Nothing Special   »   [go: up one dir, main page]

You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline
remove_circle_outline

Search Results (654)

Search Parameters:
Keywords = non-point source pollution

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
13 pages, 2222 KiB  
Article
Introducing Ferrous Sulfate to Cattle Manure and Corn Straw Composting Reduces Greenhouse Gas Emissions and Ammonia Volatilization
by Yucong Geng, Muhammad Amjad Bashir, Hongyuan Wang, Jungai Li, Qurat-Ul-Ain Raza, Weijie Kan, Shuo Tian, Abdur Rehim, Longcheng Yang and Hongbin Liu
Agronomy 2024, 14(12), 2867; https://doi.org/10.3390/agronomy14122867 - 1 Dec 2024
Viewed by 271
Abstract
Composting is a well-known method for waste management, but it causes greenhouse gas emissions. Various techniques have been used to reduce emissions and improve the quality of compost, but they resulted in an increased composting time. Keeping in view the above points, the [...] Read more.
Composting is a well-known method for waste management, but it causes greenhouse gas emissions. Various techniques have been used to reduce emissions and improve the quality of compost, but they resulted in an increased composting time. Keeping in view the above points, the current study aimed to reduce the composting time and gas emissions along with improving the nutritional value of compost using FeSO4 as an additive to cattle manure and corn straw composting. Seven treatments were established, including control (CK) without FeSO4 and six levels of FeSO4 (0.25%, 0.50%, 1%, 2%, 4%, 8%). The results revealed that FeSO4 reduced the CH4 (36.1–36.7%), H2S (10.7–34.5%), N2O (17.2–48.5%), and NH3 (18.3–69.0%) emissions compared to CK. In addition, the total N (8.4–40.0%) content in compost products was also improved. The study showed that a higher dose of applied FeSO4 can significantly reduce emissions, but it reduces the temperature at the start of composting resulting in an increase in the composting time, while the lower dose (0.5–1%) also has the capability to reduce the emissions compared with the control without negatively affecting the temperature rise. The study concludes that using 0.5–1% of FeSO4 can effectively utilize its inhibitory action of decomposition that mitigates gas emissions and prepares an N-enriched compost. Full article
Show Figures

Figure 1

Figure 1
<p>Variations in (<b>A</b>) temperature and (<b>B</b>) pH during the composting.</p>
Full article ">Figure 2
<p>Variations in (<b>A</b>) oxygen and (<b>B</b>) carbon dioxide during the composting.</p>
Full article ">Figure 3
<p>Gas emissions during composting: (<b>A</b>) CH<sub>4</sub>, (<b>B</b>) H<sub>2</sub>S, (<b>C</b>) N<sub>2</sub>O, and (<b>D</b>) NH<sub>3</sub>.</p>
Full article ">Figure 4
<p>Total emissions and reduction rates during composting: (<b>A</b>) CH<sub>4</sub>, (<b>B</b>) H<sub>2</sub>S, (<b>C</b>) N<sub>2</sub>O, and (<b>D</b>) NH<sub>3</sub>. The lowercase letters show the statistical difference between the treatments.</p>
Full article ">Figure 5
<p>N content in compost product: (<b>A</b>) NH<sub>4</sub>-N and (<b>B</b>) NO<sub>3</sub>-N.</p>
Full article ">Figure 6
<p>Changes in compost. (<b>A</b>) Total N during composting, (<b>B</b>) N increment rate, (<b>C</b>) available Fe during composting, and (<b>D</b>) composite Fe content. The lowercase letters shows the statistical difference between the treatments.</p>
Full article ">
32 pages, 14295 KiB  
Article
Assessing Non-Point Source Pollution in a Rapidly Urbanizing Sub-Basin to Support Intervention Planning
by Endaweke Assegide, Tena Alamirew, Greg O’Donnell, Bitew K. Dessie, Claire L. Walsh and Gete Zeleke
Water 2024, 16(23), 3447; https://doi.org/10.3390/w16233447 - 29 Nov 2024
Viewed by 414
Abstract
Non-point sources of pollution (NPSPs) originating from runoff from contaminated agricultural and populated areas are becoming a growing concern in developing countries, endangering the environment and public health. This requires systematic investigation, including modelling the likely impact using an appropriate hydrological model. This [...] Read more.
Non-point sources of pollution (NPSPs) originating from runoff from contaminated agricultural and populated areas are becoming a growing concern in developing countries, endangering the environment and public health. This requires systematic investigation, including modelling the likely impact using an appropriate hydrological model. This study quantified the spatiotemporal variation of the NPSP and prioritised the most vulnerable sub-watersheds for intervention planning. We investigated the effects of land use and cover (LULC) conversion on runoff generation and NPSP loads in terms of sediment, phosphate, total nitrogen, total phosphorus, and nitrate loading using the SWAT model. The principal source of data utilised to assess the change in NPSP loads was the 2003 and 2023 LULC. The analysis of the results showed that grassland and shrubland substantially changed, with 96.7% and 74.4% reductions, respectively, while the increase in agricultural land was 147.3% and that of built-up areas increased by 80.14%. The mean yearly increase in sediment yield ranges from 25.46 to 27,298.75 t, while the mean yearly increase in surface runoff ranges from 183.1 mm to 487.9 mm. The minimum recorded runoff was 10.69 mm (5.1%) in WS03, while the highest was 123.3 mm (66.5%) in WS02. The NO3 load increased from 127.6 to 20,739.7 kg, and the PO43− load increased from 3.12 to 2459.7 kg. The TN load increased from 4465.5 to 482,014.5 kg, and the TP load increased from 1383.5 to 133,641.3 kg. The monthly analysis of nitrate loading revealed that the “Belg” season has the highest nitrate load than the rainy season, probably due to nitrification. The findings clearly showed that the inputs applied to the farms were not effectively utilised for the intended purpose. Hence, efforts must be made to ensure that nutrients remain in the catchment through an appropriate land management intervention. Full article
(This article belongs to the Section Urban Water Management)
Show Figures

Figure 1

Figure 1
<p>Map of the upper Awash study area.</p>
Full article ">Figure 2
<p>The calibration and validation periods for stream flow, sediment (<b>a</b>), and nutrient (<b>b</b>).</p>
Full article ">Figure 3
<p>Maps showing land cover and use from 2003 (<b>a</b>) and 2023 (<b>b</b>).</p>
Full article ">Figure 4
<p>LULC change (2003–2023) direction of transformation (<b>a</b>), sum of change (<b>b</b>), and change matrix (<b>c</b>) analysis.</p>
Full article ">Figure 5
<p>LULC percentage change from 2003 to 2023.</p>
Full article ">Figure 6
<p>Flow calibrated and validated at Hombole (1984–2018) (<b>a</b>) and flow validated at Melka Kunture (2007–2018) (<b>b</b>) gauging stations.</p>
Full article ">Figure 7
<p>The flow simulated and observed at Hombole during calibration (<b>a</b>) and validation (<b>b</b>) and Melka Kunture during validation (<b>c</b>).</p>
Full article ">Figure 8
<p>The calibration and validation of sediment at Hombole (<b>a</b>) and Melka Kunture (<b>b</b>) gauging stations.</p>
Full article ">Figure 9
<p>Average annual soil loss rate (t/ha/year) for each upper Awash basin sub-watershed between 2003 and 2023.</p>
Full article ">Figure 10
<p>Map of average soil loss (t/h/y) severity class for the upper Awash sub-basin.</p>
Full article ">Figure 11
<p>Melka Kuture gauging station monthly nitrate (<b>a</b>), phosphate (<b>b</b>), total phosphorous (<b>c</b>), and total nitrogen (<b>d</b>) load calibration (2011–2014) and validation (2015–2019).</p>
Full article ">Figure 11 Cont.
<p>Melka Kuture gauging station monthly nitrate (<b>a</b>), phosphate (<b>b</b>), total phosphorous (<b>c</b>), and total nitrogen (<b>d</b>) load calibration (2011–2014) and validation (2015–2019).</p>
Full article ">Figure 12
<p>The runoff distribution and NPSP loads: runoff (<b>a</b>), nitrate (<b>b</b>), total nitrogen (<b>c</b>), phosphate (<b>d</b>), total phosphorous (<b>e</b>), and sediment (<b>f</b>).</p>
Full article ">Figure 13
<p>The temporal runoff and NPSP loads of upper Awash basin: average monthly runoff (<b>a</b>), average annual runoff (<b>b</b>), average monthly nitrate load (<b>c</b>), average annual nitrate (<b>d</b>), average monthly total nitrogen (<b>e</b>), average annual total nitrogen (<b>f</b>), average monthly phosphate (<b>g</b>), average annual phosphate (<b>h</b>), average monthly total phosphorous (<b>i</b>), average annual total phosphorous (<b>j</b>), average monthly sediment (<b>k</b>), and average annual sediment (<b>l</b>).</p>
Full article ">Figure 13 Cont.
<p>The temporal runoff and NPSP loads of upper Awash basin: average monthly runoff (<b>a</b>), average annual runoff (<b>b</b>), average monthly nitrate load (<b>c</b>), average annual nitrate (<b>d</b>), average monthly total nitrogen (<b>e</b>), average annual total nitrogen (<b>f</b>), average monthly phosphate (<b>g</b>), average annual phosphate (<b>h</b>), average monthly total phosphorous (<b>i</b>), average annual total phosphorous (<b>j</b>), average monthly sediment (<b>k</b>), and average annual sediment (<b>l</b>).</p>
Full article ">Figure 13 Cont.
<p>The temporal runoff and NPSP loads of upper Awash basin: average monthly runoff (<b>a</b>), average annual runoff (<b>b</b>), average monthly nitrate load (<b>c</b>), average annual nitrate (<b>d</b>), average monthly total nitrogen (<b>e</b>), average annual total nitrogen (<b>f</b>), average monthly phosphate (<b>g</b>), average annual phosphate (<b>h</b>), average monthly total phosphorous (<b>i</b>), average annual total phosphorous (<b>j</b>), average monthly sediment (<b>k</b>), and average annual sediment (<b>l</b>).</p>
Full article ">Figure 14
<p>The yearly average surface runoff (<b>a</b>), % change in surface runoff (<b>b</b>), sediment load (<b>c</b>), and percentage change in sediment load (<b>d</b>) from 2003 to 2023.</p>
Full article ">Figure 15
<p>Impact of LULC change in NO<sub>3</sub> load (<b>a</b>), change in NO<sub>3</sub> load (<b>b</b>), change in PO<sub>4</sub> load (<b>c</b>), and change in PO<sub>4</sub> (<b>d</b>).</p>
Full article ">Figure 16
<p>Sub-watershed level; TN and TP change in (t/yr.) (<b>a</b>), TN and TP change in (%) (<b>b</b>), TN and TP load (t/yr.) (<b>c</b>).</p>
Full article ">Figure 16 Cont.
<p>Sub-watershed level; TN and TP change in (t/yr.) (<b>a</b>), TN and TP change in (%) (<b>b</b>), TN and TP load (t/yr.) (<b>c</b>).</p>
Full article ">
21 pages, 7442 KiB  
Article
Spatial-Temporal Characteristics and Driving Factors of Surface Water Quality in the Jing River Basin of the Loess Plateau
by Bowen Zhang, Jing Li, Bo Yuan, Meng Li, Junqi Zhang, Mengjing Guo and Zhuannian Liu
Water 2024, 16(22), 3326; https://doi.org/10.3390/w16223326 - 19 Nov 2024
Viewed by 469
Abstract
Water quality safety in the water source constitutes a crucial guarantee for public health and the ecological environment. This study undertakes a comprehensive assessment of the water quality conditions within the Jing River Basin of the Loess Plateau, emphasizing the spatial and temporal [...] Read more.
Water quality safety in the water source constitutes a crucial guarantee for public health and the ecological environment. This study undertakes a comprehensive assessment of the water quality conditions within the Jing River Basin of the Loess Plateau, emphasizing the spatial and temporal characteristics, as well as the determinants influencing surface water quality in the Shaanxi section. We utilized data from seven monitoring stations collected between 2016 and 2022, employing an enhanced comprehensive Water Quality Index (WQI) method, redundancy analysis (RDA), and Spearman’s correlation analysis. The results show that the average annual WQI value of the water quality of the Shaanxi section of the Jing River increased from 68.01 in 2016 to 76.18 in 2022, and the river’s water quality has gradually improved, with a significant improvement beginning in 2018, and a series of water quality management policies implemented by Shaanxi Province is the primary reason for the improvement. The river’s water quality has deteriorated slightly in recent years, necessitating stricter supervision of the coal mining industry in the upper section. The river has an average WQI value of 73.70 and is rated as ‘good’. The main pollution indicators influencing the river’s water quality are CODMn, COD, BOD5, NH3-N, and TP. From the upstream to the downstream, the water quality of the river shows a pattern of increasing and then decreasing, among which S4 (Linjing Bridge in Taiping Town) and S5 (Jinghe Bridge) have the best water quality. The downstream part (S6, S7) of the Jing River near the Weihe River has poor water quality, which is mostly caused by nonpoint source contamination from livestock and poultry rearing, agricultural activities, and sewage discharge. Redundancy analysis revealed that the spatial scale of the 2500 m buffer zone best explained water quality changes, and the amount of bare land and arable land in land use categories was the key influencing factor of river water quality. Full article
Show Figures

Figure 1

Figure 1
<p>Monitoring section of the Shaanxi section of the Jing River Basin.</p>
Full article ">Figure 2
<p>Annual average change of Water Quality Index and M–K trend test.</p>
Full article ">Figure 3
<p>Annual average value of Water Quality Index concentration in each section.</p>
Full article ">Figure 4
<p>Interannual variation of Water Quality Index concentration in flood season and non-flood season.</p>
Full article ">Figure 5
<p>WQI evaluation results.</p>
Full article ">Figure 6
<p>Spatial distribution of WQI: (<b>a</b>) Annual average WQI distribution; (<b>b</b>–<b>h</b>) WQI distribution, 2016–2022.</p>
Full article ">Figure 7
<p>Spearman correlation analysis between Water Quality Index and WQI value. *: Significance <span class="html-italic">p</span>-value.</p>
Full article ">Figure 8
<p>Sorting diagram of redundancy analysis results in the Jing River Basin.</p>
Full article ">
17 pages, 835 KiB  
Article
Is the Ratoon Rice System More Sustainable? An Environmental Efficiency Evaluation Considering Carbon Emissions and Non-Point Source Pollution
by Hui Qiao, Mingzhe Pu, Ruonan Wang and Fengtian Zheng
Sustainability 2024, 16(22), 9920; https://doi.org/10.3390/su16229920 - 14 Nov 2024
Viewed by 364
Abstract
The sustainability of rice-cropping systems hinges on balancing resources, output, and environmental impacts. China is revitalizing the ancient ratoon rice (RR) system for input savings and environmental benefits. Prior research has explored the RR system’s performance using various individual indicators, but few studies [...] Read more.
The sustainability of rice-cropping systems hinges on balancing resources, output, and environmental impacts. China is revitalizing the ancient ratoon rice (RR) system for input savings and environmental benefits. Prior research has explored the RR system’s performance using various individual indicators, but few studies have focused on its overall balance of these factors. Environmental efficiency (EE) analysis addresses this gap. Using field survey data from Hunan Province in China and the slacks-based data envelopment analysis method, we quantified the EE of the RR, double-season rice (DR), and single-season rice (SR) systems. Key findings include: (1) the RR system outperforms in carbon emissions and non-point source pollution; (2) the RR system’s EE is 0.67, significantly higher than the DR (0.58) and SR (0.57) systems, indicating superior performance; and (3) despite its relatively high EE, the RR system can still improve, mainly due to input redundancy and production value shortfall. These findings provide strategies for optimizing RR systems to enhance agricultural sustainability. Full article
(This article belongs to the Special Issue Achieving Sustainable Agriculture Practices and Crop Production)
Show Figures

Figure 1

Figure 1
<p>Framework for estimating the EE of the rice-cropping systems.</p>
Full article ">Figure 2
<p>The rates of contributions of different sources to the CEs of different rice-cropping systems. Note: Given their low contributions to carbon emissions from rice production, the emissions from phosphate, potash fertilizers, and pesticides were combined for clarity in the graph. All fertilizers were calculated based on their active ingredients.</p>
Full article ">
17 pages, 10449 KiB  
Article
The Effect Characterization of Lens on LNAPL Migration Based on High-Density Resistivity Imaging Technique
by Guizhang Zhao, Jiale Cheng, Menghan Jia, Hongli Zhang, Hongliang Li and Hepeng Zhang
Appl. Sci. 2024, 14(22), 10389; https://doi.org/10.3390/app142210389 - 12 Nov 2024
Viewed by 439
Abstract
Light non-aqueous phase liquids (LNAPLs), which include various petroleum products, are a significant source of groundwater contamination globally. Once introduced into the subsurface, these contaminants tend to accumulate in the vadose zone, causing chronic soil and water pollution. The vadose zone often contains [...] Read more.
Light non-aqueous phase liquids (LNAPLs), which include various petroleum products, are a significant source of groundwater contamination globally. Once introduced into the subsurface, these contaminants tend to accumulate in the vadose zone, causing chronic soil and water pollution. The vadose zone often contains lens-shaped bodies with diverse properties that can significantly influence the migration and distribution of LNAPLs. Understanding the interaction between LNAPLs and these lens-shaped bodies is crucial for developing effective environmental management and remediation strategies. Prior research has primarily focused on LNAPL behavior in homogeneous media, with less emphasis on the impact of heterogeneous conditions introduced by lens-shaped bodies. To investigate the impact of lens-shaped structures on the migration of LNAPLs and to assess the specific effects of different types of lens-shaped structures on the distribution characteristics of LNAPL migration, this study simulates the LNAPL leakage process using an indoor two-dimensional sandbox. Three distinct test groups were conducted: one with no lens-shaped aquifer, one with a low-permeability lens, and one with a high-permeability lens. This study employs a combination of oil front curve mapping and high-density resistivity imaging techniques to systematically evaluate how the presence of lens-shaped structures affects the migration behavior, distribution patterns, and corresponding resistivity anomalies of LNAPLs. The results indicate that the migration rate and distribution characteristics of LNAPLs are influenced by the presence of a lens in the gas band of the envelope. The maximum vertical migration distances of the LNAPL are as follows: high-permeability lens (45 cm), no lens-shaped aquifer (40 cm), and low-permeability lens (35 cm). Horizontally, the maximum migration distances of the LNAPL to the upper part of the lens body decreases in the order of low-permeability lens, high-permeability lens, and no lens-shaped aquifer. The low-permeability lens impedes the vertical migration of the LNAPL, significantly affecting its migration path. It creates a flow around effect, hindering the downward migration of the LNAPL. In contrast, the high-permeability lens has a weaker retention effect and creates preferential flow paths, promoting the downward migration of the LNAPL. Under conditions with no lens-shaped aquifer and a high-permeability lens, the region of positive resistivity change rate is symmetrical around the axis where the injection point is located. Future research should explore the impact of various LNAPL types, lens geometries, and water table fluctuations on migration patterns. Incorporating numerical simulations could provide deeper insights into the mechanisms controlling LNAPL migration in heterogeneous subsurface environments. Full article
Show Figures

Figure 1

Figure 1
<p>Diagram of the experimental setup.</p>
Full article ">Figure 2
<p>Schematic diagram of the measurement method.</p>
Full article ">Figure 3
<p>Variation in the LNAPL migration velocity (No lens-shaped aquifer). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Vertical migration velocity.</p>
Full article ">Figure 3 Cont.
<p>Variation in the LNAPL migration velocity (No lens-shaped aquifer). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Vertical migration velocity.</p>
Full article ">Figure 4
<p>Variation in the LNAPL migration velocity (low-permeability lens). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Migration process.</p>
Full article ">Figure 4 Cont.
<p>Variation in the LNAPL migration velocity (low-permeability lens). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Migration process.</p>
Full article ">Figure 5
<p>Variation in the LNAPL migration velocity (high-permeability lens). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Vertical migration velocity.</p>
Full article ">Figure 5 Cont.
<p>Variation in the LNAPL migration velocity (high-permeability lens). (<b>a</b>) Migration process. (<b>b</b>) Lateral migration velocity at different heights. (<b>c</b>) Vertical migration velocity.</p>
Full article ">Figure 6
<p>Maximum migration distance for different test groups.</p>
Full article ">Figure 7
<p>Rate of change of resistance (no lens-shaped aquifer). (<b>a</b>) 30 min (<b>b</b>) 60 min (<b>c</b>) 120 min (<b>d</b>) 180 min (<b>e</b>) 240 min (<b>f</b>) 300 min.</p>
Full article ">Figure 8
<p>Resistance rate of change (low-permeability lens). (<b>a</b>) 30 min (<b>b</b>) 100 min (<b>c</b>) 300 min (<b>d</b>) 400 min (<b>e</b>) 500 min (<b>f</b>) 660 min.</p>
Full article ">Figure 9
<p>Rate of change of resistance (high-permeability lens). (<b>a</b>) 60 min (<b>b</b>) 100 min (<b>c</b>) 200 min (<b>d</b>) 300 min (<b>e</b>) 400 min (<b>f</b>) 490 min.</p>
Full article ">
29 pages, 5171 KiB  
Review
Progress and Hotspot Analysis of Bibliometric-Based Research on Agricultural Irrigation Patterns on Non-Point Pollution
by Shikai Gao, Xiaoyuan Zhang, Songlin Wang, Yuliang Fu, Weiheng Li, Yuanzhi Dong, Hongzhuo Yuan, Yanbin Li and Na Jiao
Agronomy 2024, 14(11), 2604; https://doi.org/10.3390/agronomy14112604 - 4 Nov 2024
Viewed by 535
Abstract
With the constant advancement of irrigation technology and the continuous expansion of irrigation areas, non-point source pollution (NPS) caused by agricultural activities has posed a persistent threat to ecosystems and biological safety. Against this backdrop, it is imperative to lay scientific foundations for [...] Read more.
With the constant advancement of irrigation technology and the continuous expansion of irrigation areas, non-point source pollution (NPS) caused by agricultural activities has posed a persistent threat to ecosystems and biological safety. Against this backdrop, it is imperative to lay scientific foundations for green, sustainable, and high-quality agricultural development through a thorough review of the relevant research progress. In this study, bibliometric methods are adopted to comprehensively analyze and visualize the current state and key literature on agricultural irrigation and NPS pollution from 2010 to July 2024. The focus of this study is specifically on summarizing the research hotspots and development trends of different irrigation methods and the mechanisms behind their impacts on NPS pollution. The results indicate that publications from the United States and China account for 63.8% of the total, but the fragmentation of research efforts remains, suggesting a necessity to strengthen international and regional collaboration. There are three institutions with the highest publication output, namely Northwest A&F University, Hohai University, and the Chinese Academy of Sciences. The subjects identified as the key areas of research on irrigation-related NPS pollution (IRR-NPS) include precision irrigation, rapid water pollution response, spatiotemporal management, interdisciplinary integration, wastewater treatment, and crop models. Regarding future research, it is necessary to focus attention on real-time precision irrigation, standardized crop models, data accuracy, spatiotemporal pollution coordination, pollution purification technology development, interdisciplinary integrated governance, and the innovative applications of soil improvement technologies. In addition to offering theoretical support and practical guidance for the management of agricultural NPS pollution, this study also provides management and technical support for policymakers, which is beneficial for advancing agricultural irrigation technology and environmental preservation. Full article
(This article belongs to the Section Water Use and Irrigation)
Show Figures

Figure 1

Figure 1
<p>Flow chart of the research methodology. Note: * represents the text name number for retrieving references &amp; Download.</p>
Full article ">Figure 2
<p>Disciplinary Co-occurrence Visualization.</p>
Full article ">Figure 3
<p>Annual circulation of publications.</p>
Full article ">Figure 4
<p>Author co-occurrence map for the authors producing literature related to IRR-NPS research.</p>
Full article ">Figure 5
<p>Keyword co-occurrence map displaying the most frequently used words associated with IRR-NPS research.</p>
Full article ">Figure 6
<p>Keywords timeline clustering map for keywords relating to IRR-NPS research.</p>
Full article ">Figure 7
<p>Top 20 keywords relating to IRR-NPS research with the strongest citation bursts over the period between 2010 and 2024.</p>
Full article ">Figure 8
<p>Reference clustering according to time.</p>
Full article ">Figure 9
<p>Discussion and recommendation flowchart.</p>
Full article ">
18 pages, 22321 KiB  
Article
Shallow Groundwater Quality Assessment and Pollution Source Apportionment: Case Study in Wujiang District, Suzhou City
by Lili Hou, Qiuju Qi, Quanping Zhou, Jinsong Lv, Leli Zong, Zi Chen, Yuehua Jiang, Hai Yang, Zhengyang Jia, Shijia Mei, Yang Jin, Hong Zhang, Jie Li and Fangfei Xu
Water 2024, 16(21), 3139; https://doi.org/10.3390/w16213139 - 2 Nov 2024
Viewed by 600
Abstract
Groundwater serves as a crucial resource, with its quality significantly impacted by both natural and human-induced factors. In the highly industrialized and urbanized Yangtze River Delta region, the sources of pollutants in shallow groundwater are more complex, making the identification of groundwater pollution [...] Read more.
Groundwater serves as a crucial resource, with its quality significantly impacted by both natural and human-induced factors. In the highly industrialized and urbanized Yangtze River Delta region, the sources of pollutants in shallow groundwater are more complex, making the identification of groundwater pollution sources a challenging task. In this study, 117 wells in Wujiang District of Suzhou City were sampled, and 16 groundwater quality parameters were analyzed. The fuzzy synthetic evaluation method was used to assess the current status of groundwater pollution in the study area; the principal component analysis (PCA) was employed to discern the anthropogenic and natural variables that influence the quality of shallow groundwater; and the absolute principal component scores–multiple linear regression (APCS-MLR) model was applied to quantify the contributions of various origins toward the selected groundwater quality parameters. The results indicate that the main exceeding indicators of groundwater in Wujiang District are I (28%), NH4-N (18%), and Mn (14%); overall, the groundwater quality is relatively good in the region, with localized heavy pollution: class IV and class V water are mainly concentrated in the southwest of Lili Town, the north of Songling Town, and the south of Qidu Town. Through PCA, five factors contributing to the hydrochemical characteristics of groundwater in Wujiang District were identified: water–rock interaction, surface water–groundwater interaction, sewage discharge from the textile industry, urban domestic sewage discharge, and agricultural non-point source pollution. Additionally, the APCS-MLR model determined that the contributions of the three main pollution sources to groundwater contamination are in the following order: sewage discharge from the textile industry (10.63%) > urban domestic sewage discharge (8.69%) > agricultural non-point source pollution (6.26%). Full article
(This article belongs to the Special Issue Groundwater Quality and Contamination at Regional Scales)
Show Figures

Figure 1

Figure 1
<p>Location of Wujiang District and sampling sites for groundwater with land use.</p>
Full article ">Figure 2
<p>Spatial distributions of the main exceeding indicators of groundwater in Wujiang District.</p>
Full article ">Figure 3
<p>The fuzzy synthetic evaluation result of shallow groundwater in Wujiang District.</p>
Full article ">Figure 4
<p>Correlation analysis of groundwater quality parameters in Wujiang District. The colored circles represents the degree of positive and negative correlation.</p>
Full article ">Figure 5
<p>Component loadings for 16 groundwater quality parameters after varimax rotation in Wujiang District.</p>
Full article ">Figure 6
<p>Spatial distribution of contributions of VF2, VF3, and VF4 in groundwater in Wujiang District.</p>
Full article ">Figure 7
<p>The contributions to groundwater quality parameters (<b>A</b>) and average contributions (<b>B</b>) of pollution sources in Wujiang District.</p>
Full article ">
19 pages, 6885 KiB  
Article
Adapting to Climate Change: Reducing Nonpoint Source Pollution in Agriculture: A Case Study in Gyeseong Stream, Korea
by Heongak Kwon, Suyeon Choi and Chang Dae Jo
Water 2024, 16(21), 3127; https://doi.org/10.3390/w16213127 - 1 Nov 2024
Viewed by 777
Abstract
Climate change scenarios have been used to evaluate future climate change impacts and develop adaptation measures to mitigate potential damage. This study investigated strategies to reduce nonpoint source loads in an agriculturally dominated watershed and adapt to climate change despite uncertainty. We also [...] Read more.
Climate change scenarios have been used to evaluate future climate change impacts and develop adaptation measures to mitigate potential damage. This study investigated strategies to reduce nonpoint source loads in an agriculturally dominated watershed and adapt to climate change despite uncertainty. We also investigated strategies for adapting to future meteorological conditions characterized by uncertainty. We utilized the latest future climate change scenarios—shared socioeconomic pathways—and explored measures to reduce nonpoint source loads by implementing nonpoint pollution abatement facilities in a watershed model. The simulation results indicate that the future frequency of rainfall events may decrease based on observations and the types and features of rainfall events in the scenarios. However, the variability of runoff loads in the context of future climate scenarios may increase because of factors influencing surface runoff, including the amount and intensity of rainfall. Nonpoint source loads are expected to exhibit high uncertainty in the future. Finally, the optimal solution can be determined through a simulated evaluation of the cost–benefit of installing the abatement facilities, considering the abatement efficiency and maintenance period. Overall, implementing effective management practices is crucial for reducing nonpoint source loads resulting from agricultural activities while adapting to increasingly variable meteorological conditions. Full article
Show Figures

Figure 1

Figure 1
<p>Land-use status and digital elevation model of the target watershed.</p>
Full article ">Figure 2
<p>Annual variability of the Korean Peninsula climate under the shared socioeconomic pathway (SSP) scenarios. (<b>a</b>) Precipitation, (<b>b</b>) Maximum temperature, (<b>c</b>) Minimum temperature, (<b>d</b>) Relative humidity change, (<b>e</b>) Solar radiation change, (<b>f</b>) Wind speed change.</p>
Full article ">Figure 3
<p>Reproducibility evaluation based on the number of rainfall days R30 mm and R50 mm (R30 mm: number of days of rainfall greater than 30 mm, R50 mm: number of days of rainfall greater than 50 mm).</p>
Full article ">Figure 4
<p>Representation of the number of days without rainfall for more than 5 days (CD5Day) and number of days with rainfall &gt; 50 mm following more than 10 days without rainfall (C10Day50 mm).</p>
Full article ">Figure 5
<p>Validation and calibration of HSPF model.</p>
Full article ">Figure 6
<p>Projected annual nonpoint source discharge and loads in the context of future climate change scenarios (Observed: discharge and loads based on observed climate data for 2011–2020, SSP scenarios: projected discharge and loads based on future climate for 2030–2100). (<b>a</b>) Precipitation, (<b>b</b>) Flow, (<b>c</b>) BOD load, (<b>d</b>) TP load.</p>
Full article ">Figure 7
<p>Watershed classification in HSPF model.</p>
Full article ">Figure 8
<p>Optimal management of nonpoint source loads in the target watershed in the context of future climate change scenario (GS: grassed swale; IT: infiltration trench. Cost calculation after the operation period of abatement facilities was set at 25 years).</p>
Full article ">
25 pages, 9535 KiB  
Article
An Innovative GIS-Based Policy Approach to Stream Water Quality and Ecological Risk Assessment in Mediterranean Regions: The Case of Crete, Greece
by Nektarios N. Kourgialas, Chrysoula Ntislidou, Eleana Kazila, Agathos Filintas and Catherina Voreadou
Land 2024, 13(11), 1801; https://doi.org/10.3390/land13111801 - 31 Oct 2024
Viewed by 709
Abstract
Due to the multiple pressures from human activities, many freshwater ecosystems are facing degradation. To address this issue, a new approach for assessing stream water quality and ecological (WQE) risk using a multi-criteria analysis through a GIS-based policy tool has been developed. The [...] Read more.
Due to the multiple pressures from human activities, many freshwater ecosystems are facing degradation. To address this issue, a new approach for assessing stream water quality and ecological (WQE) risk using a multi-criteria analysis through a GIS-based policy tool has been developed. The suggested methodology integrates eight different factors along the contaminant pathway from source to streams, including: (a) rainfall variability, (b) soil texture, (c) soil erodibility, (d) slope, (e) river buffer zone, (f) point source contamination buffer zone, (g) non-point source contamination of NO3, and (h) non-point source contamination of PO4. Utilizing fuzzy GIS tools, the above factors and their related maps were spatially overlaid (raster-based suitability for raster reclassification) to obtain the final stream WQE risk map. The final map depicts the spatial distribution of streams concerning their water quality risk and is represented by two classes of WQE risk. The first class is characterized as “appropriate”, in which there is no need for any further actions, while the other one is characterized as “non-appropriate”, indicating that actions should be taken to ensure the sustainability of streams’ water quality. The proposed approach was implemented for the island of Crete, which is located in the Southeast Mediterranean region. The developed methodology was validated using the Hellenic evaluation system (HESY2), an especially established and adapted to the Mediterranean river systems ecological quality metric method, obtained by in situ measurements that were conducted during different monitoring programs (1989–2015). Moreover, this study summarizes appropriate measures and practices that ensure the sustainable management of Mediterranean river basins. These practices can be adopted by local authorities, owners of polluting units, and farmers/breeders to improve the resiliency of streams’ water quality issues in the Mediterranean region. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Elevation and prefectures of Crete, (<b>b</b>) land uses in Crete.</p>
Full article ">Figure 2
<p>(<b>a</b>) River systems in Crete and surface water monitoring sites, (<b>b</b>) rainfall stations in the island of Crete.</p>
Full article ">Figure 3
<p>Flow chart of the proposed methodology.</p>
Full article ">Figure 4
<p>River WQE risk maps for (<b>a</b>) rainfall variability; (<b>b</b>) soil texture; (<b>c</b>) soil erodibility; and (<b>d</b>) slope.</p>
Full article ">Figure 5
<p>River WQE risk maps for (<b>a</b>) river buffer zone; (<b>b</b>) point source contamination buffer zone; (<b>c</b>) non-point source contamination (NO<sub>3</sub>); and (<b>d</b>) non-point source contamination (PO<sub>4</sub>).</p>
Full article ">Figure 6
<p>Validation of the final river WQE risk map (at 25 m resolution scale).</p>
Full article ">Figure 7
<p>Final river WQE risk map for the island of Crete (at 25 m resolution scale).</p>
Full article ">Figure 8
<p>(<b>a</b>) Spatial distribution of “non-appropriate” river sections in Crete (red color) and river systems that receive contamination loads; (<b>b</b>) “non-appropriate” river sections based on the proposed fuzzy GIS-based suitability method and the river basins already proposed by RBMP to which Program of Measures (PoMs) should be applied.</p>
Full article ">
13 pages, 2608 KiB  
Article
Application of Nitrate–Ammonium Nitrogen Fertilization Reduced Nitrogen Loss in Surface Runoff and Infiltration by Improving Root Morphology of Flue-Cured Tobacco
by Chengren Ouyang, Kang Yang and Zhengxiong Zhao
Agronomy 2024, 14(11), 2532; https://doi.org/10.3390/agronomy14112532 - 28 Oct 2024
Viewed by 861
Abstract
Nitrogen loss in water from farmland has become an environmental issue. Nitrogen fertilizer is the main cause of agricultural non-point source pollution in the Lake Basin, Yunnan. However, it is unclear how different nitrogen fertilizer forms affect water loss from farmland and how [...] Read more.
Nitrogen loss in water from farmland has become an environmental issue. Nitrogen fertilizer is the main cause of agricultural non-point source pollution in the Lake Basin, Yunnan. However, it is unclear how different nitrogen fertilizer forms affect water loss from farmland and how the root systems of crops respond. We established five nitrogen fertilizer treatments (100–0% [T1], 75–25% [T2], 50–50% [T3], 25–75% [T4], and 0–100% [(T5)] nitrate–ammonium) and performed an investigation to determine nitrogen loss in water and root morphological parameters of tobacco in Mile County and Chengjiang County. Compared with in the T1, T4, and T5 treatments, the total nitrogen loss in surface runoff was reduced by 4.67%, 11.85% and 9.56% in the T2 treatment and 27.32%, 23.20%, and 31.43% in the T3 treatment, respectively. Similar results were observed for the nitrogen loss due to infiltration. The root biomass was negatively correlated with nitrogen loss. There was greater root biomass, root surface area, and root spatial distribution in T2 and T3 compared with in T1, T4, and T5. These results indicate that 50–50% nitrate–ammonium nitrogen fertilizer can facilitate the root growth of tobacco and reduce nitrogen loss, which provides a reference for agricultural sustainable development. Full article
(This article belongs to the Section Plant-Crop Biology and Biochemistry)
Show Figures

Figure 1

Figure 1
<p>Schematic of the devices used to collect surface runoff and infiltration.</p>
Full article ">Figure 2
<p>Meteorological data from the two experimental sites.</p>
Full article ">Figure 3
<p>Characteristics of nitrogen nutrient loss of runoff under different nitrogen form conditions. Different small letters indicate significant differences among treatments at <span class="html-italic">p</span> &lt; 0.05; LSD test by one-way ANOVA.</p>
Full article ">Figure 4
<p>Characteristics of nitrogen nutrient loss of infiltration given different nitrogen forms. Different small letters indicate significant differences among treatments at <span class="html-italic">p</span> &lt; 0.05; LSD test by one-way ANOVA.</p>
Full article ">Figure 5
<p>Characteristics of root spatial distribution of flue-cured tobacco given different nitrogen forms.</p>
Full article ">Figure 6
<p>Relationship among fertilizer nitrogen forms, root, and nitrogen and phosphorus loss in the two field experiments.</p>
Full article ">
17 pages, 8794 KiB  
Article
Impacts of Land Use and Land Cover Change on Non-Point Source Pollution in the Nyabarongo River Catchment, Rwanda
by Justin Nsanzabaganwa, Xi Chen, Tie Liu, Egide Hakorimana, Richard Mind’je, Aboubakar Gasirabo, Bakayisire Fabiola, Adeline Umugwaneza and Niyonsenga Schadrack
Water 2024, 16(21), 3033; https://doi.org/10.3390/w16213033 - 23 Oct 2024
Viewed by 818
Abstract
The Nyabarongo river catchment in Rwanda has experienced significant changes in its land use and land cover (LULC) in recent decades, with profound implications for non-point source pollution. However, there are limited studies on non-point pollution caused by nutrient loss associated with land [...] Read more.
The Nyabarongo river catchment in Rwanda has experienced significant changes in its land use and land cover (LULC) in recent decades, with profound implications for non-point source pollution. However, there are limited studies on non-point pollution caused by nutrient loss associated with land use and land cover changes in the catchment. This study investigates the spatiotemporal impacts of these changes on water quality considering nitrogen and phosphorus within the catchment from 2000 to 2020 and 2030 as a projection. The SWAT model was used in analysis of hydrological simulations, while the CA–Markov model was used for the future projection of LULC in 2030. The results revealed (1) the important changes in LULC in the study area, where a decrease in forestland was observed with a considerable increase in built-up land, grassland, and cropland; (2) that the R2 and NSE of the TN and TP in the runoff simulation in the catchment were all above 0.70, showing good applicability during calibration and validation periods; (3) that from 2000 to 2020 and looking to the projection in 2030, the simulated monthly average TN and TP levels have progressively increased from 15.36 to 145.71 kg/ha, 2.46 to 15.47 kg/ha, 67.2 to 158.8 kg/ha, and 9.3 to 17.43 kg/ha, respectively; and (4) that the most polluted land use types are agriculture and urban areas, due to increases in human activities as a consequence of population growth in the catchment. Understanding the patterns and drivers of these changes is critical for developing effective policies and practices for sustainable land management and protection of water resources. Full article
(This article belongs to the Special Issue Research on Watershed Ecology, Hydrology and Climate)
Show Figures

Figure 1

Figure 1
<p>Geographical location of the study area: (<b>a</b>) location at the continent level; (<b>b</b>) location at the country level; (<b>c</b>) sub-catchments with rivers and hydro-meteorological station locations.</p>
Full article ">Figure 2
<p>(<b>a</b>) DEM, (<b>b</b>) soil type, (<b>c</b>) slope, (<b>d</b>–<b>f</b>) LULC.</p>
Full article ">Figure 3
<p>Fitting of simulated and measured runoff data.</p>
Full article ">Figure 4
<p>Fitting of measured TP and simulated data.</p>
Full article ">Figure 5
<p>Fitting of measured TN and simulated data.</p>
Full article ">Figure 6
<p>Gain and loss in % of land use in the study period.</p>
Full article ">Figure 7
<p>Annual load of total nitrogen and outlet points in three LULC phases.</p>
Full article ">Figure 8
<p>Spatial distribution of TN (2000, 2010, 2020) in the catchment.</p>
Full article ">Figure 9
<p>Annual load of total phosphorus at outlet points in three LULC phases.</p>
Full article ">Figure 10
<p>Spatial distribution of TP (2000, 2010, 2020) in the catchment.</p>
Full article ">Figure 11
<p>Future projections of the spatial distribution of TN (<b>A</b>) and TP (<b>B</b>) in 2030.</p>
Full article ">
19 pages, 10203 KiB  
Article
Combining SWAT with Machine Learning to Identify Primary Controlling Factors and Their Impacts on Non-Point Source Pollution
by Maowu Yin, Zaijun Wu, Qian Zhang, Yangyang Su, Qiao Hong, Qiongqiong Jia, Xiao Wang, Kan Wang and Junrui Cheng
Water 2024, 16(21), 3026; https://doi.org/10.3390/w16213026 - 22 Oct 2024
Viewed by 644
Abstract
Non-point source (NPS) pollution has a complex formation mechanism, and identifying its primary controlling factors is crucial for effective pollution treatment. In this study, the Baixi Reservoir Watershed, characterized by low-intensity development, was selected as the study area. A new methodology combining the [...] Read more.
Non-point source (NPS) pollution has a complex formation mechanism, and identifying its primary controlling factors is crucial for effective pollution treatment. In this study, the Baixi Reservoir Watershed, characterized by low-intensity development, was selected as the study area. A new methodology combining the Soil and Water Assessment Tool (SWAT) with the Random Forest (RF) algorithm was proposed to comprehensively identify the primary controlling factors of NPS pollution and analyze the interaction between factors. The results of the validated SWAT model showed that the annual intensity of total nitrogen (TN) load range was 0.677–11.014 kg ha−1 yr−1, and the total phosphorus (TP) load per unit area range was 0.020–0.110 kg ha−1 yr−1. Loads of sediment, TP, and TN exhibited significant seasonal variations, particularly in the Baixi basin, where sediment yield had the highest absolute change rate, with a value of up to 232.26. Random Forest models for TN and TP displayed high accuracy (R2 > 0.99) and robust generalization ability. Fertilization, sediment yield, and terrain slope were identified through RF models as the primary factors affecting TN and TP. By graphing partial dependency plots (PDPs) based on the results of the RF models to analyze the interaction between factors, the findings suggest a strong synergistic effect of two combined factors: fertilization and sediment yield. When fertilizer application exceeds 15 kg ha−1 yr−1 and sediment yield exceeds 3 kg ha−1 yr−1, there is a sharp increase in nitrogen and phosphorus load. Through the identification and analysis of the primary controlling factors of NPS pollution, this study provides a solid scientific foundation for developing effective watershed management strategies. Full article
(This article belongs to the Section Water Quality and Contamination)
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Geographic location of Baixi Reservoir, two meteorological stations, and one hydrological station, and distribution of rivers within the watershed; (<b>b</b>) spatial distribution of land use types; (<b>c</b>) the whole watershed divided into three smaller basins, and the distribution of 18 sub-watersheds.</p>
Full article ">Figure 2
<p>Process of importance analysis for RF factors.</p>
Full article ">Figure 3
<p>Calibration and validation results of monthly (<b>a</b>) flow discharge, (<b>b</b>) NH<sub>3</sub>-N, (<b>c</b>) TP, and (<b>d</b>) TN in the Baixi Reservoir Watershed. The dashed line divides the calibration period and validation period.</p>
Full article ">Figure 4
<p>The variation of monthly (<b>a</b>) sediment yield, (<b>b</b>) water yield, (<b>c</b>) TP load, and (<b>d</b>) TN load; (<b>e</b>) the coefficient of variation and (<b>f</b>) the absolute change rate.</p>
Full article ">Figure 5
<p>Distribution of average annual intensities of (<b>a</b>) TN and (<b>b</b>) TP loads across 18 sub-watersheds in the Baixi Reservoir Watershed.</p>
Full article ">Figure 6
<p>Pearson correlation coefficients for 14 pre-selected parameters. The size of the circle represents the magnitude of the correlation.</p>
Full article ">Figure 7
<p>Comparison of the observations and predictions made by the RF model for (<b>a</b>) TN and (<b>b</b>) TP; RF variable importance of (<b>c</b>) TN and (<b>d</b>) TP.</p>
Full article ">Figure 8
<p>Generalized PDPs for the primary controlling factors of TN.</p>
Full article ">Figure 9
<p>Generalized PDPs for the primary controlling factors of TP.</p>
Full article ">
15 pages, 2577 KiB  
Article
Optimization of Manure-Based Substrate Preparation to Reduce Nutrients Losses and Improve Quality for Growth of Agaricus bisporus
by Yucong Geng, Yuhan Wang, Han Li, Rui Li, Shengxiu Ge, Hongyuan Wang, Shuxia Wu and Hongbin Liu
Agriculture 2024, 14(10), 1833; https://doi.org/10.3390/agriculture14101833 - 18 Oct 2024
Viewed by 732
Abstract
With the growing world population, food demand has also increased, resulting in increased agricultural waste and livestock manure production. Wheat straw and cow dung are rich nutrient sources and, if not utilized properly, may lead to environmental pollution. Keeping in view the cultivation [...] Read more.
With the growing world population, food demand has also increased, resulting in increased agricultural waste and livestock manure production. Wheat straw and cow dung are rich nutrient sources and, if not utilized properly, may lead to environmental pollution. Keeping in view the cultivation of Agaricus bisporus on straw/manure-based substrate, the current study aimed to optimize the conventional manure preparation technique to reduce nutrient losses and keep the quality of manure at its best. The treatments were considered as traditional and optimized schemes for mushroom substrate preparation. The results achieved herein indicated that the nutrient losses were low in the optimum scheme. For carbon (C), the loss was 43.55% at the substrate stage in the traditional scheme and reduced to 37.75% in the optimum scheme. In the case of nitrogen (N), the loss was 22.01% in the traditional scheme and was lower (18.49%) in the optimum scheme. The nutrient concentration in Agaricus bisporus was higher with the optimum scheme compared with the traditional scheme. It was 1.74% for C, 7.17% for N, 3.58% for phosphorus (P), and 4.92% for potassium (K). The optimum scheme also improved the Agaricus bisporus yield per unit area (84.55%) and the total yield (28.92%). The net income of the optimum scheme was 102.95% higher compared to the traditional scheme. The economic analysis also revealed that the benefit–cost ratio of the optimum scheme was high (48.86%) compared with the traditional scheme. This study concludes that the use of the optimum scheme can better utilize the wheat straw and cow manure waste for substrate preparation and reducing nutrient losses. In addition, the final mushroom residue can also be used as a leftover substrate for further utilization. Full article
Show Figures

Figure 1

Figure 1
<p>Comparison of traditional and optimum schemes at the material, substrate, and mushroom residue stages. Herein, figure (<b>a</b>) shows the total dry weight, (<b>b</b>) shows the total quality of C and C content, (<b>c</b>) shows the total quality of N and N content, and (<b>d</b>) shows N content. The data represent the means ± standard deviation and the lowercase lettering indicates the statistical difference among the means.</p>
Full article ">Figure 2
<p>Comparison of traditional and optimum schemes at the material, substrate, and mushroom residue stages. Herein, figure (<b>a</b>) shows the total quality of P and P content and (<b>b</b>) shows the total quality of K and K content. The data are represented as the mean ± standard deviation and the lowercase lettering indicates the statistical difference among the means.</p>
Full article ">Figure 3
<p>Comparison of traditional and optimum schemes at the material, substrate, and mushroom residue stages. Herein, figure (<b>a</b>) shows the cellulose content, (<b>b</b>) shows the hemicellulose content, (<b>c</b>) shows the lignin content, and (<b>d</b>) shows the humic content. The data represent the means ± standard deviation and the lowercase lettering indicates the statistical difference among the means.</p>
Full article ">Figure 4
<p>The change in and loss of C, N, P, and K. C is carbon, N is nitrogen, P is phosphorus, and K is potassium.</p>
Full article ">
20 pages, 1029 KiB  
Article
The Impact of Tea Farmers’ Cognition on Green Production Behavior in Jingmai Mountain: Chain Mediation by Social and Personal Norms and the Moderating Role of Government Regulation
by Yingzhou Xianyu, Hua Long, Zhifeng Wang, Long Meng and Feiyu Duan
Sustainability 2024, 16(20), 8885; https://doi.org/10.3390/su16208885 - 14 Oct 2024
Viewed by 824
Abstract
China’s agricultural sector faces significant challenges, including fragmented farming practices, limited farmer knowledge of sustainable production, and outdated pest control technologies. These issues result in improper fertilization, pesticide application, and disposal of agricultural inputs, contributing to agricultural non-point source pollution and hindering the [...] Read more.
China’s agricultural sector faces significant challenges, including fragmented farming practices, limited farmer knowledge of sustainable production, and outdated pest control technologies. These issues result in improper fertilization, pesticide application, and disposal of agricultural inputs, contributing to agricultural non-point source pollution and hindering the transition to a green economy. Thus, promoting green production behavior among farmers is critical for achieving carbon peaking, carbon neutrality, and harmonious coexistence between humans and nature. However, the existing literature on this topic is still relatively scarce. This study aims to investigate the impact of farmers’ cognition on their green production behavior (GPB). Considering the role of policy, this study also examines the moderating effect of government regulation in this relationship. An analysis of 306 survey responses from tea farmers in Jingmai Mountain, Pu’er City, Yunnan Province, reveals that farmers’ cognition exerts a significant and positive impact on GPB. Social norms and personal norms serve as chain mediators in the relationship between farmers’ cognition and GPB. Moreover, government regulation moderates the influence of farmers’ cognition on social norms, further amplifying its impact on them. This study advances the theoretical understanding of farmers’ behavior and offers practical insights for fostering the sustainable development of the tea industry. Full article
Show Figures

Figure 1

Figure 1
<p>Research model.</p>
Full article ">Figure 2
<p>Distribution of Research Areas.</p>
Full article ">Figure 3
<p>The moderating effect of Social Norms and Farmer Cognition (<span class="html-italic">N</span> = 306).</p>
Full article ">
23 pages, 1901 KiB  
Article
Economic and Environmental Effects of Farmers’ Green Production Behaviors: Evidence from Major Rice-Producing Areas in Jiangxi Province, China
by Mengling Zhang, Li Zhou, Yuhan Zhang and Wangyue Zhou
Land 2024, 13(10), 1668; https://doi.org/10.3390/land13101668 - 13 Oct 2024
Viewed by 776
Abstract
This study examines the economic and environmental impacts of green production practices among farmers. It aims to contribute to sustainable agricultural development, mitigate agricultural non-point source (NPS) pollution, and align environmental protection with economic growth. This paper utilizes survey data from 1345 farm [...] Read more.
This study examines the economic and environmental impacts of green production practices among farmers. It aims to contribute to sustainable agricultural development, mitigate agricultural non-point source (NPS) pollution, and align environmental protection with economic growth. This paper utilizes survey data from 1345 farm households in the main rice production areas of Jiangxi Province, China, using the example of reduced fertilizer application (RFA) among rice farmers. This study constructs a slack-based measure data envelopment analysis (DEA—SBM) model with undesirable outputs to measure environmental effects and applies an endogenous switching regression model (ESRM) to test the economic and environmental effects of farmers’ adoption of green production technologies. We found the following: (1) The RFA behavior of farmers has a significant positive impact on their net profit per hectare (NPH), helping farmers increase their income, with the increase ranging from 2.05% to 6.54%. (2) Farmers’ RFA behavior has a significant positive impact on agricultural green productivity (AGP), contributing to the improvement of the environment, ranging from 44.09% to 45.35%. (3) A heterogeneity analysis found inconsistencies in the income-enhancing and environmental-enhancing effects at different quantiles of NPH and AGP. Therefore, attention should be placed on improving the agricultural product quality supervision system under the market circulation mechanism, creating land scale conditions conducive to the promotion and application of fertilizer reduction technologies and promoting the implementation of externality internalization compensation systems. Full article
Show Figures

Figure 1

Figure 1
<p>A framework of the effects of farmers’ RFA.</p>
Full article ">Figure 2
<p>The distribution of sample counties. The map data in <a href="#land-13-01668-f001" class="html-fig">Figure 1</a> are from DataV. GeoAtlas. <a href="https://datav.aliyun.com/portal/school/atlas/area_selector" target="_blank">https://datav.aliyun.com/portal/school/atlas/area_selector</a>, accessed on 27 May 2024.</p>
Full article ">Figure 3
<p>Probability density of farmers’ NPH in two scenarios.</p>
Full article ">Figure 4
<p>Probability density of AGP in two scenarios.</p>
Full article ">Figure 5
<p>Interquartile regression coefficients and trends.</p>
Full article ">
Back to TopTop