Realizing ecological product values is a key part of China’s ecological civilization construction, and a necessity for China to make policy and manage natural resources. This paper gives definition of conceptual content of ecological products according to realization need of ecological product values, and establishes a system margin of ecological product values, in which the basis of realizing ecological product values is discussed from ecological system, ecological product value constitution, ecological product accounting and balancing. Life circle rule is used to build the approaches to ecological product values, including unit processes of ecological system, ecological products, accounting, balancing, producing, trading and consuming. Alternative approaches involve three key steps, producing, trading and consuming. Selection of them is actually to define the trading ways and to turn products into consumer goods. The core in producing stage is supplier and supplying means of productive elements, the key in consuming stage is payer who is related to consuming category of ecological products. Analysis and summary of approaches to different ecological systems and realization of ecological product values provides references for the innovation of realizing ecological product values.
This paper, by means of employing statistics, cases, references, expert query, tendency extrapolation and regional analogy, estimates Chinas mine damaged land coefficient, restorable ratio and reclamation use proportion, and forecasts the damaged mine lands, lands pending for reclamation and reclamation potential. The results show: 1) the damaged land coefficient is 0.31hm^2/10^4t in underground coal mines, 0.10hm^2/10^4t in opencast coal mines,0.30hm^2/10^4t at iron mines, the damaged land area is 13.33hm^2 per 100million bricks; 2) Until 2020, the damaged mine land is estimated to amount to 806.60×10^4hm^2, of which the coal mines possess the most, up to 233.93×10^4hm^2,120.20×10^4hm^2 to be restored. The damaged coal mine land can be restored to farmland, grassland and construction, 52.99×10^4hm^2, 55.19×10^4hm^2, and 12.20×10^4hm^2, respectively; 3) Reclamation potential is big that a sum of 308.78×10^4hm^2 can be restored, of which 148.83×10^4hm^2 to farmland, 125.31×10^4hm^2 to grass or woods land, 34.64×10^4hm^2 to construction land. The damaged coal mine land is key to be restored to farmland.
Based on the analysis of conventional ecological footprint theory, this paper revises its production factor and balance factor to get an improved model. Then it uses the conventional and modified models to calculate Lanzhous farmland ecological footprint from 2000-2008, and analyzes its dynamic changes. Results from the traditional model show increasing ecological footprint, decreasing ecological carrying capacity, and a weak sustainable state with ecological surplus, but results from the improved model are just the opposite. After analysis it turns out that the modified model is more practical and conducive to the study on sustainable use of farmland in Lanzhou. This paper uses the improved model to forecast farmland ecological footprint, ecological carrying capacity and sustainable index in Lanzhou, and gives ways of raising the average ecological productivity of farmland.
This paper uses statistics and scenario simulation to classify the damaged farmland in loess hilly terrain into three categories: mild, moderate and severe. The rehabilitation fee is calculated based on three subsiding slopes by single project: 4 082 RMB for the mild, per mu, 5 455-5 610 for the moderate and 11 374-12 283 for the severe where slope is below 5 degrees; 6 635-7 389 for the mild, 7 509-8 262 for the moderate and 10 996-11 751 for the severe where slope is between 5 to 15 degrees; 8 386-9 442 for mild, 9 259-10 318 for the moderate and 12 748-13 804 for the severe where slope is between 15 to 25 degrees, which is relevant with damaged degree, slope and transporting distance of volume. At Pingshuo’s Panjiayao coal mine with the damaged degree mainly mild to moderate, estimated by means of MSAS and GIS, the average static rehabilitation fee is 7 016RMB, most contributed by land flatting works.
Mine lands are a combination of land management and ore resources management and a key component in land and resources management. Mine land intensive use is of importance in economizing and protecting farmlands. This paper, based on references, analyzes the definition of mine lands, features, supply scale, mining destroyed land scale, and presents the connotation of mine land intensive use, occupying less land, restoring farmland, quick rehabilitation, and approaches in planning, saving lands and reforming from exploration, mining and closing mine.
Fractal dimension can effectively describe complex textural features. The traditional automatic classification of remote sensing is mainly based on the spectrum feature information of data, which is difficult to utilize the textural information of remote sensing image throughly and effectively. With the wide application of HR remote sensing data in recent years, problems such as how to quantize textural features, how to classify ground objects according to their respective textural features are arousing many scholars’ concern. Based on the comparison of different effects of operator extraction on different edges, the study takes edge extractions on Quickbird data of four kinds of typical land cover types, and calculates dimensions of image sample boxes on the platform of Matlab. It is found of significant difference for box dimensions of these land cover classifications by comparison, thus fractal dimension can be utilized to quantize textural features of remote sensing images and by which, different land cover types can be classified effectively.
This paper discusses the sense of land rehabilitation planning and studies its feasibility. Rehabilitation planning is pivot to the whole rehabilitation and requires the rehabilitation be proceeded while mining, and ensures the capital and preserves the topsoil. Rehabilitation projects include soil reconstruction, vegetation reconstruction, adjuvant works, monitoring and maintenance. Rehabilitation works are poor in feasibility due to their static operation which can not match the dynamic mining, small scale maps, and absence of blocks, which can be improved through ecological ways at the early destroyed land stage, planning fitting with phased and annual designs, a local project ahead the overall project, and a detailed project execution map.
RS and GIS are a helpful tool to measure the soil erosion, to quickly monitor the dynamic changes in soil erosion distribution and extent. This paper, based on a case study of the upstream of Fenhe Reservoir in Yellow River, applies the Remote Sensing data of Landsat MSS (1976), TM (1990) and ETM+ (2002) to dynamically monitor the land erosion with the results indicating that the soil has been eroded extensively during 1976 to 1990, and turned to a good condition in general during 1990 to 2002, but still worsening locally. It is a big task to maintain the water and soil.