13 results match your criteria: "Soil Science Centre[Affiliation]"

Impacts of nitrogen fertilizer type and application rate on soil acidification rate under a wheat-maize double cropping system.

J Environ Manage

September 2020

Environmental Systems Analysis Group, Wageningen University, P.O. Box 47, 6700 AA, Wageningen, the Netherlands; Alterra-Wageningen UR, Soil Science Centre, P.O. Box 47, 6700 AA, Wageningen, the Netherlands.

Nitrogen (N) fertilizer-induced soil acidification in Chinese croplands is well-known, but insight in the impacts of different N fertilizer management approaches (fertilizer type and rate) on soil acidification rates is very limited. Here, we conducted a field experiment on a moderate acid soil to quantify soil acidification rates in response to N fertilization by different fertilizer types and N rates through monitoring the fate of elements (mainly nutrients) related to H production and consumption. Two N fertilizer types (urea and NHCl) and three N rates (control, optimized and conventional, 0/120/240 kg N ha for wheat, 0/160/320 kg N ha for maize) were included.

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Enhanced acidification in Chinese croplands as derived from element budgets in the period 1980-2010.

Sci Total Environ

March 2018

College of Resources and Environmental Sciences, Centre for Resources, Environment and Food Security, Key Lab of Plant-Soil Interactions, MOE, China Agricultural University, Beijing 100193, China.

Significant soil pH decrease has been reported in Chinese croplands in response to enhanced chemical fertilizer application and crop yields. However, the temporal and spatial variation of soil acidification rates across Chinese croplands is still unclear. We therefore assessed trends in soil acidification rates across provincial China for the period 1980-2010 by calculating inputs-outputs of major cations and anions in cropland systems.

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Modeling soil acidification in typical Chinese cropping systems.

Sci Total Environ

February 2018

Environmental Systems Analysis Group, Wageningen University, PO Box 47, 6700 AA Wageningen, The Netherlands; Alterra-Wageningen UR, Soil Science Centre, P.O. Box 47, 6700 AA Wageningen, The Netherlands. Electronic address:

We applied the adapted model VSD+ to assess cropland acidification in four typical Chinese cropping systems (single Maize (M), Wheat-Maize (W-M), Wheat-Rice (W-R) and Rice-Rice (R-R)) on dominant soils in view of its potential threat to grain production. By considering the current situation and possible improvements in field (nutrient) management, five scenarios were designed: i) Business as usual (BAU); ii) No nitrogen (N) fertilizer increase after 2020 (N2020); iii) 100% crop residues return to cropland (100%RR); iv) manure N was applied to replace 30% of chemical N fertilizer (30%MR) and v) Integrated N2020 and 30%MR with 100%RR after 2020 (INMR). Results illustrated that in the investigated calcareous soils, the calcium carbonate buffering system can keep pH at a high level for >150years.

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Model-Based Analysis of the Long-Term Effects of Fertilization Management on Cropland Soil Acidification.

Environ Sci Technol

April 2017

College of Resources and Environmental Sciences, Centre for Resources, Environment and Food Security, Key Lab of Plant-Soil Interactions, MOE, China Agricultural University, Beijing 100193, China.

Agricultural soil acidification in China is known to be caused by the over-application of nitrogen (N) fertilizers, but the long-term impacts of different fertilization practices on intensive cropland soil acidification are largely unknown. Here, we further developed the soil acidification model VSD+ for intensive agricultural systems and validated it against observed data from three long-term fertilization experiments in China. The model simulated well the changes in soil pH and base saturation over the last 20 years.

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Modeling diffusive Cd and Zn contaminant emissions from soils to surface waters.

J Contam Hydrol

September 2012

Soil Science Centre, Alterra, Wageningen-UR, PO Box 47, 6700 AA Wageningen, The Netherlands.

Modeling contaminant transport of diffusive contaminants is generally difficult, as most contaminants are located in the top soil where soil properties will vary strongly with depth and often a strong gradient in contaminant concentrations exists. When groundwater periodically penetrates the contaminated layers, stationary models (like most 3D models) cannot adequately describe contaminant transport. Therefore we have combined a hydrological instationary model using a 1D distributed column approach with a simple geochemical model to describe contaminant transport in the soil.

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Various dynamic soil chemistry models have been developed to gain insight into impacts of atmospheric deposition of sulphur, nitrogen and other elements on soil and soil solution chemistry. Sorption parameters for anions and cations are generally calibrated for each site, which hampers extrapolation in space and time. On the other hand, recently developed surface complexation models (SCMs) have been successful in predicting ion sorption for static systems using generic parameter sets.

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Element fluxes through forest ecosystems are generally based on measurements of concentrations in soil solution at regular time intervals at plot locations sampled in a regular grid. Here we present spatially averaged annual element leaching fluxes in three Dutch forest monitoring plots using a new sampling strategy in which both sampling locations and sampling times are selected by probability sampling. Locations were selected by stratified random sampling with compact geographical blocks of equal surface area as strata.

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Ion binding models such as the nonideal competitive adsorption-Donnan model (NICA-Donnan) and model VI successfully describe laboratory data of proton and metal binding to purified humic substances (HS). In this study model performance was tested in more complex natural systems. The speciation predicted with the NICA-Donnan model and the associated uncertainty were compared with independent measurements in soil solution extracts, including the free metal ion activity and fulvic (FA) and humic acid (HA) fractions of dissolved organic matter (DOM).

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Evaluation of approaches to calculate critical metal loads for forest ecosystems.

Environ Pollut

December 2009

Alterra, Wageningen University and Research Centre, Soil Science Centre, Droevendaalse steeg 3, PO Box 47, 6700AA Wageningen, The Netherlands.

This paper evaluates approaches to calculate acceptable loads for metal deposition to forest ecosystems, distinguishing between critical loads, stand-still loads and target loads. We also evaluated the influence of including the biochemical metal cycle on the calculated loads. Differences are illustrated by examples of Cd, Cu, Pb and Zn for a deciduous forest on five major soil types in the Netherlands.

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Soil biological studies are often conducted on sieved soils without the presence of plants. However, soil fungi build delicate mycelial networks, often symbiotically associated with plant roots (mycorrhizal fungi). We hypothesized that as a result of sieving and incubating without plants, the total fungal biomass decreases.

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Phosphorus workshop.

J Environ Qual

January 2006

Soil Science Centre, Wageningen University, and Research Centre, the Netherlands.

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Effect of storm events on benthic nitrifying activity.

Appl Environ Microbiol

October 1983

Water and Soil Science Centre, Ministry of Works and Development, Hamilton, New Zealand.

Storm events resulted in a marked reduction in the benthic nitrifying activity of a stream receiving geothermal inputs of ammonium. Subsequently, nitrifying activity demonstrated a logarithmic increase until a stable activity was reached 10 to 12 days after the storm event. The rate of increase of poststorm nitrifying activity was used to calculate the nitrifier growth rate in situ (0.

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Population ecology of nitrifiers in a stream receiving geothermal inputs of ammonium.

Appl Environ Microbiol

April 1983

Water and Soil Science Centre, Ministry of Works and Development, Hamilton, New Zealand.

The distribution, activity, and generic diversity of nitrifying bacteria in a stream receiving geothermal inputs of ammonium were studied. The high estimated rates of benthic nitrate flux (33 to 75 mg of N . m .

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