Summer Cover Crop System Management: New options for Upper Midwest vegetable producers

Progress report for LNC19-423

Project Type: Research and Education
Funds awarded in 2019: $199,803.00
Projected End Date: 10/31/2022
Grant Recipient: University of Minnesota
Region: North Central
State: Minnesota
Project Coordinator:
Dr. Julie Grossman
University of Minnesota
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Project Information

Summary:

This project entitled Summer Cover Crop System Management: New options for upper Midwest vegetable systems, improves grower knowledge of summer cover crop use, including species selection, planting date, and impact of growing season length. Growers are increasingly interested in adding cover crops to rotations to improve soil health, break disease cycles, and provide ecosystem services. However, identifying appropriate timing is challenging. Growers must balance cash crop goals and timing with limited availability of labor, land, and equipment. Summer cover crops are an often overlooked and minimally researched option for growers in the Upper Midwest.

This farmer-driven project will engage minority farmers to provide data on summer cover crop management systems in collaboration with UMN researchers. Objectives include to 1) Identify summer cover crop management best suited for north central growers, 2) Determine nitrogen derived from legume cover crops, including management to maximize fertility provision, and 3) Develop cover crop legume resources for immigrant and minority farmers. Growers will evaluate three cover crop species and two planting dates. Plant biomass, weed biomass, and soil will be tested at key crop management timepoints to quantify timing of plant available nitrogen, potential for nitrogen loss via leaching, cover crop productivity, and weed suppression capacity. Farmer evaluation of cover crops will provide additional qualitative data on ease of management and effectiveness of cover cropping systems. This knowledge aligns directly with SARE tenets by allowing farmers to more profitably and confidently include cover crops in seasonal rotations, improving nitrogen management for cash crops following summer cover crops, and reducing nitrogen losses that can lead to environmental degradation. Reductions in off-farm nitrogen purchase may also lead to improvements in farm economics.

Results will be shared through print fact sheets, web resources, relevant newsletters and at grower meetings and 2 grower-led field days.

Project Objectives:

Objective 1: Identify summer cover crop management best suited for north central growers. Learning outcome: 100 growers learn improved summer cover management. Action Outcome: 10 growers increase cover crop use.

Objective 2: Quantify nitrogen derived from legume covers, including identification of management strategies to maximize fertility provision.  Learning outcome: 5 educators/researchers learn to maximize nitrogen provided by cover crops. Action outcome: Educators develop and distribute recommendations to 200 farmers.

Objective 3: Develop resources for immigrant and minority farmers. Learning outcome: 50 growers learn management to maximize nitrogen. Action outcome: Growers reduce off-farm nitrogen inputs, expense, and negative environmental impacts.

Introduction:

Immigrant specialty crop farmers are a growing and often overlooked segment of our North Central region’s agricultural economy, and are particularly interested in improving soil management (McCamant 2014). The system-wide outcome of this project is to increase capacity of underserved farmers to engage in sustainable soil fertility-building practices by maximizing productivity of summer cover crops in vegetable production systems.

Nitrogen pollution as a result of fertilizer leaching from agricultural production is a major concern for ecological sustainability in the Upper Midwest and around the world. Synthetic fertilizers produced by the Haber-Bosch process have significantly contributed to the global increase of reactive nitrogen (Nr) in the past century (Galloway et al. 2006). While this process has been instrumental for increased food production, elevated Nr levels can have numerous detrimental environmental effects on air and water quality when Nr leaves agricultural soils and enters waterways. In vegetable production systems, which have high nutrient requirements and are often irrigated, there is high-risk of nitrate leaching from farm fields (Agostini et al. 2010), and thus fertilizer applications can have particularly detrimental effects. Furthermore, vegetable farmers face pressure to meet financial sustainability by maximizing production, often achieved by growing multiple crops in temporal succession, resulting in reduced soil quality.

Cover crops, which are crops grown in agricultural rotations for a primary purpose other than food, forage, or fiber, can mitigate Nr pollution by using inorganic soil nitrogen that would otherwise by subject to leaching from bare soil, and then providing Nr back to the soil during decomposition. Legume cover crops, because of their ability to form symbiotic relationships with soil rhizobia that fix atmospheric nitrogen, can also contribute Nr to the soil, thereby increasing the fertility of agroecosystems without fertilizer. The input of nitrogen from legumes may be less likely to lead to pollution because it enters the system as part of plant biomass, and must be processed by microbes before it is susceptible to leaching. Additionally, because the N-fixation from the legume-rhizobia symbiosis is responsive to endogenous soil nitrogen levels, legume cover crops may be used as a self-regulating fertility source (Blesh 2018). This benefit may be enhanced by combining legume and non-legume species. Grass-legume mixtures may simultaneously provide nitrogen fixation and retention benefits, resulting in reduced nitrate leaching, which effectively tightens the nutrient cycling loop in soil (Blesh 2018; Finney, White, and Kaye 2016). Apart from their effects on fertilization, legume cover crops also serve other ecosystem functions. Inclusion of legume species has been shown to affect microbial community structure and function by increasing overall microbial community biomass and the proportion of Gram-negative bacteria, and fungal populations (Finney, Buyer, and Kaye 2017). Importantly, legume cover crops are often grown until flowering, which provides resources for beneficial insects (Clark 2013). 

Most cover crop use is limited to cool-season over-wintering crops, which do not interfere with the summer annual cash crops that predominate in the Upper Midwest. However, vegetable production systems are well suited to take advantage of additional opportunities for cover cropping throughout the growing season, because farmers in these systems often grow both cool and warm season crops, which leads to multiple fallow periods during the growing season. A major fallow period in vegetable rotations is summer, when spring and fall vegetable crops are frequently separated by a short fallow that leaves soil bare and unused for 30-50 days in the height of summer. Unlike winter cover crops, summer cover crops do not need to be cold hardy, nor have a dormancy period. They are valued for quick, vigorous growth that may outcompete weeds. Previous research has shown that there are multiple legume and non-legume cover crops that are well suited for summer growth (Creamer and Baldwin, 2000; Grossman lab, 2018, unpublished data).

Almost no information exists to guide farmers in effectively using this summer cover crop niche. This project has objectives to both fill the research needs related to warm season summer cover crops, and develop materials to support farmer use of such crops.

Cooperators

Click linked name(s) to expand

Research

Hypothesis:

This project had two driving hypotheses:

  1. Rotations including warm season cover crops and cool season vegetables (broccoli, greens) can be successful in the Upper Midwest, in terms of biomass production and successful production of a cash crop.
  2. Warm season cover crops have the capacity to positively affect soil N cycling via supply of nutrient retention and nutrient provision ecosystem services.
Materials and methods:

Objective 1: Identify summer cover crop management practices, (including species selection, planting date, and crop duration) best suited for North Central vegetable systems.  NOTE: original design included planting density factor, which was later eliminated based on farmer preference for increased species inclusion, and limitations on field size and staffing due to covid-19.

This objective will target reductions in nitrogen application by optimizing the success of summer legume cover crops in the upper Midwest, particularly on land farmed by underserved vegetable producers. Replicated field trials will be planted collaboratively with Minnesota Food Association’s (MFA’s) Big River Farm using a randomized complete block design with 4 replications of each species and planting density combination, plus controls. The two planting times will each include these combinations. Additionally, unreplicated demonstration plots will be planted at two additional farms. The Red Lake Nation’s 4-Directions Development Gitigaanike Foods Initiative, White Earth Natural Resources Department (WELRP), and Cala Farm have all shown interest in hosting these plots (see letters of support). Cover crop species will include sunn hemp (Crotalaria juncea L.), a chickling vetch (Lathyrus sativus) and sorghum-sudangrass (Sorghum bicolor L. Moench) mix, and cowpea (Vigna unguiculata). These novel warm-season legume species were selected in previous researcher-farmer collaborative work for their likelihood of success in our northern climate. A weedy (fallow) plot as well as a bare-ground plot will serve as controls against which to compare legume contribution.

Each cover crop species will be planted at a high and standard seeding rate and grown for 50 days with two planting dates, before or after a vegetable cash crop. Planting costs of research plots will be recorded, as seed costs for uncommon species can be high. The cash crop for both planting date systems will be a vegetable cultivar with a 50 day to maturity (DTM) period of our partner’s choosing. In the first system the 50 DTM cash crop will precede cover crop planting. In system two, the 50 DTM cash crop will follow cover cropping. Both systems will be planted on June 1 and terminated in mid-September. Vegetable cash crop fertilizer rates will be adjusted to account for biomass N delivered by the cover crop.

We will collect data including both cover crop and weed biomass, to quantify capacity for weed suppression. Legume tissue N from each plot will be quantified using an Elementar vario PYRO cube EA-IRMS CNS analyzer (Elementar, Langenselbold, Germany) for carbon and nitrogen content. In addition to quantitative data, qualitative farmer feedback will be solicited related to impressions of cover crop viability, hardiness, weed competition, and ease of management.  We will form an advisory group of farmer representatives from all on-farm trials (compensated for time and effort).

Objective 2: Determine the fate of nitrogen (N) derived from cover crop legumes, including when nitrogen produced by cover crops is most available to crops or prone to loss, and the effect of species selection, planting density, and planting date on cover crop fertility provision.

This objective will quantify nitrogen availability at several time points following cover crop termination to determine optimal N availability for cash crops relative to cover crop timing and species, and opportunities to reduce external N application and N leaching. Soil samples from the field plots described in objective 1 will be collected at key management time points following cover crop termination to evaluate microbial activity, and soil carbon (C) and N pools, using permanganate oxidizable carbon labile C, available soil N, and microbial biomass assays.

Nitrogen availability in the soil profile will be monitored and quantified following cover crop termination using the buried anion resin bag method (Finney, et al. 2016). Bags will be inserted into soils at two depths, with at least one of the bags placed below the cash crop rooting zone to capture N prone to leaching losses. Bags will be removed at three time points corresponding to key management activities and in synchrony with soil sample collection. Anion resin bags will be extracted in the laboratory to measure nitrate leaching post cover crop termination.

Data from this work will provide farmers the knowledge they need to improve cover crop planting and termination timing, as well as species selection, to maximize legume cover crop derived nitrogen availability to cash crops.

Research results and discussion:

Project Year 1 (2020):

Objective 1: Identify summer cover crop management practices, (including species selection, planting date, and crop duration) best suited for North Central vegetable systems, and

Objective 2: Determine the fate of nitrogen (N) derived from cover crop legumes, including when nitrogen produced by cover crops is most available to crops or prone to loss, and the effect of species selection, planting density, and planting date on cover crop fertility provision.

Despite the impacts of covid-19 and restrictions placed upon us the University of Minnesota in terms of travel and research functions, we successfully carried out replicated experiments at both proposed sites, including the University of Minnesota St. Paul research station, and Big River Farms.  We hired a graduate student (Madison Moses), who received fellowship support in their first and second years of graduate school, and will utilize grant support in subsequent years.  Two of our less common identified species, chickling vetch and Sunn hemp, were unavailable due to covid procurement and shipping delays.  Based on combined feedback from our collaborators, and covid restrictions on lab staffing that forced us to put limits on experiment size, the proposed density factor (two crop planting densities) was eliminated and instead additional cover crop species recommended by farmers were used as treatments, resulting in 6 cover crop species treatments and two controls (below). 

Species Functional group
Crimson clover Legume
Buckwheat Non-legume; high flowering
Phacalia Non-legume; high flowering
Sunflower Non-legume; high flowering
Oat/Pea Non legume/legume mix
Sudex/Cowpea Non legume/legume mix
Weedy Fallow Control
Bare Fallow Control

All cover crops were planted in two rotational systems:

  1. Early Cover Crops: Cover crops planted in early May into mid-summer, followed by broccoli in fall
  2. Late Cover Crops: Lettuce planted in May, followed by cover crops in  late-summer into early fall

Rotatio
Rotations included cover crops paired with cool season greens of broccoli or lettuce
sunflower in bloom
In both rotations, sunflower only minimally bloomed, given cash crop and seasonal constraints
Summer cover crops, with buckwheat in bloom and sunflower in foreground
summer cover crops in bloom
A range of summer cover crop species, with blooming phacelia in foreground and sudex in background.
Students in field
Our student team always has fun on sampling days!

 

Data collected from both rotations to meet objective 1 included cover crop and weed biomass, and legume tissue total N at termination. Early-planted cover crops generally excluded weeds well, and mean cover crop biomass production ranged from 3562 lb/A (crimson clover) to 7465 lb/A (cowpea/sorghum-Sudan mix) at St. Paul, and 2717 lb/A (phacelia) to 4824 lb/A (pea/oat mix) at Marine on St. Croix. Late-planted cover crop biomass production was generally lower, and weed competition more prominent, particularly in the sunflower and crimson clover treatments. To meet objectives 1-2 we quantified nitrogen availability monthly during cover crop growth and during cash crop growth following cover incorporation. This allowed us to monitor both uptake and release of N from cover crop tissues, in order to identify cover crop timing and species selections that can optimize N availability for cash crops and provide opportunities to reduce external N application and N leaching. While data processing is still underway, preliminary analysis indicates that all cover crop treatments, as well as weedy fallow, reduced available soil nitrate during their growth period, suggesting a N retention ecosystem service provided by cover crops as they took up soil N otherwise prone to loss. Potentially mineralizable N (PMN) was measured once during cover crop growth and once during cash crop growth as an indicator of N that is available for microbial breakdown, and thus mineral N release for future plant uptake. For all assays, workflow was significantly reduced by covid-19 restrictions place upon research teams, only allowing us to be minimally staffed in laboratories, and limiting hiring of research staff. Thus, although field operations proceeded normally at two sites, sample processing and analysis for Year 1 was slowed. All plant and soil samples have now been collected, dried, ground, and in some cases analyzed. The pandemic also made it difficult to plant demonstration sites as planned, and thus only White Earth Nation received seeds, via mail, for planting in Y1.

To measure soil N loss in both systems, mesh resin bags were buried beneath the root zone and removed for extraction at the end of the season. Nitrogen is currently being extracted from bags from 2020. 

resin bags
Resin-filled mesh bags were hand-constructed and buried beneath root zone. Nitrogen collected on the resins will later be quantified to determine the effect of cover crop systems on N loss.

An undergraduate researcher, Sarah Duber, was hired to carry out project sample preparation (grinding, weighing, ect). She was recently awarded an Undergraduate Research Opportunity Program grant to conduct research to investigate the impact of cover crop treatments on soil moisture and temperature, and the relationship to soil N pools, using Decagon probes supported by this project.

Cover crop biomass production in late planted cover crops in 2020 showed buckwheat, the cowpea/sudex mix, and phacelia in St Paul  to be most competitive with weeds. Data not yet available for early planted cover crops
Soil N following cover crops
Sampling conducted at the end of cover crop growth phase supported that cover crops provided a valuable ecosystem service of soil N retention

 

 

Participation Summary
5 Farmers participating in research

Education

Educational approach:

None to report

Project Activities

Bee ID and Monitoring Workshop with Xerces Foundation
Presentation at the Great Lakes Indigenous Farming Conference
The virtues of cover crops to support soil and crop health - Great Lakes Fruit and Vegetable Expo
Soil health - Great Lakes Fruit and Vegetable Expo
Cover Crops Support Soil & Crop Health - Minnesota Fruit and Vegetable Growers Association,
Cover crops in vegetable production systems - Midwest Cover Crop Council Conference
Introduction to organic vegetable production: A training for NRCS service providers
Virtual Field Day White Earth Nation

Educational & Outreach Activities

5 Webinars / talks / presentations

Participation Summary:

200 Farmers
75 Ag professionals participated
Education/outreach description:

Objective 3: Develop new cover crop legume resources, and make existing resources more available, for immigrant and minority farmers in the North Central region.

Our third objective was greatly hampered by Covid-19, due to the need for social distancing, and all most field activities were postponed.  Events included:

1) We were fortunate to have presented at the February, 2020 MOSES Organic Farming Conference, and the March, 2020 Great Lakes Indigenous Farming Conference immediately prior to travel restrictions were put in place:

Candelaria, N., Grossman, J. , Rogers, M., and Fernandez, A. New summer cover crop options for organic vegetable farmers: Exploring ecosystem service trade-offs. MOSES Organic Farming Conference, LaCrosse, WI, January, 2020. (Graduate student won 1st Place for her poster, 150 farmers reached).

Grossman J. and Fernandez, A. Cover Crops and Soil Health. Great Lakes Indigenous Farming Conference, March 7, 2020. Callaway, MN. (25 farmer and agriculture professional attendees)

2)  On July 1, 2020, Xerces Foundation conducted a small ‘Bee ID and Monitoring’ workshop for project personnel and key staff from BRF, the Grossman lab, and White Earth. Five individuals attended, due to restrictions placed on Xerces for number of in-person attendees. We considered a virtual event, but insect ID would have been difficult in a virtual format. 

3) A collaborative educational video was produced by Extension Educator Natalie Hoidal using our SARE project field site and project personnel, meeting some of our outreach event goals. The video clearly explains the process and calculations that a farmer can use to calculate estimated N credits provided by a cover crop, including footage of cover crop biomass harvest.

4) Aesthetically-pleasing signage (with SARE logo) was placed on all treatment plots to learn about the cover crop species, benefits of summer cover crops, and project partners.  Big River Farms is an incubator farm serving emerging farmers. Signage allows for widespread dissemination of basic information on cover crop benefits to farmers (Estimated farmers reached: 50)

5) One upshot of the Pandemic is that it was easier than ever to share results virtually. Several additional invited presentations were given in a virtual format. These included:

Grossman, J. The virtues of cover crops to support soil and crop health. Great Lakes Fruit and Vegetable Expo, December 9, 2020. (Virtual, invited, 50 estimated participants)

Grossman, J. Soil Health. Great Lakes Fruit and Vegetable Expo, December 9, 2020. (Virtual, invited, 30 estimated participants)

Moses, M. Cover Crops – Support Soil & Crop Health.  Minnesota Fruit and Vegetable Growers Association, Jan 15, 2021. (Virtual, invited)

Grossman, J., Allaway, R. and Baikie, K.  Cover crops in vegetable production systems. Midwest Cover Crop Council Conference. Guelph, Ontario, Canada, Feb 25, 2021.  (virtual, invited, 94 participants + 21 views of recording after live presentation = 115 total)

Grossman, J. Introduction to organic vegetable production: A training for NRCS service providers (Led virtual 2h workshop, invited, 75 participants)

Looking forward: A virtual field day will be held in late May, 2021 in collaboration with White Earth Nation (topic: Cover Crops in White Earth).  In addition, we have planned an in-person field day to see actively growing and mature cover crops at Big River Farms, July, 2021. We are discussing plans for the Emerging Farmer Conference winter workshop to take place in 2022, as well as the fact sheet including cover crop research results.

 

Any opinions, findings, conclusions, or recommendations expressed in this publication are those of the author(s) and do not necessarily reflect the view of the U.S. Department of Agriculture or SARE.