CN116114545A - A Method of Reconstructing Vegetation Layer Using Turf with Different Disturbance Degrees - Google Patents
A Method of Reconstructing Vegetation Layer Using Turf with Different Disturbance Degrees Download PDFInfo
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- 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
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- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
- A01G24/22—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing plant material
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- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/30—Growth substrates; Culture media; Apparatus or methods therefor based on or containing synthetic organic compounds
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Abstract
Description
技术领域technical field
本发明涉及高寒草甸生态修复技术领域,具体涉及利用不同扰动程度草皮重构植生层的方法。The invention relates to the technical field of alpine meadow ecological restoration, in particular to a method for reconstructing a vegetation layer using turf with different disturbance degrees.
背景技术Background technique
随着我国对生态环境保护的愈加重视,对利用新鲜剥离草皮以及受不同程度扰动剥离草皮重构植生层技术的需求越来越强烈。As my country pays more and more attention to the protection of the ecological environment, there is an increasingly strong demand for the technology of reconstructing the vegetation layer using freshly stripped turf and stripped turf disturbed to varying degrees.
由于对利用剥离草皮回用的需求不断增加,近年来有学者提出,根据草皮剥离堆放的季节预测草皮块堆放活力变化,并采用带侧孔的土工格室作为骨架支撑材料以减缓活力衰减,回铺时夯实坡面,由下至上铺设腐殖土、底肥、草皮并对厚度进行修正使铺设面齐平。该方案施工工艺复杂;也有学者提出,根据自然植被类型与覆盖度划定草皮保护级别,根据降雨、温度与土壤因素划定植被可恢复级别,由此划分出若干生态控制段落,并在不同生态控制段落中使用不同的草皮起挖与保护工艺,最大限度地保护剥离草皮。如上所述,可见现今对于剥离草皮回用研究的着重点大多在于对剥离草皮的管养,使其在剥离后的一段时间内,仍可以满足植物萌发、生长的需求。Due to the increasing demand for reuse of stripped turf, some scholars have proposed in recent years to predict the change of turf stacking activity according to the season of turf stripping and stacking, and use geocells with side holes as the skeleton support material to slow down the decay of activity When paving, tamp the slope, lay humus, base fertilizer, and turf from bottom to top, and correct the thickness to make the paving surface flush. The construction process of this scheme is complicated; some scholars have also proposed that the turf protection level should be delineated according to the natural vegetation type and coverage, and the vegetation recovery level should be delineated according to rainfall, temperature and soil factors. Different turf excavation and protection processes are used in the control section to maximize the protection of stripped turf. As mentioned above, it can be seen that the focus of current research on the reuse of stripped turf is mostly on the management and maintenance of the stripped turf, so that it can still meet the needs of plant germination and growth within a period of time after stripping.
发明内容Contents of the invention
本发明提供了利用不同扰动程度草皮重构植生层的方法,解决了现有技术存在的施工工艺复杂、管养难度大的问题。The invention provides a method for reconstructing the vegetation layer by using turf with different disturbance degrees, and solves the problems of complicated construction technology and difficult management and maintenance in the prior art.
为了解决该技术问题,本发明提供了如下技术方案:In order to solve this technical problem, the present invention provides following technical scheme:
利用不同扰动程度草皮重构植生层的方法,包括如下步骤:The method for reconstructing the vegetation layer using turf with different disturbance degrees comprises the following steps:
(1)选择确定剥离草皮堆积区与回铺区,在剥离草皮堆积区选取不同堆放时间的草皮,用于后续重构植生层;(1) Select and determine the stripped turf accumulation area and the resurfacing area, and select turf with different stacking times in the stripped turf accumulation area for subsequent reconstruction of the vegetation layer;
(2)将步骤(1)中不同堆放时间的草皮块使用破碎机破碎,过2mm筛,与改性有机材料和植被种子混合,制成混合浆土;(2) the turf blocks of different stacking times in the step (1) are broken with a crusher, passed through a 2mm sieve, mixed with modified organic materials and vegetation seeds, and made into mixed slurry soil;
(3)将步骤(2)中的混合浆土回铺至步骤(1)中调研的回铺区域,形成一定厚度的植生层。(3) Back-pave the mixed slurry soil in step (2) to the back-paving area surveyed in step (1) to form a vegetation layer of a certain thickness.
现有的植生层重构技术多为使用草皮直接回铺,本发明利用实际工程中数量庞大的受不同程度扰动影响的剥离草皮并结合具有良好固土能力的改性有机材料重构植生层,符合生态环保要求;改性有机材料的使用可使植生层基质更加保水保肥,更利于植物的萌发与生长;材料复配简单,易于推广应用。Most of the existing vegetation layer reconstruction technologies use turf to directly cover back. The present invention uses a large number of stripped turf affected by different degrees of disturbance in actual projects and combines modified organic materials with good soil-fixing ability to reconstruct the vegetation layer. It meets the requirements of ecological and environmental protection; the use of modified organic materials can make the substrate of the vegetation layer more water- and fertilizer-retaining, which is more conducive to the germination and growth of plants; the compounding of materials is simple, and it is easy to popularize and apply.
优选的,步骤(1)中选取的草皮为剥离后堆放时间为210d、180d、90d或1d的草皮块。草皮为高寒草甸区域剥离后存放不同时长的草皮,经破碎机破碎后过筛作为生长基质。Preferably, the turf selected in step (1) is a turf block whose stacking time is 210d, 180d, 90d or 1d after stripping. The turf is the turf that has been peeled off from the alpine meadow area and stored for different periods of time. It is crushed by a crusher and sieved as a growth substrate.
优选的,所述改性有机材料的成分为羧甲基纤维素钠、壳聚糖的混合液。Preferably, the modified organic material is a mixed solution of sodium carboxymethyl cellulose and chitosan.
本发明使用的改性有机材料由两种高聚物组成,通过物理、化学力的接枝和交联对土壤进行粘结,通过改善土壤理化性质提升土壤微生物多样性与酶活性,具有环保、可降解的优势。The modified organic material used in the present invention is composed of two kinds of high polymers, which bond the soil through physical and chemical grafting and crosslinking, and improve soil microbial diversity and enzyme activity by improving soil physical and chemical properties, which are environmentally friendly, Degradable advantage.
优选的,步骤(2)中的改性有机材料的质量分数为5.5%-10%,改性有机材料与破碎草皮混合时改性有机材料与草皮的质量比为1:5-10。Preferably, the mass fraction of the modified organic material in step (2) is 5.5%-10%, and the mass ratio of the modified organic material to the turf is 1:5-10 when the modified organic material is mixed with the broken turf.
优选的,步骤(2)中种子的用量控制在每平方米20-30g。Preferably, the dosage of seeds in step (2) is controlled at 20-30g per square meter.
优选的,步骤(2)中植被种子选自青藏高原本地羊茅、早熟禾和沙蒿。Preferably, the vegetation seeds in step (2) are selected from the group consisting of native fescue, bluegrass and Artemisia annua in the Qinghai-Tibet Plateau.
优选的,植物种子的比例为高羊茅、早熟禾和沙蒿=3:3:1。Preferably, the ratio of plant seeds is tall fescue, bluegrass and artemisia = 3:3:1.
所用的植物主要有高羊茅、早熟禾和沙蒿等生长周期短、抗逆性强的耐寒耐旱的优质植物,所用含量按比例搭配。The plants used mainly include tall fescue, bluegrass and Artemisia annua, high-quality plants with short growth cycle and strong resistance to cold and drought, and the content used is matched in proportion.
优选的,步骤(3)中混合浆土回铺的植生层厚度为5-25cm。Preferably, in the step (3), the thickness of the vegetation layer covered by the mixed slurry soil is 5-25cm.
本发明和现有技术相比,具有以下优点:Compared with the prior art, the present invention has the following advantages:
本发明通过采用不同扰动程度草皮重构植生层。在原料方面,受扰动程度大、难以满足植物萌发、生长需求的草皮可以通过添加一定浓度的有机材料进行改良后重新利用,且有机材料具有环保、可降解、复配简单的特点,对生态环境的影响小;The invention reconstructs the vegetation layer by adopting turf with different disturbance degrees. In terms of raw materials, the turf that has been greatly disturbed and difficult to meet the needs of plant germination and growth can be improved and reused by adding a certain concentration of organic materials, and organic materials are environmentally friendly, degradable, and easy to compound. little impact;
本发明使用的有机材料由两种高聚物组成,通过物理、化学力的接枝和交联对土壤进行粘结,通过改善土壤理化性质提升土壤微生物多样性与酶活性,具有环保、可降解的优势。草皮为高寒草甸区域剥离后存放不同时长的草皮,经破碎机破碎后过筛作为生长基质。所用的植物主要有高羊茅、早熟禾和沙蒿等生长周期短、抗逆性强的耐寒耐旱的本地优质植物。The organic material used in the present invention is composed of two kinds of high polymers, which bond the soil through physical and chemical grafting and crosslinking, and improve soil microbial diversity and enzyme activity by improving soil physical and chemical properties, which are environmentally friendly and degradable The advantages. The turf is the turf that has been peeled off from the alpine meadow area and stored for different periods of time. It is crushed by a crusher and sieved as a growth substrate. The plants used mainly include tall fescue, bluegrass and Artemisia annua, local high-quality plants with short growth cycle and strong resistance to cold and drought.
现有的植生层重构技术多为使用草皮直接回铺,本发明利用实际工程中数量庞大的受不同程度扰动影响的剥离草皮并结合具有良好固土能力的重构植生层,符合生态环保要求;有机材料的使用可使植生层基质更加保水保肥,更利于植物的萌发与生长;材料复配简单,易于推广应用。Most of the existing vegetation layer reconstruction technologies use turf to cover directly. The present invention utilizes a large number of stripped turf affected by different degrees of disturbance in actual projects and combines the reconstructed vegetation layer with good soil-fixing ability, which meets the requirements of ecological and environmental protection. ; The use of organic materials can make the substrate of the vegetation layer more water- and fertilizer-retaining, which is more conducive to the germination and growth of plants; the compounding of materials is simple, and it is easy to popularize and apply.
本方案的方法能在高寒地区利用受不同程度扰动的草皮重构适宜植被生长的植生层,能有效修复人为破坏和自然退化的高寒草甸生态系统,其操作简便,运行成本低且生态零污染。对高寒草甸生态系统的生态恢复与可持续发展有重要意义。在实际运用方面,本发明的工艺流程较短,对大型机械的需求小,投资成本低。The method of this scheme can use the turf disturbed to different degrees to reconstruct the vegetation layer suitable for vegetation growth in the alpine area, and can effectively restore the alpine meadow ecosystem that has been destroyed by man and naturally degraded. It is easy to operate, low in operation cost and ecologically zero-pollution . It is of great significance to the ecological restoration and sustainable development of the alpine meadow ecosystem. In terms of practical application, the technical process of the present invention is relatively short, the demand for large machinery is small, and the investment cost is low.
附图说明Description of drawings
此处所说明的附图用来提供对本发明实施例的进一步理解,构成本申请的一部分,并不构成对本发明实施例的限定。在附图中:The drawings described here are used to provide a further understanding of the embodiments of the present invention, constitute a part of the application, and do not limit the embodiments of the present invention. In the attached picture:
图1是本发明利用不同扰动程度草皮重构植生层的方法的实施流程图。Fig. 1 is the flow chart of the implementation of the method for reconstructing the vegetation layer by using turf with different disturbance degrees according to the present invention.
图2是剥离时间1d草皮重构植生层与对照组的植被萌芽率的对比图。Figure 2 is a comparison chart of the vegetation germination rate between the turf reconstituted vegetation layer and the control group after stripping
图3是剥离时间1d草皮重构植生层与对照组的幼苗高度的对比图。Fig. 3 is a comparison chart of the height of the seedlings of the turf reconstituted vegetation layer and the control group at the stripping time of 1 day.
图4是剥离时间90d草皮重构植生层与对照组的植被萌芽率的对比图。Fig. 4 is a comparison chart of the vegetation germination rate of the turf reconstituted vegetation layer and the control group at a stripping time of 90 days.
图5是剥离时间90d草皮重构植生层与对照组的幼苗高度的对比图。Fig. 5 is a comparison chart of the height of the seedlings of the turf reconstituted vegetation layer and the control group at a stripping time of 90 days.
图6是剥离时间180d草皮重构植生层与对照组的植被萌芽率的对比图。Figure 6 is a comparison chart of the vegetation germination rate between the 180d turf reconstituted vegetation layer and the control group after the stripping time.
图7是剥离时间180d草皮重构植生层与对照组的幼苗高度的对比图。Fig. 7 is a comparison chart of the height of the seedlings of the reconstituted vegetative layer of the turf and the control group at a stripping time of 180 days.
图8是剥离时间210d草皮重构植生层与对照组的植被萌芽率的对比图。Fig. 8 is a comparison chart of the vegetation germination rate of the turf reconstituted vegetation layer and the control group at a stripping time of 210 days.
图9是剥离时间210d草皮重构植生层与对照组的幼苗高度的对比图。Fig. 9 is a comparison chart of the height of the seedlings of the turf reconstituted vegetation layer and the control group at a stripping time of 210 days.
图10为不同剥离时间草皮重构植生层与对照组回铺30d后的地上生物量的对比图。Fig. 10 is a comparison chart of the aboveground biomass of the turf reconstituted vegetation layer and the control group after backlaying for 30 days at different stripping times.
图11为不同剥离时间草皮重构植生层与对照组回铺30d后的植被叶绿素含量的对比图。Figure 11 is a comparison chart of the chlorophyll content of the turf reconstituted vegetation layer and the control group after 30 days of backlaying at different stripping times.
图12为不同剥离时间草皮重构植生层与对照组回铺30d后以及对照组回铺前土壤含水率的对比图。Figure 12 is a comparison chart of the soil moisture content of the turf reconstituted vegetation layer at different stripping times and the control group after 30 days of back-laying and the control group before back-laying.
图13为不同剥离时间草皮重构植生层与对照组回铺30d后以及对照组回铺前土壤pH的对比图。Figure 13 is a comparison chart of the soil pH of the turf reconstituted vegetation layer and the control group after 30 days of back-laying and before back-laying of the control group at different stripping times.
具体实施方式Detailed ways
为使本发明的目的、技术方案和优点更加清楚明白,下面结合实施例,对本发明作进一步的详细说明,本发明的示意性实施方式及其说明仅用于解释本发明,并不作为对本发明的限定。In order to make the purpose, technical solutions and advantages of the present invention clearer, the present invention will be further described in detail in conjunction with the following examples. The schematic embodiments of the present invention and their descriptions are only used to explain the present invention, and are not intended as a guideline for the present invention. limit.
实施例1Example 1
本实施例选取川藏线雅安至林芝段剥离后堆放的草皮为研究对象,如图1所示,根据剥离草皮堆积区与回铺区调研,在剥离草皮堆积区选取堆积时间1d的草皮,经破碎机破碎并过2mm筛后,添加浓度为10%的改性有机材料和抗逆性强的植被种子直接混合。将上述材料混合为浆土回铺于前期调研确定的回铺区域。In this example, the turf that was stripped and piled up in the Ya'an-Nyingchi section of the Sichuan-Tibet line was selected as the research object. After being crushed by a crusher and passed through a 2mm sieve, the modified organic material with a concentration of 10% and the vegetation seeds with strong stress resistance are added and mixed directly. Mix the above materials into paste soil and pave it back to the paved area determined in the previous investigation.
草皮经破碎机破碎并过筛的目的为剔除石子、残枝、垃圾等杂物。以改性有机材料与草皮质量之比为1:8的比例混合;所述改性有机材料的成分为质量比为1:1的羧甲基纤维素钠、壳聚糖的混合液。植被种子为高羊茅、早熟禾和沙蒿这类耐寒耐旱的优质牧草,植物种子的比例为高羊茅、早熟禾和沙蒿=3:3:1,并保证每平米植生层基质的种子质量为20-30g。回铺形成的植生层厚度控制在5-20cm,以满足植被根系发育与植被萌发、生长的基本要求。The turf is crushed and sieved by the crusher to remove stones, residual branches, garbage and other sundries. The mass ratio of the modified organic material to the turf is 1:8; the modified organic material is a mixture of sodium carboxymethyl cellulose and chitosan with a mass ratio of 1:1. Vegetation seeds are cold-resistant and drought-resistant high-quality forages such as tall fescue, bluegrass and Artemisia annua. The ratio of plant seeds is tall fescue, bluegrass and Artemisia annua = 3:3:1, and the quality of seeds per square meter of vegetation layer substrate is guaranteed 20-30g. The thickness of the vegetation layer formed by back-laying is controlled at 5-20cm to meet the basic requirements of vegetation root development, vegetation germination and growth.
采用浓度为5.5%的改性有机材料替代上述浓度为10%的改性有机材料进行上述平行试验,不添加浓度为0%的改性有机材料进行对照试验。考量指标为植被萌芽率、幼苗高度、地上生物量、叶绿素含量、土壤含水率、pH。所得数据由从三次重复分析得出。The modified organic material with a concentration of 5.5% was used instead of the modified organic material with a concentration of 10% to carry out the above parallel test, and a control test was carried out without adding the modified organic material with a concentration of 0%. The consideration indicators are vegetation germination rate, seedling height, aboveground biomass, chlorophyll content, soil moisture content, and pH. The data obtained were derived from triplicate analyses.
实施例2Example 2
本实施例选取川藏线雅安至林芝段CZXZZQ-14B标段剥离后堆放的草皮为研究对象,如图1所示,根据剥离草皮堆积区与回铺区调研,在剥离草皮堆积区选取堆积时间90d的草皮,经破碎机破碎并过2mm筛后,添加浓度为10%的改性有机材料和抗逆性强的植被种子。将上述材料混合为浆土回铺于前期调研确定的回铺区域。In this example, the turf piled up after the stripping of the CZXZZQ-14B section of the Sichuan-Tibet line from Ya’an to Nyingchi was selected as the research object. As shown in Figure 1, according to the investigation of the stripped turf accumulation area and the resurfacing area, the accumulation time was selected in the stripped turf accumulation area The 90d turf is crushed by a crusher and passed through a 2mm sieve, and the modified organic material with a concentration of 10% and vegetation seeds with strong stress resistance are added. Mix the above materials into paste soil and pave it back to the paved area determined in the previous investigation.
草皮经破碎机破碎并过筛的目的为剔除石子、残枝、垃圾等杂物。以改性有机材料与草皮质量之比为1:8的比例混合;所述改性有机材料的成分为质量比为1:1的羧甲基纤维素钠、壳聚糖的混合液。植被种子为高羊茅、早熟禾和沙蒿这类耐寒耐旱的优质牧草,植物种子的比例为高羊茅、早熟禾和沙蒿=3:3:1,并保证每平米植生层基质的种子质量为20-30g。回铺形成的植生层厚度控制在5-20cm,以满足植被根系发育与植被萌发、生长的基本要求。The turf is crushed and sieved by the crusher to remove stones, residual branches, garbage and other sundries. The mass ratio of the modified organic material to the turf is 1:8; the modified organic material is a mixture of sodium carboxymethyl cellulose and chitosan with a mass ratio of 1:1. Vegetation seeds are cold-resistant and drought-resistant high-quality forages such as tall fescue, bluegrass and Artemisia annua. The ratio of plant seeds is tall fescue, bluegrass and Artemisia annua = 3:3:1, and the quality of seeds per square meter of vegetation layer substrate is guaranteed 20-30g. The thickness of the vegetation layer formed by back-laying is controlled at 5-20cm to meet the basic requirements of vegetation root development, vegetation germination and growth.
采用浓度为5.5%的改性有机材料替代上述浓度为10%的改性有机材料进行上述平行试验,不添加浓度为0%的改性有机材料进行对照试验。考量指标为植被萌芽率、幼苗高度、地上生物量、叶绿素含量、土壤含水率、pH。所得数据由从三次重复分析得出。The modified organic material with a concentration of 5.5% was used instead of the modified organic material with a concentration of 10% to carry out the above parallel test, and a control test was carried out without adding the modified organic material with a concentration of 0%. The consideration indicators are vegetation germination rate, seedling height, aboveground biomass, chlorophyll content, soil moisture content, and pH. The data obtained were derived from triplicate analyses.
实施例3Example 3
本实施例选取川藏线雅安至林芝段CZXZZQ-14B标段剥离后堆放的草皮为研究对象,如图1所示,根据剥离草皮堆积区与回铺区调研,在剥离草皮堆积区选取堆积时间180d的草皮,经破碎机破碎并过2mm筛后,添加浓度为10%的改性有机材料和抗逆性强的植被种子。将上述材料混合为浆土回铺于前期调研确定的回铺区域。In this example, the turf piled up after the stripping of the CZXZZQ-14B section of the Sichuan-Tibet line from Ya’an to Nyingchi was selected as the research object. As shown in Figure 1, according to the investigation of the stripped turf accumulation area and the resurfacing area, the accumulation time was selected in the stripped turf accumulation area The 180d turf is crushed by a crusher and passed through a 2mm sieve, and then 10% modified organic materials and vegetation seeds with strong stress resistance are added. Mix the above materials into paste soil and pave it back to the paved area determined in the previous investigation.
草皮经破碎机破碎并过筛的目的为剔除石子、残枝、垃圾等杂物。以改性有机材料与草皮质量之比为1:8的比例混合;所述改性有机材料的成分为质量比为1:1的羧甲基纤维素钠、壳聚糖的混合液。植被种子为高羊茅、早熟禾和沙蒿这类耐寒耐旱的优质牧草,植物种子的比例为高羊茅、早熟禾和沙蒿=3:3:1,并保证每平米植生层基质的种子质量为20-30g。回铺形成的植生层厚度控制在5-20cm,以满足植被根系发育与植被萌发、生长的基本要求。The turf is crushed and sieved by the crusher to remove stones, residual branches, garbage and other sundries. The mass ratio of the modified organic material to the turf is 1:8; the modified organic material is a mixture of sodium carboxymethyl cellulose and chitosan with a mass ratio of 1:1. Vegetation seeds are cold-resistant and drought-resistant high-quality forages such as tall fescue, bluegrass and Artemisia annua. The ratio of plant seeds is tall fescue, bluegrass and Artemisia annua = 3:3:1, and the quality of seeds per square meter of vegetation layer substrate is guaranteed 20-30g. The thickness of the vegetation layer formed by back-laying is controlled at 5-20cm to meet the basic requirements of vegetation root development, vegetation germination and growth.
采用浓度为5.5%的改性有机材料替代上述浓度为10%的改性有机材料进行上述平行试验,不添加浓度为0%的改性有机材料进行对照试验。考量指标为植被萌芽率、幼苗高度、地上生物量、叶绿素含量、土壤含水率、pH。所得数据由从三次重复分析得出。The modified organic material with a concentration of 5.5% was used instead of the modified organic material with a concentration of 10% to carry out the above parallel test, and a control test was carried out without adding the modified organic material with a concentration of 0%. The consideration indicators are vegetation germination rate, seedling height, aboveground biomass, chlorophyll content, soil moisture content, and pH. The data obtained were derived from triplicate analyses.
实施例4Example 4
本实施例选取川藏线雅安至林芝段CZXZZQ-14B标段剥离后堆放的草皮为研究对象,如图1所示,根据剥离草皮堆积区与回铺区调研,在剥离草皮堆积区选取堆积时间210d的草皮,经破碎机破碎并过2mm筛后,添加浓度为10%的改性有机材料和抗逆性强的植被种子。将上述材料混合为浆土回铺于前期调研确定的回铺区域。In this example, the turf piled up after the stripping of the CZXZZQ-14B section of the Sichuan-Tibet line from Ya’an to Nyingchi was selected as the research object. As shown in Figure 1, according to the investigation of the stripped turf accumulation area and the resurfacing area, the accumulation time was selected in the stripped turf accumulation area The 210d turf is crushed by a crusher and passed through a 2mm sieve, and then 10% modified organic materials and vegetation seeds with strong stress resistance are added. Mix the above materials into paste soil and pave it back to the paved area determined in the previous investigation.
草皮经破碎机破碎并过筛的目的为剔除石子、残枝、垃圾等杂物。以改性有机材料与草皮质量之比为1:8的比例混合;所述改性有机材料的成分为质量比为1:1的羧甲基纤维素钠、壳聚糖的混合液。植被种子为高羊茅、早熟禾和沙蒿这类耐寒耐旱的优质牧草,植物种子的比例为高羊茅、早熟禾和沙蒿=3:3:1,并保证每平米植生层基质的种子质量为20-30g。回铺形成的植生层厚度控制在5-20cm,以满足植被根系发育与植被萌发、生长的基本要求。The turf is crushed and sieved by the crusher to remove stones, residual branches, garbage and other sundries. The mass ratio of the modified organic material to the turf is 1:8; the modified organic material is a mixture of sodium carboxymethyl cellulose and chitosan with a mass ratio of 1:1. Vegetation seeds are cold-resistant and drought-resistant high-quality forages such as tall fescue, bluegrass and Artemisia annua. The ratio of plant seeds is tall fescue, bluegrass and Artemisia annua = 3:3:1, and the quality of seeds per square meter of vegetation layer substrate is guaranteed 20-30g. The thickness of the vegetation layer formed by back-laying is controlled at 5-20cm to meet the basic requirements of vegetation root development, vegetation germination and growth.
采用浓度为5.5%的改性有机材料替代上述浓度为10%的改性有机材料进行上述平行试验,不添加浓度为0%的改性有机材料进行对照试验。考量指标为植被萌芽率、幼苗高度、地上生物量、叶绿素含量、土壤含水率、pH。所得数据由从三次重复分析得出。The modified organic material with a concentration of 5.5% was used instead of the modified organic material with a concentration of 10% to carry out the above parallel test, and a control test was carried out without adding the modified organic material with a concentration of 0%. The consideration indicators are vegetation germination rate, seedling height, aboveground biomass, chlorophyll content, soil moisture content, and pH. The data obtained were derived from triplicate analyses.
图2、3分别是实施例1剥离时间1d草皮重构植生层与对照组的植被萌芽率和幼苗高度的对比图。由图2、3可以看出,剥离时间1d即受扰动程度较小的草皮重构植生层与对照组相比,植被萌芽率、幼苗高度变化不大。Figures 2 and 3 are respectively the comparison charts of the vegetation germination rate and seedling height of the turf reconstituted vegetation layer and the control group in the stripping
图4、5分别是实施例2剥离时间90d草皮重构植生层与对照组的植被萌芽率和幼苗高度的对比图。由图4、5可以看出,剥离时间90d即受扰动程度中等的草皮重构植生层与对照组相比,植被萌芽率、幼苗高度变化不大。Figures 4 and 5 are respectively the comparison charts of the vegetation germination rate and the height of the seedlings of the turf reconstituted vegetation layer and the control group in Example 2 stripping time 90d. It can be seen from Figures 4 and 5 that compared with the control group, the vegetation germination rate and seedling height of the reconstituted vegetation layer of the turf with a peeling time of 90 days, which is moderately disturbed, have little change.
图6、7分别是实施例3剥离时间180d草皮重构植生层与对照组的植被萌芽率和幼苗高度的对比图。由图6、7可以看出,剥离时间180d即受扰动程度大的草皮重构植生层与对照相比,草皮重构植生层的植被萌芽率和幼苗高度均要优于对照组,其中添加10%浓度改性有机材料的草皮重构植生层对植被萌芽率和幼苗高度的提升效果最好。Figures 6 and 7 are the comparison charts of the vegetation germination rate and seedling height of the 180d turf reconstituted vegetation layer and the control group in Example 3, respectively. It can be seen from Figures 6 and 7 that the vegetation germination rate and seedling height of the turf reconstituted vegetation layer are better than those of the control group when the turf reconstituted vegetation layer was disturbed for 180 days after the stripping time was 180 days. % Concentration modified organic material turf reconstructed vegetation layer had the best effect on the improvement of vegetation germination rate and seedling height.
图8、9分别是实施例4剥离时间210d草皮重构植生层与对照组的植被萌芽率和幼苗高度的对比图。由图8、9可以看出,剥离时间210d即完全扰动草皮重构植生层与对照相比,草皮重构植生层的植被萌芽率和幼苗高度均要优于对照组,其中添加10%浓度改性有机材料的草皮重构植生层对植被萌芽率和幼苗高度的提升效果最好。Figures 8 and 9 are the comparison charts of the vegetation germination rate and seedling height of the turf reconstituted vegetation layer and the control group at the stripping time of 210d in Example 4 and the control group respectively. As can be seen from Figures 8 and 9, the stripping time of 210d, that is, the complete disturbance of the turf reconstruction vegetation layer compared with the control, the vegetation germination rate and seedling height of the turf reconstruction vegetation layer are all better than the control group, wherein 10% concentration of modified The reconstruction of vegetation layer by turf with sexual organic materials has the best effect on the improvement of vegetation germination rate and seedling height.
图10为实施例1-4不同剥离时间草皮重构植生层与对照组回铺30d后的地上生物量的对比图。由图10可以看出,剥离时间较长(>180d)即受扰动程度大的草皮与对照相比,草皮重构植生层的30d地上生物量均要优于对照组,其中添加10%浓度改性有机材料的草皮重构植生层对30d地上生物量的提升效果最好;而对于剥离时间较短(<90d)即受扰动程度小的草皮与对照相比,草皮重构植生层的30d地上生物量与对照相比变化不大。Fig. 10 is a comparison chart of the aboveground biomass of the turf reconstituted vegetation layer and the control group after backlaying for 30 days at different stripping times in Examples 1-4. As can be seen from Figure 10, the turf with a longer peeling time (> 180d), that is, the turf with a greater degree of disturbance, compared with the control, the 30d above-ground biomass of the turf reconstituted vegetation layer is better than the control group. The reconstituted vegetation layer of turf with sexual organic materials has the best effect on the improvement of aboveground biomass at 30 days; and for the turf with a shorter stripping time (<90d) that is less disturbed compared with the control, the 30d aboveground biomass of the reconstituted vegetation layer of turf Biomass did not change much compared to the control.
图11为不同剥离时间草皮重构植生层与对照组回铺30d后的植被叶绿素含量的对比图。由图11可以看出,剥离时间较长(>180d)即受扰动程度大的草皮与对照相比,草皮重构植生层的30d叶绿素含量均要优于对照组,其中添加10%浓度改性有机材料的草皮重构植生层对30d叶绿素含量的提升效果最好;而对于剥离时间较短(<90d)即受扰动程度小的草皮与对照相比,草皮重构植生层的30d叶绿素含量与对照相比变化不大。Figure 11 is a comparison chart of the chlorophyll content of the turf reconstituted vegetation layer and the control group after 30 days of backlaying at different stripping times. It can be seen from Figure 11 that the 30d chlorophyll content of the turf reconstituted vegetation layer is better than that of the control group when the turf with a long peeling time (> 180d), that is, the turf with a large degree of disturbance is compared with the control group. The 30d chlorophyll content of the turf reconstructed vegetation layer of organic materials has the best effect on improving the 30d chlorophyll content; and for the turf with a shorter stripping time (<90d) that is less disturbed compared with the control, the 30d chlorophyll content of the turf reconstructed vegetation layer is the same as that of the control. There was little change compared to the control.
图12为不同剥离时间草皮重构植生层与对照组回铺30d后以及对照组回铺前土壤含水率的对比图。由图12可以看出,通过使用改性有机材料改良草皮重构植生层,可以有效提高土壤含水率,其中添加10%浓度改性有机材料的草皮重构植生层对土壤含水率的提升效果最好。Figure 12 is a comparison chart of the soil moisture content of the turf reconstituted vegetation layer at different stripping times and the control group after 30 days of back-laying and the control group before back-laying. It can be seen from Figure 12 that the soil moisture content can be effectively increased by using modified organic materials to improve the turf reconstruction vegetation layer, and the turf reconstruction vegetation layer with 10% concentration of modified organic materials has the best effect on improving soil moisture content. good.
图13为不同剥离时间草皮重构植生层与对照组回铺30d后以及对照组回铺前土壤pH的对比图。由图13可以看出,通过使用改性有机材料改良草皮重构植生层,可以降低土壤pH,略微提升土壤酸性,使土壤pH更适合植被萌发、生长。Figure 13 is a comparison chart of the soil pH of the turf reconstituted vegetation layer and the control group after 30 days of back-laying and before back-laying of the control group at different stripping times. It can be seen from Figure 13 that by using modified organic materials to improve the turf and reconstruct the vegetation layer, the soil pH can be reduced, the soil acidity can be slightly increased, and the soil pH is more suitable for vegetation germination and growth.
以上所述的具体实施方式,对本发明的目的、技术方案和有益效果进行了进一步详细说明,所应理解的是,以上所述仅为本发明的具体实施方式而已,并不用于限定本发明的保护范围,凡在本发明的精神和原则之内,所做的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The specific embodiments described above have further described the purpose, technical solutions and beneficial effects of the present invention in detail. It should be understood that the above descriptions are only specific embodiments of the present invention and are not intended to limit the scope of the present invention. Protection scope, within the spirit and principles of the present invention, any modification, equivalent replacement, improvement, etc., shall be included in the protection scope of the present invention.
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