WO2022267297A1 - Method for side slope ecological restoration of dicranopteris dichotoma - Google Patents

Method for side slope ecological restoration of dicranopteris dichotoma Download PDF

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Publication number
WO2022267297A1
WO2022267297A1 PCT/CN2021/129277 CN2021129277W WO2022267297A1 WO 2022267297 A1 WO2022267297 A1 WO 2022267297A1 CN 2021129277 W CN2021129277 W CN 2021129277W WO 2022267297 A1 WO2022267297 A1 WO 2022267297A1
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Prior art keywords
osmanthus
soil
parts
ecological restoration
slope
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PCT/CN2021/129277
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French (fr)
Chinese (zh)
Inventor
李水雄
邹妮
曾汉良
曾祥
刘国华
蓝广中
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广东美景环境科技有限公司
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Publication of WO2022267297A1 publication Critical patent/WO2022267297A1/en

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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G22/00Cultivation of specific crops or plants not otherwise provided for
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/10Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/10Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
    • A01G24/12Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing soil minerals
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • A01G24/10Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
    • A01G24/12Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing soil minerals
    • A01G24/15Calcined rock, e.g. perlite, vermiculite or clay aggregates

Definitions

  • the present application relates to the technical field of slope restoration, and in particular to a slope ecological restoration device of Osmanthus mangosteen.
  • Slope ecological restoration is a method of applying the principles of ecology to the ecological restoration of artificially formed slopes, that is, through specific technical measures to successfully plant specific plants on the slopes to improve the ecological environment of the slopes, so as to realize the ecological restoration of the slopes. ecological restoration.
  • the specific plants used for slope restoration are generally herbs and vine propagules such as grass seeds and flower seeds, among which grass seeds are mostly ryegrass, bermudagrass, tall fescue, or bluegrass, and flower seeds and vines are mostly Petunia, Cosmos or Iris etc.
  • the purpose of this application is: to provide a side slope ecological restoration device of Osmanthus mangosteen, which can plant Osmanthus mangosteen on the side slope to repair the side slope, and can improve the effect of side slope restoration.
  • the application provides a side slope ecological restoration device of Osmanthus osmanthus, including a seedling raising bed and a plurality of Osmanthus osmanthus;
  • the seedling raising bed includes non-woven geotextiles and laying on the The substrate layer on the non-woven geotextile;
  • the Osmanthus osmanthus of a plurality of plants are respectively planted in the substrate layer;
  • the substrate layer consists of 25 to 35 parts of fire soil, 25 to 35 parts of fertile garden soil, and 25 parts of red soil core soil, and 15 to 25 parts of river sand are uniformly stirred and mixed with water to form.
  • the number of the seedling raising beds is multiple, and the plurality of seedling raising beds are distributed in a matrix, the two adjacent seedling raising beds in the horizontal direction are connected, and the two adjacent seedling raising beds in the vertical direction connect.
  • the non-woven geotextile is rectangular, and the side length of the non-woven geotextile is 0.8m to 1.2m; the thickness of the matrix layer is 3cm to 4cm.
  • it also includes a fixing mechanism for fixing the seedling raising bed on the slope.
  • the fixing mechanism includes a strip plate installed above the base layer and a plurality of fasteners; the plurality of fasteners are arranged at intervals along the extending direction of the strip plate and can respectively pass through the The strip plate and the matrix layer are connected on the side slope with fasteners.
  • the burnt soil, fertile garden soil, red soil core soil and river sand are sterilized soil respectively, and the particle diameters of the burnt soil, fertile garden soil, red soil core soil and river sand are respectively less than 0.36cm.
  • a slope ecological restoration device of Osmanthus osmanthus in the embodiment of the present application has the beneficial effect of:
  • the slope ecological restoration device of the present application uses Osmanthus as the main plant to carry out side ecological restoration, which has the characteristics of drought resistance and barrenness resistance. Compared with ryegrass, bermudagrass, tall fescue, precocious Grass grass, petunia, cosmos or horse lily, etc., have strong ability to adapt to the environment, and are suitable for growing on the slope to be repaired with harsh environment, so as to improve the repair effect of the slope.
  • the application adopts the mixed matrix formed by burning soil, fertile garden soil, red soil core soil and river sand.
  • the matrix layer material of the application is more It is easy to obtain, can obtain local materials, and can conveniently cultivate slope restoration plants, that is, Osmanthus osmanthus.
  • Fig. 1 is an axonometric view of a slope ecological restoration device for Osmanthus osmanthus according to an embodiment of the present application.
  • Fig. 2 is a schematic diagram of the application of the slope ecological restoration device of Osmanthus osmanthus according to the embodiment of the present application.
  • first and second are used for descriptive purposes only, and cannot be interpreted as indicating or implying relative importance or implicitly specifying the quantity of indicated technical features. Thus, a feature defined as “first” and “second” may explicitly or implicitly include one or more of these features.
  • “plurality” means two or more, unless otherwise specifically defined.
  • a first feature being “on” or “under” a second feature may include direct contact between the first and second features, and may also include the first and second features Not in direct contact but through another characteristic contact between them.
  • “above”, “above” and “above” the first feature on the second feature include that the first feature is directly above and obliquely above the second feature, or simply means that the first feature is horizontally higher than the second feature.
  • "Below”, “under” and “under” the first feature to the second feature include that the first feature is directly below and obliquely below the second feature, or simply means that the first feature is less horizontally than the second feature.
  • a slope ecological restoration device includes a seedling raising bed 1 and a plurality of Osmanthus osmanthus 2; Woven geotextile 11 and the substrate layer 12 laid on the non-woven geotextile 11; multiple plants of Osmanthus 2 planted in the substrate layer 12 respectively; , 25 to 35 parts of fertile garden soil, 15 to 25 parts of red loam core soil, and 15 to 25 parts of river sand are uniformly stirred and mixed with water to form.
  • the slope ecological restoration device of the present application adopts Osmanthus 2 as the main plant to carry out slope 5 restoration, which has the characteristics of drought resistance and barren resistance, compared with ryegrass, bermudagrass, tall fescue in the prior art , Bluegrass, Petunia, Cosmos, or Iris, etc., have a stronger ability to adapt to the environment, and are suitable for growing in the harsh environment of the slope 5 to be repaired, so as to improve the ecological restoration effect of the slope 5.
  • the application adopts burning soil, fertile garden soil, red soil core soil and river sand to stir to form a mixed substrate.
  • the substrate layer 12 material of the application is more It is easy to obtain, can obtain local materials, and conveniently cultivate slope 5 restoration plants, that is, Osmanthus osmanthus 2.
  • FIG. 1 to FIG. 2 it also includes a shading net erected above the base layer 12 to avoid strong light.
  • the light transmittance of the shade net is 50% to 60%.
  • a shading net with a light transmittance of 55% is selected.
  • a plurality of plants of Osmanthus 2 are distributed in a matrix on the matrix layer 12 in a staggered manner.
  • the plastic mesh cover is arranged on the multiple Osmanthus 2 plants.
  • the quantity of described nursery furrows 1 is multiple, and a plurality of described seedling furrows 1 are distributed in a matrix, and the two adjacent laterally The seedling-raising furrows 1 are connected, and two adjacent seedling-raising furrows 1 in the longitudinal direction are connected.
  • the non-woven geotextile 11 is rectangular, the length of one side of the non-woven geotextile 11 is 0.8m to 1.2m, the non-woven geotextile 11 The length of the other side of the woven geotextile 11 is 0.8m to 1.2m; the thickness of the matrix layer 12 is 3cm to 4cm.
  • the shape of the non-woven geotextile 11 is a rectangle of 1 m ⁇ 1 m.
  • FIG. 1 to FIG. 2 it also includes a support and an agricultural film for water retention; the agricultural film is erected above the multiple Osmanthus 2 plants through the support.
  • Fig. 1 to Fig. 2 it also includes a fixing mechanism for fixing the seedling raising bed 1 on the side slope 5, so as to fix the repair structure of the side slope 5 on the side slope. On slope 5.
  • the fixing mechanism includes a strip plate 4 installed above the base layer 12 and a plurality of fasteners; a plurality of the fasteners They are arranged at intervals along the extending direction of the strip plates 4 and can respectively pass through the strip plates 4 and the base layer 12 to be connected to the slope 5 with fasteners.
  • the seedling raising bed 1 is fixed by means of the strip plate 4 and fasteners, the structure is simple, and the fixing is stable.
  • the fixing mechanism includes a strip plate 4 installed above the matrix layer 12 and a plurality of locking pieces 3; the locking pieces 3 are helical iron Wire nails; a plurality of locking members 3 are arranged at intervals along the extending direction of the strip plate 4 and can respectively pass through the strip plate 4 and the matrix layer 12 to be screwed into the side slope 5 .
  • This optional embodiment provides an alternative to the fixing mechanism, which is screwed into the side slope 5 by a helical wire nail, so that the seedling raising bed 1 is firmly fixed on the side slope 5 .
  • described strip plate 4 is provided with a plurality of, and a plurality of described strip plate 4 are arranged in parallel, to respectively fix seedling raising bed in multiple positions 1, especially suitable for slopes with large slopes5. Among them, according to the slope size of the slope, adjust the number of strip plates.
  • the fixing mechanism simultaneously includes a plurality of strip plates 4, a plurality of fasteners, and a plurality of locking elements 3; the locking elements 3 are helical wire nails, and the fasteners are Helical columnar structure; some of the strip plates 4 are provided with multiple fasteners, and other strip plates 4 are provided with multiple locking members 3; a plurality of the fasteners extend along the strip plate 4
  • the extension direction of the strip plate 4 is arranged at intervals and can pass through the strip plate 4 and the substrate layer 12 to be connected to the slope 5 with fasteners; a plurality of locking members 3 are spaced apart along the extension direction of the strip plate 4 It is arranged and can pass through the strip plate 4 and the base layer 12 respectively to be screwed into the side slope 5 .
  • the fastener and the locking member 3 are set at the same time, wherein the structure of the locking member 3 is easier to drill into the side slope 5, and is not easy to occur with the side slope 5 perpendicular to the longitudinal direction of the side slope 5.
  • Slip the connection strength with the side slope 5 is higher, and the fastener has a larger cross-sectional area, so it is difficult to slip with the side slope 5 parallel to the horizontal direction of the side slope 5 . Therefore, after the fastener and the locking member 3 are set at the same time, the fixing strength of the seedling raising bed 1 and the side slope 5 can be further improved, so that the Osmanthus 2 in the seedling raising bed 1 can grow vigorously, and play a role in the side slope 5 Good ecological restoration effect.
  • the burnt soil, fertile garden soil, red soil core soil and river sand are respectively sterilized soil, and the burnt soil, fertile garden soil, red soil core soil and river sand The particle size is less than 0.36cm respectively.
  • the burned soil, fertile garden soil, red soil core soil and river sand were obtained after 50-mesh screening and disinfection, which is more favorable for the cultivation of Osmanthus osmanthus.
  • references to the terms “one embodiment,” “some embodiments,” “exemplary embodiments,” “example,” “specific examples,” or “some examples” are intended to mean that the implementation A specific feature, structure, material, or characteristic described by an embodiment or example is included in at least one embodiment or example of the present application.
  • schematic representations of the above terms do not necessarily refer to the same embodiment or example.
  • the specific features, structures, materials or characteristics described may be combined in any suitable manner in any one or more embodiments or examples.

Abstract

The present application relates to the technical field of side slope restoration. Disclosed is a device for side slope ecological restoration of Dicranopteris dichotoma. The device comprises a seedling bed and a plurality of Dicranopteris dichotoma. The seedling bed comprises a non-woven geotextile used for being laid on a side slope and a matrix layer laid on the non-woven geotextile; the plurality of Dicranopteris dichotoma are respectively planted in the matrix layer; and the matrix layer is formed by stirring mixed soil of 25 parts to 35 parts of fired clay, 25 parts to 35 parts of fertile garden soil, 15 parts to 25 parts of lateritic red earth and 15 parts to 25 parts of river sand which has been stirred uniformly with water. The device for side slope ecological restoration of Dicranopteris dichotoma of the present application uses Dicranopteris dichotoma as a main plant for side slope restoration, which plant has the characteristics of drought resistance, barren tolerance, etc. Compared with ryegrass, Cynodon dactylon, Festuca elata, Annual bluegrass, Petunia hybrid, Cosmos bipinnatus or Iris lactea, etc., in the prior art, Dicranopteris dichotoma is higher in terms of adaptability to the environment, is suitable for growing on a side slope to be restored in an adverse plant growth environment, and improves the effect of side slope ecological restoration.

Description

一种芒萁的边坡生态修复方法A slope ecological restoration method of Osmanthus fragrans 技术领域technical field
本申请涉及边坡修复技术领域,特别是涉及一种芒萁的边坡生态修复装置。The present application relates to the technical field of slope restoration, and in particular to a slope ecological restoration device of Osmanthus mangosteen.
背景技术Background technique
边坡生态修复是应用生态学的原理对人为形成的边坡进行生态恢复的方法,也就是通过特定的技术措施在边坡上成功种植特定的植物,改善边坡的生态环境,从而实现边坡的生态恢复。Slope ecological restoration is a method of applying the principles of ecology to the ecological restoration of artificially formed slopes, that is, through specific technical measures to successfully plant specific plants on the slopes to improve the ecological environment of the slopes, so as to realize the ecological restoration of the slopes. ecological restoration.
目前,用于边坡修复的特定植物一般为草籽、花籽等草本、藤本繁殖体,其中草籽多为黑麦草、狗牙根、高羊茅,或早熟禾等,花籽、藤本多为矮牵牛、波斯菊或马蔺等。At present, the specific plants used for slope restoration are generally herbs and vine propagules such as grass seeds and flower seeds, among which grass seeds are mostly ryegrass, bermudagrass, tall fescue, or bluegrass, and flower seeds and vines are mostly Petunia, Cosmos or Iris etc.
虽然,这些植物具有适应边坡生态修复的一般特性,但是,这些植物大多数种适宜在肥沃、潮湿、富含有机质的土壤中生长,耐干旱、耐贫瘠性能较差,而需要生态修复的边坡大多为坡度大、土壤干旱贫瘠、空气湿度小,不利于植物生长的小环境恶劣,因此,试验研究出适应这一特殊环境的植物材料及其配套技术,非常必要,是目前生产上亟待解决的问题。Although these plants have the general characteristics of adapting to slope ecological restoration, most of these plants are suitable for growing in fertile, moist soil rich in organic matter, and have poor tolerance to drought and barrenness. Most of the slopes have large slopes, dry and barren soil, and low air humidity, which is not conducive to the small environment of plant growth. Therefore, it is very necessary to test and research plant materials and supporting technologies that adapt to this special environment, and it is an urgent problem to be solved in production. The problem.
申请内容application content
本申请的目的是:提供一种芒萁的边坡生态修复装置,能够将芒萁种植在边坡上以修复边坡,并能提高边坡修复效果。The purpose of this application is: to provide a side slope ecological restoration device of Osmanthus mangosteen, which can plant Osmanthus mangosteen on the side slope to repair the side slope, and can improve the effect of side slope restoration.
为了实现上述目的,本申请提供了一种芒萁的边坡生态修复装置,包括 育苗畦和多株芒萁;所述育苗畦包括用于铺设在边坡上的无纺土工布和平铺在所述无纺土工布上的基质层;多株所述芒萁分别种植于所述基质层内;所述基质层由25份至35份火烧土、25份至35份肥沃园土、15份至25份赤红壤心土,以及15份至25份河沙搅拌均匀的混合土壤加水搅拌形成。In order to achieve the above object, the application provides a side slope ecological restoration device of Osmanthus osmanthus, including a seedling raising bed and a plurality of Osmanthus osmanthus; the seedling raising bed includes non-woven geotextiles and laying on the The substrate layer on the non-woven geotextile; the Osmanthus osmanthus of a plurality of plants are respectively planted in the substrate layer; the substrate layer consists of 25 to 35 parts of fire soil, 25 to 35 parts of fertile garden soil, and 25 parts of red soil core soil, and 15 to 25 parts of river sand are uniformly stirred and mixed with water to form.
进一步地,多株所述芒萁在所述基质层上呈矩阵交错分布。Further, multiple plants of Osmanthus lanceolata are distributed in a staggered matrix on the matrix layer.
进一步地,所述育苗畦的数量为多个,多个所述育苗畦呈矩阵分布,在横向上相邻的两个所述育苗畦相接,在纵向上相邻的两个所述育苗畦相接。Further, the number of the seedling raising beds is multiple, and the plurality of seedling raising beds are distributed in a matrix, the two adjacent seedling raising beds in the horizontal direction are connected, and the two adjacent seedling raising beds in the vertical direction connect.
进一步地,所述无纺土工布呈矩形,所述无纺土工布的边长为0.8m至1.2m;所述基质层的厚度为3cm至4cm。Further, the non-woven geotextile is rectangular, and the side length of the non-woven geotextile is 0.8m to 1.2m; the thickness of the matrix layer is 3cm to 4cm.
进一步地,还包括用于将所述育苗畦固定在所述边坡上的固定机构。Further, it also includes a fixing mechanism for fixing the seedling raising bed on the slope.
进一步地,所述固定机构包括安装在所述基质层上方的条形板和多个紧固件;多个所述紧固件延所述条形板的延伸方向间隔设置并分别能够穿过所述条形板和基质层以紧固件连接在边坡上。Further, the fixing mechanism includes a strip plate installed above the base layer and a plurality of fasteners; the plurality of fasteners are arranged at intervals along the extending direction of the strip plate and can respectively pass through the The strip plate and the matrix layer are connected on the side slope with fasteners.
进一步地,所述条形板设有多个,多个所述条形板平行设置。Further, there are multiple strip-shaped plates, and the multiple strip-shaped plates are arranged in parallel.
进一步地,所述火烧土、肥沃园土、赤红壤心土以及河沙分别为灭菌土壤,且所述火烧土、肥沃园土、赤红壤心土以及河沙的粒径分别小于0.36cm。Further, the burnt soil, fertile garden soil, red soil core soil and river sand are sterilized soil respectively, and the particle diameters of the burnt soil, fertile garden soil, red soil core soil and river sand are respectively less than 0.36cm.
本申请实施例一种芒萁的边坡生态修复装置与现有技术相比,其有益效果在于:Compared with the prior art, a slope ecological restoration device of Osmanthus osmanthus in the embodiment of the present application has the beneficial effect of:
第一,本申请的边坡生态修复装置采用芒萁为主植物进行边生态修复,具有耐干旱和耐贫瘠等特点,相比于现有技术中的黑麦草、狗牙根、高羊茅、早熟禾、矮牵牛、波斯菊或马蔺等,适应环境的能力强,适宜在环境恶劣的待修复边坡环境上成长,提高边坡的修复效果。First, the slope ecological restoration device of the present application uses Osmanthus as the main plant to carry out side ecological restoration, which has the characteristics of drought resistance and barrenness resistance. Compared with ryegrass, bermudagrass, tall fescue, precocious Grass grass, petunia, cosmos or horse lily, etc., have strong ability to adapt to the environment, and are suitable for growing on the slope to be repaired with harsh environment, so as to improve the repair effect of the slope.
第二,本申请采用火烧土、肥沃园土、赤红壤心土以及河沙搅拌形成的混合基质,相比于现有技术中采用如椰糠、泥炭土等材料,本申请的基质层材料更便于获取,能够就地取材,便捷地培育边坡修复植株,即芒萁。Second, the application adopts the mixed matrix formed by burning soil, fertile garden soil, red soil core soil and river sand. Compared with materials such as coconut bran and peat soil used in the prior art, the matrix layer material of the application is more It is easy to obtain, can obtain local materials, and can conveniently cultivate slope restoration plants, that is, Osmanthus osmanthus.
附图说明Description of drawings
图1是本申请实施例的芒萁的边坡生态修复装置的轴测图。Fig. 1 is an axonometric view of a slope ecological restoration device for Osmanthus osmanthus according to an embodiment of the present application.
图2是本申请实施例的芒萁的边坡生态修复装置的应用示意图。Fig. 2 is a schematic diagram of the application of the slope ecological restoration device of Osmanthus osmanthus according to the embodiment of the present application.
图中,1、育苗畦;11、无纺土工布;12、基质层;2、芒萁;3、锁紧件;4、条形板;5、边坡。In the figure, 1, nursery furrow; 11, non-woven geotextile; 12, matrix layer; 2, Osmanthus fragrans; 3, locking member; 4, strip plate; 5, side slope.
具体实施方式detailed description
下面结合附图和实施例,对本申请的具体实施方式作进一步详细描述。以下实施例用于说明本申请,但不用来限制本申请的范围。The specific implementation manners of the present application will be further described in detail below in conjunction with the drawings and embodiments. The following examples are used to illustrate the present application, but not to limit the scope of the present application.
在本申请的描述中,需要理解的是,术语“中心”、“纵向”、“横向”、“长度”、“宽度”、“厚度”、“上”、“下”、“前”、“后”、“左”、“右”、“竖直”、“水平”、“顶”、“底”“内”、“外”、“顺时针”、“逆时针”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。In the description of the present application, it should be understood that the terms "center", "longitudinal", "transverse", "length", "width", "thickness", "upper", "lower", "front", " Orientation or position indicated by "back", "left", "right", "vertical", "horizontal", "top", "bottom", "inner", "outer", "clockwise", "counterclockwise", etc. The relationship 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, rather than indicating or implying that the referred device or element must have a specific orientation, be constructed and operated in a specific orientation, therefore It should not be construed as a limitation of the application.
此外,术语“第一”、“第二”仅用于描述目的,而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”的特征可以明示或者隐含地包括一个或者更多个该特征。在本申请的描述中,“多个”的含义是两个或两个以上,除非另有明确具体的限定。In addition, the terms "first" and "second" are used for descriptive purposes only, and cannot be interpreted as indicating or implying relative importance or implicitly specifying the quantity of indicated technical features. Thus, a feature defined as "first" and "second" may explicitly or implicitly include one or more of these features. In the description of the present application, "plurality" means two or more, unless otherwise specifically defined.
在本申请中,除非另有明确的规定和限定,术语“安装”、“相连”、“连接”、“固定”等术语应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或成一体;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或两个元件的相互作用关系。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 this application, terms such as "installation", "connection", "connection" and "fixation" should be interpreted in a broad sense, for example, it can be a fixed connection or a detachable connection, unless otherwise clearly specified and limited. , or integrated; it can be mechanically connected or electrically connected; it can be directly connected or indirectly connected through an intermediary, and it can be the internal communication of two components or the interaction relationship between two components. For those of ordinary skill in the art, the specific meanings of the above terms in this application can be understood according to specific situations.
在本申请中,除非另有明确的规定和限定,第一特征在第二特征之“上”或之“下”可以包括第一和第二特征直接接触,也可以包括第一和第二特征不是直接接触而是通过它们之间的另外的特征接触。而且,第一特征在第二特征“之上”、“上方”和“上面”包括第一特征在第二特征正上方和斜上方,或仅仅表示第一特征水平高度高于第二特征。第一特征在第二特征“之下”、“下方”和“下面”包括第一特征在第二特征正下方和斜下方,或仅仅表示第一特征水平高度小于第二特征。In this application, unless otherwise expressly specified and limited, a first feature being "on" or "under" a second feature may include direct contact between the first and second features, and may also include the first and second features Not in direct contact but through another characteristic contact between them. Moreover, "above", "above" and "above" the first feature on the second feature include that the first feature is directly above and obliquely above the second feature, or simply means that the first feature is horizontally higher than the second feature. "Below", "under" and "under" the first feature to the second feature include that the first feature is directly below and obliquely below the second feature, or simply means that the first feature is less horizontally than the second feature.
如图1至图2所示,本申请优选实施例的一种边坡生态修复装置,包括育苗畦1和多株芒萁2;所述育苗畦1包括用于铺设在边坡5上的无纺土工布11和平铺在所述无纺土工布11上的基质层12;多株所述芒萁2分别种植于所述基质层12内;所述基质层12由25份至35份火烧土、25份至35份肥沃园土、15份至25份赤红壤心土,以及15份至25份河沙搅拌均匀的混合土壤加水搅拌形成。As shown in Figures 1 to 2, a slope ecological restoration device according to a preferred embodiment of the present application includes a seedling raising bed 1 and a plurality of Osmanthus osmanthus 2; Woven geotextile 11 and the substrate layer 12 laid on the non-woven geotextile 11; multiple plants of Osmanthus 2 planted in the substrate layer 12 respectively; , 25 to 35 parts of fertile garden soil, 15 to 25 parts of red loam core soil, and 15 to 25 parts of river sand are uniformly stirred and mixed with water to form.
第一,本申请的边坡生态修复装置采用芒萁2为主要植物进行边坡5修复,具有耐干旱和耐瘠薄等特点,相比于现有技术中的黑麦草、狗牙根、高羊茅、早熟禾、矮牵牛、波斯菊或马蔺等,适应环境的能力更强,适宜在环境恶劣的待修复边坡5的环境下成长,提高边坡5的生态修复效果。First, the slope ecological restoration device of the present application adopts Osmanthus 2 as the main plant to carry out slope 5 restoration, which has the characteristics of drought resistance and barren resistance, compared with ryegrass, bermudagrass, tall fescue in the prior art , Bluegrass, Petunia, Cosmos, or Iris, etc., have a stronger ability to adapt to the environment, and are suitable for growing in the harsh environment of the slope 5 to be repaired, so as to improve the ecological restoration effect of the slope 5.
第二,本申请采用火烧土、肥沃园土、赤红壤心土以及河沙搅拌形成混合基质,相比于现有技术中采用如椰糠、泥炭土等材料,本申请的基质层12材料更便于获取,能够就地取材,便捷地培育边坡5修复植株,即芒萁2。Second, the application adopts burning soil, fertile garden soil, red soil core soil and river sand to stir to form a mixed substrate. Compared with materials such as coconut bran and peat soil used in the prior art, the substrate layer 12 material of the application is more It is easy to obtain, can obtain local materials, and conveniently cultivate slope 5 restoration plants, that is, Osmanthus osmanthus 2.
进一步地,在一种实施方式中,请参阅图1至图2,还包括架设在所述基质层12上方的遮荫网,以避免强光照射。Further, in one embodiment, please refer to FIG. 1 to FIG. 2 , it also includes a shading net erected above the base layer 12 to avoid strong light.
进一步地,在一种实施方式中,请参阅图1至图2,所述遮荫网的透光度为50%至60%。优选地,选用透光度为55%的遮荫网。Further, in one embodiment, please refer to Fig. 1 to Fig. 2 , the light transmittance of the shade net is 50% to 60%. Preferably, a shading net with a light transmittance of 55% is selected.
进一步地,在一种实施方式中,请参阅图1至图2,多株所述芒萁2在 所述基质层12上呈矩阵交错分布。Further, in one embodiment, referring to Fig. 1 to Fig. 2, a plurality of plants of Osmanthus 2 are distributed in a matrix on the matrix layer 12 in a staggered manner.
优选地,还包括孔隙为8目至12目的塑料网;塑料网盖设在多株芒萁2上。Preferably, it also includes a plastic mesh with a pore size of 8 to 12 mesh; the plastic mesh cover is arranged on the multiple Osmanthus 2 plants.
进一步地,在一种实施方式中,请参阅图1至图2,所述育苗畦1的数量为多个,多个所述育苗畦1呈矩阵分布,在横向上相邻的两个所述育苗畦1相接,在纵向上相邻的两个所述育苗畦1相接。Further, in one embodiment, please refer to Fig. 1 to Fig. 2, the quantity of described nursery furrows 1 is multiple, and a plurality of described seedling furrows 1 are distributed in a matrix, and the two adjacent laterally The seedling-raising furrows 1 are connected, and two adjacent seedling-raising furrows 1 in the longitudinal direction are connected.
进一步地,在一种实施方式中,请参阅图1至图2,所述无纺土工布11呈矩形,所述无纺土工布11的一侧边长为0.8m至1.2m,所述无纺土工布11的另一侧边长为0.8m至1.2m;所述基质层12的厚度为3cm至4cm。优选地,无纺土工布11的形状为1m×1m的矩形。Further, in one embodiment, please refer to Fig. 1 to Fig. 2, the non-woven geotextile 11 is rectangular, the length of one side of the non-woven geotextile 11 is 0.8m to 1.2m, the non-woven geotextile 11 The length of the other side of the woven geotextile 11 is 0.8m to 1.2m; the thickness of the matrix layer 12 is 3cm to 4cm. Preferably, the shape of the non-woven geotextile 11 is a rectangle of 1 m×1 m.
进一步地,在一种实施方式中,请参阅图1至图2,还包括支架和用于保水的农用薄膜;所述农用薄膜通过所述支架架设在多株所述芒萁2上方。Further, in one embodiment, please refer to FIG. 1 to FIG. 2 , it also includes a support and an agricultural film for water retention; the agricultural film is erected above the multiple Osmanthus 2 plants through the support.
进一步地,在一种实施方式中,请参阅图1至图2,还包括用于将所述育苗畦1固定在所述边坡5上的固定机构,以将边坡5修复结构固定在边坡5上。Further, in one embodiment, referring to Fig. 1 to Fig. 2, it also includes a fixing mechanism for fixing the seedling raising bed 1 on the side slope 5, so as to fix the repair structure of the side slope 5 on the side slope. On slope 5.
进一步地,在一种实施方式中,请参阅图1至图2,所述固定机构包括安装在所述基质层12上方的条形板4和多个紧固件;多个所述紧固件延所述条形板4的延伸方向间隔设置并分别能够穿过所述条形板4和基质层12以紧固件连接在边坡5上。Further, in one embodiment, please refer to FIGS. 1 to 2 , the fixing mechanism includes a strip plate 4 installed above the base layer 12 and a plurality of fasteners; a plurality of the fasteners They are arranged at intervals along the extending direction of the strip plates 4 and can respectively pass through the strip plates 4 and the base layer 12 to be connected to the slope 5 with fasteners.
本实施方式中,通过条形板4和紧固件的方式固定育苗畦1,结构简单,固定稳固。In this embodiment, the seedling raising bed 1 is fixed by means of the strip plate 4 and fasteners, the structure is simple, and the fixing is stable.
可选地,在另一种实施方式中,所述固定机构包括安装在所述基质层12上方的条形板4和多个锁紧件3;所述锁紧件3为呈螺旋状的铁线钉;多个所述锁紧件3沿所述条形板4的延伸方向间隔设置并分别能够穿过所述条形板4和基质层12以旋入至边坡5内。Optionally, in another embodiment, the fixing mechanism includes a strip plate 4 installed above the matrix layer 12 and a plurality of locking pieces 3; the locking pieces 3 are helical iron Wire nails; a plurality of locking members 3 are arranged at intervals along the extending direction of the strip plate 4 and can respectively pass through the strip plate 4 and the matrix layer 12 to be screwed into the side slope 5 .
本可选的实施方式提供了一种固定机构的替代方案,通过螺旋状的铁线 钉旋入至边坡5内,实现将育苗畦1稳固地固定在边坡5上。This optional embodiment provides an alternative to the fixing mechanism, which is screwed into the side slope 5 by a helical wire nail, so that the seedling raising bed 1 is firmly fixed on the side slope 5 .
进一步地,在一种实施方式中,请参阅图1至图2,所述条形板4设有多个,多个所述条形板4平行设置,以在多个位置上分别固定育苗畦1,尤其适用于坡度较大的边坡5。其中,根据边坡的坡度大小,调整条形板的数量。Further, in one embodiment, please refer to Fig. 1 to Fig. 2, described strip plate 4 is provided with a plurality of, and a plurality of described strip plate 4 are arranged in parallel, to respectively fix seedling raising bed in multiple positions 1, especially suitable for slopes with large slopes5. Among them, according to the slope size of the slope, adjust the number of strip plates.
更进一步地,固定机构同时包括多个条形板4、多个紧固件,以及多个锁紧件3;所述锁紧件3为呈螺旋状的铁线钉,所述紧固件呈螺旋线柱状结构;部分条形板4上设置有多个紧固件,其它条形板4上设置有多个所述锁紧件3;多个所述紧固件延所述条形板4的延伸方向间隔设置并分别能够穿过所述条形板4和基质层12以紧固件连接到边坡5上;多个所述锁紧件3沿所述条形板4的延伸方向间隔设置并分别能够穿过所述条形板4和基质层12以旋入至边坡5内。Furthermore, the fixing mechanism simultaneously includes a plurality of strip plates 4, a plurality of fasteners, and a plurality of locking elements 3; the locking elements 3 are helical wire nails, and the fasteners are Helical columnar structure; some of the strip plates 4 are provided with multiple fasteners, and other strip plates 4 are provided with multiple locking members 3; a plurality of the fasteners extend along the strip plate 4 The extension direction of the strip plate 4 is arranged at intervals and can pass through the strip plate 4 and the substrate layer 12 to be connected to the slope 5 with fasteners; a plurality of locking members 3 are spaced apart along the extension direction of the strip plate 4 It is arranged and can pass through the strip plate 4 and the base layer 12 respectively to be screwed into the side slope 5 .
本进一步的实施例中,同时设置紧固件和锁紧件3,其中,锁紧件3的结构更容易钻入边坡5内,不易与边坡5发生垂直于边坡5的纵向方向发生滑移;与边坡5的连接强度更高,而紧固件的截面积较大,不易与边坡5发生平行于边坡5的水平方向发生滑移。因此,同时设置紧固件和锁紧件3后,能够更进一步地提高育苗畦1和边坡5的固定强度,从而能够使得育苗畦1内的芒萁2茁壮成长,对边坡5起到良好的生态修复效果。In this further embodiment, the fastener and the locking member 3 are set at the same time, wherein the structure of the locking member 3 is easier to drill into the side slope 5, and is not easy to occur with the side slope 5 perpendicular to the longitudinal direction of the side slope 5. Slip: the connection strength with the side slope 5 is higher, and the fastener has a larger cross-sectional area, so it is difficult to slip with the side slope 5 parallel to the horizontal direction of the side slope 5 . Therefore, after the fastener and the locking member 3 are set at the same time, the fixing strength of the seedling raising bed 1 and the side slope 5 can be further improved, so that the Osmanthus 2 in the seedling raising bed 1 can grow vigorously, and play a role in the side slope 5 Good ecological restoration effect.
进一步地,在一种实施方式中,所述火烧土、肥沃园土、赤红壤心土以及河沙分别为灭菌土壤,且所述火烧土、肥沃园土、赤红壤心土以及河沙的粒径分别小于0.36cm。Further, in one embodiment, the burnt soil, fertile garden soil, red soil core soil and river sand are respectively sterilized soil, and the burnt soil, fertile garden soil, red soil core soil and river sand The particle size is less than 0.36cm respectively.
本实施例中,火烧土、肥沃园土、赤红壤心土以及河沙经过50目筛选和消毒后获得,对于芒萁的培养更为有利。In this example, the burned soil, fertile garden soil, red soil core soil and river sand were obtained after 50-mesh screening and disinfection, which is more favorable for the cultivation of Osmanthus osmanthus.
在本说明书的描述中,参考术语“一个实施例”、“一些实施例”、“示意性实施例”、“示例”、“具体示例”、或“一些示例”等的描述意指结合该实施例或示例描述的具体特征、结构、材料或者特点包含于本申请的至少一个实 施例或示例中。在本说明书中,对上述术语的示意性表述不一定指的是相同的实施例或示例。而且,描述的具体特征、结构、材料或者特点可以在任何的一个或多个实施例或示例中以合适的方式结合。In the description of this specification, references to the terms "one embodiment," "some embodiments," "exemplary embodiments," "example," "specific examples," or "some examples" are intended to mean that the implementation A specific feature, structure, material, or characteristic described by an embodiment or example is included in at least one embodiment or example of the present application. In this specification, schematic representations of the above terms do not necessarily refer to the same embodiment or example. Furthermore, the specific features, structures, materials or characteristics described may be combined in any suitable manner in any one or more embodiments or examples.
尽管已经示出和描述了本申请的实施例,本领域的普通技术人员可以理解:在不脱离本申请的原理和宗旨的情况下可以对这些实施例进行多种变化、修改、替换和变型,本申请的范围由权利要求及其等同物限定。Although the embodiments of the present application have been shown and described, those skilled in the art can understand that various changes, modifications, substitutions and variations can be made to these embodiments without departing from the principle and spirit of the present application. The scope of the application is defined by the claims and their equivalents.

Claims (8)

  1. 一种芒萁的边坡生态修复装置,其特征在于,包括育苗畦和多株芒萁;A slope ecological restoration device for Osmanthus dimango, characterized in that it includes a nursery bed and multiple Osmanthus osmanthus plants;
    所述育苗畦包括用于铺设在边坡上的无纺土工布和平铺在所述无纺土工布上的基质层;The seedling raising bed includes a non-woven geotextile for laying on the slope and a matrix layer laid on the non-woven geotextile;
    多株所述芒萁分别种植于所述基质层内;Multiple plants of Osmanthus mangosteen are respectively planted in the matrix layer;
    所述基质层由25份至35份火烧土、25份至35份肥沃园土、15份至25份赤红壤心土,以及15份至25份河沙搅拌均匀的混合土壤加水搅拌形成。The matrix layer is formed by adding 25 to 35 parts of fire soil, 25 to 35 parts of fertile garden soil, 15 to 25 parts of crimson core soil, and 15 to 25 parts of river sand, which are uniformly stirred and mixed with water.
  2. 根据权利要求1所述的芒萁边坡生态修复装置,其特征在于,多株所述芒萁在所述基质层上呈矩阵交错分布。The ecological restoration device for Osmanthus persicum slope according to claim 1, wherein a plurality of Osmanthus persicum plants are distributed in a matrix on the matrix layer.
  3. 根据权利要求1所述的芒萁的边坡生态修复装置,其特征在于,所述育苗畦的数量为多个,多个所述育苗畦呈矩阵分布,在横向上相邻的两个所述育苗畦相接,在纵向上相邻的两个所述育苗畦相接。The slope ecological restoration device for Osmanthus persicum according to claim 1, wherein the number of the seedling beds is multiple, and the plurality of seedling beds are distributed in a matrix, and the two adjacent ones in the lateral direction The seedling-raising borders are connected, and two adjacent seedling-raising borders in the longitudinal direction are connected.
  4. 根据权利要求1所述的芒萁的边坡生态修复装置,其特征在于,所述无纺土工布呈矩形,所述无纺土工布的边长为0.8m至1.2m;所述基质层的厚度为3cm至4cm。The slope ecological restoration device of Osmanthus persicum according to claim 1, wherein the non-woven geotextile is rectangular, and the side length of the non-woven geotextile is 0.8m to 1.2m; the matrix layer The thickness is 3cm to 4cm.
  5. 根据权利要求1所述芒萁的边坡生态修复装置,其特征在于,还包括用于将所述育苗畦固定在所述边坡上的固定机构。According to claim 1, the slope ecological restoration device for Osmanthus osmanthus, further comprising a fixing mechanism for fixing the seedling bed on the slope.
  6. 根据权利要求4所述的芒萁的边坡生态修复装置,其特征在于,所述固定机构包括安装在所述基质层上方的条形板和多个紧固件;The slope ecological restoration device of Osmanthus persicum according to claim 4, wherein the fixing mechanism includes a strip plate and a plurality of fasteners installed above the matrix layer;
    多个所述紧固件延所述条形板的延伸方向间隔设置并分别能够穿过所述条形板和基质层以紧固件连接在边坡上。A plurality of the fasteners are arranged at intervals along the extending direction of the strip plate and can respectively pass through the strip plate and the base layer to be connected on the side slope with the fasteners.
  7. 根据权利要求5所述的芒萁的边坡生态修复装置,其特征在于,所述条形板设有多个,多个所述条形板平行设置。The slope ecological restoration device for Osmanthus persicum according to claim 5, characterized in that there are multiple strip-shaped plates, and the plurality of strip-shaped plates are arranged in parallel.
  8. 根据权利要求1所述的芒萁的边坡生态修复装置,其特征在于,所述火烧土、肥沃园土、赤红壤心土以及河沙分别为灭菌土壤,且所述火烧土、 肥沃园土、赤红壤心土以及河沙的粒径分别小于0.36cm。The slope ecological restoration device of Osmanthus persicum according to claim 1, characterized in that, the burned soil, fertile garden soil, red soil core soil and river sand are respectively sterilized soil, and the burned soil, fertile garden The particle diameters of soil, red soil core soil and river sand are less than 0.36cm respectively.
PCT/CN2021/129277 2021-06-24 2021-11-08 Method for side slope ecological restoration of dicranopteris dichotoma WO2022267297A1 (en)

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CN113287472A (en) * 2021-06-24 2021-08-24 广东美景环境科技有限公司 Ecological remediation method for slope of dicranopteris pedata
CN114027111B (en) * 2021-10-18 2023-07-14 西安高岭绿能科技有限公司 Method for ecologically treating high-steep slope with acid rock covered by dicranopteris pedata layer
CN114175974B (en) * 2021-11-30 2023-01-24 华中农业大学 Red soil terrace wall stability maintaining method based on root system structure

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002363990A (en) * 2001-06-12 2002-12-18 Nisshoku Corp Slope seeding and planting method
KR20070033707A (en) * 2005-09-22 2007-03-27 한남수 Nonwoven vegetation bag with rebar fixing band, slope structure and slope method using the same
CN106717888A (en) * 2016-12-09 2017-05-31 江西邓志平园林绿化有限公司 A kind of breeding method of the annual container seedling of monkey camphor tree
CN107969188A (en) * 2017-12-07 2018-05-01 山东农业大学 A kind of salt-soda soil irrigation canals and ditches side slope herbosa plants raw structure and planting and establishing method
CN111456046A (en) * 2020-05-13 2020-07-28 岭南生态文旅股份有限公司 Light ecological slope restoration structure and restoration method
JP6828210B1 (en) * 2020-07-17 2021-02-10 芽苗工法促進会株式会社 Vegetation method
CN113261479A (en) * 2021-06-24 2021-08-17 广东美景环境科技有限公司 Ecological prosthetic devices of side slope of dicranopteris pedata
CN113287472A (en) * 2021-06-24 2021-08-24 广东美景环境科技有限公司 Ecological remediation method for slope of dicranopteris pedata
CN215736160U (en) * 2021-06-24 2022-02-08 广东美景环境科技有限公司 Ecological prosthetic devices of side slope of dicranopteris pedata

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100596269C (en) * 2006-08-01 2010-03-31 深圳市铁汉生态环境股份有限公司 Plant slope protection method for low maintenance of exposed rock mass slope
CN105493819A (en) * 2015-12-03 2016-04-20 吴远彬 Factory-like rapid cultivation method for dicrano pteris pedata seedlings
CN106538393A (en) * 2016-12-08 2017-03-29 大连民族大学 A kind of method of mountain region high-yield culturing Herba Fimbristylis dichotomae
CN207574179U (en) * 2017-11-01 2018-07-06 深圳市铁汉生态环境股份有限公司 A kind of vegetation blanket
CN108746170A (en) * 2018-07-31 2018-11-06 杭州绿风生态环境建设集团有限公司 A kind of method of pteridophyte restoration of soil polluted by heavy metal
CN110512619A (en) * 2019-08-08 2019-11-29 中国恩菲工程技术有限公司 Ecological remediation type rare-earth tailing and reparation rare-earth tailing method
CN112715084B (en) * 2020-12-22 2022-06-03 广东省科学院广州地理研究所 High-altitude side slope vegetation restoration method

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002363990A (en) * 2001-06-12 2002-12-18 Nisshoku Corp Slope seeding and planting method
KR20070033707A (en) * 2005-09-22 2007-03-27 한남수 Nonwoven vegetation bag with rebar fixing band, slope structure and slope method using the same
CN106717888A (en) * 2016-12-09 2017-05-31 江西邓志平园林绿化有限公司 A kind of breeding method of the annual container seedling of monkey camphor tree
CN107969188A (en) * 2017-12-07 2018-05-01 山东农业大学 A kind of salt-soda soil irrigation canals and ditches side slope herbosa plants raw structure and planting and establishing method
CN111456046A (en) * 2020-05-13 2020-07-28 岭南生态文旅股份有限公司 Light ecological slope restoration structure and restoration method
JP6828210B1 (en) * 2020-07-17 2021-02-10 芽苗工法促進会株式会社 Vegetation method
CN113261479A (en) * 2021-06-24 2021-08-17 广东美景环境科技有限公司 Ecological prosthetic devices of side slope of dicranopteris pedata
CN113287472A (en) * 2021-06-24 2021-08-24 广东美景环境科技有限公司 Ecological remediation method for slope of dicranopteris pedata
CN215736160U (en) * 2021-06-24 2022-02-08 广东美景环境科技有限公司 Ecological prosthetic devices of side slope of dicranopteris pedata

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