Optimization of spatial allocation for soil and water conservation measures based on genetic algorithm
[Background] Configuring different types of measures reasonably in space to produce the comprehensive benefits in ecological, economic and social aspect under limited investment of soil and water conservation has become a hot research. Furthermore, solving the multi-objective optimal problem is the key because the optimal allocation of soil and water conservation measures in space refers to multi- objective. [Methods] This research focused on the area of Chanting County, Fujian Province of which soil is being serious eroded. The soil and water loss area in 2012 was as evaluation object of suitability of soil and water conservation measures. The study area was divided into the area of ecological natural restoration and artificial auxiliary control based on the suitability assessment of the enclosing measures. This paper constructed an optimal allocation model of water and soil conservation measures in space with the aim of minimum investment, maximum ecological benefits and maximum suitability in the artificial auxiliary management area, and adopted a fast and elitist multi-objective genetic algorithm (NSGA-II) to solve the model in order to screen out the best program. Moreover, the experimental results were verified and analyzed by using the reality of soil and water erosion control between 2013 and 2015. [Results] According to the optimized allocation results, the spatial distribution of soil and water conservation measures was directed by the maximization of ecological benefits and the maximization of suitability of spatial distribution in the case of stationary government investment funds. Calculating the investment cost, ecological benefits and suitability of optimization allocation layout and actual spatial layout of soil and water conservation measures, the results were as follow: the investment cost of actual layout was 6.964 5 *107, the ecological benefits of actual layout was 7.908 0 *103, and the suitability of actual layout was 1.953 3 *104. However, the investment cost of optimized allocation layout was 6.579 1 *107, the ecological benefits of optimized allocation layout was 7.907 3 *103, and the suitability of optimized allocation was 2.054 1 *104. It was found that the optimal allocation layout was significantly improved in terms of investment cost and suitability compared to the actual space layout of soil and water conservation measures. The reason that the ecological benefits were reduced was that the decrease of the invested cost inevitably led to the reduction of the ecological benefits. Moreover, the spatial distribution of soil and water conservation measures between optimal allocation and actual space layout was similar in most of regions, and the degree of similarity was 73.62%. [Conclusions] With the increase of evolution generation, the effect of optimal allocation of soil and water conservation based on NSGA-II algorithm was obvious, and the optimal allocation layout was reasonable and practicable, which can offer the decision- making basis for government implementing soil and water conservation measures.
Rainfall characteristics of Rocker Arm Top Spray rainfall simulator
[ Background] Rainfall simulator is commonly used in indoor and outdoor soil erosion research and the process of infiltration and rainfall runoff study. However, tall nozzles, small efficient rainfall area, and differences from natural rainfall constraint some rainfall simulators widely used. Based on all above, we developed a Rocker Arm Top Spray rainfall simulator which is supposed to be used widely. [Methods] The Rocker Arm Top Spray rainfall simulator we developed was composed of three rainfall nozzles (number1, 2, and 5, aperture 9 mm), two middle rainfall nozzles (number 3 and 4, aperture 13 mm), Axle tube, “cross type冶rocker arm, Axle hole, connecting rod, crank connecting rod mechanism, motor, hose, main water supply pipe, pressure gauge and water well pipeline interface. The precipitation area, rainfall intensity, average rainfall uniformity coefficient, median diameter of raindrops, terminal velocity and the kinetic energy of rain were measured, and the applicability of the rainfall simulator was discussed. [Results] Rainfall uniformity value was 41%, when the rainfall area was 100 m2, which maybe the maximum rainfall area of the simulator. When the rainfall area was 50 m2, water pressure was 0.32 kg/ cm2, the rainfall uniformity value was 82% for the maximum rainfall intensity (116.25 mm/ h) and 46% for the minimum rainfall intensity (61.01 mm/ h). Under the same pressure, the rainfall uniformity value range changed from 46% to 82%. The rainfall uniformity value was 82% when the rainfall nozzles moving forward, while the rainfall uniformity value was 80% when the rainfall nozzles moving backward. That means that when the rainfall nozzles moving forward and backward, the rainfall uniformity value was more than 80%, which accorded with the requirements of natural rainfall uniformity. But the average rainfall uniformity value was smaller than 80% when the rainfall nozzle moving left and right, which might be caused by the uneven rainfall. The rain intensity was related to the rainfall median diameter. The measured average median diameter (D50), the average terminal velocity of raindrops, and the average raindrop kinetic energy was 1.67 mm, 3.656 m/ s and 299.4 J/ (m2·cm) respectively, under the different rainfall intensity. The median diameter value presented decreasing trend with the increase of rainfall intensity, but the median diameter of natural rainfall increased with the increase of rainfall intensity, which may be caused by the definite apertures of the three rainfall nozzle. The median diameter decreased with the height increasing, or because the rainfall intensity reached 80 ~ 100 mm/ h the measured median diameter no longer increased. With the increase of rainfall intensity, the terminal velocity of raindrops tended to decrease, but the kinetic energy of raindrops showed an increasing trend. That was probably because that the droplet density was very large, the kinetic energy of rainfall increased with the rainfall intensity increasing. [Conclusions] The device was small, light, in simple operation and convenient movement, especially suitable for field rainfall simulation,which can meet the requirements of the general field and outdoor experiments.
On monitoring and the public service of soil and water conservation in the time of ecological civilization construction
[Background] In the new times of ecological civilization, monitoring and the public service of soil and water conservation is the important content of national ecological environment monitoring, and ecological environment monitoring is the key foundation shoring for ecological civilization construction. [Methods] According to the states documents of Suggestions to Quickly Propel Ecological Civilization Construction and Development Scheme of Ecological Environment Monitoring Network, etc. , the guiding ideology, construction principles, and targeted tasks of national ecological environment monitoring network were put forward. Combining with Soil and Water Conservation Plan in China approved by the State Council, the targets of monitoring soil and water conservation were analyzed contrast to the corresponding requirements of state爷s ecological environment monitoring. Based on the joint mechanism of monitoring and management, decision-making, supervision, and target assessment, the ideas on the monitoring and public services of soil and water conservation were proposed under the macro-demands of constructing the national ecological environment monitoring network. [ Results ] Soil and water conservation monitoring should be in top-level design, and new targets could be determined. They include: to speed up the construction of monitoring network in a whole system of sky and ground, up and down coordinating, and information sharing, to implement the operation mechanism of monitoring and monitoring points in a way of public welfare institution, and to clarify the responsibilities and authorities of monitoring agencies at all levels. Further, a regular investigation and dynamic monitoring system should be established, the implementation of monitoring and supervision, monitoring and assessment should be linked. Moreover, by improving the technical standards, integrating the monitoring measures, expanding the application of high and new technical equipment, and escalating the level of automation, the information could be linked and shared. [Conclusions] Such system will accurately provide the evidences and supports on-time for the ecological civilization, inspection of targets with responsibilities, and accountability of responsibilities, i. e. , serves better for society and public.
Rustic opinion of soil and water conservation monitoring in the new period
Monitoring is the basis and an important work of soil and water conservation. The new requirements and tasks are being demanded for soil and water conservation because of ecological civilization construction and social harmonious development. It is heavily responsible and extremely urgent that we accomplish soil and water conservation monitoring work in keeping with social development so as to strengthen foundation and provide support for soil and water conservation and ecological civilization construction. After analyzing and considering, the article put forward policy proposals and guarantee strategies about how to carry out soil and water conservation monitoring work keeping with the time in which we reinforce provision and lay particular emphasis on reformation to provide high-level monitoring results and services.