CN116114546A - Water and soil conservation and re-greening method for alpine region - Google Patents
Water and soil conservation and re-greening method for alpine region Download PDFInfo
- Publication number
- CN116114546A CN116114546A CN202310022522.0A CN202310022522A CN116114546A CN 116114546 A CN116114546 A CN 116114546A CN 202310022522 A CN202310022522 A CN 202310022522A CN 116114546 A CN116114546 A CN 116114546A
- Authority
- CN
- China
- Prior art keywords
- soil
- water
- field
- turf
- site
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000002689 soil Substances 0.000 title claims abstract description 93
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 74
- 238000000034 method Methods 0.000 title claims abstract description 34
- 241000196324 Embryophyta Species 0.000 claims abstract description 28
- 238000010276 construction Methods 0.000 claims abstract description 23
- 244000025254 Cannabis sativa Species 0.000 claims abstract description 6
- 238000011418 maintenance treatment Methods 0.000 claims abstract description 4
- 230000003628 erosive effect Effects 0.000 claims description 17
- 238000012544 monitoring process Methods 0.000 claims description 14
- 238000006073 displacement reaction Methods 0.000 claims description 12
- 238000011065 in-situ storage Methods 0.000 claims description 9
- 238000003860 storage Methods 0.000 claims description 7
- 238000004140 cleaning Methods 0.000 claims description 5
- 238000004321 preservation Methods 0.000 claims description 5
- 239000004575 stone Substances 0.000 claims description 5
- 239000010902 straw Substances 0.000 claims description 4
- 230000008859 change Effects 0.000 claims description 3
- 230000008635 plant growth Effects 0.000 claims description 2
- 230000003204 osmotic effect Effects 0.000 claims 2
- 241000209140 Triticum Species 0.000 claims 1
- 235000021307 Triticum Nutrition 0.000 claims 1
- 238000005553 drilling Methods 0.000 claims 1
- 230000035515 penetration Effects 0.000 claims 1
- 238000003825 pressing Methods 0.000 claims 1
- 238000004080 punching Methods 0.000 claims 1
- 230000004083 survival effect Effects 0.000 abstract description 8
- 241000894007 species Species 0.000 abstract description 6
- 238000012423 maintenance Methods 0.000 abstract description 5
- 230000009545 invasion Effects 0.000 abstract description 3
- 238000009991 scouring Methods 0.000 abstract description 3
- 239000010410 layer Substances 0.000 description 34
- 230000000694 effects Effects 0.000 description 10
- 238000005260 corrosion Methods 0.000 description 5
- 239000003337 fertilizer Substances 0.000 description 5
- 239000000835 fiber Substances 0.000 description 5
- 230000007797 corrosion Effects 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 239000002893 slag Substances 0.000 description 4
- 150000001875 compounds Chemical class 0.000 description 3
- 230000006378 damage Effects 0.000 description 3
- 230000012010 growth Effects 0.000 description 3
- 230000003020 moisturizing effect Effects 0.000 description 3
- 241001148659 Panicum dichotomiflorum Species 0.000 description 2
- 238000004873 anchoring Methods 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 230000004720 fertilization Effects 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 230000008595 infiltration Effects 0.000 description 2
- 238000001764 infiltration Methods 0.000 description 2
- 238000005457 optimization Methods 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 239000002985 plastic film Substances 0.000 description 2
- 229920006255 plastic film Polymers 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 238000004162 soil erosion Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 241000234642 Festuca Species 0.000 description 1
- 241000700189 Hystrix <Rodentia> Species 0.000 description 1
- 241000209504 Poaceae Species 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 238000009412 basement excavation Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 238000010291 electrical method Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 239000003864 humus Substances 0.000 description 1
- 230000002706 hydrostatic effect Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 235000021049 nutrient content Nutrition 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 239000002861 polymer material Substances 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000011241 protective layer Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- -1 silt Substances 0.000 description 1
- 239000002881 soil fertilizer Substances 0.000 description 1
- 239000004016 soil organic matter Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000009331 sowing Methods 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Images
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G20/00—Cultivation of turf, lawn or the like; Apparatus or methods therefor
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01B—SOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
- A01B79/00—Methods for working soil
- A01B79/02—Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G20/00—Cultivation of turf, lawn or the like; Apparatus or methods therefor
- A01G20/10—Pre-cultivated sod or turf; Apparatus therefor
- A01G20/18—Apparatus for laying sods or turfs
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Soil Sciences (AREA)
- Cultivation Of Plants (AREA)
Abstract
Description
技术领域technical field
本发明涉及生态修复技术领域,具体涉及一种高寒地区的水土保持及复绿方法。The invention relates to the technical field of ecological restoration, in particular to a method for water and soil conservation and regreening in alpine regions.
背景技术Background technique
工程水土流失指工程建设扰动地表、破坏植被,在降雨或上方汇水驱动下导致土壤、砂砾等侵蚀物质被剥离、搬运,最终流出项目建设区范围。Engineering water and soil loss refers to the disturbance of the surface and destruction of vegetation by engineering construction, and the soil, gravel and other erosive substances are stripped and transported under the driving of rainfall or upper water catchment, and finally flow out of the project construction area.
与传统水土流失相比,工程水土流失具以下特性;①、跨区域范围大(尤其是线型工程),水土流失类型多样,例如面蚀、沟蚀、重力侵蚀等,易形成“面蚀→沟蚀→重力侵蚀”的侵蚀链;②、侵蚀模数大,施工期甚至高达几万t/(km2·a),远超过极强烈侵蚀强度标准,且不同施工区域差异显著;③、弃土弃渣量大,地质灾害频发;④、人为活动影响大。Compared with traditional soil and water loss, engineering soil and water loss has the following characteristics; ①, large cross-regional range (especially linear engineering), and various types of soil and water loss, such as surface erosion, ditch erosion, gravity erosion, etc., which are easy to form "surface erosion → Gully erosion→gravity erosion” erosion chain; ②, the erosion modulus is large, and the construction period can even be as high as tens of thousands t/(km 2 ·a), far exceeding the extremely strong erosion intensity standard, and there are significant differences in different construction areas; ③, abandoned The amount of soil spoil is large, and geological disasters occur frequently; ④, the impact of human activities is large.
尤其在高寒地区,生态环境本就脆弱容易遭到破坏,由于经济发展需求,在高寒地区进行工程建设时,对土壤和植被造成了直接破坏,原本脆弱的生态环境一旦遭受认为破坏很难再次恢复。Especially in alpine regions, the ecological environment is already fragile and easily damaged. Due to the needs of economic development, the construction of projects in alpine regions has caused direct damage to soil and vegetation. Once the original fragile ecological environment is damaged, it is difficult to recover .
发明内容Contents of the invention
针对现有技术中存在的缺陷,本发明的目的在于提供一种高寒地区的水土保持及复绿方法,以解决高寒地区工程施工后,水土保持施工难度大、植物不易存活的问题。In view of the defects existing in the prior art, the object of the present invention is to provide a soil and water conservation and regreening method in the alpine region to solve the problems of difficult soil and water conservation construction and difficult survival of plants after engineering construction in the alpine region.
为达到以上目的,本发明采取的技术方案是:For achieving above object, the technical scheme that the present invention takes is:
本申请提供一种高寒地区的水土保持及复绿方法,包括以下步骤:The application provides a method for soil and water conservation and regreening in alpine regions, comprising the following steps:
在场地施工前将草皮及表土收集并处理,待上述场地施工结束后将处理后的表土重新铺设在上述场地内,并将上述草皮经过养护处理后重新铺植在上述表土上;Collect and treat the turf and topsoil before the construction of the site, and re-lay the treated topsoil in the above-mentioned site after the construction of the above-mentioned site is completed, and re-plant the above-mentioned turf on the above-mentioned topsoil after the maintenance treatment;
采用生态混凝土将上述场地的草皮层、表土层、基底层连为整体以形成水土保持层;Ecological concrete is used to connect the turf layer, topsoil layer and base layer of the above site as a whole to form a soil and water conservation layer;
选择多种特定的植物品种的苗木,配置种植在上述水土保持层上。Seedlings of a variety of specific plant varieties are selected and arranged to be planted on the above-mentioned soil and water conservation layer.
在一些可选的实施例中,在场地施工前将草皮及表土收集并处理,包括:In some optional embodiments, the turf and topsoil are collected and treated before site construction, including:
将上述场地的原有草皮剥离;Strip off the original turf of the above site;
设置高原草皮存放区对剥离的草皮进行存放,并用密目网覆盖后在上述草皮的上压重,定期对上述草皮洒水养护;Set up a plateau turf storage area to store the stripped turf, cover it with a dense mesh and press it on the above turf, and regularly sprinkle water on the above turf for maintenance;
对上述场地分区域清表,并将上述表土进行剥离收集后与上述草皮分开存放。The surface of the above-mentioned site is cleaned by area, and the above-mentioned topsoil is stripped and collected, and then stored separately from the above-mentioned turf.
在一些可选的实施例中,选择多种特定的植物品种的苗木,配置种植在上述场地内后,需对上述苗木采取保湿保温措施。In some optional embodiments, multiple seedlings of specific plant species are selected and arranged to be planted in the above-mentioned site, and measures of moisturizing and heat preservation need to be taken for the above-mentioned seedlings.
在一些可选的实施例中,对上述苗木采取保湿保温措施,包括:In some optional embodiments, the above-mentioned seedlings are taken with moisturizing and heat preservation measures, including:
植苗后就地选取直径-厘米的石块,以上述苗木为中心覆盖在锅底状的全穴面上;After planting the seedlings, select stones with a diameter of 1-10 cm on the spot, and cover the above-mentioned seedlings on the surface of the whole hole in the shape of the bottom of the pot with the above-mentioned seedlings as the center;
用无色透明膜覆盖在上述穴面上,并在膜上点状打孔若干个,便于雨水渗入穴内;Cover the surface of the hole with a colorless transparent film, and punch a number of dotted holes on the film to facilitate the infiltration of rainwater into the hole;
用杂草、麦秆、树叶等覆盖在上述苗木周围。Cover above-mentioned nursery stock with weeds, straw, leaves etc. around.
在一些可选的实施例中,待多种特定的植物品种的苗木配置种植在上述场地内后,对上述场地进行原位识别并建立三维模型,实时监测上述水土保持层的位移情况。In some optional embodiments, after seedlings of various specific plant varieties are arranged and planted in the above-mentioned site, the above-mentioned site is identified in situ and a three-dimensional model is established to monitor the displacement of the above-mentioned water and soil conservation layer in real time.
在一些可选的实施例中,实时监测上述水土保持层的位移情况,包括,在上述场地的设定区域布设表面变形测点,以边角交会法观测上述水土保持层表面测点的位移情况。In some optional embodiments, the real-time monitoring of the displacement of the above-mentioned soil and water conservation layer includes arranging surface deformation measuring points in the set area of the above-mentioned site, and observing the displacement of the surface measuring points of the above-mentioned soil and water conservation layer by the corner intersection method .
在一些可选的实施例中,对上述场地进行原位识别并建立三维模型,还需实时监测上述场地的深部变形情况、上述场地的渗透水压情况及上述场地的渗流量情况。In some optional embodiments, the in-situ identification of the site and the establishment of a three-dimensional model also require real-time monitoring of the deep deformation of the site, the seepage water pressure of the site, and the seepage volume of the site.
在一些可选的实施例中,实时监测上述场地的深部变形情况、上述场地的渗透水压情况及上述场地的渗流量情况,包括:In some optional embodiments, the real-time monitoring of the deep deformation of the above-mentioned site, the seepage water pressure of the above-mentioned site and the seepage volume of the above-mentioned site includes:
在上述场地的关键断面处垂直向钻孔埋设测斜管,以监测上述场地和防洪排导工程深部变形情况;Drill vertically to bury inclinometer pipes at key sections of the above-mentioned sites to monitor the deep deformation of the above-mentioned sites and flood control and drainage works;
在上述场地底部设置透水花管,以监测上述场地内部渗透水压变化情况;Set up permeable flower pipes at the bottom of the above-mentioned site to monitor the change of seepage water pressure inside the above-mentioned site;
在上述场地底部利用量水堰,以监测上述场地的渗漏量情况。A water measuring weir is used at the bottom of the above-mentioned site to monitor the seepage of the above-mentioned site.
在一些可选的实施例中,当上述场地的边坡坡度小于60°时,在上述表土上铺设植生袋。In some optional embodiments, when the slope of the site is less than 60°, planting bags are laid on the topsoil.
在一些可选的实施例中,将处理后的表土重新铺设在上述场地内,包括,对上述表土进行抗蚀保土增肥,以增强上述表土的抗蚀性。In some optional embodiments, relaying the treated topsoil in the above-mentioned site includes performing anti-corrosion soil conservation and fertilization on the above-mentioned topsoil, so as to enhance the corrosion resistance of the above-mentioned topsoil.
与现有技术相比,本发明的优点在于:通过将原场地上的草皮和表土进行收集并在养护后,待场地修复时重新铺植,不仅解决了草皮铺植数量不够、成活率低的问题,且降低物种入侵风险;通过选择多种特定植物品种配置种植,以适应高寒地区的种植环境,兼顾前期绿化效果及后期植被护坡功能,立体式修复;通过采用生态混凝土将上述场地的草皮层、表土层、基底层连为整体以形成水土保持层,使得场地的抗冲刷性能强,兼顾了边坡稳定和生态景观双重功能。Compared with the prior art, the present invention has the advantages that: by collecting the turf and topsoil on the original site and replanting them after the maintenance, it not only solves the problems of insufficient turf planting and low survival rate problems, and reduce the risk of species invasion; by selecting a variety of specific plant varieties for planting to adapt to the planting environment in alpine regions, taking into account the early greening effect and the later vegetation slope protection function, three-dimensional restoration; by using ecological concrete The turf layer of the above site The ground layer, topsoil layer, and base layer are connected as a whole to form a soil and water conservation layer, which makes the site have strong anti-scouring performance, and takes into account the dual functions of slope stability and ecological landscape.
附图说明Description of drawings
为了更清楚地说明本申请实施例中的技术方案,下面将对实施例描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本申请的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present application, the drawings that need to be used in the description of the embodiments will be briefly introduced below. Obviously, the drawings in the following description are only some embodiments of the present application. For those skilled in the art, other drawings can also be obtained based on these drawings without creative effort.
图1为本发明一种高寒地区的水土保持及复绿方法的流程图。Fig. 1 is a flow chart of the method for soil and water conservation and regreening in alpine regions of the present invention.
具体实施方式Detailed ways
为使本申请实施例的目的、技术方案和优点更加清楚,下面将结合本申请实施例中的附图,对本申请实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例是本申请的一部分实施例,而不是全部的实施例。基于本申请中的实施例,本领域普通技术人员在没有做出创造性劳动的前提下所获得的所有其他实施例,都属于本申请保护的范围。In order to make the purposes, technical solutions and advantages of the embodiments of the present application clearer, the technical solutions in the embodiments of the present application will be clearly and completely described below in conjunction with the drawings in the embodiments of the present application. Obviously, the described embodiments It is a part of the embodiments of this application, but not all of them. Based on the embodiments in the present application, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present application.
以下结合附图对本发明的实施例作进一步详细说明。Embodiments of the present invention will be described in further detail below in conjunction with the accompanying drawings.
如图1所示,本申请提供一种高寒地区的水土保持及复绿方法,包括以下步骤:As shown in Figure 1, the application provides a kind of soil and water conservation and regreening method in alpine regions, comprising the following steps:
S1:在场地施工前将草皮及表土收集并处理,待上述场地施工结束后将处理后的表土重新铺设在上述场地内,并将上述草皮经过养护处理后重新铺植在上述表土上。S1: Collect and treat the turf and topsoil before the construction of the site. After the construction of the above-mentioned site is completed, re-lay the treated topsoil in the above-mentioned site, and re-plant the above-mentioned turf on the above-mentioned topsoil after maintenance treatment.
在一些可选的实施例中,步骤S1包括:In some optional embodiments, step S1 includes:
S11:将上述场地的原有草皮剥离。S11: Strip off the original turf of the above field.
在场地进行工程施工之前,将场地上的原有草皮进行剥离,剥离时应尽可能保证草皮根系完整。Before the construction of the site, the original turf on the site should be stripped, and the root system of the turf should be as complete as possible when stripping.
S12:设置高原草皮存放区对剥离的草皮进行存放,并用密目网覆盖后在上述草皮的上压重,定期对上述草皮洒水养护。S12: Set up a plateau turf storage area to store the peeled turf, cover it with a dense mesh, and press it on the above turf, and regularly sprinkle water on the above turf for maintenance.
可以理解,草皮的存放应考虑高原高寒的环境影响,为提高草皮的存活率,应定期对草皮洒水养护,且避免堆放时间过长、存放生态区域不适、根下垫土不当及根侧护土不当等引起的草皮死亡。It can be understood that the storage of turf should consider the environmental impact of the high altitude and cold. In order to improve the survival rate of the turf, the turf should be regularly watered and maintained, and the stacking time should be avoided for too long, the storage ecological area is not suitable, the soil under the root is not suitable, and the soil on the root side is protected. Sod death caused by improper etc.
S13:对上述场地分区域清表,并将上述表土进行剥离收集后与上述草皮分开存放。S13: Clean the surface of the above-mentioned site by area, strip and collect the above-mentioned topsoil and store it separately from the above-mentioned turf.
由于表土是植物种子库的存储载体,且养分含量高,尤其针对高寒地区,植物种群脆弱,因此,在施工的清表过程中,应划分区域,分步逐步进行清表施工,以克服一次清表所造成的破坏范围较大的问题。清表结束后,对场地内的表土进行剥离收集,并将表土中的杂质筛除,以提高后续草皮重新铺植在表土上,及苗木种植的成活率。软弱土层、淤泥、腐殖土、大卵石、孤石、垃圾、树根以及不宜草皮和苗木生长的稻田湿土、冻土等均应筛除。Since the topsoil is the storage carrier of the plant seed bank and has high nutrient content, especially for alpine regions, the plant population is fragile. Therefore, in the process of surface cleaning during construction, areas should be divided and surface cleaning should be carried out step by step to overcome the one-time cleaning. The damage caused by the table is relatively large. After cleaning the surface, the topsoil in the site is stripped and collected, and the impurities in the topsoil are screened out, so as to improve the survival rate of subsequent turf replanting on the topsoil and planting of seedlings. Weak soil layers, silt, humus, boulders, boulders, garbage, tree roots, and paddy field wet soil and frozen soil that are not suitable for the growth of turf and seedlings should be screened out.
在一些可选的实施例中,待场地施工结束后,将原场地收集的表土重新铺设在场地内,并将原场地上的草皮重新铺植在表土上,当草皮数量不够,铺植效果较差时,还可以采用铺植与播种相结合的方法,提高场地的草皮覆盖效果。In some optional embodiments, after the construction of the site is completed, the topsoil collected from the original site is re-paved in the site, and the turf on the original site is re-planted on the topsoil. When it is poor, the method of combining planting and sowing can also be used to improve the turf coverage effect of the site.
尤其针对边坡地带,在铺植上述草皮时可以采用框格铺植与纤维毯的模式。即采用混凝土框格梁的边坡锚固方式,在混凝土格构梁内部镶嵌土工格室,将上述表土铺设在土工格室内,再将草皮与种子及营养物质混合组成植物纤维毯,在土工格室内进行铺植,不仅可以减少水土流失,还能提高草皮成活率和草皮种植质量。Especially for the slope area, the pattern of lattice paving and fiber blanket can be used when paving the above-mentioned turf. That is, the slope anchoring method of concrete frame beams is adopted, a geocell is embedded inside the concrete lattice beam, the above-mentioned topsoil is laid in the geocell, and then the turf, seeds and nutrients are mixed to form a plant fiber blanket, and the geocell is placed in the geocell. Paving can not only reduce soil erosion, but also improve the survival rate of turf and the quality of turf planting.
在一些可选的实施例中,当上述场地的边坡坡度小于60°时,在上述表土上铺设植生袋。In some optional embodiments, when the slope of the site is less than 60°, planting bags are laid on the topsoil.
具体的,将人工筛选后的种植土袋装以形成植生袋,并将上述植生袋堆放在上述表土上,使上述植生袋的底部与上述表土的基面紧密接触,减少上述植生袋表面的裸露面积,以增加边坡地带的草根生根深度。Specifically, the artificially screened planting soil is bagged to form a planting bag, and the above-mentioned planting bag is stacked on the above-mentioned topsoil, so that the bottom of the above-mentioned planting bag is in close contact with the base surface of the above-mentioned topsoil, and the exposed surface of the above-mentioned planting bag is reduced. area to increase the rooting depth of grass roots on the slope.
可以理解,种植土为理化性能好,结构疏松、通气,保水、保肥能力强,适宜于植物生长的土壤。若没有种植土,可以利用生土与有机肥或复混肥代替,粘性过大时可以增加细砂。植生袋相互交叠堆放在表土上,此时表土的铺设厚度应在4cm-6cm之间,从而提高植生袋扎入表土时根系的深度,提高场地边坡的水土保持能力。同时植生袋保土渗水的功能减小了边坡静水压力,也保证了水分在土壤中的正常交流,提供了植被赖以生存的介质,使得场地的边坡绿化效果更加明显、更加有效。It can be understood that the planting soil is a soil with good physical and chemical properties, loose structure, ventilation, strong water and fertilizer retention capacity, and suitable for plant growth. If there is no planting soil, raw soil and organic fertilizer or compound fertilizer can be used instead, and fine sand can be added when the viscosity is too high. Vegetation bags are stacked on top of each other, and the thickness of the topsoil should be between 4cm and 6cm, so as to increase the depth of the root system when the vegetation bags are inserted into the topsoil, and improve the soil and water retention capacity of the site slope. At the same time, the function of the planting bag to protect the soil and seep water reduces the hydrostatic pressure of the slope, and also ensures the normal exchange of water in the soil, providing a medium for vegetation to survive, making the slope greening effect of the site more obvious and effective.
在一些可选的实施例中,对表土需要进行处理,具体包括抗蚀保土增肥,以增强所述表土的抗蚀性。In some optional embodiments, the surface soil needs to be treated, specifically including erosion-resistant soil conservation and fertilization, so as to enhance the corrosion resistance of the surface soil.
举例说明,可以在表土上喷洒高分子复合肥,通过高分子材料的自聚作用,在表土的表层和孔隙形成固结保护层包裹表土,增强表土的强度,提升表土的抗蚀性。高分子复合肥环保,无毒可生物降解、以水为溶剂,无二次污染、施工简单,反应迅速,无需额外养护、固土增肥,促生作用明显。For example, the polymer compound fertilizer can be sprayed on the topsoil, and through the self-aggregation of the polymer material, a consolidated protective layer is formed on the surface and pores of the topsoil to wrap the topsoil, enhance the strength of the topsoil, and improve the corrosion resistance of the topsoil. Polymer compound fertilizer is environmentally friendly, non-toxic and biodegradable, uses water as a solvent, has no secondary pollution, is simple to construct, responds quickly, does not need additional maintenance, fixes soil and increases fertilizer, and has obvious growth-promoting effect.
在一些可选的实施例中,还可以对处理后的表土中采用机械、气压或水压等方式,加入连续的纤维丝或者有一定程度的短纤维丝,形成加筋土。由于纤维的作用,使加筋土体形成三维结构,他的整体性将会增强,强度会增大,抗冲击性能也会得到加强,从而可以进一步优化水土保持的效果。In some optional embodiments, continuous fiber filaments or short fiber filaments to a certain extent can be added to the treated topsoil by means of mechanical, air pressure or hydraulic pressure to form reinforced soil. Due to the effect of fibers, the reinforced soil forms a three-dimensional structure, its integrity will be enhanced, its strength will be increased, and its impact resistance will also be enhanced, so that the effect of water and soil conservation can be further optimized.
S2:采用生态混凝土将上述场地的草皮层、表土层、基底层连为整体以形成水土保持层。S2: Use ecological concrete to connect the turf layer, topsoil layer, and base layer of the above site as a whole to form a water and soil conservation layer.
可以理解,生态混凝土具有较高的抗压强度,能够满足一定的坡面载荷,且具有一定的孔隙率,具有良好的排水和透水性能,使得植草根系能够穿透生态混凝土扎入底层土壤,以提高坡体的整体性和生态性。利用生态混凝土将草皮层、表土层、基底层连为整体,使得场地的抗冲刷性能强。It can be understood that ecological concrete has high compressive strength, can meet a certain slope load, and has a certain porosity, and has good drainage and water permeability, so that the root system of planting grass can penetrate the ecological concrete and penetrate into the underlying soil, so as to Improve the integrity and ecology of the slope. Ecological concrete is used to connect the turf layer, topsoil layer, and base layer as a whole, making the site highly resistant to erosion.
S3:选择多种特定的植物品种的苗木,配置种植在上述水土保持层上。S3: Select a variety of seedlings of specific plant varieties, and arrange them to be planted on the above-mentioned soil and water conservation layer.
由于高寒高海拔地区的物种多样性相对较差,人工培育种植资源有限,以牧草和经济型植物种植较为常见。根据上繁型草本植物有利于提高植被覆盖度,而下繁型草本植物根系相对发达,护坡作用良好,豆科植物能改良土壤基质,灌木根系发达,上述植物均是生态修复后期的主要护坡植物。因此选取上述植物品种,进行配置种植,且优选本土物种以适应当地的自然环境,降低物种入侵风险。例如同德短芒披碱草、青海草地早熟禾、青海冷地早熟禾和青海中华羊茅等。同时,为避免单一物种使用而破坏物种多样性原则,应在垂直结构上考虑不同生长高度的植物品种进行配置,这样不仅可以兼顾生态修复前期的景观绿化效果,同时确保生长后期的植被护坡功能。促进形成乔木为主体、乔灌草结合、结构合理稳定和功能高效相协调的林分群落。Due to the relatively poor species diversity in the alpine and high-altitude areas, artificial cultivation and planting resources are limited, and pasture and economical plants are more common. According to the fact that up-propagating herbaceous plants are beneficial to increase vegetation coverage, while down-propagating herbaceous plants have relatively well-developed root systems and have good slope protection effects. Leguminous plants can improve soil substrates and have well-developed shrub root systems. The above-mentioned plants are the main slope protection plants in the later stage of ecological restoration. . Therefore, the above-mentioned plant varieties are selected for configuration and planting, and native species are selected to adapt to the local natural environment and reduce the risk of species invasion. For example, Tongde Elymus brevis, Qinghai Bluegrass, Qinghai Coldland Bluegrass and Qinghai Chinese Fescue, etc. At the same time, in order to avoid destroying the principle of species diversity due to the use of a single species, plant species with different growth heights should be considered in the vertical structure, so that not only the landscape greening effect in the early stage of ecological restoration can be taken into account, but also the slope protection function of vegetation in the later stage of growth can be ensured. Promote the formation of forest stand communities with trees as the main body, combination of trees, shrubs and grasses, reasonable and stable structure, and high-efficiency functions.
在一些可选的实施例中,选择多种特定的植物品种的苗木,配置种植在上述场地内后,需对上述苗木采取保湿保温措施。其具体步骤包括:In some optional embodiments, multiple seedlings of specific plant species are selected and arranged to be planted in the above-mentioned site, and measures of moisturizing and heat preservation need to be taken for the above-mentioned seedlings. Its specific steps include:
S31:植苗后就地选取直径5-15厘米的石块,以上述苗木为中心覆盖在锅底状的全穴面上。S31: After the seedlings are planted, stones with a diameter of 5-15 cm are selected on the spot, and the above-mentioned seedlings are used as the center to cover the surface of the whole hole in the shape of the bottom of the pot.
石块覆盖在以苗木为中心的穴面上,既能承渗雨水,又能有效地抑制土壤的水分蒸发。The stones cover the surface of the hole centered on the seedlings, which can not only absorb rainwater, but also effectively inhibit the evaporation of soil water.
S32:用无色透明膜覆盖在上述穴面上,并在膜上点状打孔若干个,便于雨水渗入穴内。S32: Cover the surface of the hole with a colorless transparent film, and punch a number of dotted holes on the film to facilitate rainwater to infiltrate into the hole.
塑膜覆盖是用无色透明膜,覆盖在以树苗为中心、整理成锅底状的穴面上,将四周用土压实,以防风吹散,然后在膜上点状打孔5-8个,便于雨水渗入穴内,覆盖塑膜能提高地温,保持墒情。The plastic film covering is to use a colorless transparent film to cover the surface of the pot-bottom-shaped hole centered on the sapling, compact the surrounding area with soil to prevent the wind from blowing away, and then punch 5-8 points on the film. , to facilitate the infiltration of rainwater into the hole, covering the plastic film can increase the ground temperature and maintain moisture.
S33:用杂草、麦秆、树叶等覆盖在上述苗木周围。S33: Covering the surroundings of the seedlings with weeds, straws, leaves, etc.
草类覆盖是指用杂草、麦秆、树叶等覆盖在苗木周围,覆盖厚度一般为2-3厘米,然后上面再压一层2厘米的土,以防被风吹走,覆盖草类能增加土壤有机质,提高土壤肥力。Grass mulching refers to covering the seedlings with weeds, straw, leaves, etc., the thickness of which is generally 2-3 cm, and then a layer of 2 cm of soil is placed on top to prevent them from being blown away by the wind. Increase soil organic matter and improve soil fertility.
在一些可选的实施例中,在步骤S3后,还包括:In some optional embodiments, after step S3, it also includes:
S4:对上述场地进行原位识别并建立三维模型,实时监测上述水土保持层的位移情况。S4: Carry out in-situ identification of the above-mentioned site and establish a three-dimensional model, and monitor the displacement of the above-mentioned water and soil conservation layer in real time.
可以理解,监测水土保持层的位移情况,可以对场地的水土保持情况进行监测以及时采取措施。例如增设混凝土框格梁的边坡锚固方式,或增加植生袋的铺设面积,或增加生态混凝土的厚度,或在场地内安装立桩等,以控制水土保持层位移。It can be understood that monitoring the displacement of the soil and water conservation layer can monitor the soil and water conservation of the site and take timely measures. For example, increase the slope anchoring method of concrete frame beams, or increase the laying area of planting bags, or increase the thickness of ecological concrete, or install vertical piles in the site, etc., to control the displacement of the water and soil conservation layer.
在一些可选的实施例中,实时监测上述水土保持层的位移情况,包括,在上述场地的设定区域布设表面变形测点,以边角交会法观测上述水土保持层表面测点的位移情况。In some optional embodiments, the real-time monitoring of the displacement of the above-mentioned soil and water conservation layer includes arranging surface deformation measuring points in the set area of the above-mentioned site, and observing the displacement of the surface measuring points of the above-mentioned soil and water conservation layer by the corner intersection method .
边角交会法是指,在两个及以上已知点上分别架设仪器对待定点进行水平角和距离观测,并根据已知点的坐标及观测角值和距离计算出待定点坐标的方法。针对面积较大或地形结构复杂的场地,在上述场地的顶部、坡面和防洪排导工程开挖边坡坡顶及马道、拦渣坝、挡渣墙顶面等处布设表面变形测点。The corner intersection method refers to the method of setting up instruments on two or more known points to observe the horizontal angle and distance of the point to be fixed, and calculate the coordinates of the point to be fixed according to the coordinates of the known points, the observed angle value and the distance. For sites with large areas or complex topographical structures, surface deformation measuring points shall be arranged on the tops, slopes of the above-mentioned sites, and the tops of slopes excavated for flood control and drainage works, as well as the tops of bridleways, slag retaining dams, and slag retaining walls.
在一些可选的实施例中,对上述场地进行原位识别并建立三维模型,还需实时监测上述场地的深部变形情况、上述场地的渗透水压情况及上述场地的渗流量情况。In some optional embodiments, the in-situ identification of the site and the establishment of a three-dimensional model also require real-time monitoring of the deep deformation of the site, the seepage water pressure of the site, and the seepage volume of the site.
可以理解,在场地工程施工结束后,需修建排水沟,在场地四周修筑土坝。可以根据场地的具体情况及上游汇水面积及周边地形地质条件,确定防洪排导工程的形式,包括但不限于明排与安排的组合。It is understandable that after the site construction is completed, drainage ditches and earth dams need to be built around the site. The form of flood control and drainage works can be determined according to the specific conditions of the site, the upstream catchment area and the surrounding topographic and geological conditions, including but not limited to the combination of exposed drainage and arrangement.
可选的,通过原位识别、渣土调配信息平台、无人机动态监管及视讯实时传输,四位一体的场地生态修复智慧网络管理平台,对场地进行监控和管理。Optionally, through in-situ identification, muck deployment information platform, UAV dynamic monitoring and real-time video transmission, the four-in-one site ecological restoration intelligent network management platform can monitor and manage the site.
原位识别利用无人机、探地雷达和高密度电法分别获取上述场地的轮廓形态参数、物质组成特征和上述场地内部渗流场分布,构建上述场地三维动态模型;堆置优化设计以上述场地的三维模型为基础,对上述场地堆置结构和排水路径进行优化设计,保证水土保持层的整体稳定,为后续场地的生态修复奠定基础;上述场地内的生态修复关键技术按照“坡脚加固-内部增强-表面减蚀-植被优选”思路,构建上述场地的生态修复关键技术;案例表明,可提高上述场地表土的抗蚀性86%-97%、抗冲性70%-80%、孔隙率45%-50%、透水能力350%-420%、植被覆盖率提高至90%-97%。In-situ identification uses unmanned aerial vehicle, ground penetrating radar and high-density electrical method to obtain the contour shape parameters, material composition characteristics and internal seepage field distribution of the above-mentioned site respectively, and build a three-dimensional dynamic model of the above-mentioned site; the stacking optimization design is based on the above-mentioned site Based on the 3D model of the above-mentioned site, optimize the design of the stacking structure and drainage path of the above-mentioned site to ensure the overall stability of the soil and water conservation layer, and lay the foundation for the subsequent ecological restoration of the site; Internal enhancement-surface erosion reduction-vegetation optimization" idea to build key technologies for ecological restoration of the above sites; cases show that it can improve the erosion resistance of the above site topsoil by 86%-97%, anti-scourability by 70%-80%, porosity 45%-50%, water permeability 350%-420%, and vegetation coverage increased to 90%-97%.
具体的,在一些可选的实施例中,实时监测上述场地的深部变形情况、上述场地的渗透水压情况及上述场地的渗流量情况,包括:Specifically, in some optional embodiments, the real-time monitoring of the deep deformation of the above-mentioned site, the seepage water pressure of the above-mentioned site, and the seepage volume of the above-mentioned site includes:
在上述场地的关键断面处垂直向钻孔埋设测斜管,以监测上述场地和防洪排导工程深部变形情况。Vertical boreholes are buried at key sections of the above-mentioned sites to monitor the deep deformation of the above-mentioned sites and flood control and drainage works.
在上述场地底部设置透水花管,以监测上述场地内部渗透水压变化情况。Set up permeable flower pipes at the bottom of the above-mentioned site to monitor the change of seepage water pressure inside the above-mentioned site.
在上述场地底部利用量水堰,以监测上述场地的渗漏量情况。A water measuring weir is used at the bottom of the above-mentioned site to monitor the seepage of the above-mentioned site.
对于存在高陡开挖边坡的防洪排导工程,还应在防洪排导工程开挖的边坡布置表面变形、深部变形等监测项目,在部分拦渣坝、挡渣墙顶面布置表面变形监测项目,监测设备包括全站仪器、活动式测斜仪、读数仪、电测水位计、强制对中基座、渗压计、GPS接收机和视频监控仪等。For flood control and drainage projects with high and steep excavation slopes, monitoring items such as surface deformation and deep deformation should also be arranged on the slopes excavated by flood control and drainage projects, and surface deformation monitoring items should be arranged on the top of some slag retaining dams and slag retaining walls. Monitoring items, monitoring equipment includes total station instruments, movable inclinometers, reading instruments, electric water level gauges, forced centering bases, piezometers, GPS receivers and video monitors, etc.
本发明的一种高寒地区的水土保持及复绿方法,通过在场地施工前将原有场地内的草皮和表土进行剥离收集,并对草皮和表土进行养护处理后,重新铺植在施工结束后需要修复的场地内,从而可以提高高寒地区的草皮成活率,保持高寒地区的植物种子库的存储载体,避免破坏高寒高压地区的植物种群;通过在场地的边坡地带利用框格铺植与纤维毯的模式,不仅可以减少水土流失,还能提高草皮成活率和草皮种植质量;在场地边坡坡度小于60°时,在上述表土上铺设植生袋,提高场地边坡的水土保持能力;通过对表土进行抗蚀保土增肥,以增强所述表土的抗蚀性;通过生态混凝土将上述场地的草皮层、表土层、基底层连为整体以形成水土保持层,使得场地的抗冲刷性能强;对上述场地进行原位识别并建立三维模型,实时监测上述水土保持层的位移情况,以及时采取相关措施,提高复绿速度和复绿效果。The water and soil conservation and regreening method in the alpine region of the present invention is to strip and collect the turf and topsoil in the original site before the site construction, and after the turf and the topsoil are maintained and replanted after the construction is completed In the site that needs to be repaired, it can improve the survival rate of turf in the alpine area, maintain the storage carrier of the plant seed bank in the alpine area, and avoid destroying the plant population in the alpine and high pressure area; The blanket mode can not only reduce water and soil erosion, but also improve the survival rate of turf and the quality of turf planting; when the slope of the site slope is less than 60°, lay planting bags on the above-mentioned topsoil to improve the water and soil conservation capacity of the site slope; The topsoil is protected against erosion and fertilized to enhance the corrosion resistance of the topsoil; the turf layer, topsoil layer, and base layer of the above-mentioned site are connected as a whole through ecological concrete to form a water and soil conservation layer, which makes the site's anti-scouring performance strong ; Carry out in-situ identification of the above-mentioned sites and establish a three-dimensional model, monitor the displacement of the above-mentioned soil and water conservation layer in real time, and take relevant measures in time to improve the speed and effect of regreening.
在本申请的描述中,需要说明的是,术语“上”、“下”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本申请和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本申请的限制。除非另有明确的规定和限定,术语“安装”、“相连”、“连接”应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或一体地连接;可以是机械连接,也可以是电连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通。对于本领域的普通技术人员而言,可以根据具体情况理解上述术语在本申请中的具体含义。In the description of the present application, it should be noted that the orientation or positional relationship indicated by the terms "upper", "lower" and so on is based on the orientation or positional relationship shown in the drawings, and is only for the convenience of describing the present application and simplifying the description. It is not intended to indicate or imply that the device or element referred to must have a particular orientation, be constructed, or operate in a particular orientation, and thus should not be construed as limiting the application. Unless otherwise clearly specified and limited, the terms "installation", "connection" and "connection" should be interpreted in a broad sense, for example, it may be a fixed connection, a detachable connection, or an integral connection; it may be a mechanical connection, It can also be an electrical connection; it can be a direct connection, or an indirect connection through an intermediary, or an internal communication between two components. Those of ordinary skill in the art can understand the specific meanings of the above terms in this application according to specific situations.
需要说明的是,在本申请中,诸如“第一”和“第二”等之类的关系术语仅仅用来将一个实体或者操作与另一个实体或操作区分开来,而不一定要求或者暗示这些实体或操作之间存在任何这种实际的关系或者顺序。而且,术语“包括”、“包含”或者其任何其他变体意在涵盖非排他性的包含,从而使得包括一系列要素的过程、方法、物品或者设备不仅包括那些要素,而且还包括没有明确列出的其他要素,或者是还包括为这种过程、方法、物品或者设备所固有的要素。在没有更多限制的情况下,由语句“包括一个……”限定的要素,并不排除在包括所述要素的过程、方法、物品或者设备中还存在另外的相同要素。It should be noted that in this application, relative terms such as "first" and "second" are only used to distinguish one entity or operation from another entity or operation, and do not necessarily require or imply There is no such actual relationship or order between these entities or operations. Furthermore, the term "comprises", "comprises" or any other variation thereof is intended to cover a non-exclusive inclusion such that a process, method, article, or apparatus comprising a set of elements includes not only those elements, but also includes elements not expressly listed. other elements of or also include elements inherent in such a process, method, article, or device. Without further limitations, an element defined by the phrase "comprising a ..." does not exclude the presence of additional identical elements in the process, method, article or apparatus comprising said element.
以上所述仅是本申请的具体实施方式,使本领域技术人员能够理解或实现本申请。对这些实施例的多种修改对本领域的技术人员来说将是显而易见的,本文中所定义的一般原理可以在不脱离本申请的精神或范围的情况下,在其它实施例中实现。因此,本申请将不会被限制于本文所示的这些实施例,而是要符合与本文所申请的原理和新颖特点相一致的最宽的范围。The above descriptions are only specific implementation manners of the present application, so that those skilled in the art can understand or implement the present application. Various modifications to these embodiments will be readily apparent to those skilled in the art, and the general principles defined herein may be implemented in other embodiments without departing from the spirit or scope of the application. Therefore, the present application will not be limited to the embodiments shown herein, but is to be accorded the widest scope consistent with the principles and novel features claimed herein.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202310022522.0A CN116114546A (en) | 2023-01-07 | 2023-01-07 | Water and soil conservation and re-greening method for alpine region |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202310022522.0A CN116114546A (en) | 2023-01-07 | 2023-01-07 | Water and soil conservation and re-greening method for alpine region |
Publications (1)
Publication Number | Publication Date |
---|---|
CN116114546A true CN116114546A (en) | 2023-05-16 |
Family
ID=86311223
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202310022522.0A Pending CN116114546A (en) | 2023-01-07 | 2023-01-07 | Water and soil conservation and re-greening method for alpine region |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN116114546A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116773780A (en) * | 2023-08-16 | 2023-09-19 | 中国科学院、水利部成都山地灾害与环境研究所 | Vegetation slope soil seepage erosion experiment measurement system and measurement method |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20040014725A (en) * | 2002-08-10 | 2004-02-18 | 이한승 | Transplant revegetation measure using plug sodding in on-site |
KR20040027146A (en) * | 2002-09-27 | 2004-04-01 | 이한승 | Recycling eco-revegetation measures |
CN103835298A (en) * | 2013-12-05 | 2014-06-04 | 大连环复生态技术有限公司 | Concrete-sprayed face side slope greening method and system |
CN108094057A (en) * | 2018-01-09 | 2018-06-01 | 万朋均 | A kind of High aititude meadow area original vegetation site recovery method |
CN112088749A (en) * | 2020-08-03 | 2020-12-18 | 瑞派尔(宜昌)科技集团股份有限公司 | Ecological concrete for restoring ecological planting |
CN112627245A (en) * | 2020-12-20 | 2021-04-09 | 长江水利委员会长江科学院 | Abandoned dreg site surveying and ecological restoration method based on in-situ recognition |
CN115049302A (en) * | 2022-07-05 | 2022-09-13 | 中国电建集团昆明勘测设计研究院有限公司 | Method for establishing ecological restoration system of production and construction project in dry and hot valley region |
-
2023
- 2023-01-07 CN CN202310022522.0A patent/CN116114546A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20040014725A (en) * | 2002-08-10 | 2004-02-18 | 이한승 | Transplant revegetation measure using plug sodding in on-site |
KR20040027146A (en) * | 2002-09-27 | 2004-04-01 | 이한승 | Recycling eco-revegetation measures |
CN103835298A (en) * | 2013-12-05 | 2014-06-04 | 大连环复生态技术有限公司 | Concrete-sprayed face side slope greening method and system |
CN108094057A (en) * | 2018-01-09 | 2018-06-01 | 万朋均 | A kind of High aititude meadow area original vegetation site recovery method |
CN112088749A (en) * | 2020-08-03 | 2020-12-18 | 瑞派尔(宜昌)科技集团股份有限公司 | Ecological concrete for restoring ecological planting |
CN112627245A (en) * | 2020-12-20 | 2021-04-09 | 长江水利委员会长江科学院 | Abandoned dreg site surveying and ecological restoration method based on in-situ recognition |
CN115049302A (en) * | 2022-07-05 | 2022-09-13 | 中国电建集团昆明勘测设计研究院有限公司 | Method for establishing ecological restoration system of production and construction project in dry and hot valley region |
Non-Patent Citations (8)
Title |
---|
刘荣桂等: "绿色公路品质工程施工关键技术研究与示范", 30 September 2021, 江苏大学出版社, pages: 194 - 195 * |
刘连新等: "高原环境建筑材料", 31 January 2010, 中国建材工业出版社, pages: 106 - 109 * |
史鹏飞;罗光其;齐卿;: "石门沥青混凝土心墙堆石坝安全监测技术与运行状态分析", 河南水利与南水北调, no. 04, 28 February 2015 (2015-02-28) * |
杜欣泽等: "甘肃藏区风电场项目水土流失防治技术探讨", 中国水土保持, no. 7, 5 July 2017 (2017-07-05), pages 22 - 24 * |
杨建霞;尹武君;杨晓瑞;: "草皮剥离回铺技术在高海拔风电项目中的应用", 四川环境, no. 02, 26 April 2015 (2015-04-26) * |
贺艳萍;李新平;郭晋平;: "覆盖保墒技术的研究进展", 山西林业科技, no. 01, 15 March 2008 (2008-03-15), pages 37 - 39 * |
邹丽春等: "复杂高边坡整枝理论与工程实践", 30 September 2006, 中国水利水电出版社, pages: 121 - 125 * |
马凤槐等: "平原区绿色公路路基研究与实践", 30 September 2022, 中国建材工业出版社, pages: 53 - 61 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116773780A (en) * | 2023-08-16 | 2023-09-19 | 中国科学院、水利部成都山地灾害与环境研究所 | Vegetation slope soil seepage erosion experiment measurement system and measurement method |
CN116773780B (en) * | 2023-08-16 | 2023-12-08 | 中国科学院、水利部成都山地灾害与环境研究所 | Experimental measurement system and measurement method for soil seepage and erosion on vegetated slopes |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101485275B (en) | Sylvicultural method on argillaceous saline soil | |
CN106900195B (en) | One kind taking native field ecological restoring method | |
CN108605460A (en) | Grassland region opencast coal mine dump method for recovering vegetation and ecological recovery method | |
CN101322470A (en) | A kind of coastal saline-alkali land afforestation method | |
CN111316850A (en) | High and steep slope vegetation and planting method thereof | |
CN208266847U (en) | Quickly repair structure in Gullied suitable for Canal in Loess Area | |
CN102301936A (en) | Method for afforesting abrupt slope by punching | |
CN103988684A (en) | Desert dry and semi-dry turf transplantation and re-laying method suitable for roadbed construction | |
CN103556642A (en) | High rock slope green covered plant underground habitat reconstruction method | |
CN104186137A (en) | Technology for cultivating and greening tall fescue grass on inshore mud flat saline-alkali soil | |
CN106900449A (en) | A kind of alkaline land soil improves greening construction method | |
CN109287359A (en) | A kind of high steep breakage of massif is looked unfamiliar the method that state is quickly repaired | |
CN110692453A (en) | A method suitable for planting Cistanche Cistanche in the Yellow River Delta region | |
CN115049302A (en) | Method for establishing ecological restoration system of production and construction project in dry and hot valley region | |
CN106385843A (en) | Method for increasing leaching efficiency of soil salinity in plough layer | |
CN111316853A (en) | Stone mountain damaged surface vegetation and planting method thereof | |
CN105706555B (en) | Saline land greening engineering original soil structure-improved and its construction method | |
CN111887067B (en) | Method for ecological restoration of artificial vegetation on high and steep rock slope | |
CN116830953A (en) | Method for preventing water and soil loss in forestry engineering construction | |
CN108834727A (en) | Rice field, which replants citrus, prevents the cultivation method for matching of soil top backwater | |
CN103125296B (en) | Plant water retention pit and water retention method of Yunnan phosphorite refuse dumps | |
CN104762946A (en) | Filler and method for ecologically repairing damaged mountain | |
CN115720819A (en) | A Vegetation Restoration Method in High Altitude Hydropower Development Area | |
CN112012229A (en) | An ecological restoration system for high and steep rock slopes in limestone mines | |
CN116114546A (en) | Water and soil conservation and re-greening method for alpine region |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |