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{{Short description|Crop planted to manage erosion and soil quality}} | |||
Broadly defined, a '''cover crop''' is any ], ], or ] grown as a ] (one crop type grown together) or ] (multiple crop types grown together), to improve any number of conditions associated with ]. Cover crops are fundamental, sustainable tools used to manage ], soil quality, water, ]s (unwanted plants that limit crop production potential), ] (unwanted animals, usually insects, that limit crop production potential), diseases, and diversity and wildlife, in ] (Lu ''et al.'' 2000). Agroecosystems are ecological systems managed by humans across a range of intensities to produce food, feed, or fiber. To a large degree, humans shape the ecological structure and function of natural processes that occur in agroecosystems. | |||
] | |||
{{Agriculture}} | |||
In ], '''cover crops''' are plants that are planted to ] the soil rather than for the purpose of being ]ed. Cover crops manage soil ], ], ], water, ]s, ], diseases, ] and wildlife in an ]{{mdash}}an ecological system managed and shaped by humans. Cover crops can increase ] in the soil, which has a positive effect on ], ] in ], and ]. Cover crops reduce water pollution risks and remove CO2 from the atmosphere.<ref>{{cite web | url=http://www.climatehubs.usda.gov/hubs/northeast/topic/cover-cropping-improve-climate-resilience#:~:text=Plant%20cover%20helps%20intercept%20and,reduce%20a%20farm%27s%20carbon%20footprint | title=Cover Cropping to Improve Climate Resilience | USDA Climate Hubs }}</ref> Cover crops may be an off-season crop planted after harvesting the ]. Cover crops are ]s in that they increase the survival of the main crop being harvested, and are often grown over the winter.<ref>{{Cite journal |last=Carlson |first=Sarah |date=Summer 2013 |title=Research Priorities for Advancing Adoption of Cover Crops in Agriculture-intensive Regions |url=https://www.foodsystemsjournal.org/index.php/fsj/article/view/196 |journal=Journal of Agriculture, Food Systems, and Community Development |volume=3 |pages=125–129}}</ref><ref>{{cite news |url=https://www.nytimes.com/2016/02/07/business/cover-crops-a-farming-revolution-with-deep-roots-in-the-past.html?_r=0 |newspaper=The New York Times |title=Cover Crops, a Farming Revolution With Deep Roots in the Past |year=2016}}</ref> In the United States, cover cropping may cost as much as $35 per acre.<ref>{{cite news |last1=Weise |first1=Elizabeth |date=28 December 2022 |title=Ancient farming practice makes a comeback as climate change puts pressure on crops |url=https://www.usatoday.com/story/news/2022/12/28/cover-crops-can-help-fight-climate-change-effects-us-farms/10798179002 |work=USA Today |access-date=28 December 2022}}</ref> | |||
As agroecosystems often interact with neighboring natural ecosystems in agricultural landscapes, cover crops that improve the sustainability of agroecosystem attributes may also indirectly improve qualities of neighboring natural ecosystems. Farmers choose to grow specific cover crop types and to manage them in specific ways based on their own unique needs and goals. These needs and goals are influenced by biological, environmental, social, cultural, and economic factors of the food system within which farmers operate (Snapp ''et al.'' 2005). | |||
==Soil erosion== | |||
{{Main|Erosion}} | |||
Although cover crops can perform multiple functions in an agroecosystem simultaneously, they are often grown for the sole purpose of preventing ]. Soil erosion is a process that can irreparably reduce the productive capacity of an agroecosystem. Cover crops reduce soil loss by improving soil structure and increasing infiltration, protecting the soil surface, scattering raindrop energy, and reducing the velocity of the movement of water over the soil surface.<ref>{{Cite journal |last1=Panagos |first1=Panos |last2=Borrelli |first2=Pasquale |last3=Poesen |first3=Jean |last4=Ballabio |first4=Cristiano |last5=Lugato |first5=Emanuele |last6=Meusburger |first6=Katrin |last7=Montanarella |first7=Luca |last8=Alewell |first8=Christine |date=December 2015 |title=The new assessment of soil loss by water erosion in Europe |journal=Environmental Science & Policy |language=en |volume=54 |pages=438–447 |doi=10.1016/j.envsci.2015.08.012|doi-access=free|bibcode=2015ESPol..54..438P }}</ref> Dense cover crop stands physically slow down the velocity of ] before it contacts the soil surface, preventing soil splashing and erosive ].<ref>{{cite book |last1=Römkens |first1=M. J. M. |last2=Prasad |first2=S. N. |last3=Whisler |first3=F. D. |year=1990 |chapter=Surface sealing and infiltration |pages=127–172 |editor1-last=Anderson |editor1-first=M. G. |editor2-last=Burt |editor2-first=T. P. |title=Process studies in hillslope hydrology |publisher=John Wiley and Sons, Ltd. |publication-place=Chichester, United Kingdom |isbn=0471927147}}</ref> Additionally, vast cover crop root networks help anchor the soil in place and increase soil porosity, producing suitable habitat networks for soil macrofauna.<ref>{{cite book |last1=Tomlin |first1=A. D. |last2=Shipitalo |first2=M. J. |last3=Edwards |first3=W. M. |last4=Protz |first4=R. |year=1995 |chapter=Earthworms and their influence on soil structure and infiltration |pages=159–183 |editor-last=Hendrix |editor-first=P. F. |title=Earthworm Ecology and Biogeography in North America |publisher=Lewis Publishers |publication-place=Boca Raton, Florida}}</ref> It keeps the enrichment of the soil good for the next few years. | |||
==Soil fertility management== | ==Soil fertility management== | ||
{{Main|Green manure}} | |||
Cover crops also called "green manure" are used to manage a range of soil ] and ]. For example in Nigeria, the cover crop ] (velvet bean) has been found to increase the availability of phosphorus in soil after a farmer applies rock phosphate (Vanlauwe ''et al.'' 2000). With respect to nutrients, the impact that cover crops have on nitrogen management has received by far the most attention by researchers and farmers, because nitrogen is often the most limiting nutrient in crop production. | |||
One of the primary uses of cover crops is to increase soil fertility. These types of cover crops are referred to as "]". They are used to manage a range of soil ] and ]. Of the various nutrients, the impact that cover crops have on nitrogen management has received the most attention from researchers and farmers because nitrogen is often the most limiting nutrient in crop production. | |||
Often, green manure crops are grown for a specific period, and then ] before reaching full maturity to improve soil fertility and quality. The stalks left block the soil from being eroded. | |||
Cover crops known as “]s” are grown and incorporated (by tillage) into the soil before reaching full maturity, and are intended to improve soil fertility and quality. They are commonly ], meaning they are part of the ] (pea) family. This family is unique in that all of the species in it set pods, such as bean, lentil, and alfalfa. Leguminous cover crops are typically high in nitrogen and can often, to varying degrees, provide the required quantity of nitrogen for crop production that might normally be applied in chemical fertilizer form (called fertilizer replacement value) (Thiessen-Martens ''et al.'' 2005). Another quality unique to leguminous cover crops is that they form ]s with ] bacteria that reside in legume root nodules. is nodulated by the soil microorganism Bradyrhizobium sp. (Lupinus). Bradyrhizobia are encountered as microsymbionts in other leguminous crops (Argyrolobium, Lotus, Ornithopus, Acacia, Lupinus) of Mediterranean origin. These bacteria convert biologically unavailable atmospheric nitrogen gas (N2) to biologically available mineral nitrogen (NH4+) through the process of biological nitrogen fixation. | |||
Green manure crops are commonly ], meaning they are part of the pea family, ]. This family is unique in that all of the species in it set pods, such as bean, lentil, ]s and ]. Leguminous cover crops are typically high in nitrogen and can often provide the required quantity of nitrogen for crop production. In conventional farming, this nitrogen is typically applied in chemical fertilizer form. In organic farming, nitrogen inputs may take the form of ], ], cover crop seed, and ] by ] cover crops.<ref name=":0">{{Cite journal |last1=White |first1=Kathryn E. |last2=Brennan |first2=Eric B. |last3=Cavigelli |first3=Michel A. |last4=Smith |first4=Richard F. |date=2022-04-28 |editor-last=Riaz |editor-first=Muhammad |title=Winter cover crops increased nitrogen availability and efficient use during eight years of intensive organic vegetable production |journal=PLOS ONE |language=en |volume=17 |issue=4 |pages=e0267757 |doi=10.1371/journal.pone.0267757 |issn=1932-6203 |pmc=9049554 |pmid=35482753 |bibcode=2022PLoSO..1767757W |doi-access=free }}</ref> This quality of cover crops is called fertilizer replacement value.<ref>{{cite journal |last1=Thiessen-Martens |first1=J. R. |last2=Entz |first2=M. H. |last3=Hoeppner |first3=J. W. |year=2005 |title=Legume cover crops with winter cereals in southern Manitoba: Fertilizer replacement values for oat |journal=Canadian Journal of Plant Science |volume=85 |issue=3 |pages=645–648 |doi=10.4141/p04-114| doi-access = free}}</ref> | |||
Prior to the advent of the Haber-Bosch process, an energy-intensive method developed to carry out industrial nitrogen fixation and create chemical nitrogen fertilizer, most nitrogen introduced to ecosystems arose through biological nitrogen fixation (Galloway ''et al.'' 1995). Some scientists believe that widespread biological nitrogen fixation, achieved mainly through the use of cover crops, is the only alternative to industrial nitrogen fixation in the effort to maintain or increase future food production levels (Bohlool ''et al.'' 1992, Peoples and Craswell 1992, Giller and Cadisch 1995). Industrial nitrogen fixation has been criticized as an unsustainable source of nitrogen for food production due to its reliance on fossil fuel energy and the environmental impacts associated with chemical nitrogen fertilizer use in agriculture (Jensen and Hauggaard-Nielsen 2003). Such widespread environmental impacts include nitrogen fertilizer losses into waterways, which can lead to ] (nutrient loading) and ensuing hypoxia (oxygen depletion) of large bodies of water. An example of this lies in the Mississippi Valley Basin, where years of fertilizer nitrogen loading into the watershed from agricultural production have resulted in a hypoxic “dead zone” off of the Gulf of Mexico the size of New Jersey (Rabalais ''et al.'' 2002). The ecological complexity of marine life in this zone has been diminishing as a consequence (CENR 2000). | |||
Another quality unique to leguminous cover crops is that they form ]s with the ] bacteria that reside in legume root nodules. Lupins is nodulated by the soil microorganism '']'' sp. (Lupinus). Bradyrhizobia are encountered as microsymbionts in other leguminous crops (''Argyrolobium'', ''Lotus'', ''Ornithopus'', ''Acacia'', ''Lupinus'') of Mediterranean origin. These bacteria convert biologically unavailable atmospheric nitrogen gas ({{chem|N|2}}) to biologically available ammonium ({{chem|N|H|4|+}}) through the process of biological ]. In general, cover crops increase soil microbial activity, which has a positive effect on nitrogen availability in the soil, nitrogen uptake in target crops, and crop yields.<ref name=":0" /> | |||
As well as bringing nitrogen into agroecosystems through biological nitrogen fixation, cover crops known as “]s” are used to retain and recycle soil nitrogen already present. The catch crops take up surplus nitrogen remaining from fertilization of the previous crop, preventing it from being lost through ] (Morgan ''et al.'' 1942), or gaseous ] or ] (Thorup-Kristensen ''et al.'' 2003). Catch crops are typically fast-growing annual cereal species adapted to scavenge available nitrogen efficiently from the soil (Ditsch and Alley 1991). The nitrogen tied up in catch crop biomass is released back into the soil once the catch crop is incorporated as a green manure or otherwise begins to decompose | |||
Prior to the advent of the ], an energy-intensive method developed to carry out industrial nitrogen fixation and create chemical nitrogen fertilizer, most nitrogen introduced to ecosystems arose through biological nitrogen fixation.<ref>{{cite journal |last1=Galloway |first1=J. N. |last2=Schlesinger |first2=W. H. |last3=Levy |first3=H. |last4=Michaels |first4=A. |last5=Schnoor |first5=J. L. |year=1995 |title=Nitrogen-Fixation - Anthropogenic Enhancement-Environmental Response |journal=Global Biogeochemical Cycles |volume=9 |issue=2 |pages=235–252 |doi=10.1029/95gb00158 |bibcode=1995GBioC...9..235G |citeseerx=10.1.1.143.8150}}</ref> Some scientists believe that widespread biological nitrogen fixation, achieved mainly through the use of cover crops, is the only alternative to industrial nitrogen fixation in the effort to maintain or increase future food production levels.<ref>{{cite journal |last1=Bohlool |first1=B. B. |last2=Ladha |first2=J. K. |last3=Garrity |first3=D. P. |last4=George |first4=T. |year=1992 |title=Biological nitrogen fixation for sustainable agriculture: A perspective |journal=Plant and Soil |volume=141 |issue=1–2 |pages=1–11 |doi=10.1007/bf00011307 |bibcode=1992PlSoi.141....1B |s2cid=93573}}</ref><ref>{{cite journal |last1=Peoples |first1=M. B. |last2=Craswell |first2=E. T. |year=1992 |title=Biological nitrogen fixation: Investments, expectations and actual contributions to agriculture |journal=Plant and Soil |volume=141 |issue=1–2 |pages=13–39 |doi=10.1007/BF00011308 |bibcode=1992PlSoi.141...13P |s2cid=24030223}}</ref> Industrial nitrogen fixation has been criticized as an unsustainable source of nitrogen for food production due to its reliance on fossil fuel energy and the environmental impacts associated with chemical nitrogen fertilizer use in agriculture.<ref>{{cite journal |last1=Jensen |first1=E. S. |last2=Hauggaard-Nielsen |first2=H. |year=2003 |title=How can increased use of biological N-2 fixation in agriculture benefit the environment? |journal=Plant and Soil |volume=252 |issue=1 |pages=177–186 |doi=10.1023/A:1024189029226 |bibcode=2003PlSoi.252..177J |s2cid=42527851}}</ref> Such widespread environmental impacts include nitrogen fertilizer losses into waterways, which can lead to ] (nutrient loading) and ensuing hypoxia (oxygen depletion) of large bodies of water. | |||
An example of this is in the Mississippi Valley Basin, where years of fertilizer nitrogen loading into the watershed from agricultural production have resulted in an annual summer hypoxic ] that reached an area of over 22,000 square kilometers in 2017.<ref>{{cite journal |last1=Rabalais |first1=N. N. |last2=Turner |first2=R. E. |last3=Wiseman |first3=W. J. |year=2002 |title=Gulf of Mexico hypoxia, aka "The dead zone" |journal=Annual Review of Ecology and Systematics |volume=33 |pages=235–263 |doi=10.1146/annurev.ecolsys.33.010802.150513}}</ref><ref>{{cite web |url=http://www.noaa.gov/media-release/gulf-of-mexico-dead-zone-is-largest-ever-measured |title=NOAA: Gulf of Mexico 'dead zone' is the largest ever measured |publisher=National Oceanic and Atmospheric Administration (NOAA) |date=August 3, 2017 |access-date=August 3, 2017 |archive-url=https://web.archive.org/web/20170802173757/http://www.noaa.gov/media-release/gulf-of-mexico-dead-zone-is-largest-ever-measured |archive-date= August 2, 2017}}</ref> The ecological complexity of marine life in this zone has been diminishing as a consequence.<ref>{{cite report |author=National Science and Technology Council Committee on Environment and Natural Resources |year=2000 |title=Integrated Assessment of Hypoxia in the Northern Gulf of Mexico |url=http://www.oceanservice.noaa.gov/products/hypox_final.pdf | publication-place=Washington, DC.}}</ref> | |||
As well as bringing nitrogen into agroecosystems through biological nitrogen fixation, types of cover crops known as "]s" are used to retain and recycle soil nitrogen already present. The catch crops take up surplus nitrogen remaining from fertilization of the previous crop, preventing it from being lost through ],<ref>{{cite tech report |last1=Morgan |first1=M. F. |last2=Jacobson |first2=H. G. M. |last3=LeCompte |first3=S. B. Jr. |year=1942 |title=Drainage water losses from a sandy soil as affected by cropping and cover crops |series=Windsor Lysimeter Series C |publisher=Connecticut Agricultural Experiment Station |pages=731-759 |publication-place=New Haven}}</ref> or gaseous ] or ].<ref>{{cite journal |last1=Thorup-Kristensen |first1=K. |first2=J. |last2=Magid |first3=L. S. |last3=Jensen |year=2003 |title=Catch crops and green manures as biological tools in nitrogen management in temperate zones |pages=227–302 |journal=Advances in Agronomy |volume=79 |publisher=Academic Press Inc. |doi=10.1016/S0065-2113(02)79005-6 |isbn=9780120007974 |publication-place=San Diego, California}}</ref> | |||
Catch crops are typically fast-growing annual cereal species adapted to scavenge available nitrogen efficiently from the soil.<ref>{{cite journal |last1=Ditsch |first1=D. C. |last2=Alley |first2=M. M. |year=1991 |title=Nonleguminous Cover Crop Management for Residual N Recovery and Subsequent Crop Yields |journal=Journal of Fertilizer Issues |volume=8 |pages=6–13}}</ref> The nitrogen fixed in catch crop biomass is released back into the soil once the cash crop is incorporated as a green manure or otherwise begins to decompose. | |||
An example of green manure use comes from Nigeria, where the cover crop '']'' (velvet bean) has been found to increase the availability of phosphorus in soil after a farmer applies rock phosphate.<ref>{{cite journal |last1=Vanlauwe |first1=B. |last2=Nwoke |first2=O. C. |last3=Diels |first3=J. |last4=Sanginga |first4=N. |last5=Carsky |first5=R. J. |last6=Deckers |first6=J. |last7=Merckx |first7=R. |year=2000 |title=Utilization of rock phosphate by crops on a representative toposequence in the Northern Guinea savanna zone of Nigeria: response by Mucuna pruriens, Lablab purpureus and maize |journal=Soil Biology & Biochemistry |volume=32 |issue=14 |pages=2063–2077 |doi=10.1016/s0038-0717(00)00149-8|bibcode=2000SBiBi..32.2063V }}</ref> | |||
==Soil quality management== | ==Soil quality management== | ||
Cover crops can improve soil quality by increasing |
Cover crops can also improve soil quality by increasing ] levels through the input of cover crop biomass over time. Increased soil ] enhances ] as well as the water and nutrient holding and buffering capacities of the soil.<ref>{{cite journal |last1=Patrick |first1=W. H. |last2=Haddon |first2=C. B. |last3=Hendrix |first3=J. A. |year=1957 |title=The effects of longtime use of winter cover crops on certain physical properties of commerce loam |journal=Soil Science Society of America Journal |volume=21 |issue=4 |pages=366–368 |doi=10.2136/sssaj1957.03615995002100040004x |bibcode=1957SSASJ..21..366P}}</ref> It can also lead to increased soil ], which has been promoted as a strategy to help offset the rise in atmospheric carbon dioxide levels.<ref>{{cite journal |last1=Kuo |first1=S. |last2=Sainju |first2=U. M. |last3=Jellum |first3=E. J. |year=1997 |title=Winter cover crop effects on soil organic carbon and carbohydrate in soil |journal=Soil Science Society of America Journal |volume=61 |issue=1 |pages=145–152 |doi=10.2136/sssaj1997.03615995006100010022x |bibcode=1997SSASJ..61..145K}}</ref><ref>{{cite journal |last1=Sainju |first1=U. M. |last2=Singh |first2=B. P. |last3=Whitehead |first3=W. F. |year=2002 |title=Long-term effects of tillage, cover crops, and nitrogen fertilization on organic carbon and nitrogen concentrations in sandy loam soils in Georgia, USA |journal=Soil & Tillage Research |volume=63 |issue=3–4 |pages=167–179 |doi=10.1016/s0167-1987(01)00244-6|bibcode=2002STilR..63..167S }}</ref><ref>{{cite journal |last1=Lal |first1=R |year=2003 |title=Offsetting global CO2 emissions by restoration of degraded soils and intensification of world agriculture and forestry |journal=Land Degradation & Development |volume=14 |issue=3 |pages=309–322 |doi=10.1002/ldr.562 |bibcode=2003LDeDe..14..309L |s2cid=129950927}}</ref> | ||
Although cover crops can perform multiple functions in an agroecosystem simultaneously, they are often grown for the sole purpose of preventing soil erosion. Soil erosion is a process that can irreparably reduce the productive capacity of an agroecosystem. Dense cover crop stands physically slow down the velocity of rainfall before it contacts the soil surface, preventing soil splashing and erosive ] (Romkens ''et al.'' 1990). Additionally, vast cover crop root networks help anchor the soil in place and increase soil porosity, creating suitable habitat networks for soil macrofauna (Tomlin ''et al.'' 1995). | |||
Soil quality is managed to produce optimum |
Soil quality is managed to produce optimum conditions for crops to flourish. The principal factors affecting soil quality are ], ], ] balance, and the prevention of ]. It is noted that if soil quality is properly managed and maintained, it forms the foundation for a healthy and productive environment. One can design and manage a crop that will produce a healthy environment for quite some time.<ref>{{Cite web |title=Managing Soil Health: Concepts and Practices |url=https://extension.psu.edu/managing-soil-health-concepts-and-practices |access-date=2023-07-14 |website=extension.psu.edu |language=en}}</ref> | ||
==Water management== | ==Water management== | ||
By reducing soil erosion, cover crops often also reduce both the rate and quantity of water that drains off the field, |
By reducing soil erosion, cover crops often also reduce both the rate and quantity of water that drains off the field, which would normally pose environmental risks to waterways and ecosystems downstream.<ref>{{cite journal |last1=Dabney |first1=S. M. |last2=Delgado |first2=J. A. |last3=Reeves |first3=D. W. |year=2001 |title=Using winter cover crops to improve soil quality and water quality |journal=Communications in Soil Science and Plant Analysis |volume=32 |issue=7–8 |pages=1221–1250 |doi=10.1081/css-100104110 |s2cid=55768619}}</ref> Cover crop biomass acts as a physical barrier between rainfall and the soil surface, allowing raindrops to steadily trickle down through the soil profile. Also, as stated above, cover crop root growth results in the formation of soil pores, which, in addition to enhancing soil macrofauna habitat provides pathways for water to filter through the soil profile rather than draining off the field as surface flow. With increased water infiltration, the potential for soil water storage and the recharge of aquifers can be improved.<ref>{{cite journal |last1=Joyce |first1=B. A. |last2=Wallender |first2=W. W. |last3=Mitchell |first3=J. P. |last4=Huyck |first4=L. M. |last5=Temple |first5=S. R. |last6=Brostrom |first6=P. N. |last7=Hsiao |first7=T. C. |year=2002 |title=Infiltration and soil water storage under winter cover cropping in California's Sacramento Valley |journal=Transactions of the ASAE |volume=45 |issue=2 |pages=315–326 |doi=10.13031/2013.8526}}</ref> | ||
Just before cover crops are killed (by such practices including mowing, tilling, discing, rolling, herbicide application) they contain a large amount of moisture. When the cover crop is incorporated into the soil, or left on the soil surface, it often increases soil moisture. In agroecosystems where water for crop production is in short supply, cover crops can be used as a mulch to conserve water by shading and cooling the soil surface. This reduces evaporation of soil moisture. |
Just before cover crops are killed (by such practices including mowing, tilling, discing, rolling, or herbicide application) they contain a large amount of moisture. When the cover crop is incorporated into the soil, or left on the soil surface, it often increases soil moisture. In agroecosystems where water for crop production is in short supply, cover crops can be used as a mulch to conserve water by shading and cooling the soil surface. This reduces the evaporation of soil moisture and helps preserve soil nutrients.<ref>{{Cite journal |last1=Arlauskienė |first1=Aušra |last2=Šarūnaitė |first2=Lina |date=2023-08-16 |title=Cover Crop Yield, Nutrient Storage and Release under Different Cropping Technologies in the Sustainable Agrosystems |journal=Plants |volume=12 |issue=16 |pages=2966 |doi=10.3390/plants12162966 |doi-access=free |issn=2223-7747 |pmid=37631177|pmc=10457803 }}</ref> | ||
While cover crops can help to conserve water, in temperate regions (particularly in years with below average precipitation) they can draw down soil water supply in the spring, particularly if climatic growing conditions are good. In these cases, just before crop planting, farmers often face a tradeoff between the benefits of increased cover crop growth and the drawbacks of reduced soil moisture for cash crop production that season. | |||
==Weed management== | ==Weed management== | ||
] | |||
Thick cover crop stands often compete well with ]s during the cover crop growth period, and can prevent most germinated weed seeds from completing their life cycle and reproducing. If the cover crop is left on the soil surface rather than incorporated into the soil as a green manure after its growth is terminated, it can form a nearly impenetrable mat. This drastically reduces light transmittance to weed seeds, which in many cases reduces weed seed germination rates (Teasdale 1993). Furthermore, even when weed seeds germinate, they often run out of stored energy for growth before building the necessary structural capacity to break through the cover crop ] layer. This is often termed the ''cover crop smother effect'' (Kobayashi ''et al.'' 2003). | |||
Thick cover crop stands often compete well with ]s during the cover crop growth period, and can prevent most germinated weed seeds from completing their life cycle and reproducing. If the cover crop is flattened down on the soil surface rather than incorporated into the soil as a green manure after its growth is terminated, it can form a nearly impenetrable mat. This drastically reduces light transmittance to weed seeds, which in many cases reduces weed seed germination rates.<ref>{{cite journal |last1=Teasdale |first1=J. R. |year=1993 |title=Interaction of light, soil moisture, and temperature with weed suppression by hairy vetch residue |journal=Weed Science |volume=41 |pages=46–51 |doi=10.1017/S0043174500057568 |s2cid=90672916}}</ref> Furthermore, even when weed seeds germinate, they often run out of stored energy for growth before building the necessary structural capacity to break through the cover crop ] layer. This is often termed the ''cover crop smother effect''.<ref>{{cite journal |last1=Kobayashi |first1=Y. |last2=Ito |first2=M. |last3=Suwanarak |first3=K. |year=2003 |title=Evaluation of smothering effect of four legume covers on Pennisetum polystachion ssp. setosum (Swartz) Brunken |journal=Weed Biology and Management |volume=3 |issue=4 |pages=222–227 |doi=10.1046/j.1444-6162.2003.00107.x}}</ref> | |||
Some cover crops suppress weeds both during growth and after death.<ref name=Blackshaw2001>{{cite journal |last1=Blackshaw |first1=R. E. |last2=Moyer |first2=J. R. |last3=Doram |first3=R. C. |last4=Boswell |first4=A. L. |year=2001 |title=Yellow sweetclover, green manure, and its residues effectively suppress weeds during fallow |journal=Weed Science |volume=49 |issue=3 |pages=406–413 |doi=10.1614/0043-1745(2001)0492.0.co;2 |s2cid=86040044}}</ref> During growth these cover crops compete vigorously with weeds for available space, light, and nutrients, and after death they smother the next flush of weeds by forming a mulch layer on the soil surface.<ref name=":1">{{Cite journal |last1=Gazoulis |first1=Ioannis |last2=Kanatas |first2=Panagiotis |last3=Antonopoulos |first3=Nikolaos |last4=Tataridas |first4=Alexandros |last5=Travlos |first5=Ilias |date=2022-10-10 |title=Νarrow Row Spacing and Cover Crops to Suppress Weeds and Improve Sulla (Hedysarum coronarium L.) Biomass Production |journal=Energies |language=en |volume=15 |issue=19 |pages=7425 |doi=10.3390/en15197425 |issn=1996-1073 |doi-access=free }}</ref> For example, researchers found that when using '']'' (yellow sweetclover) as a cover crop in an improved ] system (where a fallow period is intentionally improved by any number of different management practices, including the planting of cover crops), weed biomass only constituted between 1–12% of total standing biomass at the end of the cover crop growing season.<ref name=Blackshaw2001 /> Furthermore, after cover crop termination, the yellow sweetclover residues suppressed weeds to levels 75–97% lower than in fallow (no yellow sweetclover) systems. | |||
] | |||
In addition to competition-based or physical weed suppression, certain cover crops are known to suppress weeds through ].<ref>{{cite journal |last1=Creamer |first1=N. G. |last2=Bennett |first2=M. A. |last3=Stinner |first3=B. R. |last4=Cardina |first4=J. |last5=Regnier |first5=E. E. |year=1996 |title=Mechanisms of weed suppression in cover crop-based production systems |journal=HortScience |volume=31 |issue=3 |pages=410–413 |doi=10.21273/HORTSCI.31.3.410 | doi-access = free}}</ref><ref>{{cite Q|Q56019215 |last1=Singh |first1=H. P. |last2=Batish |first2=D. R. |last3=Kohli |first3=R. K.|author3-link=R. K. Kohli}}</ref> This occurs when certain biochemical cover crop compounds are degraded that happen to be toxic to, or inhibit seed germination of, other plant species. Some well known examples of allelopathic cover crops are '']'' (rye), '']'' (hairy vetch), '']'' (red clover), '']'' (sorghum-sudangrass), and species in the family ], particularly ]s.<ref>{{cite journal |last1=Haramoto |first1=E. R. |last2=Gallandt |first2=E. R. |year=2004 |title=Brassica cover cropping for weed management: A review |journal=Renewable Agriculture and Food Systems |volume=19 |issue=4 |pages=187–198 |doi=10.1079/raf200490}}</ref> In one study, rye cover crop residues were found to have provided between 80% and 95% control of early season broadleaf weeds when used as a mulch during the production of different cash crops such as ], ], ], and ].<ref>{{cite journal |last1=Nagabhushana |first1=G. G. |last2=Worsham |first2=A. D. |last3=Yenish |first3=J. P. |year=2001 |title=Allelopathic cover crops to reduce herbicide use in sustainable agricultural systems |journal=Allelopathy Journal |volume=8 |pages=133–146}}</ref> In general, cover crops need not compete with cash crops, as they can be grown and terminated early on the season before other crops are established.<ref name=":1" /> | |||
In a 2010 study released by the ] (ARS),<ref>{{Cite web |title=In Organic Cover Crops, More Seeds Means Fewer Weeds : USDA ARS |url=https://www.ars.usda.gov/news-events/news/research-news/2010/in-organic-cover-crops-more-seeds-means-fewer-weeds/ |access-date=2024-01-15 |website=www.ars.usda.gov}}</ref> scientists examined how rye ] and ] affected cover crop production. The results show that planting more pounds per acre of rye increased the cover crop's production as well as decreased the amount of weeds. The same was true when scientists tested seeding rates on legumes and oats; a higher density of seeds planted per acre decreased the amount of weeds and increased the yield of legume and oat production. The planting patterns, which consisted of either traditional rows or grid patterns, did not seem to have a significant impact on the cover crop's production or on the weed production in either cover crop. The ARS scientists concluded that increased seeding rates could be an effective method of weed control.<ref>{{cite web |url=http://www.ars.usda.gov/is/pr/2010/100125.htm |title=In Organic Cover Crops, More Seeds Means Fewer Weeds |publisher=USDA Agricultural Research Service |date=January 25, 2010}}</ref> | |||
Cornell University's released a study in May 2023 investigating the effectiveness of time-sensitive planting and strategic coupling of cover crop variants with phylogenetically similar cash crops. The primary researcher, Uriel Menalled, discovered that if cover and cash crops are planted in accordance with his research findings, farmers can decrease weed growth by up to 99%. The study provides farmers with a comprehensive framework to identify cover crops that would best suit their existing cropping rotations. In sum, the results from this study support an understanding that phylogenetic relatedness can be harnessed to significantly suppress weed growth.<ref>{{cite journal |last1=Menalled |first1=Uriel |title=Ecological Weed Management for Field Crop Production |journal=ProQuest |date=2023 |pages=102–126}}</ref> | |||
Some cover crops suppress weeds both during growth and after death (Blackshaw ''et al.'' 2001). During growth these cover crops compete vigorously with weeds for available space, light, and nutrients, and after death they smother the next flush of weeds by forming a mulch layer on the soil surface. For example, Blackshaw ''et al.'' (2001) found that when using ''Melilotus officinalis'' (yellow sweetclover) as a cover crop in an improved fallow system (where a fallow period is intentionally improved by any number of different management practices, including the planting of cover crops), weed biomass only constituted between 1-12% of total standing biomass at the end of the cover crop growing season. Furthermore, after cover crop termination, the yellow sweetclover residues suppressed weeds to levels 75-97% lower than in fallow (no yellow sweetclover) systems. | |||
In addition to competition-based or physical weed suppression, certain cover crops are known to suppress weeds through ] (Creamer ''et al.'' 1996, Singh ''et al.'' 2003). This occurs when certain biochemical cover crop compounds are degraded that happen to be toxic to, or inhibit seed germination of, other plant species. Some well known examples of allelopathic cover crops are ''Secale cereale'' (]), ''Vicia villosa'' (]), ''Trifolium pretense'' (]), ''Sorghum bicolor'' (]-sudangrass), and species in the ] family, particularly ]s (Haramoto and Gallandt 2004). In one study, rye cover crop residues were found to have provided between 80% and 95% control of early season broadleaf weeds when used as a mulch during the production of different cash crops such as ], ], ], and ] (Nagabhushana ''et al.'' 2001). | |||
==Disease management== | ==Disease management== | ||
In the same way that allelopathic properties of cover crops can suppress weeds, they can also break disease cycles and reduce populations of bacterial and fungal diseases |
In the same way that allelopathic properties of cover crops can suppress weeds, they can also break disease cycles and reduce populations of bacterial and fungal diseases,<ref>{{cite journal |last1=Everts |first1=K. L. |year=2002 |title=Reduced fungicide applications and host resistance for managing three diseases in pumpkin grown on a no-till cover crop |journal=Plant Dis |volume=86 |issue=10 |pages=1134–1141 |doi=10.1094/pdis.2002.86.10.1134 |pmid=30818508 | doi-access = free}}</ref> and parasitic nematodes.<ref>{{cite journal |last1=Potter |first1=M. J. |last2=Davies |first2=K. |last3=Rathjen |first3=A. J. |year=1998 |title=Suppressive impact of glucosinolates in Brassica vegetative tissues on root lesion nematode Pratylenchus neglectus |doi=10.1023/A:1022336812240 |journal=Journal of Chemical Ecology |volume=24 |pages=67–80 |s2cid=41429379}}</ref><ref>{{cite journal |last1=Vargas-Ayala |first1=R. |last2=Rodriguez-Kabana |first2=R. |last3=Morgan-Jones |first3=G. |last4=McInroy |first4=J. A. |last5=Kloepper |first5=J. W. |year=2000 |title=Shifts in soil microflora induced by velvetbean (Mucuna deeringiana) in cropping systems to control root-knot nematodes |journal=Biological Control |volume=17 |issue=1 |pages=11–22 |doi=10.1006/bcon.1999.0769 |bibcode=2000BiolC..17...11V |citeseerx=10.1.1.526.3937}}</ref> Species in the family ], such as mustards, have been widely shown to suppress fungal disease populations through the release of naturally occurring toxic chemicals during the degradation of glucosinolate compounds in their plant cell tissues.<ref>{{cite journal |last1=Lazzeri |first1=L. |last2=Manici |first2=L. M. |year=2001 |title=Allelopathic effect of glucosinolate-containing plant green manure on Pythium sp and total fungal population in soil |journal=HortScience |volume=36 |issue=7 |pages=1283–1289 |doi=10.21273/HORTSCI.36.7.1283 | doi-access = free}}</ref> | ||
==Pest management== | ==Pest management== | ||
Some cover crops are used as so-called "trap crops", to attract pests away from the crop of value and toward what the pest sees as a more favorable habitat |
Some cover crops are used as so-called "trap crops", to attract pests away from the crop of value and toward what the pest sees as a more favorable habitat.<ref>{{cite journal |last1=Shelton |first1=A. M. |last2=Badenes-Perez |first2=E. |year=2006 |title=Concepts and applications of trap cropping in pest management |journal=Annual Review of Entomology |volume=51 |pages=285–308 |doi=10.1146/annurev.ento.51.110104.150959 |pmid=16332213}}</ref> Trap crop areas can be established within crops, within farms, or within landscapes. In many cases, the trap crop is grown during the same season as the food crop being produced. The limited area occupied by these trap crops can be treated with a pesticide once pests are drawn to the trap in large enough numbers to reduce pest populations. In some organic systems, farmers drive over the trap crop with a large ] to physically pull the pests off the plants and out of the field.<ref>{{cite tech report |first1=George |last1=Kuepper |first2=Raeven |last2=Thomas |title="Bug vacuums" for organic crop protection |institution=Appropriate Technology Transfer for Rural Areas |date=February 2002 | publication-place=Fayetteville, Arkansas |url=https://attra.ncat.org/attra-pub-summaries/?pub=128}}</ref> This system has been recommended for use to help control the ] in organic strawberry production.<ref>{{cite report |last1=Zalom |first1=F. G. |last2=Phillips |first2=P. A. |last3=Toscano |first3=N. C. |last4=Udayagiri |first4=S. |year=2001 |title=UC Pest Management Guidelines: Strawberry: Lygus Bug |publisher=University of California Department of Agriculture and Natural Resources |publication-place=Berkeley, CA}}</ref> Another example of trap crops is nematode-resistant ] and ]. They can be grown after a main (cereal) crop and trap nematodes, for example, the beet cyst ]<ref>{{Cite journal |title=Transfer of resistance to the beet cyst nematode (Heterodera Schachtii Schm.) from Sinapis alba L. (white mustard) to the Brassica napus L. gene pool by means of sexual and somatic hybridization |journal=Theoretical and Applied Genetics |date=1993-02-01 |issn=0040-5752 |pages=688–696 |volume=85 |issue=6–7 |doi=10.1007/BF00225006 |pmid=24196037 |first1=C. L. C. |last1=Lelivelt |first2=E. H. M. |last2=Leunissen |first3=H. J. |last3=Frederiks |first4=J. P. F. G. |last4=Helsper |first5=F. A. |last5=Krens |s2cid=22433897}}</ref><ref>{{Cite journal |title=Reproduction of Heterodera schachtii Schmidt on Resistant Mustard, Radish, and Sugar Beet Cultivars |journal=Journal of Nematology |date=2004-06-01 |issn=0022-300X |pmc=2620762 |pmid=19262796 |pages=123–130 |volume=36 |issue=2 |first1=Heidi J. |last1=Smith |first2=Fred A. |last2=Gray |first3=David W. |last3=Koch}}</ref> and the Columbian root knot nematode.<ref>{{Cite journal |title=Relative susceptibilities of five fodder radish varieties (Raphanus sativus var. Oleiformis) to Meloidogyne chitwoodi |journal=Nematology |date=2014-05-28 |issn=1568-5411 |pages=577–590 |volume=16 |issue=5 |doi=10.1163/15685411-00002789 |first1=Misghina G. |last1=Teklu |first2=Corrie H. |last2=Schomaker |first3=Thomas H. |last3=Been}}</ref> When grown, nematodes hatch and are attracted to the roots. After entering the roots they cannot reproduce in the root due to a ] resistance reaction of the plant. Hence the nematode population is greatly reduced, by 70–99%, depending on species and cultivation time. | ||
Other cover crops are used to attract natural predators of pests by providing elements of their habitat. This is a form of ] known as habitat augmentation, but achieved with the use of cover crops (Bugg and Waddington 1994). Findings on the relationship between cover crop presence and predator/pest population dynamics have been mixed, pointing toward the need for detailed information on specific cover crop types and management practices to best complement a given ] strategy. For example, the predator mite Euseius tularensis (Congdon) is known to help control the pest citrus thrips in Central California citrus orchards. Researchers found that the planting of several different leguminous cover crops (such as bell bean, woollypod vetch, New Zealand white clover, and Austrian winter pea) provided sufficient pollen as a feeding source to cause a seasonal increase in Congdon populations, which with good timing could potentially introduce enough predatory pressure to reduce pest populations of citrus thrips (Grafton-Cardwell ''et al.'' 1999). | |||
Other cover crops are used to attract natural predators of pests by imitating elements of their habitat. This is a form of ] known as habitat augmentation, but achieved with the use of cover crops.<ref>{{cite journal |last1=Bugg |first1=R. L. |last2=Waddington |first2=C. |year=1994 |title=Using Cover Crops to Manage Arthropod Pests of Orchards - a Review |journal=Agriculture, Ecosystems & Environment |volume=50 |issue=1 |pages=11–28 |doi=10.1016/0167-8809(94)90121-x|bibcode=1994AgEE...50...11B }}</ref> Findings on the relationship between cover crop presence and predator–pest population dynamics have been mixed, suggesting the need for detailed information on specific cover crop types and management practices to best complement a given ] strategy. For example, the predator mite ''Euseius tularensis'' (Congdon) is known to help control the pest citrus thrips in Central California citrus orchards. Researchers found that the planting of several different leguminous cover crops (such as bell bean, woollypod vetch, New Zealand white clover, and Austrian winter pea) provided sufficient pollen as a feeding source to cause a seasonal increase in ''E. tularensis'' populations, which with good could potentially introduce enough predatory pressure to reduce pest populations of citrus thrips.<ref>{{cite journal |last1=Grafton-Cardwell |first1=E. E. |last2=Ouyang |first2=Y. L. |last3=Bugg |first3=R. L. |year=1999 |title=Leguminous cover crops to enhance population development of Euseius tularensis (Acari : Phytoseiidae) in citrus |journal=Biological Control |volume=16 |issue=1 |pages=73–80 |doi=10.1006/bcon.1999.0732|bibcode=1999BiolC..16...73G }}</ref> | |||
==Diversity and wildlife== | |||
Although cover crops are normally used to serve one of the above discussed purposes, they often simultaneously improve farm habitat for wildlife. The use of cover crops adds at least one more dimension of plant diversity to a cash crop rotation. Since the cover crop is typically not a crop of value, its management is usually less intensive, providing a window of “soft” human influence on the farm. This relatively “hands-off” management, combined with the increased on-farm heterogeneity created by the establishment of cover crops, increases the likelihood that a more complex ] will develop to support a higher level of wildlife diversity (Freemark and Kirk 2001). In one study, researchers compared arthropod and songbird species composition and field use between conventionally and cover cropped cotton fields in the Southern United States. The cover cropped cotton fields were planted to clover, which was left to grow in between cotton rows throughout the early cotton growing season (stripcover cropping). During the migration and breeding season, they found that songbird densities were 7–20 times higher in the cotton fields with integrated clover cover crop than in the conventional cotton fields. Arthropod abundance and biomass was also higher in the clover cover cropped fields throughout much of the songbird breeding season, which was attributed to an increased supply of flower nectar from the clover. The clover cover crop enhanced songbird habitat by providing cover and nesting sites, and an increased food source from higher arthropod populations (Cederbaum ''et al.'' 2004). | |||
==Biodiversity and wildlife== | |||
Although cover crops are normally used to serve one of the above discussed purposes, they often serve as habitat for wildlife. The use of cover crops adds at least one more dimension of plant diversity to a cash crop rotation. Since the cover crop is typically not a crop of value, its management is usually less intensive, providing a window of "soft" human influence on the farm. This relatively "hands-off" management, combined with the increased on-farm heterogeneity produced by the establishment of cover crops, increases the likelihood that a more complex ] will develop to support a higher level of wildlife diversity.<ref>{{cite journal |last1=Freemark |first1=K. E. |last2=Kirk |first2=D. A. |year=2001 |title=Birds on organic and conventional farms in Ontario: partitioning effects of habitat and practices on species composition and abundance |journal=Biological Conservation |volume=101 |issue=3 |pages=337–350 |doi=10.1016/s0006-3207(01)00079-9|bibcode=2001BCons.101..337F }}</ref> | |||
In one study, researchers compared ] and songbird ] and field use between conventionally and cover cropped cotton fields in the Southern United States. The cover cropped cotton fields were planted to clover, which was left to grow in between cotton rows throughout the early cotton growing season (stripcover cropping). During the migration and breeding season, they found that songbird densities were 7–20 times higher in the cotton fields with an integrated clover cover crop than in the conventional cotton fields. Arthropod abundance and biomass was also higher in the clover c-cover fields throughout much of the songbird breeding season, which was attributed to an increased supply of flower nectar from the clover. The clover cover crop enhanced songbird habitat by providing covering sites, and an increased food source from higher arthropod populations.<ref>{{cite journal |last1=Cederbaum |first1=S. B. |last2=Carroll |first2=J. P. |last3=Cooper |first3=R. J. |year=2004 |title=Effects of alternative cotton agriculture on avian and arthropod populations |journal=Conservation Biology |volume=18 |issue=5 |pages=1272–1282 |doi=10.1111/j.1523-1739.2004.00385.x |bibcode=2004ConBi..18.1272C |s2cid=84945560}}</ref> | |||
==Conclusions== | |||
{{Inappropriate tone|date=December 2007}} | |||
Cover crops have an unparalleled range of potential to improve the sustainability of agroecosystems. Various forms of cover cropping have been utilized historically by different groups around the world. However, cover crops were popularized by the organic agriculture movement, which has been experiencing phenomenal growth as an industry. This exposure has attracted substantial cover crop research attention, and has led to the advancement of findings across agroecologically related disciplines, as discussed above. Many of these findings will likely provide some of the building blocks for the successful integration of cover crops into agroecosystems, to ultimately improve their sustainability. | |||
==See also== | ==See also== | ||
{{Portal|Agriculture}} | |||
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==References== | |||
{{Reflist}} | |||
==Further reading== | ==Further reading== | ||
*SARE National. Topic: Cover Crops. | |||
*Hartwig, N. L., and H. U. Ammon. 2002. 50th Anniversary - Invited article - Cover crops and living mulches. Weed Science 50:688-699. | |||
*Midwest Cover Crops Council. Resources for growers, researchers, and educators. | |||
*Sullivan, P. 2003. Overview of cover crops and green manures. ATTRA, Fayetteville, AR. | |||
*{{cite book |editor-last=Clark |editor-first=Andy |year=2007 |title=Managing Cover Crops Profitably |edition=3rd |publisher=Sustainable Agriculture Network |publication-place=Beltsville, Maryland |url=http://www.sare.org/content/download/29733/413984/ManagingCoverCropsProfitably_0812.pdf}} | |||
*University of California Sustainable Agriculture Research and Education Program. UCSAREP cover crop resource page. | |||
*{{cite journal |last1=Giller |first1=K. E. |last2=Cadisch |first2=G. |year=1995 |title=Future benefits from biological nitrogen fixation: An ecological approach to agriculture |journal=Plant and Soil |volume=174 |issue=1–2 |pages=255–277 |doi=10.1007/bf00032251 |bibcode=1995PlSoi.174..255G |s2cid=24604997}} | |||
*{{cite journal |last1=Hartwig |first1=N. L. |last2=Ammon |first2=H. U. |year=2002 |title=50th Anniversary - Invited article - Cover crops and living mulches |journal=Weed Science |volume=50 |issue=6 |pages=688–699 |doi=10.1614/0043-1745(2002)0502.0.co;2 |s2cid=86045745}} | |||
*{{cite journal |last1=Hill |first1=E. C. |last2=Ngouajio |first2=M. |last3=Nair |first3=M. G. |year=2006 |title=Differential responses of weeds and vegetable crops to aqueous extracts of hairy vetch and cowpea |journal=HortScience |volume=31 |issue=3 |pages=695–700 |doi=10.21273/HORTSCI.41.3.695|doi-access=free }} | |||
*{{cite journal |last1=Lu |first1=Y. C. |last2=Watkins |first2=K. B. |last3=Teasdale |first3=J. R. |last4=Abdul-Baki |first4=A. A. |year=2000 |title=Cover crops in sustainable food production |journal=Food Reviews International |volume=16 |issue=2 |pages=121–157 |doi=10.1081/fri-100100285 |s2cid=28356685}} | |||
*{{cite journal |last1=Snapp |first1=S. S. |last2=Swinton |first2=S. M. |last3=Labarta |first3=R. |last4=Mutch |first4=D. |last5=Black |first5=J. R. |last6=Leep |first6=R. |last7=Nyiraneza |first7=J. |last8=O'Neil |first8=K. |year=2005 |title=Evaluating cover crops for benefits, costs and performance within cropping system niches |journal=Agron. J. |volume=97 |issue=1 |pages=1–11 |doi=10.2134/agronj2005.0322a|bibcode=2005AgrJ...97..322S }} | |||
*{{cite journal |last1=Thomsen |first1=I. K. |last2=Christensen |first2=B. T. |year=1999 |title=Nitrogen conserving potential of successive ryegrass catch crops in continuous spring barley |journal=Soil Use and Management |volume=15 |issue=3 |pages=195–200 |doi=10.1111/j.1475-2743.1999.tb00088.x |bibcode=1999SUMan..15..195T |s2cid=96397423}} | |||
== |
==External links== | ||
*, ''Cyclopedia of American Agriculture'', vol. 2, ed. by L. H. Bailey (1911). A short encyclopedia article, early primary source on varieties and uses of cover crops. | |||
*Blackshaw, R. E., J. R. Moyer, R. C. Doram, and A. L. Boswell. 2001. Yellow sweetclover, green manure, and its residues effectively suppress weeds during fallow. Weed Science 49:406-413. | |||
*Bohlool, B. B., J. K. Ladha, D. P. Garrity, and T. George. 1992. Biological nitrogen fixation for sustainable agriculture: A perspective. Plant and Soil (Historical Archive) 141:1-11. | |||
*Bugg, R. L., and C. Waddington. 1994. Using Cover Crops to Manage Arthropod Pests of Orchards - a Review. Agriculture Ecosystems & Environment 50:11-28. | |||
*Cederbaum, S. B., J. P. Carroll, and R. J. Cooper. 2004. Effects of alternative cotton agriculture on avian and arthropod populations. Conservation Biology 18:1272-1282. | |||
*CENR. 2000. Integrated Assessment of Hypoxia in the Northern Gulf of Mexico. National Science and Technology Council Committee on Environment and Natural Resources, Washington, DC. | |||
*Creamer, N. G., M. A. Bennett, B. R. Stinner, J. Cardina, and E. E. Regnier. 1996. Mechanisms of weed suppression in cover crop-based production systems. HortScience 31:410-413. | |||
*Dabney, S. M., J. A. Delgado, and D. W. Reeves. 2001. Using winter cover crops to improve soil quality and water quality. Communications in Soil Science and Plant Analysis 32:1221-1250. | |||
*Ditsch, D. C., and M. M. Alley. 1991. Nonleguminous Cover Crop Management for Residual N Recovery and Subsequent Crop Yields. Journal of Fertilizer Issues 8:6-13. | |||
*Everts, K. L. 2002. Reduced fungicide applications and host resistance for managing three diseases in pumpkin grown on a no-till cover crop. Plant dis 86:1134-1141. | |||
*Freemark, K. E., and D. A. Kirk. 2001. Birds on organic and conventional farms in Ontario: partitioning effects of habitat and practices on species composition and abundance. Biological Conservation 101:337-350. | |||
*Galloway, J. N., W. H. Schlesinger, H. Levy, A. Michaels, and J. L. Schnoor. 1995. Nitrogen-Fixation - Anthropogenic Enhancement-Environmental Response. Global Biogeochemical Cycles 9:235-252. | |||
*Giller, K. E., and G. Cadisch. 1995. Future benefits from biological nitrogen fixation: An ecological approach to agriculture. Plant and Soil (Historical Archive) 174:255-277. | |||
*Grafton-Cardwell, E. E., Y. L. Ouyang, and R. L. Bugg. 1999. Leguminous cover crops to enhance population development of Euseius tularensis (Acari : Phytoseiidae) in citrus. Biological Control 16:73-80. | |||
*Haramoto, E. R., and E. R. Gallandt. 2004. Brassica cover cropping for weed management: A review. Renewable Agriculture and Food Systems 19:187-198. | |||
*Jensen, E. S., and H. Hauggaard-Nielsen. 2003. How can increased use of biological N-2 fixation in agriculture benefit the environment? Plant and Soil 252:177-186. | |||
*Joyce, B. A., W. W. Wallender, J. P. Mitchell, L. M. Huyck, S. R. Temple, P. N. Brostrom, and T. C. Hsiao. 2002. Infiltration and soil water storage under winter cover cropping in California's Sacramento Valley. Transactions of the Asae 45:315-326. | |||
*Kobayashi, Y., M. Ito, and K. Suwanarak. 2003. Evaluation of smothering effect of four legume covers on Pennisetum polystachion ssp. setosum (Swartz) Brunken. Weed Biology and Management 3:222-227. | |||
*Kuepper, G., and R. Thomas. 2002. "Bug vacuums" for organic crop protection. ATTRA, Fayetteville, AR. | |||
*Kuo, S., U. M. Sainju, and E. J. Jellum. 1997. Winter cover crop effects on soil organic carbon and carbohydrate in soil. Soil Science Society of America Journal 61:145-152. | |||
*Lal, R. 2003. Offsetting global CO2 emissions by restoration of degraded soils and intensification of world agriculture and forestry. Land Degradation & Development 14:309-322. | |||
*Lazzeri, L., and L. M. Manici. 2001. Allelopathic effect of glucosinolate-containing plant green manure on Pythium sp and total fungal population in soil. Hortscience 36:1283-1289. | |||
*Lu, Y. C., K. B. Watkins, J. R. Teasdale, and A. A. Abdul-Baki. 2000. Cover crops in sustainable food production. Food Reviews International 16:121-157. | |||
*Morgan, M. F., H. G. M. Jacobson, and S. B. LeCompte. 1942. Drainage water losses from a sandy soil as affected by cropping and cover crops : Windsor lysimeter series c. Connecticut Agricultural Experiment Station, 1942. p. -759 : ill., . | |||
*Nagabhushana, G. G., A. D. Worsham, and J. P. Yenish. 2001. Allelopathic cover crops to reduce herbicide use in sustainable agricultural systems. Allelopathy Journal 8:133-146. | |||
*New Farm, The. Plans for no-till cover crop roller free for the downloading. | |||
*Patrick, W. H., C. B. Haddon, and J. A. Hendrix. 1957. The effects of longtime use of winter cover crops on certain physical properties of commerce loam. Soil Science Society of America 21:366-368. | |||
*Peoples, M. B., and E. T. Craswell. 1992. Biological nitrogen fixation: Investments, expectations and actual contributions to agriculture. Plant and Soil (Historical Archive) 141:13-39. | |||
*Potter, M. J., K. Davies, and A. J. Rathjen. 1998. Suppressive impact of glucosinolates in Brassica vegetative tissues on root lesion nematode Pratylenchus neglectus. Journal of Chemical Ecology 24:67-80. | |||
*Rabalais, N. N., R. E. Turner, and W. J. Wiseman. 2002. Gulf of Mexico hypoxia, aka "The dead zone". Annual Review of Ecology and Systematics 33:235-263. | |||
*Romkens, M. J. M., S. N. Prasad, and F. D. Whisler. 1990. Surface sealing and infiltration. Pages 127-172 in M. G. Anderson and T. P. Butt, editors. Process studies in hillslope hydrology. John Wiley and Sons, Ltd. | |||
*Sainju, U. M., B. P. Singh, and W. F. Whitehead. 2002. Long-term effects of tillage, cover crops, and nitrogen fertilization on organic carbon and nitrogen concentrations in sandy loam soils in Georgia, USA. Soil & Tillage Research 63:167-179. | |||
*Shelton, A. M., and E. Badenes-Perez. 2006. Concepts and applications of trap cropping in pest management. Annual Review of Entomology 51:285-308. | |||
*Singh, H. P., D. R. Batish, and R. K. Kohli. 2003. Allelopathic interactions and allelochemicals: New possibilities for sustainable weed management. Critical Reviews in Plant Sciences 22:239-311. | |||
*Snapp, S. S., S. M. Swinton, R. Labarta, D. Mutch, J. R. Black, R. Leep, J. Nyiraneza, and K. O'Neil. 2005. Evaluating cover crops for benefits, costs and performance within cropping system niches. Agron. J. 97:1-11. | |||
*Teasdale, J. R. 1993. Interaction of light, soil moisture, and temperature with weed suppression by hairy vetch residue. Weed sci 41:46-51. | |||
*Thiessen-Martens, J. R., M. H. Entz, and J. W. Hoeppner. 2005. Legume cover crops with winter cereals in southern Manitoba: Fertilizer replacement values for oat. Canadian Journal of Plant Science 85:645-648. | |||
*Thomsen, I. K., and B. T. Christensen. 1999. Nitrogen conserving potential of successive ryegrass catch crops in continuous spring barley. Soil Use and Management 15:195-200. | |||
*Thorup-Kristensen, K., J. Magid, and L. S. Jensen. 2003. Catch crops and green manures as biological tools in nitrogen management in temperate zones. Pages 227-302 in Advances in Agronomy, Vol 79. ACADEMIC PRESS INC, San Diego. | |||
*Tomlin, A. D., M. J. Shipitalo, W. M. Edwards, and R. Protz. 1995. Earthworms and their influence on soil structure and infiltration. Pages 159-183 in P. F. Hendrix, editor. Earthworm Ecology and Biogeography in North America. Lewis Pub., Boca Raton, FL. | |||
*Vanlauwe, B., O. C. Nwoke, J. Diels, N. Sanginga, R. J. Carsky, J. Deckers, and R. Merckx. 2000. Utilization of rock phosphate by crops on a representative toposequence in the Northern Guinea savanna zone of Nigeria: response by Mucuna pruriens, Lablab purpureus and maize. Soil Biology & Biochemistry 32:2063-2077. | |||
*Vargas-Ayala, R., R. Rodriguez-Kabana, G. Morgan-Jones, J. A. McInroy, and J. W. Kloepper. 2000. Shifts in soil microflora induced by velvetbean (Mucuna deeringiana) in cropping systems to control root-knot nematodes. Biological Control 17:11-22. | |||
*Zalom, F. G., P. A. Phillips, N. C. Toscano, and S. Udayagiri. 2001. UC Pest Management Guidelines: Strawberry: Lygus Bug. University of California Department of Agriculture and Natural Resources, Berkeley, CA. | |||
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Latest revision as of 13:35, 27 September 2024
Crop planted to manage erosion and soil qualityIn agriculture, cover crops are plants that are planted to cover the soil rather than for the purpose of being harvested. Cover crops manage soil erosion, soil fertility, soil quality, water, weeds, pests, diseases, biodiversity and wildlife in an agroecosystem—an ecological system managed and shaped by humans. Cover crops can increase microbial activity in the soil, which has a positive effect on nitrogen availability, nitrogen uptake in target crops, and crop yields. Cover crops reduce water pollution risks and remove CO2 from the atmosphere. Cover crops may be an off-season crop planted after harvesting the cash crop. Cover crops are nurse crops in that they increase the survival of the main crop being harvested, and are often grown over the winter. In the United States, cover cropping may cost as much as $35 per acre.
Soil erosion
Main article: ErosionAlthough cover crops can perform multiple functions in an agroecosystem simultaneously, they are often grown for the sole purpose of preventing soil erosion. Soil erosion is a process that can irreparably reduce the productive capacity of an agroecosystem. Cover crops reduce soil loss by improving soil structure and increasing infiltration, protecting the soil surface, scattering raindrop energy, and reducing the velocity of the movement of water over the soil surface. Dense cover crop stands physically slow down the velocity of rainfall before it contacts the soil surface, preventing soil splashing and erosive surface runoff. Additionally, vast cover crop root networks help anchor the soil in place and increase soil porosity, producing suitable habitat networks for soil macrofauna. It keeps the enrichment of the soil good for the next few years.
Soil fertility management
Main article: Green manureOne of the primary uses of cover crops is to increase soil fertility. These types of cover crops are referred to as "green manure". They are used to manage a range of soil macronutrients and micronutrients. Of the various nutrients, the impact that cover crops have on nitrogen management has received the most attention from researchers and farmers because nitrogen is often the most limiting nutrient in crop production.
Often, green manure crops are grown for a specific period, and then plowed under before reaching full maturity to improve soil fertility and quality. The stalks left block the soil from being eroded.
Green manure crops are commonly leguminous, meaning they are part of the pea family, Fabaceae. This family is unique in that all of the species in it set pods, such as bean, lentil, lupins and alfalfa. Leguminous cover crops are typically high in nitrogen and can often provide the required quantity of nitrogen for crop production. In conventional farming, this nitrogen is typically applied in chemical fertilizer form. In organic farming, nitrogen inputs may take the form of organic fertilizers, compost, cover crop seed, and fixation by legume cover crops. This quality of cover crops is called fertilizer replacement value.
Another quality unique to leguminous cover crops is that they form symbiotic relationships with the rhizobial bacteria that reside in legume root nodules. Lupins is nodulated by the soil microorganism Bradyrhizobium sp. (Lupinus). Bradyrhizobia are encountered as microsymbionts in other leguminous crops (Argyrolobium, Lotus, Ornithopus, Acacia, Lupinus) of Mediterranean origin. These bacteria convert biologically unavailable atmospheric nitrogen gas (N
2) to biologically available ammonium (NH
4) through the process of biological nitrogen fixation. In general, cover crops increase soil microbial activity, which has a positive effect on nitrogen availability in the soil, nitrogen uptake in target crops, and crop yields.
Prior to the advent of the Haber–Bosch process, an energy-intensive method developed to carry out industrial nitrogen fixation and create chemical nitrogen fertilizer, most nitrogen introduced to ecosystems arose through biological nitrogen fixation. Some scientists believe that widespread biological nitrogen fixation, achieved mainly through the use of cover crops, is the only alternative to industrial nitrogen fixation in the effort to maintain or increase future food production levels. Industrial nitrogen fixation has been criticized as an unsustainable source of nitrogen for food production due to its reliance on fossil fuel energy and the environmental impacts associated with chemical nitrogen fertilizer use in agriculture. Such widespread environmental impacts include nitrogen fertilizer losses into waterways, which can lead to eutrophication (nutrient loading) and ensuing hypoxia (oxygen depletion) of large bodies of water.
An example of this is in the Mississippi Valley Basin, where years of fertilizer nitrogen loading into the watershed from agricultural production have resulted in an annual summer hypoxic "dead zone" off the Gulf of Mexico that reached an area of over 22,000 square kilometers in 2017. The ecological complexity of marine life in this zone has been diminishing as a consequence.
As well as bringing nitrogen into agroecosystems through biological nitrogen fixation, types of cover crops known as "catch crops" are used to retain and recycle soil nitrogen already present. The catch crops take up surplus nitrogen remaining from fertilization of the previous crop, preventing it from being lost through leaching, or gaseous denitrification or volatilization.
Catch crops are typically fast-growing annual cereal species adapted to scavenge available nitrogen efficiently from the soil. The nitrogen fixed in catch crop biomass is released back into the soil once the cash crop is incorporated as a green manure or otherwise begins to decompose.
An example of green manure use comes from Nigeria, where the cover crop Mucuna pruriens (velvet bean) has been found to increase the availability of phosphorus in soil after a farmer applies rock phosphate.
Soil quality management
Cover crops can also improve soil quality by increasing soil organic matter levels through the input of cover crop biomass over time. Increased soil organic matter enhances soil structure as well as the water and nutrient holding and buffering capacities of the soil. It can also lead to increased soil carbon sequestration, which has been promoted as a strategy to help offset the rise in atmospheric carbon dioxide levels.
Soil quality is managed to produce optimum conditions for crops to flourish. The principal factors affecting soil quality are soil salination, pH, microorganism balance, and the prevention of soil contamination. It is noted that if soil quality is properly managed and maintained, it forms the foundation for a healthy and productive environment. One can design and manage a crop that will produce a healthy environment for quite some time.
Water management
By reducing soil erosion, cover crops often also reduce both the rate and quantity of water that drains off the field, which would normally pose environmental risks to waterways and ecosystems downstream. Cover crop biomass acts as a physical barrier between rainfall and the soil surface, allowing raindrops to steadily trickle down through the soil profile. Also, as stated above, cover crop root growth results in the formation of soil pores, which, in addition to enhancing soil macrofauna habitat provides pathways for water to filter through the soil profile rather than draining off the field as surface flow. With increased water infiltration, the potential for soil water storage and the recharge of aquifers can be improved.
Just before cover crops are killed (by such practices including mowing, tilling, discing, rolling, or herbicide application) they contain a large amount of moisture. When the cover crop is incorporated into the soil, or left on the soil surface, it often increases soil moisture. In agroecosystems where water for crop production is in short supply, cover crops can be used as a mulch to conserve water by shading and cooling the soil surface. This reduces the evaporation of soil moisture and helps preserve soil nutrients.
Weed management
Thick cover crop stands often compete well with weeds during the cover crop growth period, and can prevent most germinated weed seeds from completing their life cycle and reproducing. If the cover crop is flattened down on the soil surface rather than incorporated into the soil as a green manure after its growth is terminated, it can form a nearly impenetrable mat. This drastically reduces light transmittance to weed seeds, which in many cases reduces weed seed germination rates. Furthermore, even when weed seeds germinate, they often run out of stored energy for growth before building the necessary structural capacity to break through the cover crop mulch layer. This is often termed the cover crop smother effect.
Some cover crops suppress weeds both during growth and after death. During growth these cover crops compete vigorously with weeds for available space, light, and nutrients, and after death they smother the next flush of weeds by forming a mulch layer on the soil surface. For example, researchers found that when using Melilotus officinalis (yellow sweetclover) as a cover crop in an improved fallow system (where a fallow period is intentionally improved by any number of different management practices, including the planting of cover crops), weed biomass only constituted between 1–12% of total standing biomass at the end of the cover crop growing season. Furthermore, after cover crop termination, the yellow sweetclover residues suppressed weeds to levels 75–97% lower than in fallow (no yellow sweetclover) systems.
In addition to competition-based or physical weed suppression, certain cover crops are known to suppress weeds through allelopathy. This occurs when certain biochemical cover crop compounds are degraded that happen to be toxic to, or inhibit seed germination of, other plant species. Some well known examples of allelopathic cover crops are Secale cereale (rye), Vicia villosa (hairy vetch), Trifolium pratense (red clover), Sorghum bicolor (sorghum-sudangrass), and species in the family Brassicaceae, particularly mustards. In one study, rye cover crop residues were found to have provided between 80% and 95% control of early season broadleaf weeds when used as a mulch during the production of different cash crops such as soybean, tobacco, corn, and sunflower. In general, cover crops need not compete with cash crops, as they can be grown and terminated early on the season before other crops are established.
In a 2010 study released by the Agricultural Research Service (ARS), scientists examined how rye seeding rates and planting patterns affected cover crop production. The results show that planting more pounds per acre of rye increased the cover crop's production as well as decreased the amount of weeds. The same was true when scientists tested seeding rates on legumes and oats; a higher density of seeds planted per acre decreased the amount of weeds and increased the yield of legume and oat production. The planting patterns, which consisted of either traditional rows or grid patterns, did not seem to have a significant impact on the cover crop's production or on the weed production in either cover crop. The ARS scientists concluded that increased seeding rates could be an effective method of weed control.
Cornell University's Sustainable Cropping Systems Lab released a study in May 2023 investigating the effectiveness of time-sensitive planting and strategic coupling of cover crop variants with phylogenetically similar cash crops. The primary researcher, Uriel Menalled, discovered that if cover and cash crops are planted in accordance with his research findings, farmers can decrease weed growth by up to 99%. The study provides farmers with a comprehensive framework to identify cover crops that would best suit their existing cropping rotations. In sum, the results from this study support an understanding that phylogenetic relatedness can be harnessed to significantly suppress weed growth.
Disease management
In the same way that allelopathic properties of cover crops can suppress weeds, they can also break disease cycles and reduce populations of bacterial and fungal diseases, and parasitic nematodes. Species in the family Brassicaceae, such as mustards, have been widely shown to suppress fungal disease populations through the release of naturally occurring toxic chemicals during the degradation of glucosinolate compounds in their plant cell tissues.
Pest management
Some cover crops are used as so-called "trap crops", to attract pests away from the crop of value and toward what the pest sees as a more favorable habitat. Trap crop areas can be established within crops, within farms, or within landscapes. In many cases, the trap crop is grown during the same season as the food crop being produced. The limited area occupied by these trap crops can be treated with a pesticide once pests are drawn to the trap in large enough numbers to reduce pest populations. In some organic systems, farmers drive over the trap crop with a large vacuum-based implement to physically pull the pests off the plants and out of the field. This system has been recommended for use to help control the lygus bugs in organic strawberry production. Another example of trap crops is nematode-resistant white mustard (Sinapis alba) and radish (Raphanus sativus). They can be grown after a main (cereal) crop and trap nematodes, for example, the beet cyst nematode and the Columbian root knot nematode. When grown, nematodes hatch and are attracted to the roots. After entering the roots they cannot reproduce in the root due to a hypersensitive resistance reaction of the plant. Hence the nematode population is greatly reduced, by 70–99%, depending on species and cultivation time.
Other cover crops are used to attract natural predators of pests by imitating elements of their habitat. This is a form of biological control known as habitat augmentation, but achieved with the use of cover crops. Findings on the relationship between cover crop presence and predator–pest population dynamics have been mixed, suggesting the need for detailed information on specific cover crop types and management practices to best complement a given integrated pest management strategy. For example, the predator mite Euseius tularensis (Congdon) is known to help control the pest citrus thrips in Central California citrus orchards. Researchers found that the planting of several different leguminous cover crops (such as bell bean, woollypod vetch, New Zealand white clover, and Austrian winter pea) provided sufficient pollen as a feeding source to cause a seasonal increase in E. tularensis populations, which with good could potentially introduce enough predatory pressure to reduce pest populations of citrus thrips.
Biodiversity and wildlife
Although cover crops are normally used to serve one of the above discussed purposes, they often serve as habitat for wildlife. The use of cover crops adds at least one more dimension of plant diversity to a cash crop rotation. Since the cover crop is typically not a crop of value, its management is usually less intensive, providing a window of "soft" human influence on the farm. This relatively "hands-off" management, combined with the increased on-farm heterogeneity produced by the establishment of cover crops, increases the likelihood that a more complex trophic structure will develop to support a higher level of wildlife diversity.
In one study, researchers compared arthropod and songbird species composition and field use between conventionally and cover cropped cotton fields in the Southern United States. The cover cropped cotton fields were planted to clover, which was left to grow in between cotton rows throughout the early cotton growing season (stripcover cropping). During the migration and breeding season, they found that songbird densities were 7–20 times higher in the cotton fields with an integrated clover cover crop than in the conventional cotton fields. Arthropod abundance and biomass was also higher in the clover c-cover fields throughout much of the songbird breeding season, which was attributed to an increased supply of flower nectar from the clover. The clover cover crop enhanced songbird habitat by providing covering sites, and an increased food source from higher arthropod populations.
See also
- Agroecology
- Allelopathy
- Biological control
- Green manure
- Ground cover
- Nitrogen cycle
- Nitrogen fixation
- Organic matter
- Soil contamination
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- Zalom, F. G.; Phillips, P. A.; Toscano, N. C.; Udayagiri, S. (2001). UC Pest Management Guidelines: Strawberry: Lygus Bug (Report). Berkeley, CA: University of California Department of Agriculture and Natural Resources.
- Lelivelt, C. L. C.; Leunissen, E. H. M.; Frederiks, H. J.; Helsper, J. P. F. G.; Krens, F. A. (1993-02-01). "Transfer of resistance to the beet cyst nematode (Heterodera Schachtii Schm.) from Sinapis alba L. (white mustard) to the Brassica napus L. gene pool by means of sexual and somatic hybridization". Theoretical and Applied Genetics. 85 (6–7): 688–696. doi:10.1007/BF00225006. ISSN 0040-5752. PMID 24196037. S2CID 22433897.
- Smith, Heidi J.; Gray, Fred A.; Koch, David W. (2004-06-01). "Reproduction of Heterodera schachtii Schmidt on Resistant Mustard, Radish, and Sugar Beet Cultivars". Journal of Nematology. 36 (2): 123–130. ISSN 0022-300X. PMC 2620762. PMID 19262796.
- Teklu, Misghina G.; Schomaker, Corrie H.; Been, Thomas H. (2014-05-28). "Relative susceptibilities of five fodder radish varieties (Raphanus sativus var. Oleiformis) to Meloidogyne chitwoodi". Nematology. 16 (5): 577–590. doi:10.1163/15685411-00002789. ISSN 1568-5411.
- Bugg, R. L.; Waddington, C. (1994). "Using Cover Crops to Manage Arthropod Pests of Orchards - a Review". Agriculture, Ecosystems & Environment. 50 (1): 11–28. Bibcode:1994AgEE...50...11B. doi:10.1016/0167-8809(94)90121-x.
- Grafton-Cardwell, E. E.; Ouyang, Y. L.; Bugg, R. L. (1999). "Leguminous cover crops to enhance population development of Euseius tularensis (Acari : Phytoseiidae) in citrus". Biological Control. 16 (1): 73–80. Bibcode:1999BiolC..16...73G. doi:10.1006/bcon.1999.0732.
- Freemark, K. E.; Kirk, D. A. (2001). "Birds on organic and conventional farms in Ontario: partitioning effects of habitat and practices on species composition and abundance". Biological Conservation. 101 (3): 337–350. Bibcode:2001BCons.101..337F. doi:10.1016/s0006-3207(01)00079-9.
- Cederbaum, S. B.; Carroll, J. P.; Cooper, R. J. (2004). "Effects of alternative cotton agriculture on avian and arthropod populations". Conservation Biology. 18 (5): 1272–1282. Bibcode:2004ConBi..18.1272C. doi:10.1111/j.1523-1739.2004.00385.x. S2CID 84945560.
Further reading
- SARE National. Topic: Cover Crops.
- Midwest Cover Crops Council. Resources for growers, researchers, and educators.
- Clark, Andy, ed. (2007). Managing Cover Crops Profitably (PDF) (3rd ed.). Beltsville, Maryland: Sustainable Agriculture Network.
- Giller, K. E.; Cadisch, G. (1995). "Future benefits from biological nitrogen fixation: An ecological approach to agriculture". Plant and Soil. 174 (1–2): 255–277. Bibcode:1995PlSoi.174..255G. doi:10.1007/bf00032251. S2CID 24604997.
- Hartwig, N. L.; Ammon, H. U. (2002). "50th Anniversary - Invited article - Cover crops and living mulches". Weed Science. 50 (6): 688–699. doi:10.1614/0043-1745(2002)050[0688:aiacca]2.0.co;2. S2CID 86045745.
- Hill, E. C.; Ngouajio, M.; Nair, M. G. (2006). "Differential responses of weeds and vegetable crops to aqueous extracts of hairy vetch and cowpea". HortScience. 31 (3): 695–700. doi:10.21273/HORTSCI.41.3.695.
- Lu, Y. C.; Watkins, K. B.; Teasdale, J. R.; Abdul-Baki, A. A. (2000). "Cover crops in sustainable food production". Food Reviews International. 16 (2): 121–157. doi:10.1081/fri-100100285. S2CID 28356685.
- Snapp, S. S.; Swinton, S. M.; Labarta, R.; Mutch, D.; Black, J. R.; Leep, R.; Nyiraneza, J.; O'Neil, K. (2005). "Evaluating cover crops for benefits, costs and performance within cropping system niches". Agron. J. 97 (1): 1–11. Bibcode:2005AgrJ...97..322S. doi:10.2134/agronj2005.0322a.
- Thomsen, I. K.; Christensen, B. T. (1999). "Nitrogen conserving potential of successive ryegrass catch crops in continuous spring barley". Soil Use and Management. 15 (3): 195–200. Bibcode:1999SUMan..15..195T. doi:10.1111/j.1475-2743.1999.tb00088.x. S2CID 96397423.
External links
- "Cover Crops", Cyclopedia of American Agriculture, vol. 2, ed. by L. H. Bailey (1911). A short encyclopedia article, early primary source on varieties and uses of cover crops.