AMP grazing requires twice as much land than FL, if effectively implemented over a large area, total C sequestration in the Upper Midwest could increase substantially.”
Quote in the paperSubstantial claim - Findingown data
Adoption of improved grazing management can facilitate soil C sequestration.
“In doing so, our results show that not only can adoption of improved grazing management facilitate soil C sequestration, but that the finishing phase of the beef production system may serve as an overall GHG sink.”
Quote in the paperSubstantial claim - Premisecitation
The few studies that considered low rates of soil carbon sequestration in greenhouse gas accounting for beef production indicated potential emissions decreases of 24-535%.
“The few studies that considered low rates of soil C sequestration in GHG accounting for beef production indicated potential emissions decreases of 24-535%”
Quote in the paperSubstantial claim0 of 3 sources checked - Premisecitation
Different assumptions about fertilization rates on pasture have resulted in a 5-fold difference in N2O emissions.
“For example, different assumptions about fertilization rates on pasture have resulted in a 5fold difference in N 2 O emissions”
Quote in the paperNot a substantial claim0 of 2 sources checked - Interpretationown data
Even lower soil organic carbon sequestration rates than those measured would still reduce adaptive multi-paddock emissions relative to feedlot emissions.
“While the SOC sequestration rates measured here were relatively high, lower rates would still reduce the AMP emissions relative to the FL emissions.”
Quote in the paperSubstantial claim - Premisecitation
The land, ecosystem, and greenhouse gas emission impacts resulting from beef production are highly dependent on the type of grazing management system utilized.
“Accordingly, the land, ecosystem, and GHG emission impacts resulting from beef production are highly dependent on the type of grazing management system utilized”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Brilli et al., 2017 source
- cites Rowntree et al., 2016
- Premisereasoning
Most of the differences in beef production environmental impact arise from the finishing strategy employed.
“However, most of the differences in beef production environmental impact arise from the finishing strategy employed.”
Quote in the paperSubstantial claim - Premisecitation
Emissions from grass-fed systems vary greatly due to differences in regional and on-farm practices.
“Additionally, emissions from grass-fed systems vary greatly due to differences in regional and on-farm practices.”
Quote in the paperNot a substantial claim - Premisereasoning
Beef life cycle assessments often assume soil carbon equilibrium.
“For these reasons, beef LCAs often assume soil C equilibrium.”
Quote in the paperSubstantial claim - Study design and conductnone given
System boundaries were limited to the finishing phase because most management differences and much of the variability among beef production systems are concentrated within the finishing phase.
“Because most management differences and much of the variability among beef production systems are concentrated within the finishing phase, system boundaries were limited to this phase only, thus excluding cow-calf and backgrounding stages.”
Quote in the paperSubstantial claim - Study design and conductcitation
Greenhouse gas emissions from crop irrigation were not included because less than 10% of all cropland in Michigan is irrigated.
“GHG emissions from crop irrigation were not included because < 10% of all cropland in Michigan is irrigated”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites USDA, 2014
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- Premisecitation
Each 25.4 kg of corn used in dry-mill ethanol production generates 7.89 kg of dried distillers grains with solubles.
“It was estimated that each 25.4 kg of corn used in dry-mill ethanol production generates 7.89 kg of DDGS”
Quote in the paperSubstantial claim0 of 1 sources checked- cites USDA, 2016a
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- Premisecitation
Mean carbon content for soils under a conventionally managed corn-soybean-wheat rotation typical in the Upper Midwest was 10.4 g C kg-1 soil.
“Mean C content for soils under a conventionally managed corn-soybean-wheat rotation, which is typical in the Upper Midwest, was 10.4 g C kg -1 soil”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Syswerda et al., 2011 source
- Premisecitation
According to USDA (2015), mean sheet and rill soil erosion on cropland in Michigan is 8.12 Mg ha-1 yr-1.
“According to the USDA (2015), mean sheet and rill soil erosion on cropland in Michigan is 8.12 Mg ha -1 yr -1 .”
Quote in the paperSubstantial claim0 of 1 sources checked- cites USDA, 2015
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- Interpretationreasoning
The higher manure emissions per kg CW for AMP are the result of greater DMI and lower final CW in the AMP grazing scenario than in the FL scenario.
“This is the result of greater DMI and lower final CW in the AMP grazing scenario than in the FL scenario.”
Quote in the paperNot a substantial claim - Interpretationreasoning
Levels of N application and related assumptions about associated emissions from pasture and cropland are primary contributors to discrepancies among beef production LCA models.
“Levels of N application and related assumptions about associated emissions from pasture and cropland are primary contributors to discrepancies among beef production LCA models.”
Quote in the paperNot a substantial claim - Interpretationreasoning
Improved management can increase the output of grassfed beef.
“showing that improved management can increase the output of grassfed beef.”
Quote in the paperNot a substantial claim - Interpretationreasoning
The difference in adaptive multi-paddock performance can be explained by improved forage quality and utilization in the adaptive multi-paddock grazing system versus the more conventional continuous grazing system.
“This difference can be explained by improved forage quality and utilization in the AMP grazing system versus the more conventional continuous grazing system.”
Quote in the paperNot a substantial claim - Interpretationown data
The greater C sequestration and resulting net GHG sink in the AMP grazing system illustrated in this study, compared to continuous grazing systems in other LCAs, calls into question the common assumption that FL intensification reduces the overall GHG footprint through greater productivity.
“The greater C sequestration and resulting net GHG sink in the AMP grazing system illustrated in this study, compared to continuous grazing systems in other LCAs, calls into question the common assumption that FL intensification reduces the overall GHG footprint through greater productivity.”
Quote in the paperSubstantial claim - Premisecitation
Recent studies indicate that grazing management can be a key driver promoting the relatively high SOC levels that we observed.
“While we did not contrast the more standard continuous grazing to AMP grazing, recent studies indicate that grazing management can be a key driver promoting the relatively high SOC levels that we observed.”
Quote in the paperSubstantial claim - Interpretationown data
It is possible that long-term AMP grazing finishing in the Upper Midwest could contribute considerably more to climate change mitigation and adaptation than previously thought.
“Therefore, it is possible that long-term AMP grazing finishing in the Upper Midwest could contribute considerably more to climate change mitigation and adaptation than previously thought.”
Quote in the paperSubstantial claim - Interpretationreasoning
When full consideration of land impacts is given to GHG emissions in both FL and AMP grazing-based finishing, environmental benefits may outweigh productivity losses.
“This study shows that when full consideration of land impacts is given to GHG emissions in both FL and AMP grazing-based finishing, environmental benefits may outweigh productivity losses.”
Quote in the paperSubstantial claim - Interpretationown data
If soil C is sequestered through best management practices, our results suggest that enteric CH4 from the finishing phase can be substantially mitigated.
“In fact, if soil C is sequestered through best management practices, our results suggest that enteric CH 4 from the finishing phase can be substantially mitigated.”
Quote in the paperSubstantial claim - Interpretationown data
Under AMP grazing, more extensive (grass-based) but intensively managed beef finishing can deliver environmental benefits with less environmental impact per kg CW than intensive FL finishing.
“However, as illustrated by this study in the Upper Midwest, under AMP grazing, more extensive (grass-based) but intensively managed beef finishing can deliver environmental benefits (such as soil C sequestration and other ecosystem services) with less environmental impact per kg CW than intensive FL finishing.”
Quote in the paperSubstantial claim - Interpretationreasoning
If effectively implemented over a large area, total C sequestration in the Upper Midwest could increase substantially.
“While AMP grazing requires twice as much land than FL, if effectively implemented over a large area, total C sequestration in the Upper Midwest could increase substantially.”
Quote in the paperSubstantial claim - Interpretationnone given
Integrating on-farm soil C data within the studied management system contributes significantly to existing LCAs.
“Integrating on-farm soil C data within the studied management system contributes significantly to existing LCAs.”
Quote in the paperSubstantial claim - Interpretationreasoning
Different regions are likely to demonstrate different outcomes as several variables shift.
“Therefore, different regions are likely to demonstrate different outcomes as several variables shift.”
Quote in the paperNot a substantial claim - Interpretationcitation
Greater rates of C sequestration may be possible for several years.
“Furthermore, greater rates of C sequestration may be possible for several years.”
Quote in the paperNot a substantial claim - Interpretationcitation
This lower offset is in part due to the greater average fertilization rate reported by USDA (2017) used in the present study than in the 2010 USDA data used by Lupo et al. (2013).
“This, in part, is due to the greater average fertilization rate reported by USDA (2017) used in the present study than in the 2010 USDA data used by Lupo et al. (2013).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites USDA (2017)
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- Interpretationcitation
The slightly greater feed production emissions were likely because the FL ration included only a small proportion of legume forages and a larger proportion of DDGS and corn grain which have greater emissions per kg than other feedstuffs.
“Feed production emissions in the FL finishing scenario were slightly greater than those reported by Lupo et al. (2013) and Pelletier et al. (2010), likely because our FL ration included only a small proportion of legume forages and a larger proportion of DDGS and corn grain which have greater emissions per kg than other feedstuffs (Camargo et al., 2013).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Camargo et al., 2013 source
- May combine two claims. 47
- Classified as probably not a substantial claim. 30
- The quote only partly states this claim. 1
May combine two claims.
PremisecitationSoil carbon sequestration is a critical ecosystem service of grasslands that can be maximized using best management practices for livestock grazing.
“Soil C sequestration is a critical ecosystem service of grasslands, which can be maximized using best management practices for livestock grazing”
Quote in the paperSubstantial claim1 of 3 sources checked- cites Griscom et al., 2017 source
In Results and Discussion, under “Specific Pathway Contributions” (page unavailable), the paper says two improved livestock-grazing pathways—Optimal Intensity and Legumes—increase soil carbon. It supports the value of grazing management for carbon sequestration, but does not establish that best management practices maximize sequestration in grasslands. (LLM, conf=0.82)
Experimental — accuracy not yet measured - cites Liebig et al., 2010 source
- cites McSherry and Ritchie, 2013 source
May combine two claims.
PremisecitationAdaptive multi-paddock grazing can improve animal and forage productivity and potentially sequester more soil organic carbon than continuous grazing.
“By managing for more optimal forage growth and recovery, adaptive multi-paddock (AMP) grazing can improve animal and forage productivity, potentially sequestering more soil organic carbon (SOC) than continuous grazing.”
- Also stated in: § 1. Introduction · hedged
“Potential AMP grazing benefits include reductions in overgrazing and soil erosion, improved forage utilization and animal productivity, and increased soil carbon (C) sequestration, which might reduce net GHG emissions”
Quote in the paperSubstantial claim1 of 3 sources checked- Also stated in: § 1. Introduction · hedged
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationGriscom et al. (2017) identified adaptive multi-paddock grazing as a potentially important climate change mitigation strategy but were unable to include it in their analysis due to lack of robust data.
“This need for on-farm SOC data was discussed by Griscom et al. (2017), who identified AMP grazing as a potentially important climate change mitigation strategy, but were unable to include it in their analysis due to lack of robust data.”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Griscom et al., 2017 source
Probably not a substantial claim: may not pass S3 (load-bearing).
FindingcitationAverage finishing weights for the feedlot steers were similar to those reported by others.
“Average finishing weights for the FL steers (Table 2) were similar to those reported by others”
Quote in the paperNot a substantial claim1 of 3 sources checkedMay combine two claims.
PremisecitationUtilization of AMP grazing as a regenerative agriculture management system can improve soil ecological function, lessening damage from tillage and inorganic fertilizers and can improve biodiversity and wildlife habitat.
“Utilization of AMP grazing as a regenerative agriculture management system can improve soil ecological function, lessening damage from tillage and inorganic fertilizers and can improve biodiversity and wildlife habitat (Teague et al., 2016).”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Teague et al., 2016 source
The Table 1 passage says regenerative AMP grazing aims to restore the ecological function of degraded grasslands, and the Conclusions say appropriate grazing management can improve biodiversity and wildlife habitat. The Table 2 passage links eliminating tillage damage and reducing nitrogen fertilizer use to broader soil-management practices, not to AMP grazing alone. The claim therefore overattributes those benefits to AMP grazing by itself. (LLM, conf=0.84)
Experimental — accuracy not yet measured
Probably not a substantial claim: may not pass S3 (load-bearing).
InterpretationcitationIf adopted, these practices may also promote soil C sequestration.
“If adopted, these practices may also promote soil C sequestration (Chambers et al., 2016).”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Chambers et al., 2016 source
May combine two claims.
PremisecitationWang et al. (2015) reported 3.53 Mg C ha-1 yr-1 of C sequestration for pastures transitioned from heavy continuous grazing to AMP grazing in northern Texas, U.S., a value close to our rate (3.59 Mg C ha-1 yr-1).
“Assuming management similar to that in our study, for pastures transitioned from heavy continuous grazing to AMP grazing in northern Texas, U.S., Wang et al. (2015) reported 3.53 Mg C ha -1 yr -1 of C sequestration, a value close to our rate (3.59 Mg C ha -1 yr -1 ).”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Wang et al. (2015) source
- The authors state this as an assumption: Management similar to that in our study for pastures transitioned from heavy continuous grazing to AMP grazing in northern Texas, U.S. (Wang et al. 2015).
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationSoil erosion magnified by intensive cropping systems has important negative impacts on other ecosystem services that are vital to food production, water quality, nutrient cycling and habitat support.
“Although soil erosion contributed negligibly (< 0.5%) to net GHG emissions of FL finishing, soil erosion magnified by intensive cropping systems, such as under conventional feed production in the FL scenario, has important negative impacts on other ecosystem services that are vital to food production, water quality, nutrient cycling and habitat support (Olson et al., 2017).”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites Olson et al., 2017 source
May combine two claims.
InterpretationcitationBecause soils further from C saturation accumulate C faster than soils near saturation, and because our estimated soil C sequestration rate is much greater than 0.41 Mg C ha-1 yr-1, we expect continued sequestration, likely to diminish over time.
“However, because soils that are further from C saturation will accumulate C faster than soils near saturation, and because our estimated soil C sequestration rate is much greater than the 0.41 Mg C ha -1 yr -1 indicated by Conant et al. (2003), we expect continued sequestration, likely to diminish over time (Minasny et al., 2017;Stewart et al., 2007).”
Quote in the paperSubstantial claim1 of 3 sources checkedMay combine two claims.
PremisecitationStudies indicate that in general, well-managed grasslands continue to sequester C at greater rates than improved cropland, and transitions from cropland to grassland show some of the greatest rates of C sequestration, ranging from 0.22 to 8.0 Mg C ha-1 yr-1.
“Nevertheless, studies indicate that in general, well-managed grasslands continue to sequester C at greater rates than improved cropland, and transitions from cropland to grassland show some of the greatest rates of C sequestration, ranging from 0.22 to 8.0 Mg C ha -1 yr -1 (Machmuller et al., 2015;Mathew et al., 2017;Minasny et al., 2017;Powlson et al., 2011).”
Quote in the paperNot a substantial claim2 of 3 sources checked- cites Machmuller et al., 2015 source
Split into 2 atoms — 0 confirmed, 2 partially supported, 0 disputed, 0 misattributed, 0 unverifiable. Expand the claim to see per-atom verdicts.
Experimental — accuracy not yet measured - cites Mathew et al., 2017 source
- cites Minasny et al., 2017 source
Split into 2 atoms — 0 confirmed, 2 partially supported, 0 disputed, 0 misattributed, 0 unverifiable. Expand the claim to see per-atom verdicts.
Experimental — accuracy not yet measured
May combine two claims.
Findingown dataAfter accounting for the 31.4% fertilizer offset in feedlot finishing, estimated greenhouse gas emissions associated with feedlot and adaptive multi-paddock finishing were 6.09 and 9.62 kg CO2-e kg carcass weight-1, respectively.
“After accounting for the 31.4% fertilizer offset (the percentage of synthetic fertilizer N that was replaced by land-applied manure) in FL finishing, estimated GHG emissions associated with FL and AMP finishing were 6.09 and 9.62 kg CO 2 -e kg CW -1 , respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataFeed greenhouse gas emissions were the largest source in the feedlot, 77% greater than those in adaptive multi-paddock finishing and a greater percentage of total emissions (37% and 19%, respectively).
“Feed GHG emissions were the largest source in the FL, 77% greater than those in AMP finishing and a greater percentage of total emissions (37% and 19%, respectively).”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataEnteric methane was the largest source for adaptive multi-paddock and intermediary for feedlot finishing, contributing 53% and 31%, respectively.
“Enteric CH 4 was the largest source for AMP and intermediary for FL finishing, contributing 53% and 31%, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataAverage daily gain was 100% greater and dry matter intake 10% lower for steers in the feedlot than those in the adaptive multi-paddock grazing scenario.
“Average daily gain was 100% greater and DMI 10% lower for steers in the FL than those in the AMP grazing scenario.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenTotal carbon sequestration was 3.59 Mg C ha-1 yr-1, equally -17.54 kg CO2-e carcass weight-1, assuming this carbon sequestration was possible for all the land in the adaptive multi-paddock grazing finishing scenario.
“Total C sequestration was 3.59 Mg C ha -1 yr -1 , equally -17.54 kg CO 2 -e CW -1 , assuming this C sequestration was possible for all the land in the AMP grazing finishing scenario.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Carbon sequestration was possible for all the land in the adaptive multi-paddock grazing finishing scenario.
May combine two claims.
Findingown dataOur sensitivity analysis indicates that using on-farm SF6 tracer gas data instead of IPCC default Ym would reduce the enteric methane footprint in the adaptive multi-paddock grazing scenario by 36%, representing a decrease from 42 to 27 kg CH4 steer-1, and a reduction in overall greenhouse gas footprint of 1.81 kg CO2-e kg carcass weight-1 (19% decrease).
“Our sensitivity analysis indicates that using the on-farm SF 6 tracer gas data instead of IPCC default Y m would reduce the enteric CH 4 footprint in the AMP grazing scenario by 36%, representing a decrease from 42 to 27 kg CH 4 steer -1 , and a reduction in overall GHG footprint of 1.81 kg CO 2 -e kg CW -1 (19% decrease)”
Quote in the paperNot a substantial claimMay combine two claims.
Findingreasoning0.30 and 0.67 hectares were required to produce 500 kg beef carcass weight in the feedlot and adaptive multi-paddock grazing systems, respectively.
“In other words, 0.30 and 0.67 ha was required to produce 500 kg beef CW in the FL and AMP grazing systems, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataManure emissions represented 30% of feedlot emissions and 26% of adaptive multi-paddock emissions.
“Manure emissions (comprised of both N 2 O and CH 4 ) represented 30% of FL emissions and 26% of AMP emissions.”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataWhen compared to the 2012 baseline soil carbon stock of the sandy-loam soil (33.97 ± 0.71 Mg C ha-1 in the top 30 cm), 2016 soil carbon stocks were 15.18, 8.16, and 19.75 Mg C ha-1 greater in sandy-loam, sandy, and clay loam soils, respectively.
“When compared to the 2012 baseline soil C stock of the SL soil (33.97 ± 0.71 Mg C ha -1 in the top 30 cm), 2016 soil C stocks were 15.18, 8.16, and 19.75 Mg C ha -1 greater in SL, S, and CL soils, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenFeedlot and adaptive multi-paddock finishing produced 1655 and 751 kg carcass weight ha feed-1, respectively.
“FL and AMP finishing produced 1655 and 751 kg CW ha feed -1 , respectively.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Findingown dataAverage dressing percentage calculated from carcass data was 53% among all 5 years.
“Average dressing percentage calculated from carcass data was 53% among all 5 years.”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataOn average, cattle in the feedlot finished in 29 fewer days with carcass weights 45% greater than those of adaptive multi-paddock grazed cattle.
“On average, cattle in the FL finished in 29 less days with CWs 45% greater than those of AMP grazed cattle.”
Quote in the paperSubstantial claimMay combine two claims.
FindingreasoningAdaptive multi-paddock grazed steers finished in 150 days shorter and 99 kg heavier than the continuously grazed steers in Lupo et al. (2013).
“Our AMP-grazed steers finished in 150 days shorter and 99 kg heavier than the continuously grazed steers in Lupo et al. (2013).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Lupo et al., 2013 source
May combine two claims.
FindingreasoningApplication of manure produced in the FL in the present study offset 31.4% of N fertilizer application, which is lower than the 69% used in the study of Lupo et al. (2013).
“Application of manure produced in the FL in the present study offset 31.4% of N fertilizer application, which is lower than the 69% used in the study of Lupo et al. (2013).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Lupo et al. (2013) source
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Findingnone givenEmissions from on-farm energy use and transportation and mineral supplement production represented small percentages of total GHG emissions (< 2.5% and < 0.05%, respectively).
“Emissions from on-farm energy use and transportation and mineral supplement production represented small percentages of total GHG emissions (< 2.5% and < 0.05%, respectively).”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataWe demonstrated this based on measurements of soil C and cattle productivity at the Lake City AgBioResearch Center from 2012 to 2016, which indicates a sink during the finishing phase of -6.65 kg CO2-e kg CW-1 which is similar to the results of Beauchemin et al. (2011).
“We demonstrated this based on measurements of soil C and cattle productivity at the Lake City AgBioResearch Center from 2012 to 2016, which indicates a sink during the finishing phase of -6.65 kg CO 2 -e kg CW -1 which is similar to the results of Beauchemin et al. (2011).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Beauchemin et al. (2011) source
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationA majority of greenhouse gas emissions from beef production are attributed to the cow-calf sector.
“A majority of GHG emissions are attributed to the cow-calf sector”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Beauchemin et al., 2010 source
May combine two claims.
Interpretationown dataAdaptive multi-paddock grazing can contribute to climate change mitigation through soil carbon sequestration and challenges existing conclusions that only feedlot intensification reduces the overall beef greenhouse gas footprint through greater productivity.
“This research suggests that AMP grazing can contribute to climate change mitigation through SOC sequestration and challenges existing conclusions that only feedlot-intensification reduces the overall beef GHG footprint through greater productivity.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationMany studies did not consider the potential for soil carbon sequestration in well-managed grasslands, and emissions from feedlot finishing might be underestimated due to a lacking representation of soil changes during feed production, such as soil erosion.
“However, as noted above, many of these studies did not consider the potential for soil C sequestration in well-managed grasslands, and emissions from feedlot finishing might be underestimated due to a lacking representation of soil changes during feed production, such as soil erosion”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Janzen, 2011 source
May combine two claims.
PremisereasoningBecause soil organic matter consists of 40-75% carbon, erosion constitutes a significant loss of soil fertility and water-holding capacity and can contribute to greenhouse gas emissions.
“Because soil organic matter (SOM) consists of 40-75% C, erosion constitutes a significant loss of soil fertility and water-holding capacity and can contribute to GHG emissions.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationContinuous grazing can negatively impact plant regrowth and recovery, plant communities, and has low productivity.
“This grazing management approach, while still the most common, can negatively impact plant regrowth and recovery, as well as plant communities, and has low productivity”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Oates et al., 2011 source
May combine two claims.
Interpretationown dataAdaptive multi-paddock grazing has the potential to offset greenhouse gas emissions through soil carbon sequestration, and therefore the finishing phase could be a net carbon sink.
“This indicates that AMP grazing has the potential to offset GHG emissions through soil C sequestration, and therefore the finishing phase could be a net C sink.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductcitationMean modeled finishing weight was 654 kg, similar to the 2015 average reported by USDA.
“Mean modeled finishing weight was 654 kg, similar to the 2015 average reported by USDA (2016a).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites USDA, 2016a
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
Probably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductreasoningSensitivity of enteric methane emissions to a reduction of IPCC default Ym from 6.5 to 5.5 to represent increased forage quality was also considered.
“Sensitivity of enteric CH 4 emissions to a reduction of IPCC default Y m from 6.5 to 5.5. to represent an increase in forage quality, was also considered”
Quote in the paperNot a substantial claimClassified as probably not a substantial claim. The quote only partly states this claim.
Study design and conductreasoningTo be conservative for the purposes of the life cycle assessment, the lower sequestration rate of 3.59 Mg C ha-1 yr-1 was used for the adaptive multi-paddock grazing scenario.
“To be conservative for the purposes of the LCA, we used this lower sequestration rate for the AMP grazing scenario.”
Quote in the paperSubstantial claimClassified as probably not a substantial claim. May combine two claims.
PremisecitationStudies have identified gaps and called for more robust research and inclusion of soil carbon in future life cycle assessment models.
“Studies have identified these gaps and have called for more robust research and inclusion of soil C in future LCA models”
Quote in the paperSubstantial claim0 of 2 sources checkedMay combine two claims.
Study design and conductcitationBecause 90 days is not a representative timeline for feedlot finishing, observed 90-day data were used to simulate an extension to 170 days on-feed, a more common time-to-finish in the Upper Midwest and feedlots.
“Because 90 days is not a representative timeline for FL finishing, the observed data were used to simulate an extension from 90 to 170 days on-feed (Table A.3.1), a more common time-to-finish in the Upper Midwest and in FLs”
Quote in the paperSubstantial claim0 of 1 sources checked- cites National Academies of Sciences, 2016
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
Probably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductcitationOn-farm energy use per head of cattle was taken from Ryan and Tiffany (1998) in the absence of current or on-farm data.
“As Pelletier et al. (2010) did, on-farm energy use per head of cattle was taken from Ryan and Tiffany (1998) in the absence of current or on-farm data.”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Pelletier et al., 2010 source
- cites Ryan and Tiffany, 1998
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Premisenone givenThe permanent pastures at Lake City AgBioResearch Center were established approximately 30 years ago and were continuously grazed and hayed until 2010 when adaptive multi-paddock management was initiated.
“The permanent pastures (grasslands) were established approximately 30 years ago and were continuously grazed and hayed until 2010 when AMP management was initiated.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductnone givenThe authors acknowledge that locational variation between sampling sites could influence the results.
“We acknowledge the locational variation between sampling sites could influence the results.”
Quote in the paperNot a substantial claimMay combine two claims.
Study design and conductcitationCalculated dry matter intake, average daily gain, and feed conversion ratio were within 0.1 kg of values observed by Cassady et al. (2016), indicating the simulation method was sound.
“Calculated DMI, ADG, and feed conversion ratio were within 0.1 kg of the values observed by Cassady et al. (2016), indicating that the simulation method was sound.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Cassady et al., 2016 source
Classified as probably not a substantial claim. May combine two claims.
Study design and conductreasoningBecause emissions data from cultivation of feed ingredients and manufacture of feed were not available for the study region except for dried distillers grains with solubles, the Farm Energy Analysis Tool was used, an open-source database greenhouse gas emission model calibrated with an extensive crop production literature database.
“Because emissions data from cultivation of feed ingredients and manufacture of feed were not available for our study region (except for DDGS), we used the Farm Energy Analysis Tool, an open-source database GHG emission model calibrated with an extensive crop production literature database”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Camargo et al., 2013 source
Classified as probably not a substantial claim.
Study design and conductreasoningTo estimate soil organic carbon sequestration conservatively, mean soil carbon stock from all 2016 sites was averaged before comparing to the 2012 sandy-loam mean soil carbon stock.
“Therefore, to estimate SOC sequestration conservatively, we averaged mean soil C stock from all 2016 sites before comparing them to the 2012 (SL) mean soil C stock.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductown dataA sensitivity analysis was conducted comparing the impact of IPCC default methods to results based on SF6 tracer gas data from the Lake City AgBioResearch Farm.
“However, a sensitivity analysis was conducted comparing the impact of IPCC default methods to results based on SF 6 tracer gas data from the Lake City AgBioResearch Farm.”
Quote in the paperNot a substantial claimClassified as probably not a substantial claim. May combine two claims.
Study design and conductown dataThe partial 90-day data were used because they represent actual on-farm data from animals of the same genetic background, despite the trade-off of not having complete 170-day field data.
“While it was a trade-off not to have complete 170-day field data, we chose to use the partial data from these animals because they represent actual on-farm data from animals of the same genetic background.”
Quote in the paperSubstantial claimClassified as probably not a substantial claim.
Study design and conductnone givenIn lieu of on-farm data for soil erosion and soil organic matter from cropland used to grow feed ingredients, representative literature values were used.
“In lieu of on-farm data for soil erosion and SOM from cropland used to grow feed ingredients, representative literature values were used.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductnone givenDespite distance in monitoring sites, the soil types were consistent and reflective in soil carbon change over time.
“Despite the distance in monitoring sites, the soil types were consistent and reflective in soil C change overtime.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductcitationTertiary emissions from manufacture of machines, equipment, and infrastructure were excluded based on their assumed minor contributions.
“Tertiary emissions, including those from manufacture of machines, equipment, and infrastructure were excluded, based on their assumed minor contributions”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Lupo et al., 2013 source
Probably not a substantial claim: may not pass S3 (load-bearing).
InterpretationcitationIn the western U.S., irrigation might represent an important source of GHG emissions not included in this model.
“Additionally, in the western U.S., where irrigation is more predominant, irrigation might represent an important source of GHG emissions not included in this model.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningFor AMP grazing to produce comparable amounts of beef, either more cows would be needed or cattle would remain longer; either scenario would increase overall emissions and land requirement.
“Likewise, for the AMP grazing system to produce comparable amounts of beef, either more cows would be needed to produce additional animals for the system, or the cattle would have to remain in the system for a longer period of time.Either scenario would increase the overall emissions and land requirement.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationAccording to Stewart et al. (2009), reduction in fertilizer use resulted in the largest decrease (30%) in modeled overall emissions from beef production.
“According to Stewart et al. (2009), reduction in fertilizer use resulted in the largest decrease (30%) in modeled overall emissions from beef production.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Stewart et al. (2009) source
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
InterpretationreasoningIn a closed system, this implies somewhat lower per capita beef consumption, but greater environmental benefits from what is consumed.
“Ultimately, in a closed system, this implies somewhat lower per capita beef consumption, but greater environmental benefits from what is consumed.”
Quote in the paperNot a substantial claimMay combine two claims.
Interpretationown dataThe higher enteric CH4 emissions emphasize the major benefits of utilizing more highly digestible, higher energy feeds, and a shorter finishing phase, resulting in productivity gains in the FL model.
“This emphasizes the major benefits of utilizing more highly digestible, higher energy feeds, and a shorter finishing phase, resulting in productivity gains in our FL model.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningThe 45% lower GHG emissions were most likely due to their longer finishing time, lower animal productivity, and high application rate of fertilizer on pasture.
“This was most likely due to their longer finishing time, lower animal productivity, and high application rate of fertilizer on pasture.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationAccording to Sloggett (1992), 23% of the on-farm energy used for crop production in the U.S. was for on-farm pumping of water.
“According to Sloggett (1992), 23% of the on-farm energy used for crop production in the U.S. was for on-farm pumping of water.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Sloggett (1992) source
May combine two claims.
PremisecitationThis overestimation has also been reported in other studies and reflects the uncertainty embedded in the use of IPCC methodology to represent a wide variety of diets and different management strategies in beef finishing systems.
“This overestimation has also been reported in other studies (Rowntree et al., 2016;Stackhouse-Lawson et al., 2012) and reflects the uncertainty embedded in the use of IPCC methodology to represent a wide variety of diets and different management strategies in beef finishing systems.”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Rowntree et al., 2016
- cites Stackhouse-Lawson et al., 2012 source
Classified as probably not a substantial claim. May combine two claims.
PremisecitationIn beef LCA studies from the Northern Great Plains and the Upper Midwest in which soil C dynamics were estimated, hypothetical C sequestration rates of 0.41 and 0.12 Mg C ha-1 yr-1 reduced emissions from continuous grass-fed beef production by 24% and 30%, respectively.
“In beef LCA studies from the Northern Great Plains and the Upper Midwest in which soil C dynamics were estimated, hypothetical C sequestration rates of 0.41 and 0.12 Mg C ha -1 yr -1 reduced emissions from continuous grass-fed beef production by 24% and 30%, respectively (Lupo et al., 2013;Pelletier et al., 2010).”
Quote in the paperSubstantial claim0 of 2 sources checkedMay combine two claims.
Study design and conductown dataOur model used 5 years of on-farm finishing data and 4 years of comparative soil C data from paddocks under AMP grazing.
“While these studies were models generated from the literature, our model used 5 years of on-farm finishing data and 4 years of comparative soil C data from paddocks under AMP grazing.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningOur results differ from many of those in the current literature, reflecting the importance of considering emissions and sinks from the entire system in a geographically localized area, including the soil ecosystem, when modeling beef production systems.
“Yet, our results differ from many of those in the current literature, reflecting the importance of considering emissions and sinks from the entire system in a geographically localized area, including the soil ecosystem, when modeling beef production systems.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningProducing the same amount of cattle using land that is less productive would yield lower C sequestration per ha, but also lower stocking rates and reduce beef production (and associated emissions) per ha.
“Thus, producing the same amount of cattle using land that is less productive would yield lower C sequestration per ha, but also lower stocking rates and reduce beef production (and associated emissions) per ha.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
InterpretationreasoningThis is likely due to use of the IPCC Tier 2 methods in the current study instead of the Tier 1 methodology used in prior studies, greater precipitation in our study area than in those of the others, and handling manure in the FL as a liquid instead of a solid.
“This is likely due to use of the IPCC Tier 2 methods in the current study instead of the Tier 1 methodology used in prior studies, greater precipitation in our study area than in those of the others, and handling manure in the FL as a liquid instead of a solid.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationThe LCA model of Camargo et al. (2013) included production of inputs and processes not included in conventional beef production LCAs, such as feed-associated pest management and transportation of inputs.
“Additionally, the LCA model of Camargo et al. (2013) included production of inputs and processes not included in conventional beef production LCAs, such as feed-associated pest management and transportation of inputs.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Camargo et al. (2013) source
Probably not a substantial claim: may not pass S2 (checkable).
InterpretationreasoningOur analyses and results reflect the key importance of geographically localized LCAs to more accurately estimate impacts of grazing on C sequestration rates.
“However, at a minimum, our analyses and results reflect the key importance of geographically localized LCAs to more accurately estimate impacts of grazing on C sequestration rates.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningSoil C dynamics are directly linked to both land potential and the productivity of both pasture and cattle, and both stocking rates and productivity influence the net GHG footprints estimated here.
“It should be noted that soil C dynamics are directly linked to both land potential and the productivity of both pasture and cattle, and that both stocking rates and productivity influence the net GHG footprints estimated here.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
InterpretationcitationThe high rate of C sequestration observed in our study may be the result of the recent management intervention from continuous grazing to AMP in 2010.
“The high rate of C sequestration observed in our study may be the result of the recent management intervention from continuous grazing to AMP in 2010 (Smith, 2014).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Smith, 2014 source
May combine two claims.
InterpretationreasoningThis implies less overall beef production in the region, albeit with greater environmental benefits from what is produced.
“This does imply less overall beef production in the region, albeit with greater environmental benefits from what is produced.”
Quote in the paperSubstantial claim
The authors state this as an assumption.
Soil nitrogen dynamics for the pasture itself do not significantly change in response to animal production.
“Soil N dynamics for the pasture itself were not modeled, under the assumption that these emissions do not significantly change in response to animal production.”
The authors state this as an assumption.
Feed crops were produced on existing cropland and grass-fed cattle were grazed on existing pasture or grassland in Michigan or other regions of the Upper Midwest.
“Additionally, GHG emissions associated with land-use change, either for feed production or grazing land, were not considered, under the assumption that feed crops were produced on existing cropland and that grass-fed cattle were grazed on existing pasture/grassland in Michigan or other regions of the Upper Midwest.”
The authors state this as an assumption.
Soil carbon was at a steady state on the land used to grow hay.
“We assumed that soil C was at a steady state on the land used to grow hay.”
The authors state this as an assumption.
For the feedlot scenario, an intensive cropping system with no soil carbon sequestration was assumed.
“For the FL scenario, we assumed an intensive cropping system with no soil C sequestration, as croplands are often eroded”
The authors state this as an assumption.
Zero soil erosion was assumed in the adaptive multi-paddock grazing scenario.
“Because our data indicated C sequestration in the AMP grazing scenario over the 4-year interval, we assumed zero soil erosion based on Olson et al. (2016).”
The authors state this as an assumption.
Soil carbon sequestration was linear over the 4-year interval.
“these increases were divided by 4 to estimate Mg C sequestered ha -1 yr -1 , assuming linear sequestration over that time.”
The authors state this as an assumption.
Carbon sequestration was possible for all the land in the adaptive multi-paddock grazing finishing scenario.
“Total C sequestration was 3.59 Mg C ha -1 yr -1 , equally -17.54 kg CO 2 -e CW -1 , assuming this C sequestration was possible for all the land in the AMP grazing finishing scenario.”
The authors state this as an assumption.
The croplands used for the FL scenario experience soil erosion rather than carbon sequestration.
“Although we assumed in this study that the croplands used for the FL scenario experience soil erosion rather than carbon sequestration”
The authors state this as an assumption.
Management similar to that in our study for pastures transitioned from heavy continuous grazing to AMP grazing in northern Texas, U.S. (Wang et al. 2015).
“Assuming management similar to that in our study, for pastures transitioned from heavy continuous grazing to AMP grazing in northern Texas, U.S., Wang et al. (2015) reported 3.53 Mg C ha -1 yr -1 of C sequestration, a value close to our rate (3.59 Mg C ha -1 yr -1 ).”
Claims other papers make about this one
Each is checked against this paper’s own text: does it say what the citing paper says it does?
Existing studies generally determine one single value, calculated as the sum of annual GHG emissions minus CO2 removal by soil C-sequestration.
“To explore the potential for SOC increases to mitigate climate change, existing studies generally determine one single value, calculated as the sum of annual GHG emissions minus CO2 removal by soil C-sequestration11,16.”
From Risk to rely on soil carbon sequestration to offset global ruminant emissions (2023) · cites this paper as [11]
Section 2.7.3 describes calculating a single net GHG value by combining beef-production emissions with reductions from soil C sequestration, so the paper uses the stated calculation itself. But the Introduction says many other studies did not consider soil C sequestration, and section 4.5 says SOC measurements have not typically been factored into their outcomes. That contradicts the claim that existing studies generally use this calculation. (LLM, conf=0.84)
Checked by a reasoning model — may be wrong.
Experimental — accuracy not yet measuredMost LCAs on AMP grazing compare fully AMP-managed systems to fully conventional ones, which may be interpreted as AMP and feedlots being incompatible, even though AMP grazing could be integrated into earlier production phases.
“Additionally, most LCAs on AMP grazing compare fully AMPmanaged systems to fully conventional ones (Rowntree et al., 2020;Stanley et al., 2018), which may be interpreted as AMP and feedlots being incompatible, even though AMP grazing could be integrated into earlier production phases.”
From Impact of 10 years of adaptive multi-paddock grazing on soil carbon and beef's greenhouse gas footprint in the US Upper Midwest (2026) · cites this paper as Stanley et al., 2018
The Introduction describes this paper as a comparison of feedlot and AMP-grazing finishing, so it supports the citation as an example of that comparison. But it explicitly calls the study a partial LCA of the finishing phase; it does not establish that most AMP-grazing LCAs compare fully AMP-managed systems with fully conventional ones. The sentence’s interpretation about compatibility and earlier production phases is the citing authors’ framing, not a finding attributed to this source. (LLM, conf=0.85)
Experimental — accuracy not yet measuredStanley et al. (2018) reported average SOC sequestration after five-year conversion from continuous haying and grazing to AMP grazing (analogous to the HPG system used at WOP, but with cattle grazing only).
“For example, Stanley et al. (2018) reported average SOC sequestration after five-year conversion from continuous haying and grazing to AMP grazing (analogous to the HPG system used at WOP, but with cattle grazing only).”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al., 2018
The Methods (§2.7.1) say the pastures were continuously grazed and hayed until AMP management began in 2010. The Results (§3.4) report an average SOC sequestration rate of 3.59 Mg C ha⁻¹ yr⁻¹, but calculate it from 2012–2016 samples—a four-year interval, not five years after conversion. The comparison to WOP’s HPG system is the citing authors’ framing, not a finding attributed to Stanley et al. (LLM, conf=0.88)
Experimental — accuracy not yet measuredUse of improved grazing practices in some pasture-finished systems has sequestered enough carbon to offset production emissions from finishing.
“Use of improved grazing practices in some pasture-finished systems has sequestered enough carbon to offset production emissions from finishing [11].”
From Carbon opportunity cost increases carbon footprint advantage of grain-finished beef (2023) · cites this paper as [11]
Previous studies on beef systems that included soil organic carbon used fixed values based on literature, measured data over limited periods, or modelled soil carbon fluxes.
“Previous studies on beef systems that have included SOC have used fixed values based on literature data (e.g.Pelletier et al., 2010), relied on measured data during a limited period of time (e.g.Stanley et al. (2018) used data from soil measurements on-site over four years) or used modelled soil carbon fluxes (Alemu et al., 2017).”
From Time-dependent climate impact of beef production – can carbon sequestration in soil offset enteric methane emissions? (2022) · cites this paper as Stanley et al. (2018)
Initial evidence from beef LCAs incorporating AMP grazing induced SOC accrual suggests substantial GHG mitigation potential, with reported reductions from 65 to 169% lower relative to footprints without SOC offsets.
“Initial evidence from beef life cycle assessments (LCAs) incorporating AMP grazing induced SOC accrual suggest substantial GHG mitigation potential.Relative to GHG footprints calculated without considering offsets from SOC accrual, reported GHG footprints incorporating measured SOC accrual suggested reductions from 65 to 169% lower (Mehre et al., 2024;Rowntree et al., 2020;Stanley et al., 2018).”
From Impact of 10 years of adaptive multi-paddock grazing on soil carbon and beef's greenhouse gas footprint in the US Upper Midwest (2026) · cites this paper as Stanley et al., 2018
Existing studies on AMP and SOC have evaluated only short-term shifts from conventional grazing.
“or evaluated only short-term shifts from conventional grazing (Stanley et al., 2018).”
From Impact of 10 years of adaptive multi-paddock grazing on soil carbon and beef's greenhouse gas footprint in the US Upper Midwest (2026) · cites this paper as Stanley et al., 2018
Livestock-induced soil C changes can have large impacts on the GHG balance of production systems.
“Recent studies show that livestock-induced soil C changes can have large impacts on the GHG balance of these production systems (Beauchemin et al., 2011;Teague et al., 2016;Stanley et al., 2018).”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al., 2018
Including soil C changes in LCA parameters can considerably decrease overall CO2-e.
“Some studies have shown that when including soil C changes to LCA parameters, the overall CO 2 -e can decrease considerably (Pelletier et al., 2010b;Stanley et al., 2018).”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al., 2018
Grass-finished carcass weights are ∼33% lower than existing grain-finishing beef LCAs.
“Importantly, these results show that grass-finished CWs are ∼33% lower than existing grain-finishing beef LCAs (Pelletier et al., 2010b;Lupo et al., 2013;Stanley et al., 2018).”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al., 2018
Our estimated soil C sequestration rate lies toward the higher end of reported values, both above and below some other literature values.
“Compared to other literature, our estimated soil C sequestration rate lies toward the higher end-both above (Wang et al., 2015;Conant et al., 2017) and below (Stanley et al., 2018) reported values from others.”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al., 2018
The reported MSPR finished beef carcass weight closely aligns with Stanley et al. (2018), who reported 280 kg hd-1 in an adaptive multipaddock grazing system.
“However, our reported MSPR finished beef CW closely aligns with Stanley et al. (2018), who reported a 280 kg hd -1 in an adaptive multipaddock (AMP) grazing system-a similar management strategy, but using beef cattle only.”
From Ecosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System (2020) · cites this paper as Stanley et al. (2018)
Self-check
Percentages, sums and reported differences re-computed from the paper’s own numbers.
Each contradiction between two passages listed here was confirmed by an independent check.
Reported daily gains do not match weights and finishing times
MinorThe feedlot weights imply a gain of 293 kg over 171.5 days, or 1.71 kg/day rather than 1.8. The AMP weights imply 166 kg over 200.8 days, or 0.83 kg/day rather than 0.9.
“| Days in the finishing phase | 171.5 | 200.8 | | Beginning-Ending live weight (kg) | 361-654 | 362-528 |”
“| Average daily gain (kg) | 1.8 | 0.9 |”
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BackgroundGRAZING SYSTEMS, ECOSYSTEM RESPONSES, AND GLOBAL CHANGE
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Sequestering Soil Organic Carbon: A Nitrogen Dilemma
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“However, our 4-year AMP animal performance and days to finish were considerably different than that of previous studies (Nguyen et al., 2010; Picasso et al., 2014).”
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Do grasslands act as a perpetual sink for carbon?
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“The high rate of C sequestration observed in our study may be the result of the recent management intervention from continuous grazing to AMP in 2010 (Smith, 2014).”
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MethodCrop Production Summary - 2021
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BackgroundAn approach to include soil carbon changes in life cycle assessments
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Emerging land use practices rapidly increase soil organic matter
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BackgroundMethodInfluentialThe role of ruminants in reducing agriculture's carbon footprint in North America
Teague, W. R., Apfelbaum, S., Lal, R., Kreuter, U. P., Rowntree, J., Davies, C. A., Conser, R., Rasmussen, M., Hatfield, J., Wang, T., et al. (2016) · Journal of Soil and Water Conservation · doi:10.2489/jswc.71.2.156 · Cited by 179 · see citing works
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“…methane (CH4) emissions (due to microbial ruminal fermentation), attributed to the more fibrous diet and longer finishing times, and lower overall carcass weights (Capper, 2012; Desjardins et al., 2012; Lupo et al., 2013; Pelletier et al., 2010; Stackhouse-Lawson et al., 2012; Swain et al., 2018).”
BackgroundResultGrazing management that regenerates ecosystem function and grazingland livelihoods
Teague, R., & Barnes, M. (2017) · African Journal of Range & Forage Science · doi:10.2989/10220119.2017.1334706 · Cited by 171 · see citing works
Beauchemin, K. A., Janzen, H. H., Little, S. M., McAllister, T. A., & McGinn, S. M. (2011) · Animal Feed Science and Technology · doi:10.1016/j.anifeedsci.2011.04.047 · Cited by 167 · see citing works
Impact of soil erosion on soil organic carbon stocks
Olson, K. R., Al‐Kaisi, M., Lal, R., et al. (2016) · Journal of Soil and Water Conservation · doi:10.2489/jswc.71.3.61a · Cited by 165 · cited 2× · see citing works
“For the FL scenario, we assumed an intensive cropping system with no soil C sequestration, as croplands are often eroded (Izaurralde et al., 2007; Olson et al., 2016).”
MethodConant, R. T., Six, J., & Paustian, K. (2003) · Biology and Fertility of Soils · doi:10.1007/s00374-003-0652-z · Cited by 163 · cited 4× · see citing works
“…will accumulate C faster than soils near saturation, and because our estimated soil C sequestration rate is much greater than the 0.41Mg C ha−1 yr−1 indicated by Conant et al. (2003), we expect continued sequestration, likely to diminish over time (Minasny et al., 2017; Stewart et al., 2007).”
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“Soil C sequestration is a critical ecosystem service of grasslands, which can be maximized using best management practices for livestock grazing (Griscom et al., 2017; Liebig et al., 2010; McSherry and Ritchie, 2013; Wang et al., 2015).”
BackgroundClimate‐change adaptation on rangelands: linking regional exposure with diverse adaptive capacity
Briske, D. D., Joyce, L. A., Polley, H. W., et al. (2015) · Frontiers in Ecology and the Environment · doi:10.1890/140266 · Cited by 148 · cited 2× · see citing works
“…of grazing lands (~336million ha of land in the United States; (Chambers et al., 2016)) and their importance to livelihoods (Asner et al., 2004; Briske et al., 2015; Desjardins et al., 2012), grassland C sinks might represent a significant GHG mitigation strategy that should be included in…”
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“…and the terrestrial C pool (Olson et al., 2017), as well as the extensiveness of grazing lands (~336million ha of land in the United States; (Chambers et al., 2016)) and their importance to livelihoods (Asner et al., 2004; Briske et al., 2015; Desjardins et al., 2012), grassland C sinks…”
BackgroundInfluentialCarbon footprint of beef cattle
Desjardins, R., Worth, D., Vergé, X., Maxime, D., Dyer, J., & Cerkowniak, D. (2012) · Sustainability · doi:10.3390/su4123279 · Cited by 124 · cited 6× · see citing works
“…(~336million ha of land in the United States; (Chambers et al., 2016)) and their importance to livelihoods (Asner et al., 2004; Briske et al., 2015; Desjardins et al., 2012), grassland C sinks might represent a significant GHG mitigation strategy that should be included in beef production models.”
BackgroundInfluentialLife cycle assessment of fuel ethanol derived from corn grain via dry milling
Kim, S., & Dale, B. E. (2007) · Bioresource Technology · doi:10.1016/j.biortech.2007.09.034 · Cited by 118 · cited 1× · see citing works
“GHG emissions from production of DDGS were taken from a Michigan model (Kim and Dale, 2008), because of the proximity of the study to the Lake City AgBioResearch Center; this model included corn crop production and dry-milling, but not ethanol distillation.”
MethodPicasso, V. D., Modernel, P. D., Becoña, G., Salvo, L., Gutiérrez, L., & Astigarraga, L. (2014) · Meat Science · doi:10.1016/j.meatsci.2014.07.005 · Cited by 113 · see citing works
What place for livestock on a re-greening earth?
Janzen, H. H. (2011) · Animal Feed Science and Technology · doi:10.1016/j.anifeedsci.2011.04.055 · Cited by 109 · cited 1× · see citing works
“However, as noted above, many of these studies did not consider the potential for soil C sequestration in well-managed grasslands, and emissions from feedlot finishing might be underestimated due to a lacking representation of soil changes during feed production, such as soil erosion (Janzen, 2011).”
BackgroundCarbon footprint and ammonia emissions of California beef production systems1
Stackhouse-Lawson, K. R., Rotz, C. A., Oltjen, J. W., & Mitloehner, F. M. (2012) · Journal of Animal Science · doi:10.2527/jas.2011-4653 · Cited by 103 · cited 6× · see citing works
“Generally, GHG emissions (per kg CW) were within the range of those reported in other studies for the Northern Great Plains (Lupo et al., 2013), Upper Midwest (Pelletier et al., 2010), and California (Stackhouse-Lawson et al., 2012) within the U.S. Compared to results of the grass-finishing model of Pelletier et al. (…”
BackgroundMethodResultInfluentialLife-cycle assessment of the beef cattle production system for the northern Great Plains, USA
Lupo, C. D., Clay, D. E., Benning, J. L., & Stone, J. J. (2013) · Journal of Environmental Quality · doi:10.2134/jeq2013.03.0101 · Cited by 93 · cited 19× · see citing works
“GHG emissions from the manufacture of mineral supplements for rations were predicted using methodology of Lupo et al. (2013) and were scaled to represent the difference in finishing time for both finishing systems.”
BackgroundMethodResultInfluentialWhat crop type for atmospheric carbon sequestration: results from a global data analysis
Mathew, I., Shimelis, H., Mutema, M., & Chaplot, V. (2017) · Agriculture, Ecosystems & Environment · doi:10.1016/j.agee.2017.04.008 · Cited by 90 · see citing works
Reducing the environmental impact of global diets
Swain, M., Blomqvist, L., McNamara, J., et al. (2017) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2017.08.125 · Cited by 90 · see citing works
Long-term modeling of soil C erosion and sequestration at the small watershed scale
Izaurralde, R. C., Williams, J. R., Post, W. M., Thomson, A. M., McGill, W. B., Owens, L. B., & Lal, R. (2006) · Climatic Change · doi:10.1007/s10584-006-9167-6 · Cited by 87 · cited 1× · see citing works
“For the FL scenario, we assumed an intensive cropping system with no soil C sequestration, as croplands are often eroded (Izaurralde et al., 2007; Olson et al., 2016).”
BackgroundNguyen, T. T. H., van der Werf, H. M. G., Eugène, M., Veysset, P. P., Devun, J., Chesneau, G., & Doreau, M. (2012) · Livestock Science · doi:10.1016/j.livsci.2012.02.010 · Cited by 82 · see citing works
Oates, L. G., Undersander, D. J., Gratton, C., Bell, M. M., & Jackson, R. D. (2011) · Crop Science · doi:10.2135/cropsci2010.04.0216 · Cited by 80 · see citing works
GHG mitigation potential of different grazing strategies in the united states southern great plains
Wang, T., Teague, W., Park, S., & Bevers, S. (2015) · Sustainability · doi:10.3390/su71013500 · Cited by 69 · see citing works
Alemu, A. W., Janzen, H., Little, S., Hao, X., Thompson, D. J., Baron, V., Iwaasa, A., Beauchemin, K. A., & Kröbel, R. (2017) · Agricultural Systems · doi:10.1016/j.agsy.2017.08.003 · Cited by 61 · cited 2× · see citing works
“Although many used modeled C sequestration from beef simulation studies (Alemu et al., 2017; Beauchemin et al., 2011; Nguyen et al., 2010, 2012), such estimates might not represent actual, on-farm changes in SOC (Petersen et al., 2013; Teague et al., 2011).”
MethodSTEWART, A. A., LITTLE, S. M., OMINSKI, K. H., WITTENBERG, K. M., & JANZEN, H. H. (2009) · The Journal of Agricultural Science · doi:10.1017/s0021859609008764 · Cited by 42 · see citing works
Soil ecosystem services and intensified cropping systems
Olson, K. R., Al-Kaisi, M., Lal, R., & Morton, L. W. (2017) · Journal of Soil and Water Conservation · doi:10.2489/jswc.72.3.64a · Cited by 42 · see citing works
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Enteric methane from lactating beef cows managed with high- and low-input grazing systems
Chiavegato, M. B., Rowntree, J. E., Carmichael, D., & Powers, W. J. (2015) · Journal of Animal Science · doi:10.2527/jas.2014-8128 · Cited by 19 · cited 2× · see citing works
“To determine soil C stock, analysis was conducted as reported by Chiavegato et al. (2015b).”
BackgroundMethodSelf-citation379 Effects of diet type and feeding phase on intake and feed efficiency of beef cattle
Cassady, C., Felix, T. L., & Shike, D. W. (2016) · Journal of Animal Science · doi:10.2527/msasas2016-379 · Cited by 14 · see citing works
Estimating Energy Use in World Irrigation
SLOGGETT, G. (1992) · Energy in Farm Production · doi:10.1016/b978-0-444-88681-1.50019-3 · Cited by 12 · see citing works
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Carbon flux assessment in cow-calf grazing systems1
Chiavegato, M. B., Rowntree, J. E., & Powers, W. J. (2015) · Journal of Animal Science · doi:10.2527/jas.2015-9031 · Cited by 4 · see citing works
Self-citationSchroeder, J. C. (2012) · Epidemiology · doi:10.1097/01.ede.0000416980.07695.1b
VOISIN, A. (1960) · Soil Science · doi:10.1097/00010694-196002000-00022
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Direct air capture: process technology, techno-economic and socio-political challenges
Erans, M., Sanz-Pérez, E. S., Hanak, D. P., Clulow, Z., Reiner, D. M., & Mutch, G. A. (2022) · Energy & Environmental Science · doi:10.1039/d1ee03523a · Cited by 688 · see citing works
Managing Grazing to Restore Soil Health, Ecosystem Function, and Ecosystem Services
Teague, R., & Kreuter, U. P. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.534187 · Cited by 377 · see citing works
Life cycle assessment of carbon dioxide removal technologies: a critical review
Terlouw, T., Bauer, C., Rosa, L., & Mazzotti, M. (2021) · Energy & Environmental Science · doi:10.1039/d0ee03757e · Cited by 366 · see citing works
Grassland Management Affects Delivery of Regulating and Supporting Ecosystem Services
Sollenberger, L. E., Kohmann, M. M., Dubeux, J. C. B., & Silveira, M. L. (2019) · Crop Science · doi:10.2135/cropsci2018.09.0594 · Cited by 209 · see citing works
Plant-Based Meats, Human Health, and Climate Change
van Vliet, S., Kronberg, S. L., & Provenza, F. D. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.00128 · Cited by 207 · see citing works
“Pastured beef systems that use land management practices such as rotational grazing—where lands are allowed to properly recover after a grazing period— and/or cover crop grazing suggest that the amounts of carbon sequestered in the soil more than offsets the ruminants’ GHGE, resulting in a net negative carbon footprin…”
BackgroundMosier, S., Apfelbaum, S., Byck, P., Calderon, F., Teague, R., Thompson, R., & Cotrufo, M. F. (2021) · Journal of Environmental Management · doi:10.1016/j.jenvman.2021.112409 · Cited by 176 · see citing works
“Conversely, several types of rotational grazing can restore grassland ecosystem function and have beneficial impacts on soils as well (Conant et al., 2003; Dubeux et al., 2006; Teague et al., 2011; Machmuller et al., 2014; Teague, 2018; Stanley et al., 2019).”
BackgroundLeroy, F., Abraini, F., Beal, T., Domínguez-Salas, P., Gregorini, P., Manzano, P., Rowntree, J. E., & van Vliet, S. (2022) · animal · doi:10.1016/j.animal.2022.100457 · Cited by 147 · see citing works
Self-citationInvited Review: Methane Sources, Quantification, and Mitigation in Grazing Beef Systems
Thompson, L. R., & Rowntree, J. E. (2020) · Applied Animal Science · doi:10.15232/aas.2019-01951 · Cited by 112 · see citing works
Self-citationHealth-Promoting Phytonutrients Are Higher in Grass-Fed Meat and Milk
van Vliet, S., Provenza, F. D., & Kronberg, S. L. (2021) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.555426 · Cited by 119 · see citing works
“Pasture-based grazing systems, when managed in ways that mimic natural ecosystems, can improve plant diversity (Teague, 2018), soil carbon levels (Allard et al., 2007; Stanley et al., 2018), ecosystem function (Krausman et al.”
BackgroundEcosystem Impacts and Productive Capacity of a Multi-Species Pastured Livestock System
Rowntree, J. E., Stanley, P. L., Maciel, I. C. F., Thorbecke, M., Rosenzweig, S. T., Hancock, D. W., Guzman, A., & Raven, M. R. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.544984 · Cited by 110 · see citing works
“Recent studies show that livestock-induced soil C changes can have large impacts on the GHG balance of these production systems (Beauchemin et al., 2011; Teague et al., 2016; Stanley et al., 2018).”
BackgroundMethodResultInfluentialSelf-citationEnvironmental sustainability of negative emissions technologies: A review
Jeswani, H. K., Saharudin, D. M., & Azapagic, A. (2022) · Sustainable Production and Consumption · doi:10.1016/j.spc.2022.06.028 · Cited by 110 · see citing works
Systematic Review of Dietary Patterns and Sustainability in the United States
Reinhardt, S., Boehm, R., Blackstone, N. T., El-Abbadi, N., Brandow, J. S. M., Taylor, S. F., & DeLonge, M. S. (2020) · Advances in Nutrition · doi:10.1093/advances/nmaa026 · Cited by 109 · see citing works
Self-citationIs Grassfed Meat and Dairy Better for Human and Environmental Health?
Provenza, F. D., Kronberg, S. L., & Gregorini, P. (2019) · Frontiers in Nutrition · doi:10.3389/fnut.2019.00026 · Cited by 102 · see citing works
“Managed grazing can moderate climate change, an outcome that challenges the view of feedlots as the best way to reduce GHGE from livestock (29, 30).”
BackgroundEcosystem carbon sequestration service supports the Sustainable Development Goals progress
Yin, C., Zhao, W., Ye, J., Muroki, M., & Pereira, P. A. D. S. (2023) · Journal of Environmental Management · doi:10.1016/j.jenvman.2022.117155 · Cited by 98 · see citing works
Gosnell, H., Charnley, S., & Stanley, P. (2020) · Interface Focus · doi:10.1098/rsfs.2020.0027 · Cited by 94 · see citing works
“Additionally, there is increasing evidence that RR can reduce enteric methane emissions, which are often high in grazing systems [13,59].”
BackgroundSelf-citationCusack, D. F., Kazanski, C. E., Hedgpeth, A., Chow, K., Cordeiro, A. L., Karpman, J., & Ryals, R. (2021) · Global Change Biology · doi:10.1111/gcb.15509 · Cited by 93 · see citing works
“…C sequestration) with improved management in temperate ecosystem grazed lands (Herrero et al., 2016; Paustian et al., 2016; Rowntree et al., 2016; Stanley et al., 2018; Teague et al., 2016), although management- related soil C sequestration rates may diminish over time, with added soil C storage…”
BackgroundInfluentialSher, A., Li, H., Ullah, A., Hamid, Y., Nasir, B., & Zhang, J. (2024) · Discover Sustainability · doi:10.1007/s43621-024-00662-z · Cited by 94 · see citing works
Ruminating on soil carbon: applying current understanding to inform grazing management
Stanley, P. L., Wilson, C., Patterson, E., Machmuller, M. B., & Cotrufo, M. F. (2024) · Global Change Biology · doi:10.1111/gcb.17223 · Cited by 82 · see citing works
“…support more accurate model development to better represent, generalize, and predict SOC response from grazing at scale, which is necessary to predict the SOC sequestration potential of these systems as a natural climate solution and to inform appropriate incentive structures and climate policies.”
Self-citationEldesouky, A., Díaz, F. J. M., Elghannam, A., & Escribano, M. (2018) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2018.07.279 · Cited by 79 · see citing works
Climate Change, Rangelands, and Sustainability of Ranching in the Western United States
Holechek, J. L., Geli, H. M. E., Cibils, A. F., & Sawalhah, M. N. (2020) · Sustainability · doi:10.3390/su12124942 · Cited by 77 · see citing works
“In a Midwestern US study, it was found that adaptive multi-paddock rotation grazing could sequester large amounts of soil carbon and completely offset grazing cattle carbon emissions [51].”
BackgroundGrazing management for soil carbon in Australia: A review
McDonald, S. E., Badgery, W. B., Clarendon, S., Orgill, S. E., Sinclair, K., Meyer, R., Butchart, D. B., Eckard, R., Rowlings, D. W., Grace, P., et al. (2023) · Journal of Environmental Management · doi:10.1016/j.jenvman.2023.119146 · Cited by 78 · see citing works
Horrillo, A., Gaspar, P., & Escribano, M. (2020) · Animals · doi:10.3390/ani10010162 · Cited by 71 · see citing works
“Life cycle assessment (LCA) is one of the methods most frequency used to calculate the balance of greenhouse gas emissions (GHG) in livestock farms, as it is a standard and internationally-accepted means to effectively quantify the environmental impact of a product, and also allows to take into account carbon sequestr…”
BackgroundMethodHow big is the energy efficiency resource?
Lovins, A. B. (2018) · Environmental Research Letters · doi:10.1088/1748-9326/aad965 · Cited by 70 · see citing works
Moberg, E., Walker Andersson, M., Säll, S., Hansson, P.-A., & Röös, E. (2019) · The International Journal of Life Cycle Assessment · doi:10.1007/s11367-019-01597-8 · Cited by 67 · see citing works
“As LCA studies neglecting to account for soil carbon have been criticised repeatedly by researchers (e.g. Stanley et al. 2018) and by proponents of grass-fed ruminant production (e.g. Rundgren and Bremen 2017), including soil carbon changes can be especially important for acceptance of a climate…”
BackgroundSoil carbon sequestration in grazing systems: managing expectations
Godde, C. M., de Boer, I. J. M., Ermgassen, E. Z., Herrero, M., van Middelaar, C. E., Muller, A., Röös, E., Schader, C., Smith, P., van Zanten, H. H. E., et al. (2020) · Climatic Change · doi:10.1007/s10584-020-02673-x · Cited by 63 · see citing works
Shaw, W. J., Kidder, M. K., Bare, S. R., Delferro, M., Morris, J. R., Toma, F. M., Senanayake, S. D., Autrey, T. S., Biddinger, E. J., Boettcher, S. W., et al. (2024) · Nature Reviews Chemistry · doi:10.1038/s41570-024-00587-1 · Cited by 66 · see citing works
Gislon, G., Ferrero, F., Bava, L., Borreani, G., Prà, A. D., Pacchioli, M. T., Sandrucci, A., Zucali, M., & Tabacco, E. (2020) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2020.121012 · Cited by 61 · see citing works
Oliveira, P. P. A., Berndt, A., Pedroso, A. D. F., Alves, T. C., Pezzopane, J. R. M., Sakamoto, L. S., Henrique, F. L., & Rodrigues, P. H. M. (2020) · animal · doi:10.1017/s1751731120001822 · Cited by 63 · see citing works
Grass-fed vs. grain-fed beef systems: performance, economic, and environmental trade-offs
Klopatek, S. C., Marvinney, E., Duarte, T., Kendall, A. M., Yang, X., & Oltjen, J. W. (2021) · Journal of Animal Science · doi:10.1093/jas/skab374 · Cited by 61 · see citing works
Voisin Rational Grazing as a Sustainable Alternative for Livestock Production
Filho, L. C. P. M., Seó, H. L. S., Daros, R. R., Enríquez-Hidalgo, D., Wendling, A. V., & Machado, L. C. P. (2021) · Animals · doi:10.3390/ani11123494 · Cited by 60 · see citing works
“[59] used the same guidelines to consider C sequestration.”
Review: Impact of Food and Climate Change on Pastoral Industries
Uddin, M. E., & Kebreab, E. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.543403 · Cited by 56 · see citing works
Gutiérrez-Peña, R., Guerrero, Y. M., Batalla, I., & Mancilla-Leytón, J. M. (2018) · Journal of Environmental Management · doi:10.1016/j.jenvman.2018.12.005 · Cited by 54 · see citing works
“In recent years, several research studies have shown that C sequestration can be maximized by using adequate management practices for livestock grazing, for example through rotational grazing management (multi-paddock systems) or with an appropriate grazing intensity according to each specific context (soil texture, p…”
BackgroundKooch, Y., Moghimian, N., Wirth, S. J., & Noghre, N. (2019) · Geoderma · doi:10.1016/j.geoderma.2019.114100 · Cited by 53 · see citing works
Adaptive multi-paddock grazing improves water infiltration in Canadian grassland soils
Döbert, T. F., Bork, E. W., Apfelbaum, S. I., Carlyle, C. N., Chang, S. X., Khatri‐Chhetri, U., Sobrinho, L. S., Thompson, R., & Boyce, M. S. (2021) · Geoderma · doi:10.1016/j.geoderma.2021.115314 · Cited by 51 · see citing works
Management options to reduce the environmental impact of dairy goat milk production
Zucali, M., Lovarelli, D., Celozzi, S., Bacenetti, J., Sandrucci, A., & Bava, L. (2019) · Livestock Science · doi:10.1016/j.livsci.2019.103888 · Cited by 49 · see citing works
Lileikis, T., Nainienė, R., Bliznikas, S., & Uchockis, V. (2023) · Animals · doi:10.3390/ani13162586 · Cited by 59 · see citing works
“Apart from the nutritional approach described abov e, well - managed grazing systems could indirectly mitigate emissions through extensive carbon sequestration [3,28,29].”
BackgroundBriones-Hidrovo, A., Rey, J. R. C., Dias, A. C., Tarelho, L. A. C., & Beauchet, S. (2022) · Energy Conversion and Management · doi:10.1016/j.enconman.2022.116014 · Cited by 48 · see citing works
“…abatement and reduction in the same accounting [14 – 16]; b) C accounting and storage are not clearly stated in quantitative terms, e.g., [17 – 20]; c) C storage is represented in terms of climate change impact which is quantitatively misleading [3,21]; d) so far, only static LCA has been…”
BackgroundGislon, G., Colombini, S., Borreani, G., et al. (2020) · Journal of Dairy Science · doi:10.3168/jds.2019-18134 · Cited by 47 · see citing works
Carbon sequestration offsets a large share of GHG emissions in dehesa cattle production
Reyes-Palomo, C., Aguilera, E., Llorente, M., Díaz-Gaona, C., Moreno, G., & Rodríguez‐Estévez, V. (2022) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2022.131918 · Cited by 44 · see citing works
Holistic Management and Adaptive Grazing: A Trainers’ View
Mann, C., & Sherren, K. (2018) · Sustainability · doi:10.3390/su10061848 · Cited by 46 · see citing works
“Although it is difficult to untangle the effects of grazing from other livestock production methods like concentrated animal feeding operations [12], the numbers are nonetheless staggering.”
BackgroundDowhower, S. L., Teague, W. R., Casey, K. D., & Daniel, R. (2019) · Agriculture Ecosystems & Environment · doi:10.1016/j.agee.2019.106647 · Cited by 47 · see citing works
Hải, L. T., Tran, Q. B., Tra, V. T., et al. (2020) · Environmental Pollution · doi:10.1016/j.envpol.2020.114853 · Cited by 44 · see citing works
Escribano, M., Horrillo, A., & Díaz, F. J. M. (2022) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2022.133779 · Cited by 42 · see citing works
Protein pluralism and food systems transition: A review of sustainable protein meta-narratives
Katz-Rosene, R. M., Heffernan, A., & Arora, A. (2022) · World Development · doi:10.1016/j.worlddev.2022.106121 · Cited by 40 · see citing works
Life Cycle Assessment of Iberian Traditional Pig Production System in Spain
García-Gudiño, J., Monteiro, A., Espagnol, S., et al. (2020) · Sustainability · doi:10.3390/su12020627 · Cited by 41 · see citing works
Damian, J. M., Matos, E. D. S., Pedreira, B. C. E., Carvalho, P. C. D. F., Premazzi, L. M., & Cerri, C. E. P. (2022) · CATENA · doi:10.1016/j.catena.2022.106750 · Cited by 43 · see citing works
Risk to rely on soil carbon sequestration to offset global ruminant emissions
Wang, Y., de Boer, I. J. M., Persson, U. M., Ripoll-Bosch, R., Cederberg, C., Gerber, P. J., Smith, P., & van Middelaar, C. E. (2023) · Nature Communications · doi:10.1038/s41467-023-43452-3 · Cited by 39 · see citing works
Delta Life Cycle Assessment of Regenerative Agriculture in a Sheep Farming System
Colley, T., Olsen, S. I., Birkved, M., & Hauschild, M. Z. (2019) · Integrated Environmental Assessment and Management · doi:10.1002/ieam.4238 · Cited by 39 · see citing works
A land-based approach for climate change mitigation in the livestock sector
Chiriacò, M. V., & Valentini, R. (2020) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2020.124622 · Cited by 39 · see citing works
Dillon, J. A., Stackhouse-Lawson, K. R., Thoma, G. J., Gunter, S. A., Rotz, C. A., Kebreab, E., Riley, D. G., Tedeschi, L. O., Villalba, J. J., Mitloehner, F. M., et al. (2021) · Animal Frontiers · doi:10.1093/af/vfab043 · Cited by 39 · see citing works
Are Livestock Always Bad for the Planet? Rethinking the Protein Transition and Climate Change Debate
Houzer, E., & Scoones, I. (2021) · doi:10.19088/steps.2021.003 · Cited by 38 · see citing works
Eenennaam, A. L. V., & Werth, S. J. (2021) · animal · doi:10.1016/j.animal.2021.100360 · Cited by 37 · see citing works
Herron, J., Curran, T. P., MOLONEY, A. P., McGee, M., O’Riordan, E. G., & O’Brien, D. (2021) · animal · doi:10.1016/j.animal.2021.100247 · Cited by 36 · see citing works
Maciel, I. C. D. F., Barbosa, F. A., Tomich, T. R., Ribeiro, L. G. P., Alvarenga, R. C., Lopes, L. S., Malacco, V. M. R., Rowntree, J. E., Thompson, L. R., & Lana, Â. M. Q. (2019) · PLoS ONE · doi:10.1371/journal.pone.0220247 · Cited by 34 · see citing works
“However, the majority of studies evaluated the continuous grazing management system and assumed steady-state soil carbon (C) to model the grass-finishing environmental impact [7].”
BackgroundSelf-citationChallenges in using soil carbon modelling in LCA of agricultural products—the devil is in the detail
Joensuu, K., Rimhanen, K., Heusala, H., Saarinen, M., Usva, K., Leinonen, I., & Palosuo, T. (2021) · The International Journal of Life Cycle Assessment · doi:10.1007/s11367-021-01967-1 · Cited by 37 · see citing works
“A similar assumption has also been made in most of the previous LCA studies, taking into account that SOC changes have only considered single crops (Petersen et al. 2013; van Middelaar et al. 2016; Stanley et al. 2018; Knudsen et al. 2019).”
Resultdel Prado, A., Manzano, P., & Pardo, G. O. (2021) · Journal of Dairy Research · doi:10.1017/s0022029921000157 · Cited by 33 · see citing works
Monteiro, A., Wilfart, A., Utzeri, V. J., et al. (2019) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2019.117843 · Cited by 32 · see citing works
Fire, deforestation, and livestock: When the smoke clears
Silva, R. D. O., Barioni, L. G., & Moran, D. (2020) · Land Use Policy · doi:10.1016/j.landusepol.2020.104949 · Cited by 31 · see citing works
Arndt, K. A., Campbell, E. E., Dorich, C. D., Grandy, A. S., Griffin, T. S., Ingraham, P., Perry, A. L., Varner, R. K., & Contosta, A. R. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.152195 · Cited by 32 · see citing works
Surface‐soil carbon stocks greater under well‐managed grazed pasture than row crops
Becker, A. E., Horowitz, L. S., Ruark, M. D., et al. (2022) · Soil Science Society of America Journal · doi:10.1002/saj2.20388 · Cited by 31 · see citing works
Challenges in Sustainable Beef Cattle Production: A Subset of Needed Advancements
Hubbart, J. A., Blake, N., Holásková, I., et al. (2023) · Challenges · doi:10.3390/challe14010014 · Cited by 30 · see citing works
“Grassland-based animal agriculture has the potential to be carbon-negative if proper management techniques, including the incorporation of rotational grazing and diverse botanical compositions that include N-fixing leguminous forages, can reduce N2O emissions [40,41].”
BackgroundEffects of herd management and the use of ivermectin on dung arthropod communities in grasslands
Pecenka, J., & Lundgren, J. G. (2019) · Basic and Applied Ecology · doi:10.1016/j.baae.2019.07.006 · Cited by 30 · see citing works
Liebe, D. M., Hall, M. B., & White, R. R. (2020) · Journal of Dairy Science · doi:10.3168/jds.2020-18570 · Cited by 29 · see citing works
Jackson, R. D. (2022) · Agricultural & Environmental Letters · doi:10.1002/ael2.20059 · Cited by 30 · see citing works
“B: Grass-finished pasture beef 0 75.8 19.0 Sanford, 2014 (320) 60.9 15.2 Becker et al., 2022 (840) 36.8 9.2 Franzluebbers, 2010 (1,630) 0 0 – (3,590) (91.5) (22.9) Stanley et al., 2018 before they are rotated to new paddocks.”
BackgroundInfluentialSabia, E., Kühl, S., Flach, L. F., Lambertz, C., & Gauly, M. (2020) · Sustainability · doi:10.3390/su12052128 · Cited by 29 · see citing works
Livestock in Evolving Foodscapes and Thoughtscapes
Leroy, F., Hite, A. H., & Gregorini, P. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.00105 · Cited by 29 · see citing works
Implementing the Soil Enrichment Protocol at Scale: Opportunities for an Agricultural Carbon Market
Hammond, A. A. J., Motew, M. M., Brummitt, C. D., DuBuisson, M. L., Pinjuv, G., Harburg, D. V., Campbell, E. E., & Kumar, A. A. (2021) · Frontiers in Climate · doi:10.3389/fclim.2021.686440 · Cited by 28 · see citing works
Deniz, M., De-Sousa, K. T., Moro, M. F., do Vale, M. M., Dittrich, J. R., Filho, L. C. P. M., & Hötzel, M. J. (2021) · Applied Animal Behaviour Science · doi:10.1016/j.applanim.2021.105467 · Cited by 29 · see citing works
Fernandes, M. H. M. R., Fernandes, J., Adams, J. M., Lee, M., Reis, R. A., & Tedeschi, L. O. (2024) · Scientific Reports · doi:10.1038/s41598-024-59160-x · Cited by 28 · see citing works
“After forests, grasslands are a significant source of carbon sinks 3 and thus play an essential role in regulating global carbon atmospheric concentration 4,5 .”
BackgroundDietz, C. L., Jackson, R. D., Ruark, M. D., et al. (2024) · Communications Earth & Environment · doi:10.1038/s43247-024-01500-w · Cited by 28 · see citing works
Do Differences in Livestock Management Practices Influence Environmental Impacts?
Kleppel, G. S. (2020) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2020.00141 · Cited by 28 · see citing works
“Although regenerative production will not slow population growth and will never, in and of itself, provide the solution to world hunger, agriculture, including animal agriculture, can play an important role in GHG mitigation, soil-health restoration, and water and biodiversity conservation (Lal, 2004; Herrero and Thor…”
BackgroundArca, P., Vagnoni, E., Duce, P., et al. (2021) · Italian Journal of Agronomy · doi:10.4081/ija.2021.1789 · Cited by 28 · see citing works
“Ac ce pt ed p ap er For instance, according to Stanley et al. (2018), the increase of grazing surface together with the improvement of grazing management in SE contributed to enhance the soil Cseq of production system.”
BackgroundMcGee, M., Lenehan, C., Crosson, P., O’Riordan, E. G., Kelly, A. K., Morán, L., & MOLONEY, A. P. (2022) · Agricultural Systems · doi:10.1016/j.agsy.2022.103379 · Cited by 27 · see citing works
Raihan, A. (2023) · Environmental Processes · doi:10.1007/s40710-023-00650-x · Cited by 27 · see citing works
“Utilizing end disposal on the field (as organic fertilizer) is one method of reducing greenhouse gas emissions from the production of slurry (Stanley et al. 2018).”
BackgroundMethodDurigan, G., Pilon, N. A. L., Souza, F. M., et al. (2022) · Biotropica · doi:10.1111/btp.13105 · Cited by 26 · see citing works
“However, in livestock systems with ruminants consuming only grazed forages and managed appropriately, carbon sequestration by plants exceeds carbon emissions by cattle diggestion (Stanley et al., 2018).”
BackgroundDahal, S., Franklin, D. H., Subedi, A., Cabrera, M. L., Hancock, D. W., Mahmud, K., Ney, L., Park, C., & Mishra, D. R. (2020) · Sustainability · doi:10.3390/su12020558 · Cited by 25 · see citing works
Carbon sequestration potential and the multiple functions of Nordic grasslands
Norderhaug, A., Clemmensen, K. E., Kardol, P., Þorhallsdóttir, A. G., & Aslaksen, I. (2023) · Climatic Change · doi:10.1007/s10584-023-03537-w · Cited by 25 · see citing works
Examining the role of ruminants in sustainable food systems
Place, S. E. (2024) · Grass and Forage Science · doi:10.1111/gfs.12673 · Cited by 24 · see citing works
Wang, F., Apfelbaum, S. I., Thompson, R., Teague, R., & Byck, P. (2021) · Landscape Ecology · doi:10.1007/s10980-021-01273-z · Cited by 24 · see citing works
de Faria, Á. J. G., Silva, S. H. G., Andrade, R., et al. (2021) · Geoderma Regional · doi:10.1016/j.geodrs.2021.e00461 · Cited by 24 · see citing works
Shrestha, B. M., Bork, E. W., Chang, S. X., et al. (2020) · Agronomy · doi:10.3390/agronomy10111781 · Cited by 23 · see citing works
“These results are indicative of a smaller GHG footprint in grasslands subject to AMP grazing and in line with findings of other studies such as CH4 sink capacity of the Northern Great Plains pastures [9] and lower GHG emissions from AMP-grazed than feedlot beef productions [66].”
ResultTedeschi, L. O., & Beauchemin, K. A. (2023) · Journal of Animal Science · doi:10.1093/jas/skad024 · Cited by 23 · see citing works
“Stanley et al. (2018) showed that when using a rotational-type grass management system (Voisin, 1959), the 4-yr C sequestration rate was 3.59 Mg C/ha/yr, leading to −6.65 kg CO 2e/kg carcass (a sink of C) when compared to feedlot finished systems (6.12 kg CO2e/kg carcass).”
BackgroundInfluentialBeck, M. R., Thompson, L. R., Rowntree, J. E., Thompson, T. N., Koziel, J. A., Place, S. E., & Stackhouse-Lawson, K. R. (2023) · Frontiers in Sustainable Food Systems · doi:10.3389/fsufs.2023.1209541 · Cited by 23 · see citing works
Self-citationHammar, T., Hansson, P.-A., & Röös, E. (2022) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2021.129948 · Cited by 22 · see citing works
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Lecegui, A., Tolosana, A. O., & Varela, E. (2022) · Forest Ecology and Management · doi:10.1016/j.foreco.2022.120273 · Cited by 22 · see citing works
Rancher Experiences and Perceptions of Climate Change in the Western United States
Saliman, A., & Petersen-Rockney, M. (2022) · Rangeland Ecology & Management · doi:10.1016/j.rama.2022.06.001 · Cited by 22 · see citing works
Zhang, M., Li, H., Chen, S., et al. (2023) · Environmental Impact Assessment Review · doi:10.1016/j.eiar.2023.107212 · Cited by 22 · see citing works
Khatri‐Chhetri, U., Thompson, K. A., Quideau, S. A., Boyce, M. S., Chang, S. X., Kaliaskar, D., Bork, E. W., & Carlyle, C. N. (2022) · Applied Soil Ecology · doi:10.1016/j.apsoil.2022.104590 · Cited by 23 · see citing works
Tran, D. X., Pearson, D. M., Palmer, A., Gray, D., Lowry, J. H., & Dominati, E. (2022) · Agricultural Systems · doi:10.1016/j.agsy.2022.103494 · Cited by 21 · see citing works
Grazing livestock move by Lévy walks: Implications for soil health and environment
Romero‐Ruiz, A., Rivero, M. J., Milne, A. E., et al. (2023) · Journal of Environmental Management · doi:10.1016/j.jenvman.2023.118835 · Cited by 21 · see citing works
Soil carbon and nitrogen after eight years of rotational grazing in the Nebraska Sandhills meadows
Abagandura, G. O., Mamo, M., Schacht, W. H., Shropshire, A., & Volesky, J. D. (2024) · Geoderma · doi:10.1016/j.geoderma.2024.116776 · Cited by 21 · see citing works
“High stocking density rotational grazing in the US Midwestern states sequestered large amounts of soil C as reported by Stanley et al. (2018), however; in this study, MOB gazing did not affect C and N sequestration rates in the experimental period when compared to low stocking density treatments…”
BackgroundIncluding long-term soil organic carbon changes in life cycle assessment of agricultural products
Sevenster, M., Luo, Z., Eady, S. J., et al. (2019) · The International Journal of Life Cycle Assessment · doi:10.1007/s11367-019-01660-4 · Cited by 21 · see citing works
Kamilaris, C., Dewhurst, R. J., Sykes, A. J., & Alexander, P. M. (2019) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2019.119888 · Cited by 23 · see citing works
Lee, J. G., Chae, H. G., Kim, G. W., Kim, P. J., & Cho, S. R. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.151015 · Cited by 21 · see citing works
Meat as a Pharmakon: An Exploration of the Biosocial Complexities of Meat Consumption
Leroy, F. (2018) · Advances in food and nutrition research · doi:10.1016/bs.afnr.2018.07.002 · Cited by 21 · see citing works
The influence of meat consumption on greenhouse gas emissions in Argentina
Raihan, A. (2023) · Resources Conservation & Recycling Advances · doi:10.1016/j.rcradv.2023.200183 · Cited by 20 · see citing works
Managed Grazing on California Annual Rangelands in the Context of State Climate Policy
Biggs, N. B., & Huntsinger, L. (2021) · Rangeland Ecology & Management · doi:10.1016/j.rama.2021.01.007 · Cited by 19 · see citing works
Contosta, A. R., Arndt, K. A., Campbell, E. E., Grandy, A. S., Perry, A. L., & Varner, R. K. (2021) · Agriculture Ecosystems & Environment · doi:10.1016/j.agee.2021.107471 · Cited by 19 · see citing works
Optimizing livestock feed provision to improve the efficiency of the agri-food system
Wyngaarden, S., Lightburn, K. K., & Martin, R. C. (2019) · Agroecology and Sustainable Food Systems · doi:10.1080/21683565.2019.1633455 · Cited by 21 · see citing works
“Stanley et al. (2018) noted that 6.65 kg CO2 equivalent per kg carcass weight could be sequestered with adaptive multipaddock grazing.”
BackgroundInfluential
- Authors
- Stanley, P. L., Rowntree, J. E., Beede, D. K., DeLonge, M. S., & Hamm, M. W.
- Affiliations
- Michigan State University (US)
- Union of Concerned Scientists (US)
- Corresponding author
- Rowntree, Jason E.
- Venue
- Agricultural Systems
- Publisher
- Elsevier BV
- Published
- 2018-05
- Volume
- 162
- Pages
- 249-258
- ISSN
- 0308-521X (ISSN-L)
- OpenAlex
- W2792041063
- Semantic Scholar
- 07dc7d76048beb65844d17e217fe44e8ae7096bd
- Cited by
- 266
- References
- 61
- Citations by year
- 2026: 25 · 2025: 36 · 2024: 37 · 2023: 33 · 2022: 39 · 2021: 37 · 2020: 32 · 2019: 20 · 2018: 7
- FWCI
- 17.36
- Type
- journal article
- Language
- en
- Open access
- hybrid
- doi.org
- Locations
- Agricultural Systems (publishedVersion, cc-by)
- RePEc: Research Papers in Economics (submittedVersion)
- Topics
- Physical Sciences › Environmental Science › Ecology › Agriculture Sustainability and Environmental Impact
- Physical Sciences › Environmental Science › Environmental Chemistry › Sustainable Agricultural Systems Analysis
- Life Sciences › Agricultural and Biological Sciences › Agronomy and Crop Science › Ruminant Nutrition and Digestive Physiology
- Keywords
- soil organic carbon sequestration, beef cattle, feedlot finishing, adaptive multi-paddock grazing, greenhouse gas emissions, enteric methane, manure management, soil erosion, climate change mitigation, carbon sink
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