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The Interdependence of Soil Function and Biological Diversity: Lessons from an 8-year Cover Crop Study in Semi-Arid Montana, USA Zabinski, C. 1 , Miller, P. 1 , Jones, C. 1 , Tallman, S. 1,2 , Housman, M. 1,3 , D’Agati, K. 1 1 Montana State University, Department of Land Resources and Environmental Sciences, Bozeman, Montana, USA; 2 USDA Natural Resource Conservation Service, USA, 3 J.R. Simplot Co. 1) Can CCMs change soil biological parameters compared to summer fallow? 2) Does functional group composition of the cover crop affect soil biological parameters? Selected Functional Groups for Cover Crop Mixture Fibrous roots extensive root network Oat Avena sativa Canaryseed Phalaris canariensis Nitrogen fixers add N to soil Lentil Lens culinaris Spring Pea Pisum sativum Brassicas rapid ground cover Tap roots reduce compaction Turnip Brassica rapa Safflower Carthamus tinctorius Winter Canola Brassica napus Daikon radish Raphanus sativus METHODS Our study took place in Montana, with two sites seeded to cover crops in 2012, and two additional sites seeded to cover crops in 2013. After 4 years, we continued with just two sites for an additional 4 years. Treatments were established in 10x12 m plots, randomly assigned within 4 blocks. Year Amsterdam, Conrad Bozeman, Dutton 2012 cover crop -- 2013 wheat cover crop 2014 cover crop wheat 2015 wheat cover crop 2016 cover crop wheat 2017 wheat -- 2018 cover crop -- 2019 wheat -- Response variables measured Soil enzyme activity (3,9) Potentially mineralizable N (PMN) (6) Microbial biomass (4) Mycorrhizal colonization (7) Soil compaction Soil water and N Cover crop biomass Wheat yield and grain protein Treatments 1. Fallow (SF) 2. Pea (PEA) 3. Full mix (FULL) 4. Nitrogen fixers 5. Fibrous roots 6. Tap roots 7. Brassicas 8. Full mix minus N- fixers 9. Full mix minus fibrous roots 10. Full mix minus tap roots 11. Full mix minus brassicas Potentially Mineralizable Nitrogen (PMN) We predicted that cover crops should increase PMN relative to fallow. This was true after 2 CCM cycles in 4 of the 8 site- years. (Just 2 sites shown on right) After 4 rotations, across two sites, the pattern of higher rates of PMN after cover crops than fallow was consistent at one site only. Soil Enzymes After 2 CCM cycles, soil response to cover crops relative to fallow appeared cumulative, with greater differences after 2 rotations than 1 rotation. After 4 rotations, the increase in soil enzyme activity persisted at one of the two sites. Additionally, the amount of biomass produced by the cover crop mixture was more important than plant functional group identity. RESULTS DISCUSSION We did not measure differences in soil biological parameters between the single functional group treatments, suggesting that the diversity of cover crops is not as important as we expected. PMN and other responses were correlated to cover crop biomass and not species diversity. Additionally, in semi-arid systems, with a short period of cover crop growth between alternate year crops, soil biological traits increased in response to cover crops relative to fallow only during years with average or above average rainfall (5). These findings are complementary to studies that document shifts in biological communities with cropping intensification (8). Acknowledgements Funding was provided by Western SARE (Sustainable Agriculture, Research & Education), Montana Fertilizer Advisory Committee, USDA NIFA MONB00397. Thanks to producer partners Eric and Chad Doheny, Carl Vandermolen, and Herb Oehlke. Fig. 1: Crop field INTRODUCTION Measuring soil biological diversity is a significant task, but even more challenging is interpreting what that diversity means in terms of ecological function. We provide an example in a study on the effects of cover crop mixtures (CCM) on soil properties in a semi-arid system. Dryland wheat farming in the northern Great Plains (USA) occurs in climates with just enough precipitation to grow wheat profitably. Summer fallow has been widely practiced for decades as a way to store part of one year’s precipitation for the next year’s crop. While effective as a way to increase crop yield, the fallow year impacts soil quality as a result of reduced organic matter inputs and increased erodibility (1,2). We measured the effects of cover crop mixtures relative to fallow or a single-species pea cover crop on soil biological, chemical and physical parameters, along with yield and protein content of the subsequent year’s wheat crop. Our questions: Table 1: Types of crops by year Fig. 3: Geometric mean of all enzymes Fig. 2: Selected functional groups for cover crop mixture Table 2: Treatments and response variables measured Fig. 4: Potentially mineralizable nitrogen

The Interdependence of Soil Function and Biological Diversity: … · 2021. 4. 12. · Chad Doheny, Carl Vandermolen, and Herb Oehlke. Fig. 1: Crop field. INTRODUCTION. Measuringsoil

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Page 1: The Interdependence of Soil Function and Biological Diversity: … · 2021. 4. 12. · Chad Doheny, Carl Vandermolen, and Herb Oehlke. Fig. 1: Crop field. INTRODUCTION. Measuringsoil

The Interdependence of Soil Function and Biological Diversity: Lessons from an 8-year Cover Crop Study in

Semi-Arid Montana, USA

Zabinski, C.1, Miller, P.1, Jones, C.1, Tallman, S.1,2, Housman, M.1,3, D’Agati, K.1

1Montana State University, Department of Land Resources and Environmental Sciences, Bozeman,Montana, USA; 2USDA Natural Resource Conservation Service, USA, 3J.R. Simplot Co.

1) Can CCMs change soil biological parameterscompared to summer fallow?

2) Does functional group composition of thecover crop affect soil biological parameters?

Selected Functional Groups for Cover Crop Mixture

Fibrous roots extensive root network

Oat Avena sativa

CanaryseedPhalaris canariensis

Nitrogen fixers add N to soil

LentilLens culinaris

Spring PeaPisum sativum

Brassicas rapid ground cover Tap roots reduce compaction

TurnipBrassica rapa

SafflowerCarthamus tinctorius

Winter CanolaBrassica napus

Daikon radish Raphanus sativus

METHODSOur study took place in Montana, with twosites seeded to cover crops in 2012, and twoadditional sites seeded to cover crops in 2013.After 4 years, we continued with just two sitesfor an additional 4 years. Treatments wereestablished in 10x12 m plots, randomlyassigned within 4 blocks.

Year Amsterdam, Conrad

Bozeman, Dutton

2012 cover crop --

2013 wheat cover crop

2014 cover crop wheat

2015 wheat cover crop

2016 cover crop wheat

2017 wheat --

2018 cover crop --

2019 wheat --

Response variables measured

Soil enzyme activity (3,9)Potentially mineralizable

N (PMN) (6)Microbial biomass (4)Mycorrhizal colonization

(7)Soil compactionSoil water and NCover crop biomassWheat yield and grain

protein

Treatments1. Fallow (SF)2. Pea (PEA)3. Full mix (FULL)4. Nitrogen fixers5. Fibrous roots6. Tap roots7. Brassicas8. Full mix minus N- fixers9. Full mix minus fibrous

roots10. Full mix minus tap roots11. Full mix minus brassicas

Potentially Mineralizable Nitrogen (PMN)

• We predicted that cover crops shouldincrease PMN relative to fallow. This wastrue after 2 CCM cycles in 4 of the 8 site-years. (Just 2 sites shown on right)

• After 4 rotations, across two sites, thepattern of higher rates of PMN after covercrops than fallow was consistent at one siteonly.

Soil Enzymes

• After 2 CCM cycles, soil response to cover cropsrelative to fallow appeared cumulative, withgreater differences after 2 rotations than 1rotation.

• After 4 rotations, the increase in soil enzymeactivity persisted at one of the two sites.Additionally, the amount of biomass produced bythe cover crop mixture was more important thanplant functional group identity.

RESULTS

DISCUSSION

We did not measure differences in soil biological parameters between the single functional group treatments, suggesting that the diversity of cover crops is not as important as we expected. PMN and other responses were correlated to cover crop biomass and not species diversity. Additionally, in semi-arid systems, with a short period of cover crop growth between alternate year crops, soil biological traits increased in response to cover crops relative to fallow only during years with average or above average rainfall (5). These findings are complementary to studies that document shifts in biological communities with cropping intensification (8).

AcknowledgementsFunding was provided by Western SARE (Sustainable Agriculture, Research & Education), Montana Fertilizer Advisory Committee, USDA NIFA MONB00397. Thanks to producer partners Eric and Chad Doheny, Carl Vandermolen, and Herb Oehlke.

Fig. 1: Crop field

INTRODUCTION

Measuring soil biological diversity is a significant task, but even more challenging is interpreting what that diversity means in terms of ecological function. We provide an example in a study on the effects of cover crop mixtures (CCM) on soil properties in a semi-arid system. Dryland wheat farming in the northern Great Plains (USA) occurs in climates with just enough precipitation to grow wheat profitably. Summer fallow has been widely practiced for decades as a way to store part of one year’s precipitation for the next year’s crop. While effective as a way to increase crop yield, the fallow year impacts soil quality as a result of reduced organic matter inputs and increased erodibility (1,2). We measured the effects of cover crop mixtures relative to fallow or a single-species pea cover crop on soil biological, chemical and physical parameters, along with yield and protein content of the subsequent year’s wheat crop. Our questions:

Table 1: Types of crops by year

Fig. 3: Geometric mean of all enzymes

Fig. 2: Selected functional groups for cover crop mixture

Table 2: Treatments and response variables measured

Fig. 4: Potentially mineralizable nitrogen