Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska
- Autores
- Wingeyer, Ana Beatriz; Mamo, Martha; Schacht, Walter; McCallister, Dennis; Sutton, Pamela
- Año de publicación
- 2018
- Idioma
- inglés
- Tipo de recurso
- artículo
- Estado
- versión publicada
- Descripción
- As a precautionary principle, the National Pollutant Discharge Elimination System (NPDES) permit establishes that the primary pollutant in concrete grinding residue (CGR) is its alkalinity and restricts CGR roadside discharge to 11 Mg ha-1 or the agronomic liming rate, whichever is lower. We evaluated the effect of CGR application on roadside soil chemical properties, existing vegetation, and rainfall runoff. Five CGR rates (0, 11, 22, 45, and 90 dry Mg ha-1) were tested on roadsides slopes at two different locations in eastern Nebraska. Vegetation, soil, and runoff characteristics were evaluated before CGR application and 30 d and 1 yr after CGR application. Soil pH of control plots averaged 8.3 and 8.5 for each site respectively, across depths and slope positions, thus not requiring any liming for agronomic purposes. Soil electrical conductivity (EC, 1:1) averages of control plots were 0.79 and 1.24 dS m-1 across depths and slope positions. In the short term (30 d) the highest CGR application affected the 0- to 7.5-cm soil depth by increasing soil extractable Ca (21 and 25% for each site, respectively), soil pH (0.2, south site), and soil EC (0.2 dS m-1) compared with the control. However, these changes in soil did not persist 1 yr after CGR application. The pH buffering capacity of soil prevented post-CGR-application pH from exceeding 8.9, even at the highest application rate. Application of CGR did not produce any differences in biomass production, botanical composition, and runoff characteristics at either site. From our study, CGR up to ~90 dry Mg ha-1-about the amount produced during diamond grinding operations-can be one-time applied to roadside soils of similar characteristics on already established vegetation.
Fil: Wingeyer, Ana Beatriz. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Entre Ríos. Estación Experimental Agropecuaria Paraná; Argentina
Fil: Mamo, Martha. University of Nebraska; Estados Unidos
Fil: Schacht, Walter. University of Nebraska; Estados Unidos
Fil: McCallister, Dennis. University of Nebraska; Estados Unidos
Fil: Sutton, Pamela. University of Nebraska; Estados Unidos - Materia
-
Concrete Grinding Residue Application
Soil pollution
Vegetation response
Runoff - Nivel de accesibilidad
- acceso abierto
- Condiciones de uso
- https://creativecommons.org/licenses/by-nc-sa/2.5/ar/
- Repositorio
.jpg)
- Institución
- Consejo Nacional de Investigaciones Científicas y Técnicas
- OAI Identificador
- oai:ri.conicet.gov.ar:11336/98856
Ver los metadatos del registro completo
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Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraskaWingeyer, Ana BeatrizMamo, MarthaSchacht, WalterMcCallister, DennisSutton, PamelaConcrete Grinding Residue ApplicationSoil pollutionVegetation responseRunoffhttps://purl.org/becyt/ford/4.1https://purl.org/becyt/ford/4As a precautionary principle, the National Pollutant Discharge Elimination System (NPDES) permit establishes that the primary pollutant in concrete grinding residue (CGR) is its alkalinity and restricts CGR roadside discharge to 11 Mg ha-1 or the agronomic liming rate, whichever is lower. We evaluated the effect of CGR application on roadside soil chemical properties, existing vegetation, and rainfall runoff. Five CGR rates (0, 11, 22, 45, and 90 dry Mg ha-1) were tested on roadsides slopes at two different locations in eastern Nebraska. Vegetation, soil, and runoff characteristics were evaluated before CGR application and 30 d and 1 yr after CGR application. Soil pH of control plots averaged 8.3 and 8.5 for each site respectively, across depths and slope positions, thus not requiring any liming for agronomic purposes. Soil electrical conductivity (EC, 1:1) averages of control plots were 0.79 and 1.24 dS m-1 across depths and slope positions. In the short term (30 d) the highest CGR application affected the 0- to 7.5-cm soil depth by increasing soil extractable Ca (21 and 25% for each site, respectively), soil pH (0.2, south site), and soil EC (0.2 dS m-1) compared with the control. However, these changes in soil did not persist 1 yr after CGR application. The pH buffering capacity of soil prevented post-CGR-application pH from exceeding 8.9, even at the highest application rate. Application of CGR did not produce any differences in biomass production, botanical composition, and runoff characteristics at either site. From our study, CGR up to ~90 dry Mg ha-1-about the amount produced during diamond grinding operations-can be one-time applied to roadside soils of similar characteristics on already established vegetation.Fil: Wingeyer, Ana Beatriz. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Entre Ríos. Estación Experimental Agropecuaria Paraná; ArgentinaFil: Mamo, Martha. University of Nebraska; Estados UnidosFil: Schacht, Walter. University of Nebraska; Estados UnidosFil: McCallister, Dennis. University of Nebraska; Estados UnidosFil: Sutton, Pamela. University of Nebraska; Estados UnidosAmerican Society of Agronomy2018-05info:eu-repo/semantics/articleinfo:eu-repo/semantics/publishedVersionhttp://purl.org/coar/resource_type/c_6501info:ar-repo/semantics/articuloapplication/pdfapplication/pdfhttp://hdl.handle.net/11336/98856Wingeyer, Ana Beatriz; Mamo, Martha; Schacht, Walter; McCallister, Dennis; Sutton, Pamela; Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska; American Society of Agronomy; Journal of Environmental Quality; 47; 3; 5-2018; 554-5610047-2425CONICET DigitalCONICETenginfo:eu-repo/semantics/altIdentifier/url/https://dl.sciencesocieties.org/publications/jeq/abstracts/47/3/554info:eu-repo/semantics/altIdentifier/doi/10.2134/jeq2017.11.0459info:eu-repo/semantics/openAccesshttps://creativecommons.org/licenses/by-nc-sa/2.5/ar/reponame:CONICET Digital (CONICET)instname:Consejo Nacional de Investigaciones Científicas y Técnicas2025-10-22T11:06:25Zoai:ri.conicet.gov.ar:11336/98856instacron:CONICETInstitucionalhttp://ri.conicet.gov.ar/Organismo científico-tecnológicoNo correspondehttp://ri.conicet.gov.ar/oai/requestdasensio@conicet.gov.ar; lcarlino@conicet.gov.arArgentinaNo correspondeNo correspondeNo correspondeopendoar:34982025-10-22 11:06:25.658CONICET Digital (CONICET) - Consejo Nacional de Investigaciones Científicas y Técnicasfalse |
| dc.title.none.fl_str_mv |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| title |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| spellingShingle |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska Wingeyer, Ana Beatriz Concrete Grinding Residue Application Soil pollution Vegetation response Runoff |
| title_short |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| title_full |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| title_fullStr |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| title_full_unstemmed |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| title_sort |
Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska |
| dc.creator.none.fl_str_mv |
Wingeyer, Ana Beatriz Mamo, Martha Schacht, Walter McCallister, Dennis Sutton, Pamela |
| author |
Wingeyer, Ana Beatriz |
| author_facet |
Wingeyer, Ana Beatriz Mamo, Martha Schacht, Walter McCallister, Dennis Sutton, Pamela |
| author_role |
author |
| author2 |
Mamo, Martha Schacht, Walter McCallister, Dennis Sutton, Pamela |
| author2_role |
author author author author |
| dc.subject.none.fl_str_mv |
Concrete Grinding Residue Application Soil pollution Vegetation response Runoff |
| topic |
Concrete Grinding Residue Application Soil pollution Vegetation response Runoff |
| purl_subject.fl_str_mv |
https://purl.org/becyt/ford/4.1 https://purl.org/becyt/ford/4 |
| dc.description.none.fl_txt_mv |
As a precautionary principle, the National Pollutant Discharge Elimination System (NPDES) permit establishes that the primary pollutant in concrete grinding residue (CGR) is its alkalinity and restricts CGR roadside discharge to 11 Mg ha-1 or the agronomic liming rate, whichever is lower. We evaluated the effect of CGR application on roadside soil chemical properties, existing vegetation, and rainfall runoff. Five CGR rates (0, 11, 22, 45, and 90 dry Mg ha-1) were tested on roadsides slopes at two different locations in eastern Nebraska. Vegetation, soil, and runoff characteristics were evaluated before CGR application and 30 d and 1 yr after CGR application. Soil pH of control plots averaged 8.3 and 8.5 for each site respectively, across depths and slope positions, thus not requiring any liming for agronomic purposes. Soil electrical conductivity (EC, 1:1) averages of control plots were 0.79 and 1.24 dS m-1 across depths and slope positions. In the short term (30 d) the highest CGR application affected the 0- to 7.5-cm soil depth by increasing soil extractable Ca (21 and 25% for each site, respectively), soil pH (0.2, south site), and soil EC (0.2 dS m-1) compared with the control. However, these changes in soil did not persist 1 yr after CGR application. The pH buffering capacity of soil prevented post-CGR-application pH from exceeding 8.9, even at the highest application rate. Application of CGR did not produce any differences in biomass production, botanical composition, and runoff characteristics at either site. From our study, CGR up to ~90 dry Mg ha-1-about the amount produced during diamond grinding operations-can be one-time applied to roadside soils of similar characteristics on already established vegetation. Fil: Wingeyer, Ana Beatriz. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina. Instituto Nacional de Tecnología Agropecuaria. Centro Regional Entre Ríos. Estación Experimental Agropecuaria Paraná; Argentina Fil: Mamo, Martha. University of Nebraska; Estados Unidos Fil: Schacht, Walter. University of Nebraska; Estados Unidos Fil: McCallister, Dennis. University of Nebraska; Estados Unidos Fil: Sutton, Pamela. University of Nebraska; Estados Unidos |
| description |
As a precautionary principle, the National Pollutant Discharge Elimination System (NPDES) permit establishes that the primary pollutant in concrete grinding residue (CGR) is its alkalinity and restricts CGR roadside discharge to 11 Mg ha-1 or the agronomic liming rate, whichever is lower. We evaluated the effect of CGR application on roadside soil chemical properties, existing vegetation, and rainfall runoff. Five CGR rates (0, 11, 22, 45, and 90 dry Mg ha-1) were tested on roadsides slopes at two different locations in eastern Nebraska. Vegetation, soil, and runoff characteristics were evaluated before CGR application and 30 d and 1 yr after CGR application. Soil pH of control plots averaged 8.3 and 8.5 for each site respectively, across depths and slope positions, thus not requiring any liming for agronomic purposes. Soil electrical conductivity (EC, 1:1) averages of control plots were 0.79 and 1.24 dS m-1 across depths and slope positions. In the short term (30 d) the highest CGR application affected the 0- to 7.5-cm soil depth by increasing soil extractable Ca (21 and 25% for each site, respectively), soil pH (0.2, south site), and soil EC (0.2 dS m-1) compared with the control. However, these changes in soil did not persist 1 yr after CGR application. The pH buffering capacity of soil prevented post-CGR-application pH from exceeding 8.9, even at the highest application rate. Application of CGR did not produce any differences in biomass production, botanical composition, and runoff characteristics at either site. From our study, CGR up to ~90 dry Mg ha-1-about the amount produced during diamond grinding operations-can be one-time applied to roadside soils of similar characteristics on already established vegetation. |
| publishDate |
2018 |
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2018-05 |
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article |
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publishedVersion |
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http://hdl.handle.net/11336/98856 Wingeyer, Ana Beatriz; Mamo, Martha; Schacht, Walter; McCallister, Dennis; Sutton, Pamela; Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska; American Society of Agronomy; Journal of Environmental Quality; 47; 3; 5-2018; 554-561 0047-2425 CONICET Digital CONICET |
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http://hdl.handle.net/11336/98856 |
| identifier_str_mv |
Wingeyer, Ana Beatriz; Mamo, Martha; Schacht, Walter; McCallister, Dennis; Sutton, Pamela; Vegetation and soil responses to concrete grinding residue application on highway roadsides of eastern nebraska; American Society of Agronomy; Journal of Environmental Quality; 47; 3; 5-2018; 554-561 0047-2425 CONICET Digital CONICET |
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eng |
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eng |
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info:eu-repo/semantics/altIdentifier/url/https://dl.sciencesocieties.org/publications/jeq/abstracts/47/3/554 info:eu-repo/semantics/altIdentifier/doi/10.2134/jeq2017.11.0459 |
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American Society of Agronomy |
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American Society of Agronomy |
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CONICET Digital (CONICET) - Consejo Nacional de Investigaciones Científicas y Técnicas |
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dasensio@conicet.gov.ar; lcarlino@conicet.gov.ar |
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