Accuracy test of model simulation by linear regression analysis.

Accuracy test of model simulation by linear regression analysis.

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Riparian buffers can influence water quality in downstream lakes or rivers by buffering non-point source pollution in upstream agricultural fields. With increasing nitrogen (N) pollution in small agricultural watersheds, a major function of riparian buffers is to retain N in the soil. A series of field experiments were conducted to monitor pollutan...

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Context 1
... shown in Table 2, the 1-and 3-m-wide models showed a small proportion of variables that could not be explained. Probabilities (Sig.) for the significance test of regression equations were 0.047 and 0.000 (<0.05), indicating that the simulation results are valid. ...
Context 2
... shown in Table 2, the 1- and 3-m-wide models showed a small proportion of variables that could not be explained. Probabilities (Sig.) for the significance test of regression equations were 0.047 and 0.000 (<0.05), indicating that the simulation results are valid. ...

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Citations

... Nonpoint source pollutant diffusion simulation methods are typically used for plain river networks with complex tributary distribution and pollutant sources. Currently, some studies [5][6][7] conducted in-depth investigations of the numerical simulation of river and groundwater systems and pollutant source tracing technology. Makri et al. [8] conducted an in-depth study on how the hydrological characteristics of groundwater systems affect the diffusion and attenuation of heavy metal pollutants such as benzene. ...
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... Sun et al. [22] studied the impact of the construction of artificial groundwater reservoirs on the groundwater flow and water quality of the reservoir and its downstream and found that the construction of groundwater reservoirs led to the accumulation of nitrate in the storage water. Lin et al. [23] studied the migration of total nitrogen in the riparian buffer zone of agricultural watersheds based on the finite element simulation method and found that the riparian buffer zone had a certain retention effect on soil pollutants. Malinovsky et al. [24] took the Khibiny apatite-nepheline mine in Kola Peninsula, Russia, as an example, collected snow, surface water, and deposited and suspended sediments samples for analysis. ...
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A qualitative evaluation of ecosystem services after stream restoration measures and a quantitative analysis of nitrogen reduction, greenhouse gas balance and (semi-)natural biomass production in the restored parts of the creek De Kaweise Loop as a test case. Master Thesis To attain the Master of Science Biology, track 'Transnational ecosystem-based Water Management' (TWM) at the Radboud University, Abstract In this study, methods were developed in order to assess the change of ecosystem services after freshwater stream restoration and accompanied management. The term ecosystem service was explained and applied to lotic aquatic ecosystems. By a literature review, restoration, measures and management options were linked to ecosystem components and processes, which were subsequently linked to the delivery of, and change in ecosystem services. An overview was created in the form of a table that also included potential negative effects of altered conditions, restoration and management. A score system was developed based on the linkage between restoration/rehabilitation measures and change of ES, in order to provide a semi-qualitative method for the assessment of ecosystem service changes. Methods for quantification were developed for three environmental parameters (nitrogen reduction, change in greenhouse gas balance, natural biomass production available for harvest) closely related to three ecosystem services (water purification, atmospheric composition and climate regulation, and biomass). The quantification was based on land cover units (vegetation types and land use) and processes linked to these units (e.g fertilization, nutrient flow, denitrification, carbon sequestration, carbon emission, growth). An additional goal of this study was to provide insight into the change in ecosystem services as a result of a restoration project. The framework developed was tested for a small, restored stream in the Netherlands as a case study. At the end, an economic valuation was carried out on request of the water board concerned. In the present study, restoration/rehabilitation measures and management could successfully be linked to changes in ecosystem services. Although an increase in the provision of ecosystem services was found with the semi-qualitative method, negative effects were also shown and the provision of ecosystem services was low during the first 5 years. For the quantification, it was found that the restoration project had resulted in a total reduction of 845 up to 5001 N kg per year, an average reduction in CO2-e of 141.2 ton per year and a natural biomass production of 430.22 ton dry matter for a total area of 20 ha. The economic valuation showed that the change of the three environmental parameters amounted to a value of 22,827 euro per year. However, as this value was calculated using conservative process values, real values may be much higher, up to 38, 000 euros per year (using prevention costs). With this study, an overview and assessment method for the change in ecosystem services due to restoration/rehabilitation measures and management in lotic aquatic temperate ecosystems becomes available to water management.
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Abstract To identify a vegetation configuration pattern with a high-efficiency purification ability for total nitrogen (TN), available nitrogen (AN), total phosphorous (TP), available phosphorous (AP), and chemical oxygen demand (COD) based on comprehensive assessment results, a water discharge experiment was performed in the Luan River in China with the following riparian forests: I, pure broad-leaved; II, mixed broad-leaved; III, mixed coniferous and broad-leaved; IV, mixed coniferous; and V, pure coniferous. From the riparian buffer zone to the river channel, the evaluation showed that pattern I had the highest purification ability at 1 m and 2 m; at a width of 4 m, pattern III had the highest purification ability; at a distance of 7 m, pattern V showed the highest purification ability; at 10 m, pattern IV showed the highest purification ability, pattern II the lowest. It is advisable to give priority to plant coniferous species from 0 m to 4 m from the river bank, while it is advisable to give priority to plant broad-leaved species from 4 m to 10 m from the river bank. We therefore recommend these vegetation configuration patterns in the development and management of runoff purification systems.