River Nitrous Oxide Emission Estimation via Land-River-Atmosphere Simulation

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Solution Overview

Problem

Current methods for estimating N2O emissions from rivers are inaccurate due to the use of constant emission factors and failure to account for the nitrogen conversion efficiency based on hydrological and water quality status, leading to overestimation or underestimation and poor coordination of greenhouse gas pollution control.

Innovation Solution

A method involving land-river-atmosphere simulation using Random Forest regression models and air-water interface gas exchange models to predict nitrogen emissions from various sources, incorporating geographical, climate, and hydrological parameters to calculate river N2O emissions at a sub-basin level.

Engineering Contradictions & Design Principles

VSEngineering Contradiction Analysis

1Ease of manufacture

If constant emission factors are used to estimate river N2O emissions, then the estimation process is simple, but the accuracy of emission estimates deteriorates due to overestimation or underestimation

Engineering Contradiction:
Improvesimplicity of estimation processVSAvoidaccuracy of N2O emission estimates
Core Design Contradiction:
Ease of manufactureVSMeasurement precision

Solution Approach 1:

The patent transforms the constant emission factor into a dynamic parameter that varies with hydrological conditions (flow rate, water level) and water quality parameters (nitrogen concentration, temperature). This allows the emission factor to adapt to different river conditions, improving accuracy while maintaining computational feasibility through standardized measurement protocols.

Inventive Principle:
Principle #35Parameter changes

Solution Approach 2:

The patent replaces the simple constant-factor calculation method with a comprehensive simulation model that integrates hydrological processes, water quality transformations, and gas exchange mechanisms. This substitution enables accurate representation of the complex land-river-atmosphere nitrogen transfer process.

Inventive Principle:
Principle #28Mechanics substitution (Replace mechanical system)

2Ease of operation

If the emission coefficient method is used, then the calculation process is straightforward, but the ability to determine nitrogen conversion efficiency based on hydrological and water quality status deteriorates

Engineering Contradiction:
Improvestraightforwardness of calculationVSAvoidnitrogen conversion efficiency information
Core Design Contradiction:
Ease of operationVSLoss of information

Solution Approach 1:

The patent segments the nitrogen transformation process into distinct stages: land-based nitrogen emission, riverine nitrogen transport and conversion, and atmospheric gas exchange. Each stage is modeled separately with its own governing equations and parameters, allowing detailed tracking of nitrogen conversion efficiency while maintaining a structured calculation framework.

Inventive Principle:
Principle #1Segmentation

Solution Approach 2:

The patent introduces an integrated simulation model as an intermediary system that connects hydrological conditions, water quality parameters, and nitrogen conversion processes. This intermediary enables the determination of nitrogen conversion efficiency by mediating between input data (flow rate, nitrogen concentration) and output results (N2O emission estimates).

Inventive Principle:
Principle #24Intermediary (Mediator)

3Ease of manufacture

If existing estimation methods are used, then the methodology is simple to implement, but the coordination of greenhouse gas pollution control deteriorates due to poor accuracy

Engineering Contradiction:
Improveease of implementationVSAvoidcoordination of pollution control
Core Design Contradiction:
Ease of manufactureVSReliability

Solution Approach 1:

The patent develops a universal simulation framework that can estimate N2O emissions across diverse river systems with varying hydrological and water quality conditions. The model integrates multiple functions: hydrological process simulation, water quality transformation modeling, and gas exchange calculation, enabling reliable pollution control coordination at different spatial and temporal scales.

Inventive Principle:
Principle #6Universality (Multi-functionality)

Applied Scientific Principles

This section explains which scientific principles are used to turn an abstract innovation direction into a practical engineering solution.

Function Achieved in This Case

This approach provides accurate and precise estimation of river N2O emissions, improving calculation accuracy to a monthly scale and catchment area resolution, enabling effective coordinated control of land, river, and air pollution.

Implementation Method 1

providing an air-water interface gas exchange model and inputting the hydrological parameters of each sub-basin and water quality concentration of each sub-basin in each region of the river; and processing concentration conversion to obtain a total river N2O emission

Methodology Applied
Scientific EffectGas exchange: Diffusion

Data Source

PatentUS20240321403A1Method of Determining River Nitrous Oxide Emission based on Land-River-Atmosphere Simulation
Publication Date: 2024.09.26 HARBIN INST OF TECH
  • US20240321403A1 patent drawing
  • US20240321403A1 patent drawing
  • US20240321403A1 patent drawing

AI summary

A method of determining nitrous oxide emission of a river based on land-river-atmosphere simulation, includes the steps of: obtaining nitrogen emission from land in each region; dividing the nitrogen emission into a prediction set and a test set; using nitrogen emission prediction set, and geographical variables and climate variables under the nitrogen emission prediction set to process RF regression model training to obtain a trained RF regression model, using nitrogen emission test set, and geographical variables and climate variables under the nitrogen emission test set to process RF regression model training to obtain a trained RF regression model, and outputting a river water quality concentration of each sub-basin in each region; obtaining river hydrological parameters of each sub-basin, inputting the river hydrological parameters and river water quality concentration of each sub-basin to an air-water interface gas exchange model to obtain a total river N2O emission in each sub-basin.