Impact of a Winter Rye Cover Crop on Edge-of-Field Nutrient Losses and Corn Silage Production PDF Download
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Author: Keegan E. Griffith
Publisher:
ISBN:
Category : Cover crops
Languages : en
Pages : 230
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Book Description
Cover crops have the potential to reduce environmental impacts of corn production. The objective of this study was to quantify differences in nitrogen (N) and phosphorus (P) loading between corn plots with or without a winter rye cover crop (Secale cerale). Four field plots (30 x 46 m) in Chazy, NY with edge-of-field monitoring were used for the study. Two plots were randomly assigned a rye cover crop treatment and planted with a grain drill at a rate of 112 kg ha-1 after corn silage harvest in 2015 and 2016. Continuous water flows were monitored from surface runoff and tile drain hydrologic pathways dur-ing runoff events. Soluble reactive P (SRP), total P (TP), nitrate-N, total N (TN), and to-tal suspended solids (TSS) concentrations were measured and multiplied by runoff vol-umes to estimate nutrient export. Surface runoff from rye plots had lower nutrient loss compared to control plots. Cumulative nitrate-N exports were similar between treatments (15.7 vs. 14.8 kg nitrate-N ha-1 for rye and control, respectively). Cumulative TN exports were numerically higher for control plots compared to rye plots, (18.8 vs. 21.4 kg TN ha-1). Cumulative TP and SRP exports (surface + tile) for rye were 2.2 and 3-fold greater than control plots, (0.51 vs. 1.19 kg TP ha-1 and 0.33 vs. 0.96 kg SRP ha-1). Total P and SRP loads in surface runoff were 3.0-fold greater for control plots compared to rye plots (0.36 vs. 1.12 kg TP ha-1 and 0.32 vs. 0.94 kg SRP ha-1). TSS load in surface runoff was numerically higher for control plots compared to rye (5.7 vs. 20.6 kg ha-1). Cumulative surface runoff was 1.8-fold greater in control plots compared to rye plots (112.6 mm vs. 207.7 mm), while cumulative tile runoff was numerically higher in rye plots compared to control (83.2 mm vs. 66.1mm). Snowmelt events contributed the majority of phosphorus losses (96% of SRP and 92% of TP), emphasizing the need to implement management techniques that reduce P transport risk during the non-growing season. Winter rye re-duced snowmelt TP export by 3-fold compared to the control plots (0.33 kg TP ha-1 and 1.03 kg TP ha-1). The winter rye cover crop planted after corn silage harvest effectively reduced erosion and P transport in surface water runoff compared to corn silage left fal-low after harvest. In addition to significantly reducing P exports, farms have the option of harvesting rye as a forage crop and double cropping with corn. In this way, more total forage is possible for the farm in addition to offering environmental conservation and wa-ter quality benefits.
Author: Keegan E. Griffith
Publisher:
ISBN:
Category : Cover crops
Languages : en
Pages : 230
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Book Description
Cover crops have the potential to reduce environmental impacts of corn production. The objective of this study was to quantify differences in nitrogen (N) and phosphorus (P) loading between corn plots with or without a winter rye cover crop (Secale cerale). Four field plots (30 x 46 m) in Chazy, NY with edge-of-field monitoring were used for the study. Two plots were randomly assigned a rye cover crop treatment and planted with a grain drill at a rate of 112 kg ha-1 after corn silage harvest in 2015 and 2016. Continuous water flows were monitored from surface runoff and tile drain hydrologic pathways dur-ing runoff events. Soluble reactive P (SRP), total P (TP), nitrate-N, total N (TN), and to-tal suspended solids (TSS) concentrations were measured and multiplied by runoff vol-umes to estimate nutrient export. Surface runoff from rye plots had lower nutrient loss compared to control plots. Cumulative nitrate-N exports were similar between treatments (15.7 vs. 14.8 kg nitrate-N ha-1 for rye and control, respectively). Cumulative TN exports were numerically higher for control plots compared to rye plots, (18.8 vs. 21.4 kg TN ha-1). Cumulative TP and SRP exports (surface + tile) for rye were 2.2 and 3-fold greater than control plots, (0.51 vs. 1.19 kg TP ha-1 and 0.33 vs. 0.96 kg SRP ha-1). Total P and SRP loads in surface runoff were 3.0-fold greater for control plots compared to rye plots (0.36 vs. 1.12 kg TP ha-1 and 0.32 vs. 0.94 kg SRP ha-1). TSS load in surface runoff was numerically higher for control plots compared to rye (5.7 vs. 20.6 kg ha-1). Cumulative surface runoff was 1.8-fold greater in control plots compared to rye plots (112.6 mm vs. 207.7 mm), while cumulative tile runoff was numerically higher in rye plots compared to control (83.2 mm vs. 66.1mm). Snowmelt events contributed the majority of phosphorus losses (96% of SRP and 92% of TP), emphasizing the need to implement management techniques that reduce P transport risk during the non-growing season. Winter rye re-duced snowmelt TP export by 3-fold compared to the control plots (0.33 kg TP ha-1 and 1.03 kg TP ha-1). The winter rye cover crop planted after corn silage harvest effectively reduced erosion and P transport in surface water runoff compared to corn silage left fal-low after harvest. In addition to significantly reducing P exports, farms have the option of harvesting rye as a forage crop and double cropping with corn. In this way, more total forage is possible for the farm in addition to offering environmental conservation and wa-ter quality benefits.
Author: Christian D. Kessler
Publisher:
ISBN:
Category : Corn
Languages : en
Pages : 0
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Book Description
Cover crops are often planted during the fallow periods of cash crop harvests to cover the soil and reduce erosion but also to provide other ecosystem benefits including capturing residual nutrients and thus, reducing environmental losses of nitrogen (N) and phosphorus (P) in agroecosystems. Among these cover crops, winter rye (Secale cereale) is popular due to its winter hardiness and relatively cheap seed costs. However, growers in the Midwest, USA are reluctant to use winter rye prior to corn (Zea mays L.) due to the potential yield penalty in corn. This thesis introduces two strategies that could minimize winter rye's effect on corn while providing nutrient loss reduction benefits are precision planting and reducing the seeding rate of winter rye ahead of corn. One study evaluates whether precision planting (planting winter rye strategically to avoid intersecting zones with corn) of winter rye at low seeding rate (37.5 kg ha-1) could produce similar cover crop biomass and quality to normal planted winter rye (50 kg ha-1) and if precision planting can improve performance and N requirement of corn (Chapter 1). The study was conducted in central Indiana during 2020-2021 (CIN21), and southern Illinois during 2021-2022 (SIL22), and 2022-2023 (SIL23) growing seasons. The experiment was arranged in a randomized block design with split plot arrangement. Main plots were three cover crops (a no-cover crop control (NoCC), conventional planted winter rye (CR), and precision planted winter rye (PR). Subplots were six rates of N fertilizer that ranged from 0-280 kg ha-1 for the CIN21 and 0-359 kg ha-1 for SIL22 and SIL23. Our results indicated that shifting from normal planting to precision planting resulted in similar cover crop biomass production with limited effect on winter rye quality [N concentration, Carbon (C):N ratio] and N and C accumulation. In CIN21, the nocover crop control had higher yield and lower N requirements which was consistent with those of SIL22. The economic optimum rate of N (EORN) was below the typical recommended range for central Indiana and was above the recommended range for southern Illinois. Precision planting resulted in a slight increase in corn yield and N requirement, but overall was more profitable than normal planting due to a reduction in the number of seeds required and higher corn to fertilizer prices. Therefore, we recommend that (i) decision support tools for N management in corn should be revised for addition of cover crops in the Midwest, and (ii) precision planting should be implemented instead of normal planting for greater economic benefit. Future research should evaluate ecosystem services of precision vs. normal planting of winter rye over time. The other study evaluates whether planting method of winter rye (precision vs. conventional) at medium and low seeding rates of winter rye influence cover crop biomass production, N and C concentrations and accumulations, and corn performance (Chapter 2). A trial was conducted in 7 site-yrs in Indiana and Illinois during 2020-2021, 2021-2022, and 2022- 2023 growing seasons. The trial was arranged in a randomized complete block design with four replicates. Cover crops [conventional planting (CR) and precision planting (PR)] were factorially arranged with two seeding rates (18.75 vs. 37.5 kg ha-1) for PR and (25 vs. 50 kg ha-1) for CR. Two extra treatments were included as control which were no-cover crop with zero-N and a 224 kg N ha-1 addition to corn. Cover crop biomass, C, N, their uptake, and C:N ratio were evaluated along with corn plant population, and corn grain yield. Our results indicated that winter rye had similar aboveground biomass, N uptake, and C accumulation regardless of planting method and seeding rate suggesting a precision planting at low seeding rate is most economical for cover crop establishment. Corn plant population was only affected by winter rye in one site-yr (CIL23) in which precision planting did not help with minimizing the negative effect of winter rye on corn population. In this study, lack of N fertilization did not decrease corn population but significantly reduced corn grain yield in all site-yrs. Corn grain yield was similar among cover crop treatments (with exception of no cover crop no N) but in one of the site-yrs, precision planting at 18.75 kg ha-1 resulted in greater corn yield than the no-cover crop with 224 N ha-1. We concluded that growers that plant winter rye prior to corn could use precision planting at a seeding rate of 18.75 kg ha-1 to take up residual soil N with limited interference with corn production at a reduced cost compared to conventional winter rye management.
Author: Andy Clark
Publisher: DIANE Publishing
ISBN: 1437903797
Category : Technology & Engineering
Languages : en
Pages : 248
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Book Description
Cover crops slow erosion, improve soil, smother weeds, enhance nutrient and moisture availability, help control many pests and bring a host of other benefits to your farm. At the same time, they can reduce costs, increase profits and even create new sources of income. You¿ll reap dividends on your cover crop investments for years, since their benefits accumulate over the long term. This book will help you find which ones are right for you. Captures farmer and other research results from the past ten years. The authors verified the info. from the 2nd ed., added new results and updated farmer profiles and research data, and added 2 chap. Includes maps and charts, detailed narratives about individual cover crop species, and chap. about aspects of cover cropping.
Author: Oladapo Adeyemi
Publisher:
ISBN:
Category : Agricultural ecology
Languages : en
Pages : 0
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Book Description
Winter cereal cover crops (WCCCs) could provide extra profit by being harvested as forage or for biofuel purposes, could benefit soil, and the following cash crops, and are considered an effective practice in reducing the nitrate-N (NO3-N) leaching especially in corn (Zea mays L.) and soybean (Glycine max L.) fields. The extend at which WCCCs and their residue management (e.g. harvesting vs. terminating at different times) improve farm profit, influence the following cash crop, especially corn is less studied. Also, literature is scant on the residue management effects on NO3-N leaching potential and its tradeoff with soil nitrous oxide (N2O) emissions especially in Alfisols with claypans. Two trials (chapter 1-2) were conducted to evaluate the time of harvest of winter wheat (Triticum aestivum L.) or winter cereal rye (WCR; Secale cereale L.) to determine the best time of harvest for maximizing profit through improving biomass production at high quality. In chapter 1, a five site-yr trial was conducted in Colorado (CO) and Illinois (IL) to evaluate the effect of harvest date on WCR forage yield, quality, and its economic performance. From March to April, WCR dry matter (DM) yield increased exponentially in CO and linearly in IL. The DM yield at DOY 112-116 in CO was 6.9, 5.0, and 5.2 Mg ha-1 in 2018, 2019, and 2020, respectively compared to 4.7 and 2.7 Mg ha-1 in IL in 2019 and 2020. Delayed harvesting increased acid detergent fiber (ADF) and neutral detergent fiber (NDF) concentrations and decreased crude protein (CP), total digestible nutrients (TDN), and relative feed quality (RFQ). Yield-quality trade-off showed that forage yield increased rapidly but forage quality declined after DOY 105-108. Economic analysis, including cost of nutrient removal and 10% corn yield penalty following WCR production revealed harvesting WCR biomass as forage was economically feasible in four out of five site-yrs at hay price over 132 $ Mg-1. Eliminating corn yield penalty indicated profitability in four site-yrs at hay price of ≥110 $ Mg-1 and removing nutrient removal costs made all site-yrs profitable at hay price of ≥110 $ Mg-1. It was concluded that harvesting WCR biomass can be a profitable and effective strategy for sustainable intensification that can offer environmental stewardship and economic benefit. In chapter 2, a four-year trial was conducted in the 2017-2018, 2018-2029, 2019-2020, and 2020- 2021 growing seasons to evaluate the effect of harvesting time (late-March to mid-May considering the growth stage) on winter wheat biomass yield, quality, and farm profit in single season corn vs. wheat-corn rotation. A delay in harvest of wheat resulted in increased DM biomass and lower CP and RFQ. The RFQ that was suitable for dairy production occurred at GDD of 1849 in which the DM biomass was 6.2 Mg ha-1 leading to $1526.46 ha-1 income. The RFQ for heifer production was 126 at 2013 GDD in which the DM biomass was 6.8 Mg ha-1 leading to $1290.85 ha-1 income. These results suggested that wheat-corn rotation could provide extra income while covering the soil year-round. A series of trials were conducted to evaluate the effects of cover crop (CC) and nitrogen (N) management on (i) corn growth, (ii) grain yield and yield components, (iii) the economic optimum N rate (EONR) for corn and farm profit, (iv) N removal, and balances, (v) N use metrics, (vi) soil NO3-N and ammonium-N (NH4-N), along with (vii) N2O emissions and factors associated with it. In chapter 3, an experiment was conducted as a randomized complete block design with split plot arrangement and four replicates to study winter wheat cover crop management practices on corn growth, production, N requirement, soil N, and farm profit. The main plots were four CC treatments: no CC (control), early terminated wheat CC (four weeks to corn planting; ET), late terminated wheat CC (just prior to corn planting; LT), and harvested wheat CC (residue removal; RR), and the subplots were six N fertilizer application rates (0-280 kg N ha-1 ) for 2018 and 2019 and seven N fertilizer application rates (0-336 kg N ha-1 ) for 2020 and 2021. Wheat cover crop management influenced corn grain yield where fallow was consistently high yielding while RR decreased corn grain yield drastically due to its negative effects on the corn plant population. All cover crop treatments immobilized N as shown by lower corn grain yields at zero-N control compared to the fallow treatment. The EONR generally ranged from 151.4 kg ha-1 to 206.4 kg ha-1 in fallow, 192.8 kg ha-1 to 275.8 kg ha-1 in ET, 225 kg ha-1 to 325 kg ha-1 in LT, and 175.3 kg ha-1 to 257.5 kg ha-1 in RR. At the EONR, corn grain yields ranged from 12.2 Mg ha-1 to 13.7 Mg ha-1 in the fallow treatment, 9.7 Mg ha-1 to 13.0 Mg ha-1 in the ET, 9.51 Mg ha-1 to 13.3 Mg ha-1 in the LT, and 8.2 Mg ha-1 to 10.5 Mg ha-1 in the RR treatment. Adding N beyond EONR resulted in a drastic increase in end of season soil N which could be subject to leaching emphasizing targeting EONR is critical for avoiding high N leaching and that if N is applied at rates beyond EONR, then cover cropping becomes even a more critical practice to avoid N losses. In chapter 4 and 5, we evaluated whether splitting N fertilization along with the two (no-cover crop vs. early termination; ET) (chapter 4) or four above-mentioned cover crops treatments (chapter 5) could improve corn production and farm profit through improved N use efficiency (NUE). Therefore, for chapter 4, a two-yr field trail was implemented at the Agronomy Research Center in Carbondale, IL in 2018 and 2019 to evaluate whether split N application to corn changes N use efficiency (NUE) in no-cover crop vs. following an early terminated (ET) wheat cover crop. A four-replicated randomized completed block design with split plot arrangements were used. Main treatments were a no cover crop (control) vs. ET and subplots were five N timing applications to succeeding corn: (1) 168 kg N ha-1 at planting; (2) 56 kg N ha-1 at planting + 112 kg N ha-1 at sidedress; (3) 112 kg N ha-1 at planting + 56 kg N ha-1 at sidedress (4) 168 kg N ha-1 at sidedress, and (5) zero kg N ha-1 (control). Corn yield was higher in 2018 than 2019 reflecting more timely precipitation in that year. Grain yield declined by 12.6% following the wheat cover crop compared to no cover crop control indicating corn yield penalty when wheat was planted prior to corn. In 2018, a year with timely and sufficient rainfall, there were no differences among N application timing while in 2019, delaying the N addition improved NUE and corn grain yield due to excessive rainfall early in the season reflecting on N losses. Overall, our findings elucidate necessity of revisiting guidelines for current N management practices in Midwestern United States and incorporating cover crop component into MRTN prediction tool. For chapter 5, a four-year trial conducted with a split plot arrangement and four replicates. Main plots were four cover crop management [no cover crop control (fallow); ET, late termination (LT), and residue removal at late termination (RR) and five N fertilizer application timings (all at planting, most at planting + sidedress; half-half; less at planting and more at sidedress; and all sidedress). Our results indicated that RR resulted in corn population and grain yield reduction compared to other treatments. Fallow was consistently high-yielding and 112-56 N management during the first two years for fallow worked the best (10.1 Mg ha-1 ). In 2020 and 2021, both applying all N upfront or sidedressing yielded similar for fallow giving growers options with N timing. For both ET and LT, in all years, delaying the N addition to sidedress timing resulted in high yields (9.1 - 11.7 Mg ha-1 ). Some N addition upfront plus sidedressing the rest (56-168) resulted in the highest yield in ET in 2021 (11.6 Mg ha-1 ). For RR, split application of N (56-112 or 56-168) was consistently most productive in all years (8.7 Mg ha-1 ) suggesting that there is an advantage to sidedressing than upfront N application in cover crop systems. The high productive N management practices generally resulted in higher NUE (24.0 - 38.6 kg grain kg N-1 ) and lower N balance (20.6 - 50.2 kg ha-1 for 2018-2019, and 74 - 106.4 kg ha-1 for 2020-2021) which are critical to achieve not only for farm profit but also minimizing environmental footprints. Except for N0, N balance was positive in all treatments in all years indicating the inefficiency of fertilizer N that was corroborated by low NUE and PFP data. We concluded that to optimize corn production and reducing nutrient loss, split N addition or sidedressing N is most suitable especially in cover cropping systems. For chapter six, a four-times replicated randomized complete block design trial was conducted to evaluate the effects of winter wheat cover crop management practices (ET, LT, and RR) vs. a no-cover crop control (fallow) on corn grain yield, N removal and balances, soil N dynamics, soil volumetric water content (VWC) and temperature dynamics, N2O-N emissions, yield-scaled N2O-N emissions, and factors that drive N2O-N and corn grain yield in 2019-2020 and 2020-2021 growing seasons in a silt loam soil with clay and fragipans. Our results indicated that corn grain yield decreased by both ET and RR as compared to the fallow and LT. Soil temperature was similar among all treatments, but soil VWC was higher in LT and ET than fallow and RR. The LT treatment always had lower soil NO3-N than the other treatments in both years. In 2021, the ET also had less soil nitrate-N than fallow and RR. Averaged over the two years, cumulative soil N2O-N was higher in LT (14.85 kg ha-1 ) and ET (12.85 kg ha-1 ) than RR (11.10 kg ha-1 ) and fallow (7.65 kg ha-1 ) indicating while these treatments are effective in reducing NO3-N leaching, they could increase soil N2O-N emissions. Principal component analysis indicated that higher N2O-N emissions in LT and ET was related to higher VWC suggesting at optimal N management scenarios, other factors than soil N drive N2O-N emissions. In this study, fallow had the least yield-scaled N2O-N emissions followed by RR. The yield-scaled emissions were similar between ET and LT. These results indicate the importance of evaluating N2O-N emissions in cereal cover crops prior to corn for informing best management practice for winter cereal cover crop adoption. Future studies should focus on manipulating cover crop management to capture residual N without creating microclimates with high VWC to avoid increase of N2O-N emissions. While a lot is known about CC effects on the following cash crop, less is known about rotational benefits of late terminated (planting green) wheat and nitrogen (N) management on the following WCR and soybean in rotation. Therefore, for chapter 7, a trial was conducted with a split plot arrangement in a randomized complete block design set up. The main plots were two cover crop treatments (a no cover crop control vs. LT) and the subplots were three N rates [0 (N0), 224 (N224), and 336 (N336) kg N ha-1 ). Each treatment was replicated four times and rye and soybean was planted in all of the plots in rotation. Our results indicated wheat, when terminated late, can uptake 50-80 kg N ha-1 and result in belowground:aboveground ratio of 0.18 in which belowground had much higher C:N than the aboveground biomass. The soil NO3-N was affected by wheat presence and often reduced due to wheat N uptake and also N immobilization negatively affecting the following corn especially at both N0 and N224. Nitrogen fertilization at 336 kg N ha-1 resulted in high end of season N, reduced NUE, increased N balance, and thus, potential for N loss especially in the fallow treatment. The end of season N was lower and NUE was higher in LT which was coincided with reduced rye N uptake in LT suggesting wheat effect lingers longer than just during the corn season and could potentially reduce N loss potential during the fallow period following corn harvest. Soybean yields were higher in LT than the fallow which could be due to (i) higher rye biomass in fallow or (ii) positive legacy effect of wheat in rotation. Improved soybean yields could offset some of the economic loss during the corn phase and push growers in the Midwestern USA to be willing to adopt cover cropping to minimize N loss while protecting soil and stay profitable. Our results from chapter 3-7, indicate a need to change in cover crop management strategy to make it more user friendly with lower costs. In general, in the Midwestern USA, growers are reluctant to plant WCR especially prior to corn due to N immobilization and establishment issues. Precision planting of WCR or --Skipping the corn row‖ (STCR) can minimize some issues associated with WCR ahead of corn while reducing cover crop seed costs. The objective of this study was to compare the effectiveness of --STCR‖ vs. normal planting of WCR at full seeding rate (NP) on WCR biomass, nutrient uptake, and composition in three site-yrs (ARC2019, ARC2020, BRC2020). Our results indicated no differences in cover crop dry matter (DM) biomass production between the STCR (2.40 Mg ha-1 ) and NP (2.41 Mg ha-1 ) supported by similar normalized difference vegetative index (NDVI) and plant height for both treatments. Phosphorus, potassium (K), calcium (Ca), and magnesium (Mg) accumulation in aboveground biomass was only influenced by site-yr and both STCR and NP removed similar amount of P, K, Ca, and Mg indicating STCR could be as effective as NP in accumulating nutrients. Aboveground carbon (C) content (1086.26 kg h-1 average over the two treatments) was similar between the two treatments and only influenced by site-yr differences. Lignin, lignin:N, and C:N ratios were higher in STCR than NP in one out of three site-years (ARC2019) indicating greater chance of N immobilization when WCR was planted later than usual. Implementing STCR saved 8.4 $ ha-1 for growers and could incentivize growers to adopt this practice. Future research should evaluate corn response to STCR compared with NP and assess if soil quality declines by STCR practice over time.
Author: Kirsten Cynthia Workman
Publisher:
ISBN:
Category : Corn
Languages : en
Pages : 180
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Cover crops play an important role in decreasing erosion and nutrient runoff associated with corn silage production in northern New England. Winter rye (Secale cereal L.) is the primary cover crop species used in this region. While winter rye (rye) monocultures are easily established, they can be challenging to manage in the spring, expensive to establish at recommended seeding rates, and can interfere with the planting of subsequent corn crops. We hypothesized that adding forage radish (Raphunus sativus L.) to a rye cover crop could augment fall performance and enhance the ecosystem services provided by the cover crop and allow for a lower rye seeding rate. A field study was conducted at five locations over a two-year period (five site-years, SY) on commercial dairy farms in Addison County, VT. Treatments included three rye seeding rates, two of which were repeated with and without radish. These were planted with a grain drill and broadcast seeder, for a total of ten cover crop treatments and a fallow (no cover crop) control. Overall, planting method had the greatest impact on cover crop performance. Drilled treatments had significantly greater soil cover in the fall compared to broadcast treatments, ranging from 53.3% to 98.8% cover. The broadcast treatments did not provide better fall soil cover than even the fallow control, except in one SY, and ranged from 25.8% to 68.8% cover. Spring soil cover varied by site year, with little difference between treatments. Similar results were observed in aboveground biomass. Drilled treatments outperformed broadcast in the fall, with drilled treatments measuring 57-776 kg ha-1 and broadcast 22-404 kg ha-1. There was very little difference between treatments in spring biomass, with overall results between 614 and 2496 kg ha-1. The addition of forage radish (3.5 kg ha-1 seeding rate) to the lowest drilled rye seeding rate (67 kg ha-1) showed some evidence of increased fall aboveground biomass and decreased spring biomass compared to rye monoculture, a combination desirable for farmers. Nitrogen and phosphorus concentration in cover crop leaf tissue saw some differences in individual site years, but was not strongly associated with treatment. Total N and P uptake by the cover crop was strongly correlated with biomass production. Soil temperature and soil NO3- were impacted by the presence of cover crop, but there were not significant differences between cover crop treatments. Available soil test phosphorus (modified Morgan), soil moisture and soil NH4+ were not impacted by any cover crop treatment compared to the control. While adding forage radish did not significantly impact the performance of rye cover crops, it did show some promise for optimizing biomass distribution (higher in fall, lower in spring) and warrants further study to identify the seeding rates and planting dates that result in this outcome. This study provides compelling evidence to recommend the use of a grain drill for planting winter cover crops in order to maximize performance and minimize seeding rates.
Author: Kelsey Vaughn
Publisher:
ISBN:
Category : Adaptive harvest management
Languages : en
Pages : 0
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Sustainability of dairy production depends on their production of feed and finding ways to increase profitability through dairy production or even carbon (C) crediting and adding C inputs into the soil to sequester C. To increase farm profitability, dairy producers in Illinois, has intensified their feed production through integrating winter cereals such as winter cereal rye (Secale cereale) (WCR) into single season corn for silage (double cropping). Intensified cropping system allows for increased feed production, covering the soil year-round, and adding C inputs while minimizing nutrient loss mainly through runoff or leaching. Two management practices that improve the sustainability of corn silage - WCR double crop are harvesting date and nitrogen (N) management during the WCR phase of the production. This thesis has two main chapters. Chapter 1 evaluates the effect of harvesting date (five weekly harvest from late-March to early-May) with and without optimum N addition (0 vs. 47 kg N ha-1). Our objective was to evaluate harvesting date and spring N fertilization effect on WCR morphology, forage yield, nutrient removal, and quality. A quadratic model best explained an increase in WCR biomass in response to GDD (growing degree days) accumulation (R2 = 0.81). Increase in GDD linearly decreased WCR relative forage quality (RFQ). Benchmarking RFQ at 150 for dairy milk production indicates that WCR should be harvested at a GDD of 543 at which WCR plant height was 31.8 cm and dry matter (DM) biomass was 0.77 Mg ha-1. Benchmarking RFQ at 125 for heifer production indicated that harvest should occur at a GDD of 668 at which the WCR was 71 cm tall and its DM yield was 2.25 Mg ha-1. Nitrogen balances were negative at the no-N control treatment indicating a need for some N to maximize WCR yield. We found that a rate between 21 and 42 kg N ha-1 maximizes yields reflecting on slightly positive balances. Our results suggest that harvesting date can be predicted by GDD and should be adjusted for RFQ. We conclude that smaller than 42 kg N ha-1 N fertilizer is required for WCR production in soils with manure history and high soil organic matter (>30 g kg-1). Chapter 2 hypothesized that N fertilization of WCR as cover crop can increase nutrient recycling and C sequestration which offers C trading benefits to growers. We evaluated the effects of N fertilizer application in fall (0 vs. 56 kg N ha-1), and N fertilizer rates in spring (0, 23, 47, and 71 kg ha-1) on WCR dry matter (DM) biomass and cover crop quality. Results indicated that fall N fertilization had no effect on WCR biomass or quality reflecting on loss of applied N in the fall. Spring N application did not affect WCR biomass yield but increased N, P, and K concentrations, their uptake, C concentration, and decreased C:N and lignin:N ratios. We concluded that only spring N fertilization improves WCR cover crop benefits. Overall, we suggest that for high-quality forage, (RFQ at 150) WCR should be harvested at a GDD of 543 at which WCR plant height was 31.8 cm and dry matter (DM) biomass was 0.77 Mg ha-1. For RFQ of 125 (for heifer production), harvest should occur at a GDD of 668 at which the WCR was 71 cm tall and its DM yield was 2.25 Mg ha-1. Neither in fall nor in spring, N fertilization increase WCR C accumulation. Spring N fertilization reduces WCR C:N and lignin:N which are desirable for crop production.
Author: Carinthia Alden Grayson
Publisher:
ISBN:
Category : Conservation tillage
Languages : en
Pages : 232
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Author: Tom Misselbrook
Publisher: Frontiers Media SA
ISBN: 288963227X
Category :
Languages : en
Pages : 249
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This eBook presents highlight papers from the 17th International conference of the Recycling of Agricultural, Municipal and Industrial Residues to Agriculture Network (RAMIRAN) that was held in Wexford, Ireland in September 2017. The book contains a broad range of papers around this multidisciplinary theme covering topics including regional and national organic resource use planning, impact of livestock diet on manure composition, fate and utilisation of excreta from grazing livestock, anaerobic digestion, overcoming barriers to resource reuse, hygienic aspects of residue recycling and impacts on soil health. The overarching theme being addressed is the sustainable recycling of organic residues to agriculture, to promote effective nutrient use and minimise environmental impact.
Author: Madhabi Tiwari
Publisher:
ISBN:
Category : Corn
Languages : en
Pages : 0
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Food production security and resiliency require combination of agricultural management practices that are environmentally friendly and economically viable. Cover crops and tillage are two typical management practices that influence corn (Zea mays L.) and soybean (Glycine max L.) production in Illinois and the Midwest, USA. Finding practices that could potentially reduce nitrous oxide (N2O) emissions and sequester carbon (C) in the soil can improve agricultural resiliency to climate change. Generally, shifting from reduced tillage (RT) to no-till (NT) improves soil structure and decreases C emissions or sequesters soil C but might increase N2O emissions. Including a legume cover crop such as hairy vetch (Vicia villosa L.) before corn is preferred to winter cereal cover crops (WCCCs) to avoid yield penalty in corn and ensure high grain production. Winter cereal cover crops such as winter cereal rye (Secale cereale) (WCR) could potentially decrease soil N2O emissions during fallow period by capturing residual N and reducing soil moisture. These conditions could change in soils with legacy tillage (RT vs. NT) effects due to changes in soil physical, chemical, and biological over time. We utilized a medium-term (six-year-old) trial to test several hypotheses. We hypothesized that RT increases the soil temperature, accelerates soil organic matter mineralization, and especially in combination with hairy vetch could increase soil N in the soil leading to increased corn grain yield and N2O emission (Chapter 1). We also hypothesized that WCR takes up residual N after harvesting corn, decrease soil N, use soil moisture, and therefore, could decrease soil N2O emission (Chapter 2). For study 1 (Chapter 1), our objective was to evaluate the influence of cover crop (hairy vetch) vs. a no CC control and tillage systems (RT vs. NT) on (i) corn yield, N uptake, removal, and N balance; (ii) N2O emissions during corn season; (iii) yield scaled N2O emissions on a long-term (eight years) tillage × cover cropping system during the corn growing season in 2019 and 2021. We also analyzed factors that influence N2O emissions via principal component analysis in corn season. In corn growing seasons, we found that corn grain yield was higher in RT than NT reflecting on more N in the soil in RT than NT. Hairy vetch increased corn grain yield, soil N, and N2O-N indicating increased corn grain yield by hairy vetch N contribution let to higher N loss. Yield-scaled N2O-N emissions in NT-2019 (3696.4 g N2O-N Mg-1) were twofold higher than RT-2019 (1872.7 g N2O-N Mg-1) and almost fourfold higher than NT-2021 and RT-2021 indicating in a wet year like 2019, yield-scaled N2O-N emissions were higher in NT than RT. Principal component analysis indicated N2O-N fluxes were less driven by soil N and more by environmental conditions and N balances reflecting on N application at planting in this trial. The objectives for chapter 2 were to evaluate the legacy effect of tillage (RT vs. NT) and cover crops (WCR vs. a no cover crop control) on soil nitrate-N (NO3-N), volumetric water content (VWC), temperature, and N2O emission trends during a fallow period after corn in a six-yr trial. In spring 2020 we also estimated WCR biomass and N uptake as affected by tillage practices and compared WCR biomass to weeds in the no cover crop treatment. In rye growing season, winter cereal rye biomass was 55% higher than weeds in the fallow treatment. A linear positive relation between WCR biomass and N uptake (R2= 0.93) and C accumulation (R2 = 0.99) indicates WCR captures more N and adds more C inputs than weeds. Winter cereal rye biomass was also higher in RT than NT reflecting on higher soil temperature and N availability in RT than NT. Soil VWC was lower in WCR plots and there was a negative linear relation between days of the year (DOY) and VWC (R2 = 0.6). Despite all these differences, soil N2O-N values were mainly less than 5 g N2O-N ha-1d-1 in all sampling dates regardless of tillage or cover crop treatment. We conclude that in poorly drained Alfisols with claypan and fragipans, NT is not an effective strategy to decrease N2O-N fluxes. Hairy vetch benefits corn grain yield and supplement N but that increases N loss through N2O-N emissions. We concluded that we should focus on decreasing N2O emissions early in corn season since majority of N is lost during that time sometimes 300 times higher than those reported during the WCR phase. Some changes in management practices that could reduce N2O losses are shifting from upfront N application to sidedress N management, terminating hairy vetch at or even after corn planting, and combine these efforts with enhanced efficiency fertilizers that control nitrification and denitrification.
Author: Gary Wayne Feyereisen
Publisher:
ISBN:
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Languages : en
Pages : 446
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