Data from: Afforestation mitigates soil nitrogen limitation by enhancing mineralization and lowering denitrification in central China
Data files
Mar 27, 2026 version files 71.84 KB
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README.md
8.70 KB
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Soil_Nitrogen_Transformation_Data.xlsx
63.14 KB
Abstract
Afforestation has profoundly altered soil nitrogen (N) transformation, particularly the key processes governing soil organic N and inorganic N dynamics, which determine soil N availability. However, the divergences in soil N transformation and the main influencing factors following different afforestation types have not been systematically clarified. Here, we examined soil net N mineralization rate (NMR), net nitrification rate (NNR), and potential denitrification rate (PDR) at 144 paired sampling sites by comparing different afforestation types (initial land use types and tree species) in central China. Afforestation significantly enhanced soil NMR, but lowered NNR and PDR, respectively, compared to non-afforested lands. Soil NMR and PDR responses to afforestation from cropland were more sensitive than those from shrubland. Notably, broadleaf afforestation (i.e., Quercus variabilis) had a stronger effect on altering NMR compared to coniferous afforestation (i.e., Platycladus orientalis) from cropland. These variations in soil NMR and NNR responses were primarily attributed to soil properties [e.g., soil organic nitrogen (SON), soil organic carbon (SOC), C: N ratio] across both non-afforested and afforested lands, whereas the main influencing factor for PDR shifted from microbial traits in non-afforested lands to soil properties in afforested lands. Although higher SON contents promoted soil NMR in afforested lands, significantly higher microbial biomass N in the afforested lands compared to non-afforested lands suggested intensified microbial inorganic N assimilation, which consequently constrained NNR and PDR relative to non-afforested lands, further avoiding N loss and N limitation. Our findings emphasized that afforestation types divergently influenced soil net N transformation rates with overall impacts on alleviating possible soil N constraints, thereby providing a theoretical basis for the regulation of soil N cycling under future afforestation and forest management.
DOI: https://doi.org/10.5061/dryad.m37pvmdhc
Description of the data and file structure
Data Description
This dataset contains measurements of soil nitrogen transformation rates, soil physicochemical properties, and microbial characteristics collected from central China. The study aimed to assess how different afforestation types influence soil nitrogen (N) cycling processes, particularly those governing soil N availability.
Experimental Efforts:
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Sample Collection: During October to November 2021, paired sampling surveys were conducted across four subbasins in central China. Non-afforested lands (i.e., cropland or shrubland) were paired with adjacent afforested lands dominated by coniferous trees (Platycladus orientalis, Pinus massoniana) and broad-leaved trees (Quercus variabilis).
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Sample Preparation: Six afforestation types were established in each subbasin:
(1) afforestation with P. orientalis from cropland;
(2) afforestation with P. massoniana from cropland;
(3) afforestation with Q. variabilis from cropland;
(4) afforestation with P. orientalis from shrubland;
(5) afforestation with P. massoniana from shrubland;
(6) afforestation with Q. variabilis from shrubland.Each type included three replicates, resulting in a total of 144 soil samples (4 subbasins × 6 afforestation types × 2 paired lands × 3 replicates).Radon Detection: Soil nitrogen transformation rates, physicochemical properties, microbial biomass, and enzyme activities were measured using standard ecological methods.
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Data Analysis: Nitrogen transformation rates were calculated and analyzed to evaluate differences between afforested and non-afforested lands.
Parameters Measured:
- Net N mineralization rate (NMR)
- Net nitrification rate (NNR)
- Potential denitrification rate (PDR)
- Soil physicochemical properties (e.g., SOC, SON, C:N ratio)
- Soil inorganic and organic nitrogen fractions (e.g., NH₄⁺–N, NO₃⁻–N, DON)
- Microbial biomass (MBC, MBN, MBP)
- Soil enzyme activities (BG, NAG, LAP, AP)
Applications:
The dataset supports studies on:
- Soil nitrogen cycling under afforestation
- Controls of N mineralization, nitrification, and denitrification
- Interactions among soil properties, microbial traits, and enzyme activities
- Ecological processes related to soil nutrient limitation and ecosystem functioning
Files and variables
File: Soil_Nitrogen_Transformation_Data.xlsx
Description:
Variables
File Description:This Excel file contains data collected from soil samples analyzed for nitrogen transformation rates and associated environmental variables across all sampling sites in central China.
Sheet 1: Soil Data
| Variable Name | Description | Units | Abbreviation |
|---|---|---|---|
| Plot name | Unique identifier for each sampling plot | - | - |
| Afforestation Plot | 4 subbasins | - | - |
| Afforestation types | Afforested or non-afforested lands | ||
| Initial land use types | Cropland or Shrubland | - | - |
| Afforestation Tree | Platycladus orientalis, Pinus massoniana and Quercus variabilis | - | - |
| Net N mineralization rate | Soil net nitrogen mineralization rate | mg·kg⁻¹·d⁻¹ | NMR |
| Net nitrification rate | Soil net nitrification rate | mg·kg⁻¹·d⁻¹ | NNR |
| Potential denitrification rate | Soil potential denitrification rate | μg·kg⁻¹·h⁻¹ | PDR |
| Soil moisture | Soil moisture content | % | SM |
| Soil temperature | Soil temperature | °C | ST |
| pH | Soil pH value | - | pH |
| Bulk density | Soil bulk density | g·cm⁻³ | BD |
| Soil organic carbon | Soil organic carbon content | g·kg⁻¹ | SOC |
| Total nitrogen | Soil total nitrogen | g·kg⁻¹ | TN |
| C:N ratio | Ratio of soil carbon to nitrogen | - | C:N |
| Dissolved organic nitrogen | Dissolved organic nitrogen | mg·kg⁻¹ | DON |
| Ammonium nitrogen | Ammonium nitrogen | mg·kg⁻¹ | NH₄⁺ |
| Nitrate nitrogen | Nitrate nitrogen | mg·kg⁻¹ | NO₃⁻ |
| Total phosphorus | Soil total phosphorus | g·kg⁻¹ | TP |
| β-1,4-glucosidase | Enzyme activity | nmol g -1 h -1 | BG |
| N-acetylglucosaminidase | Enzyme activity | nmol g -1 h -1 | NAG |
| Alkaline phosphatase | Enzyme activity | nmol g -1 h -1 | AP |
| L-leucine aminopeptidase | Enzyme activity | nmol g -1 h -1 | LAP |
| Microbial biomass carbon | Microbial biomass carbon | mg·kg⁻¹ | MBC |
| Microbial biomass nitrogen | Microbial biomass nitrogen | mg·kg⁻¹ | MBN |
| Microbial biomass phosphorus | Microbial biomass phosphorus | mg·kg⁻¹ | MBP |
| Leaf carbon | Carbon content in leaves | g·kg⁻¹ | LeafC |
| Leaf nitrogen | Nitrogen content in leaves | g·kg⁻¹ | LeafN |
| Litter carbon | Carbon content in litter | g·kg⁻¹ | LitterC |
| Litter nitrogen | Nitrogen content in litter | g·kg⁻¹ | LitterN |
| Root carbon | Carbon content in roots | g·kg⁻¹ | RootC |
| Root nitrogen | Nitrogen content in roots | g·kg⁻¹ | RootN |
| Litter mass | Litter biomass or mass | g·m⁻² | Litter |
Missing Values:
- Missing data, if any, are indicated by blank cells.
Code/software
Software Requirements:
- Microsoft Excel (Version 2010 or later) – To view and analyze the dataset
- Optional: R, Python, or SPSS for statistical analysis
