CN101974910A - Ecological restoration method for side slope of tailing pond later dam under condition of no earthing - Google Patents

Ecological restoration method for side slope of tailing pond later dam under condition of no earthing Download PDF

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Publication number
CN101974910A
CN101974910A CN 201010285841 CN201010285841A CN101974910A CN 101974910 A CN101974910 A CN 101974910A CN 201010285841 CN201010285841 CN 201010285841 CN 201010285841 A CN201010285841 A CN 201010285841A CN 101974910 A CN101974910 A CN 101974910A
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vetiver
fertilizer
restoration method
slope
grass
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CN101974910B (en
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戴宏文
周连碧
郑学敏
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Beijing General Research Institute of Mining and Metallurgy
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Beijing General Research Institute of Mining and Metallurgy
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Abstract

The invention belongs to the technical field of ecological restoration of mine wasteland, and relates to a slope vegetation stable ecological restoration technology of a tailing pond non-covered soil later-stage dam, which is realized by planting vetiver grass and sowing slope greening grass seeds between vetiver grass seedling rows to form a sand-fixing root system network. Wherein the slope greening grass seeds are bermudagrass, alfalfa, white clover and Shazhangwang in a ratio of 5-10: 1-2. The method provided by the invention is used for carrying out ecological restoration on the side slope of the tailing later dam under the condition without earthing, a stable vegetation layer is established, and the side slope is stabilized, the water and soil are kept, and runoff and tailing sand dust are inhibited.

Description

The ecological restoring method of later stage dam, the mine tailing storehouse side slope under the no earthing condition
Technical field
The invention belongs to abandoned land ecological reestablishment field, mine, the side slope vegetation that relates to a kind of mine tailing storehouse and do not have mulching soil later stage dam is stablized ecological reestablishment.
Background technology
The mine tailing storehouse is an indispensable important component part in the mine ore dressing production procedure facility.Mine tailing storehouse dam body is stablizing of later stage dam side slope particularly, is the lifeline of mine tailing storehouse safe operation.How the later stage dam, mine tailing storehouse of China's wet method discharging mine tailing is built to have the thick CHARACTERISTICS OF TAILINGS SAND heap that satisfies the engineering mechanics requirement of strength.Build technology according to this a pile, follow the tailings discharging process, by rising certain absolute altitude on the mine tailing storehouse, constructing mine tailing later stage dam step by step stage by stage.Store up mine tailing storage capacity to satisfy, to force down phreatic line and make the safe operation requirement of mine tailing storehouse.
After mine tailing storehouse later stage Ba Dui built and finishes, owing to the bulk characteristics of CHARACTERISTICS OF TAILINGS SAND, side slope was met precipitation and is very easily produced soil erosion, in the serious zone of wind erosion, easily produce the CHARACTERISTICS OF TAILINGS SAND airborne dust, even " mine tailing sandstorm " generation frequency was also very high.For preventing erosion and harm such as serious airborne dust, guarantee later stage dam stability of slope, traditional measure is outside each after date phase dam on the side slope, the mulching soil layer, general overlying soil thickness 300~500mm, then, plant grass planting on the overburden layer surface and irritate kind, with ecology recovering.
The numerous mines of China are distributed in stone district, remote mountains, and it is desirable that particularly southern many mines do not have soil, and fetching earth in purchase that have even other arable land, not only causing the loss of ploughing, and having improved the mine cost of production greatly.
Summary of the invention
The purpose of this invention is to provide a kind of later stage dam, mine tailing storehouse side slope ecological renovation method that does not have under the earthing condition, by plantation vetiver and sowing greening side slope grass seeds, the root system network that constitutes solid sand is realized.
Described greening side slope grass seeds is Bermuda grass, alfalfa, Bai Sanye and prairie milk vetch, and the seed quality ratio is 5~10: 1~2: 1~2: 1~2, be preferably 8: 1: 1: 1.
Later stage dam, mine tailing storehouse side slope ecological renovation method under the no earthing condition provided by the invention specifically comprises the steps:
1) mine tailing storehouse later stage dam side slope is divided the operation area every 30~50m;
2) excavate wide 20cm by later stage dam, mine tailing storehouse isohypse, the seedling plantation ditch of dark 15cm, described plantation ditch begins excavation apart from sloping body top 0.5m, every contour interval 1m excavation delegation, totally 3 goes, down, by contour interval 1.5m excavation plantation ditch.
3) executing mass ratio in the ditch is 1~2: 1~2: 0.5~1 fertilizer, phosphate fertilizer and composite fertilizer are as base fertilizer, and total amount is 80~100g/m 2
4) 1~3 strain vetiver down in the plantation ditches of 3~4 row, is planted every the 10cm kind in top, side slope top, and the top down in the following plantation ditches of 3~4 row plantation ditches, is planted 1~3 strain vetiver every the 15cm kind, and watered normal root water;
5) seedling capable between the grass seeds of the above-mentioned greening side slope of sowing, depth of planting is 2~3cm, application rate is 8~12g/m 2, and to impose mass ratio be 1~2: 2~3 fertilizer and composite fertilizer.
Also comprise fostering and control measures of later stage, specific as follows:
1) annual vegetation turn green, before the rainy season before freeze-up, the vetiver growing area is respectively applied fertilizer: phosphate fertilizer: composite fertilizer's ratio is 1~2: 1~2; 0.5~1, consumption is 30~50g/m 2
2) arrange in full summer every year to prune vetiver once, keep careless height of seedling degree 0.8m~1.2m;
3) utilize many vetiver plant that tillers in early days, in time the damage plant is reseeded;
4), add water 1~2 time, the solar heat protection evil as dry year;
5) in time remove the CHARACTERISTICS OF TAILINGS SAND of gland vegetable layer;
6) routine observation vegetation growing way is in time taked pest control measure.
The present invention utilizes the powerful root system power (dark Gen Keda 2m) of bank protection plant vetiver, the root system network of dark, the shallow collocation of crawling that the high fast grass seeds of well developed root system, coverage forms for the face of land of representative with Bermuda grass, realize directly fixedly mine tailing storehouse sand side slope, constitute and stablize the domatic vegetational type's system of controlling.Mine tailing storehouse side slope does not need earthing, can directly be planted on the thick CHARACTERISTICS OF TAILINGS SAND dam, has realized stablizing mine tailing storehouse side slope with bioanalysis.According to method provided by the invention later stage dam, mine tailing storehouse side slope under the no earthing condition is carried out restoration of the ecosystem, set up firm vegetable layer, have stable side slope simultaneously, conserve water and soil, suppress the effect of runoff, CHARACTERISTICS OF TAILINGS SAND airborne dust.
The specific embodiment
Following examples are used to illustrate the present invention, but are not used for limiting the scope of the invention.Without departing from the spirit and substance of the case in the present invention, modification or replacement to the inventive method, step or condition are done all belong to scope of the present invention.
If do not specialize the conventional means that used technological means is well known to those skilled in the art among the embodiment.
Embodiment 1
Area carries out restoration of the ecosystem in the copper mining tailing storehouse CHARACTERISTICS OF TAILINGS SAND side slope more than 13 hectares, comprises the steps:
1) smooth for the protection later stage dam scope of operation, do not change the loose media design grade, last side slope is carried out the division of operation area every 50m;
2) press later stage dam, mine tailing storehouse isohypse excavation seedling plantation ditch, begin excavation apart from top 0.5m, close on the ditch spacing to spacing 1m, excavation 3 row, plantation ditch spacing 1.5m down guarantees that stronger wind resistance, rain ability are arranged at top.Plantation furrow width 20cm, dark 15cm.
3) executing mass ratio in the ditch is 1: 1: 0.6 fertilizer, phosphate fertilizer, composite fertilizer, and total consumption is decided according to area, is 100g/m 2Wherein fertilizer is the chicken manure fermenting fertilizer, and phosphate fertilizer is calcium superphosphate, and composite fertilizer is N, P, K composite fertilizer, available from jiangsu wuxi Poly chemical fertilizer Co., Ltd.
4) plantation vetiver in the plantation ditch, the vetiver spacing in the rows of top 3 row plantation ditches is 10cm, the spacing in the rows of vetiver is 15cm in this 3 row plantation ditch plantation ditch down, according to the specification size of vetiver plant, plantation 1~3 strain of every place.After the plantation, water normal root water.
5) seedling of vetiver capable between the sowing ratio be 8: 1: 1: 1 Bermuda grass, alfalfa, Bai Sanye and prairie milk vetch seed, the seed consumption is decided according to area, is 10g/m 2The planting seed degree of depth is 3cm.Apply fertilizer behind the planting seed, use mass ratio and be 1: 2 fertilizer and composite fertilizer.
6) formulate the detailed later stage and fostered and managed and protected measure:
1. annual vegetation turned green before rainy season before preceding, freeze-up, and the vetiver growing area is respectively applied fertilizer: phosphate fertilizer: composite fertilizer's ratio is that 1: 1: 0.6 consumption is 40g/m 2
2. arrange in full summer every year to prune vetiver once, generally keep about careless height of seedling degree 1m.
3. find to have on domatic the plant damage, in time reseed careless seedling, can utilize many plant that tillers in early days.
4. meet dry year, add water 1~2 time, the solar heat protection evil.
5. in time remove the CHARACTERISTICS OF TAILINGS SAND of gland vegetable layer.
6. routine observation vegetation growing way, the prevention and elimination of disease and pests of in time taking measures.
Later stage dam side slope after the reparation, vegetation is stable, and conservation of soil and water amount is more than 95%, dark green, the dense vegetation of the side slope face of land, reservoir area a slice, coverage surpasses 90%, and control airborne dust ecological effect is obvious.Reservoir area side slope part vegetation kind is procreation voluntarily.The place vegetation does not require meticulous fostering, and is low level management substantially.Group's long-term stability that various plants constitutes, reached plant behind the earthing by effect, vegetable layer does not have obvious degradation phenomena, has tangible economy, society and environmental benefit.
Embodiment 2
Basic process is with embodiment 1, and the mass ratio of different is Bermuda grass, alfalfa, Bai Sanye and prairie milk vetch seed is 10: 2: 2: 2, and the sowing total amount is 12g/m 2
Embodiment 3
Basic process is with embodiment 1, and the ratio of the fertilizer that different is uses in the vetiver plantation ditch, phosphate fertilizer, composite fertilizer is 2: 2: 1, and using total amount is 80g/m 2

Claims (8)

1.一种无覆土条件下的尾矿后期坝边坡的生态修复方法,其特征在于,种植香根草和播种边坡绿化的草种,构成固砂的根系网络。1. The ecological restoration method of the tailings late stage dam slope under a kind of no covering soil condition, it is characterized in that, the grass seed of planting vetiver and sowing slope greening constitutes the root system network of sand fixation. 2.根据权利要求1所述的修复方法,其特征在于,所述边坡绿化草种播种于香根草种苗行之间。2. The restoration method according to claim 1, characterized in that, the slope greening grass seeds are sown between the rows of vetiver seedlings. 3.根据权利要求1或2所述的修复方法,其特征在于,所述边坡绿化草种为狗牙根、紫花苜蓿、白三叶和沙打旺。3. The restoration method according to claim 1 or 2, characterized in that, the slope greening grass species are bermudagrass, alfalfa, white clover and sandawang. 4.根据权利要求3所述的修复方法,其特征在于,所述狗牙根、紫花苜蓿、白三叶和沙打旺的种子质量比为5~10∶1~2∶1~2∶1~2。4. The restoration method according to claim 3, characterized in that, the mass ratio of the seeds of bermudagrass, alfalfa, white clover and sandawang is 5~10:1~2:1~2:1~2 . 5.根据权利要求4所述的修复方法,其特征在于,所述狗牙根、紫花苜蓿、白三叶和沙打旺的种子质量比为8∶1∶1∶1。5. The restoration method according to claim 4, characterized in that the mass ratio of the seeds of bermudagrass, alfalfa, white clover and sandawang is 8:1:1:1. 6.根据权利要求1至5任一项所述的修复方法,包括如下步骤:6. The repair method according to any one of claims 1 to 5, comprising the steps of: 1)尾矿库后期坝边坡每隔30~50m划分作业区;1) The dam slope in the later stage of the tailings pond is divided into operation areas every 30-50m; 2)按尾矿后期坝等高线开挖宽20cm,深15cm的种苗种植沟,所述种植沟距顶部0.5m开挖,每隔等高线间距1m开挖3行,往下,按等高线间距1.5m开挖;2) Excavate a seedling planting ditch with a width of 20 cm and a depth of 15 cm according to the contour line of the dam in the later stage of the tailings. The planting ditch is excavated 0.5 m from the top, and 3 rows are excavated every 1 m between the contour lines. Excavation with a contour spacing of 1.5m; 3)沟内施质量比为1~2∶1~2∶0.5~1的有机肥、磷肥、复合肥作为底肥;3) Apply organic fertilizer, phosphate fertilizer, and compound fertilizer with a mass ratio of 1 to 2:1 to 2:0.5 to 1 in the ditch as base fertilizer; 4)在步骤2)所述的上部3行种植沟内每隔10cm种植1~3株香根草,上部3行种植沟往下的种植沟内,每隔15cm种植1~3株香根草,并浇定根水;4) Plant 1-3 vetiver plants every 10cm in the upper 3 rows of planting ditch described in step 2), and plant 1-3 vetiver plants every 15cm in the planting ditch of the upper 3 rows of planting ditch , and water the roots; 5)香根草种苗行之间播种所述的边坡绿化草种,播种深度为2~3cm,并施以质量比为1~2∶2~3的有机肥和复合肥。5) Sow the above-mentioned slope greening grass seeds between the rows of vetiver seedlings, the sowing depth is 2-3 cm, and apply organic fertilizer and compound fertilizer with a mass ratio of 1-2:2-3. 7.根据权利要求6所述的修复方法,还包括后期的抚育和管理措施,具体如下:7. The restoration method according to claim 6, further comprising the care and management measures in the later stage, specifically as follows: 1)每年植被返青前、封冻之前的雨季前,对香根草种植区各施加有机肥,磷肥和复合肥,质量比为1~2∶1~2∶0.5~1,总用量为30~50g/m21) Every year before the vegetation turns green and before the rainy season before freezing, apply organic fertilizer, phosphorus fertilizer and compound fertilizer to the vetiver planting area, the mass ratio is 1-2:1-2:0.5-1, and the total dosage is 30-50g /m 2 ; 2)每年在盛夏安排修剪香根草一次,保持草苗高度0.8m~1.2m;2) Prune the vetiver once a year in midsummer to keep the height of the grass seedlings at 0.8m-1.2m; 3)利用早期分蘖多的植株,及时对损毁草苗进行补种;3) Use the plants with many early tillers to replant the damaged grass seedlings in time; 4)如遇干旱年,补加水1~2次,防热害;4) In case of drought, add water 1 or 2 times to prevent heat damage; 5)及时清除压盖植被层的尾矿砂;5) timely remove the tailing sand of the cover vegetation layer; 6)定期观察植被长势,及时防治病虫害。6) Regularly observe the growth of vegetation and timely prevent and control pests and diseases. 8.根据权利要求6所述的修复方法,其特征在于,所述边坡绿化草种的播种量为8~12g/m28 . The restoration method according to claim 6 , characterized in that, the sowing rate of the slope greening grass seeds is 8-12 g/m 2 .
CN2010102858413A 2010-09-17 2010-09-17 Ecological Restoration Method of Tailings Dam Slope in the Later Stage of Tailings Reservoir without Covering Soil Expired - Fee Related CN101974910B (en)

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Cited By (10)

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CN102577789A (en) * 2012-01-20 2012-07-18 内蒙古沁园欧李生态研发有限责任公司 Method of cyclic sustainable vegetation recovery for waste dump of grassland mining area
CN103814747A (en) * 2014-03-13 2014-05-28 紫金矿业集团股份有限公司 Ecological management method of gold ore tailings after hydrometallurgy
CN103821154A (en) * 2014-02-12 2014-05-28 北京矿冶研究总院 Ecological restoration method for sintering red mud storage yard side slope
CN104396551A (en) * 2014-12-15 2015-03-11 仲恺农业工程学院 Method for ecological restoration of soil in rare earth mining area by using herbaceous plants
CN105145038A (en) * 2015-07-09 2015-12-16 常州大学 Method for repairing vegetation of coal mine storage yard
CN105724006A (en) * 2016-02-02 2016-07-06 大连地拓重工有限公司 Mine-wasteland vegetation ecological recovery method
CN108951666A (en) * 2018-07-06 2018-12-07 中国地质调查局西安地质调查中心 A kind of with iron milltailings is the slope reinforcement and ecological reestablishment to gather materials
CN109526606A (en) * 2018-11-22 2019-03-29 北京市农林科学院 A method of the induction fast quick-recovery of open ground natural vegetation
CN111990189A (en) * 2020-08-31 2020-11-27 西南科技大学 Mine broken stone slope ecological restoration method driven by vetiver grass
CN118958319A (en) * 2024-08-02 2024-11-15 江西省、中国科学院庐山植物园 A method for protecting wetland slope

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Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102577789A (en) * 2012-01-20 2012-07-18 内蒙古沁园欧李生态研发有限责任公司 Method of cyclic sustainable vegetation recovery for waste dump of grassland mining area
CN102577789B (en) * 2012-01-20 2013-09-25 内蒙古沁园欧李生态研发有限责任公司 Method of cyclic sustainable vegetation recovery for waste dump of grassland mining area
CN103821154B (en) * 2014-02-12 2016-01-06 北京矿冶研究总院 Ecological restoration method for sintering red mud storage yard side slope
CN103821154A (en) * 2014-02-12 2014-05-28 北京矿冶研究总院 Ecological restoration method for sintering red mud storage yard side slope
CN103814747A (en) * 2014-03-13 2014-05-28 紫金矿业集团股份有限公司 Ecological management method of gold ore tailings after hydrometallurgy
CN104396551A (en) * 2014-12-15 2015-03-11 仲恺农业工程学院 Method for ecological restoration of soil in rare earth mining area by using herbaceous plants
CN105145038A (en) * 2015-07-09 2015-12-16 常州大学 Method for repairing vegetation of coal mine storage yard
CN105724006A (en) * 2016-02-02 2016-07-06 大连地拓重工有限公司 Mine-wasteland vegetation ecological recovery method
CN108951666A (en) * 2018-07-06 2018-12-07 中国地质调查局西安地质调查中心 A kind of with iron milltailings is the slope reinforcement and ecological reestablishment to gather materials
CN109526606A (en) * 2018-11-22 2019-03-29 北京市农林科学院 A method of the induction fast quick-recovery of open ground natural vegetation
CN109526606B (en) * 2018-11-22 2021-05-25 北京市农林科学院 Method for inducing open field natural vegetation to quickly recover
CN111990189A (en) * 2020-08-31 2020-11-27 西南科技大学 Mine broken stone slope ecological restoration method driven by vetiver grass
CN118958319A (en) * 2024-08-02 2024-11-15 江西省、中国科学院庐山植物园 A method for protecting wetland slope

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