CN101790931B - A method for restoring damaged ecosystems in steep slope areas of reservoir drawdown zones - Google Patents
A method for restoring damaged ecosystems in steep slope areas of reservoir drawdown zones Download PDFInfo
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Abstract
本发明涉及一种水库消落带陡坡地区受损生态系统修复方法。在蓄水水位最低时,对消落带迎水坡面进行清理,人工夯实;坡面顶部开挖种植穴,种植马尾松等,构成多功能防护林带。在消落带范围内挖种植槽和种植穴,铺设黄麻土工布,消落深度2m以内的范围种植香根草,构成植物篱带。消落深度2-10m之间的范围混合种植香根草与狗牙根,构成复合植被坡面恢复带。本发明的防护林带、植物篱带及复合植被坡面恢复带共同构成一个立体恢复空间,保证植物在消落带陡坡地区上生根恢复。通过大面积恢复植被,有效减少地表径流和土壤侵蚀,改善土壤肥力和性质,使受损生态系统修复。本发明施工便捷、投入小、不易被水毁,适用于消落范围大,地势陡峭的水库消落带地区。
The invention relates to a method for restoring a damaged ecosystem in a steep slope area of a water-fluctuation zone of a reservoir. When the storage water level is the lowest, clean up the slope facing the water-fluctuating zone and compact it manually; excavate planting holes at the top of the slope and plant masson pine, etc., to form a multi-functional shelterbelt. Dig planting grooves and planting holes within the water-fluctuating zone, lay jute geotextiles, and plant vetiver within the water-fluctuating depth of 2m to form a plant hedge. Vetiver and Bermudagrass are planted mixedly in the range between 2-10m to form a composite vegetation slope restoration zone. The protection forest belt, the hedgerow belt and the composite vegetation slope restoration belt of the present invention together form a three-dimensional restoration space, which ensures that plants take root and restore on the steep slope area of the water-fluctuation zone. Through large-scale restoration of vegetation, surface runoff and soil erosion can be effectively reduced, soil fertility and properties can be improved, and damaged ecosystems can be restored. The invention has the advantages of convenient construction, small investment, and is not easy to be destroyed by water, and is suitable for areas in the water-fluctuation zone of reservoirs with large water-fluctuation range and steep terrain.
Description
技术领域technical field
本发明涉及一种水库消落带陡坡地区受损生态系统修复方法。The invention relates to a method for restoring a damaged ecosystem in a steep slope area of a water-fluctuation zone of a reservoir.
背景技术Background technique
丹江口水库是“南水北调”中线工程的水源地,位于汉江和丹江的交汇处,是我国大型的水利枢纽工程之一。丹江口水库初期工程于1973年建成,正常蓄水位157m,夏季防洪限制水位149m,消落带面积148km2。二期大坝加高工程于2011年完成后,正常蓄水位达到170m。水库调度将是每年10月汛末开始蓄水,到12月水位上升至170m;次年5月,水位又由170m逐渐降低至防洪限制水位,汛期内保持在160-163.5m水位运行。新的消落带将上移至库岸海拔160-170m的地段,面积约为205km2。消落带植被的好坏是水库能否健康运行的重要表征,在河流生态系统中也发挥着重要的作用。然而,由于水库调蓄运行和自然条件等原因,导致水库水位频繁和大幅度波动以及淹没时间过长,水库边缘植被容易遭受破坏,特别是在一些坡度陡、水流急且土壤贫瘠的区域,其植被可能因此淹没消失,则意味着丹江口库区失去了一道生态屏障,消落带会出现污染加重、水土流失加剧、地质灾害频繁等多种生态环境问题,从而威胁到水库的可持续利用与库区生态系统的良性循环。对消落带受损生态系统进行植物生态修复是国内外专家认为非常有效的治理途径之一,对水库消涨带进行植被防护的技术则是一大难题,主要困难在于:①消落带范围的土壤易受水体冲刷流失,植物生长的基础条件不断被破坏;②消落带的生态环境恶劣,植物要长期忍受深水、低温、缺肥等不良影响以及洪水的冲刷;③水库工程的运行特征使得稳定型消落带的植被不能简单地在新的消落带上重建。Danjiangkou Reservoir is the water source of the middle route project of "South-to-North Water Diversion". It is located at the confluence of Han River and Dan River. The initial project of Danjiangkou Reservoir was completed in 1973. The normal storage level is 157m, the restricted water level for flood control in summer is 149m, and the area of the water-fluctuating zone is 148km 2 . After the second phase of the dam heightening project was completed in 2011, the normal water storage level reached 170m. The reservoir dispatching will begin to store water at the end of the flood season in October every year, and the water level will rise to 170m in December; in May of the following year, the water level will gradually decrease from 170m to the flood control limit water level, and the water level will remain at 160-163.5m during the flood season. The new water-fluctuation zone will be moved up to the bank bank at an altitude of 160-170m, with an area of about 205km 2 . The quality of the vegetation in the hydrofluctuation zone is an important indicator of the healthy operation of the reservoir, and it also plays an important role in the river ecosystem. However, due to reservoir adjustment and storage operation and natural conditions, the water level of the reservoir frequently fluctuates greatly and the submersion time is too long, and the vegetation on the edge of the reservoir is easily damaged, especially in some areas with steep slopes, rapid water flow and poor soil. Vegetation may be submerged and disappear, which means that the Danjiangkou reservoir area has lost an ecological barrier, and various ecological and environmental problems such as increased pollution, increased soil erosion, and frequent geological disasters will appear in the water-fluctuating zone, which threatens the sustainable use of the reservoir and the reservoir quality. A virtuous cycle of the regional ecosystem. Plant ecological restoration of the damaged ecosystem in the water-fluctuating zone is one of the most effective treatment methods considered by experts at home and abroad. The technology of vegetation protection in the water-fluctuating zone of the reservoir is a major problem. The main difficulties lie in: ① The scope of the water-fluctuating zone The soil is vulnerable to water erosion and loss, and the basic conditions for plant growth are constantly being destroyed; ②The ecological environment in the water-fluctuating zone is harsh, and plants have to endure the adverse effects of deep water, low temperature, lack of fertilizers, and floods for a long time; ③Operation characteristics of the reservoir project The vegetation in the stable-type water-fluctuation zone cannot be simply rebuilt on the new water-fluctuation zone.
目前已经开始对一些较大型的水电工程的消落带进行生态恢复,以改善库区的生物多样性与环境状况。如《一种用于河堤水库防冲护岸的新型植物配置及生态工程技术》(中国专利申请号03146885.3),它是一种以香根草为主体,再配置其它的植物材料,通过现场勘测、技术设计、选苗育种、施工种植、专业养护管理,用于河堤水库防冲护岸的生态工程技术。《一种用于改善水库消落区生态环境的湿地治理方法》(中国专利申请号200910099098.X),对开挖区域进行开挖,对填筑区进行填筑,对开挖填筑体顶面及迎水面进行防护,消落深度3-5m之间区域种植沉水植物和浮叶沉水植物,消落深度3m以内区域种植挺水植物和湿生乔灌木。《用狗牙根修复水库消落带和河岸受损生态系统的方法》(中国专利申请号200810032895.1),筛选狗牙根作为修复植物,采用无性繁殖或有性繁殖后进行种植或移植到修复区,然后进行养护,确保来年生长,从而重建和恢复库消落带和河岸带生态。At present, the ecological restoration of the water-fluctuating zones of some relatively large-scale hydropower projects has begun to improve the biodiversity and environmental conditions in the reservoir area. For example, "A New Type of Plant Configuration and Ecological Engineering Technology for Anti-scour and Bank Protection of Embankments and Reservoirs" (Chinese Patent Application No. 03146885.3), it is a kind of vetiver as the main body, and then configures other plant materials. , Technical design, seedling selection and breeding, construction and planting, professional maintenance management, ecological engineering technology used for anti-scour and revetment of embankments and reservoirs. "A Wetland Treatment Method for Improving the Ecological Environment of the Reservoir's Fluctuation Area" (Chinese Patent Application No. 200910099098.X), the excavation area is excavated, the filling area is filled, and the top of the excavated filling body Protect the water surface and the water surface, plant submerged plants and floating leaf submerged plants in the area between the sinking depth of 3-5m, and plant emergent plants and hygroscopic trees and shrubs in the area within the sinking depth of 3m. "The Method for Restoring Reservoir Fluctuation Zone and Riverbank Damaged Ecosystem with Bermudagrass" (Chinese Patent Application No. 200810032895.1), screens Bermudagrass as a restoration plant, adopts asexual reproduction or sexual reproduction to plant or transplant to the restoration area, and then Carry out maintenance to ensure growth in the coming year, thereby rebuilding and restoring the ecology of the sink-fluctuation zone and the riparian zone.
丹江口库区消落带在蓄水后将被季节性的淹没,一些地方水淹将达到6个月,其间10m水位落差,选择水位回落时耐干旱、耐土壤瘦瘠,水位回升后能耐长期淹没的两栖植物对消落带进行恢复极为重要。同时,丹江口库区消落带部分区域坡度陡、水流急、土壤贫瘠、立地条件差,直接种植,所需水分和肥分缺乏,坡面冲刷比较严重,植被生长困难,不易存活,需要采用实用有效的一些辅助措施。同时还要考虑到植被对来自库岸的水土流失以及农业面源污染的拦截和过滤功能,对其进行合适配置。综上所述,以上发明均不适合在该地区使用。The hydrofluctuation zone in the Danjiangkou Reservoir area will be submerged seasonally after impoundment, and some places will be flooded for 6 months, with a 10m water level drop during the period. The water level should be resistant to drought and poor soil when the water level drops, and can withstand long-term submersion after the water level rises. Amphibians are extremely important for restoration of the water-fluctuation zone. At the same time, part of the water-fluctuating zone in the Danjiangkou Reservoir area has steep slopes, rapid water flow, poor soil, and poor site conditions. Direct planting requires insufficient water and fertilizers, and serious slope erosion makes it difficult for vegetation to grow and survive. Some effective auxiliary measures. At the same time, the interception and filtering functions of vegetation on water and soil loss from reservoir banks and agricultural non-point source pollution should also be considered, and proper configuration should be made. In summary, none of the above inventions is suitable for use in this region.
发明内容Contents of the invention
本发明的目的是针对上述现状,旨在提供一种施工便捷、投入小、适用广、不易被水毁、效果好、可满足丹江口水库消落带地区进行有效水土保持、污染控制的水库消落带陡坡地区受损生态系统修复方法。The purpose of the present invention is to address the above-mentioned current situation, aiming to provide a reservoir fading that is convenient in construction, small in investment, wide in application, not easily destroyed by water, good in effect, and can meet the requirements of effective water and soil conservation and pollution control in the Danjiangkou Reservoir's fading zone. Restoration of damaged ecosystems in areas with steep slopes.
本发明目的的实现方式为,一种水库消落带陡坡地区受损生态系统修复方法,具体步骤如下:The way to achieve the object of the present invention is a method for restoring the damaged ecosystem in the steep slope area of the reservoir drawdown zone, the specific steps are as follows:
1)选择在蓄水水位最低时,对消落带迎水坡面进行修理平整,清理石块、杂草、垃圾,并进行适当的人工夯实;1) Choose to repair and level the facing slope of the water-fluctuation zone when the storage water level is the lowest, clean up stones, weeds, garbage, and perform appropriate manual compaction;
2)消落带外坡面顶部采用鱼鳞坑整地方式开挖种植穴,种植穴内种植马尾松或其他适宜树种;2) Excavate planting holes at the top of the outer slope of the water-fluctuation zone by means of fish-scale pit preparation, and plant masson pine or other suitable tree species in the planting holes;
3)在消落深度2m以内区域,采用沿水平等高线带状整地方式开挖种植槽,在消落深度2-10m之间区域采用穴状、鱼鳞坑整地方式开挖种植穴,在种植穴外区域采用切茎撤压法种植狗牙根;3) In the area within 2m of sinking depth, excavate planting troughs along the horizontal contour strip-shaped soil preparation method, and excavate planting holes in the area of sinking depth 2-10m in the form of pits and fish scale pits. The area outside the acupoint is planted with bermudagrass by cutting the stem and withdrawing pressure;
4)沿消落带迎水坡面铺设一层黄麻土工布,黄麻土工布的上端和下端均采用U形锚钉固定在土基中;4) Lay a layer of jute geotextile along the water-facing slope of the water-fluctuation zone, and the upper and lower ends of the jute geotextile are fixed in the soil foundation with U-shaped anchors;
5)在消落深度2m以内区域的种植槽内,消落深度2-10m之间区域的种植穴中移植香根草;5) Transplant vetiver in the planting grooves within the area of the water level within 2m, and in the planting hole of the area between the water level of 2-10m;
6)及时浇灌定根水;6) Timely irrigate fixed root water;
7)常规护理。7) Routine care.
本发明采用具有多功能生态效益的黄麻土工布进行坡面防护,黄麻土工布是由低等黄红麻原料和麻纺下脚料织成的一种可生物降解的开口网眼织物,是一种可快速控制坡面侵蚀的新型材料,在防止土壤侵蚀的同时给植物提供一种稳定的生长环境,促进植物在坡面的成活与生长发育。The present invention adopts the jute geotextile with multifunctional ecological benefits to protect the slope. The jute geotextile is a biodegradable open mesh fabric woven from low-grade jute raw materials and hemp spinning waste. A new type of material for controlling slope erosion can provide a stable growth environment for plants while preventing soil erosion, and promote the survival, growth and development of plants on slopes.
本发明在坡顶种植马尾松等适生树种,形成具有保持水土、涵养水源、改善水质等作用的多功能防护林;在消落带区域上端密植香根草,形成香根草植物篱带,可改善土壤肥力和土壤性质,有效地减少地表径流和土壤侵蚀;在消落带香根草植物篱带以下区域将香根草与狗牙根混合种植,充分利用香根草根系发达、护坡固土能力强的特点以及狗牙根匍匐茎和根茎快速扩展蔓延的特点,形成复合植被坡面恢复带。本发明的防护林带、植物篱带及复合植被坡面恢复带共同构成一个立体恢复空间,保证植物在消落带陡坡地区上生根恢复。通过大面积恢复植被,改善消落带的土壤肥力和土壤性质,有效地减少地表径流和土壤侵蚀,拦截、过滤农业面源污染,达到受损生态系统修复的目的。According to the invention, suitable tree species such as masson pine are planted on the top of the slope to form a multi-functional protective forest with the functions of maintaining water and soil, conserving water sources, and improving water quality; densely planting vetiver at the upper end of the water-fluctuating zone area to form a vetiver hedgerow, which can Improve soil fertility and soil properties, effectively reduce surface runoff and soil erosion; plant vetiver and bermudagrass in the area below the vetiver hedgerow in the water-fluctuation zone, and make full use of the well-developed root system of vetiver and its ability to protect slopes and soil The strong characteristics and the rapid expansion and spread of bermudagrass stolons and rhizomes form a composite vegetation slope restoration zone. The protection forest belt, the hedgerow belt and the composite vegetation slope restoration belt of the present invention together form a three-dimensional restoration space, which ensures that plants take root and restore on the steep slope area of the water-fluctuation zone. By restoring vegetation on a large scale, improving soil fertility and soil properties in water-fluctuating zones, effectively reducing surface runoff and soil erosion, intercepting and filtering agricultural non-point source pollution, and achieving the purpose of restoring damaged ecosystems.
本发明施工便捷、投入小、适用广、不易被水毁、效果好,适用于消落范围大、地势陡峭的水库消落带地区的水土保持和污染控制。The invention has the advantages of convenient construction, small investment, wide applicability, not easy to be destroyed by water, good effect, and is suitable for water and soil conservation and pollution control in reservoir water-fluctuation zone areas with large water-fluctuation range and steep terrain.
附图说明Description of drawings
图1是消落带坡面植被恢复结构正视图,Figure 1 is the front view of the vegetation restoration structure on the slope of the water-fluctuating zone.
图2是消落带坡面植被恢复结构侧视图。Fig. 2 is a side view of the vegetation restoration structure on the slope of the hydrofluctuation zone.
具体实施方式Detailed ways
本发明是针对丹江口水库消落带的陡坡地区,坡度较大、土壤贫瘠、立地条件差,特别是水库调蓄运行后,水位频繁和大幅度波动以及淹没时间过长,导致水库边缘植被容易遭受破坏且生长困难,进一步引起水土流失及污染加重问题,无法实现生态恢复的状况而发明的一种方法。The present invention is aimed at the steep slope area of the drawdown zone of the Danjiangkou Reservoir, where the slope is relatively large, the soil is barren, and the site conditions are poor. Especially after the reservoir is adjusted and stored, the water level fluctuates frequently and greatly and the submerged time is too long, which makes the vegetation on the edge of the reservoir vulnerable to damage. It is a method invented for the situation that it is destroyed and difficult to grow, further causing soil erosion and pollution aggravation, and unable to achieve ecological restoration.
下面参照图1、2,以丹江口水库消落带陡坡地区为实施例详述本发明。Referring to Fig. 1, 2 below, the present invention is described in detail with the steep slope area of the water-fluctuating zone of Danjiangkou Reservoir as an example.
消落带陡坡地区受损生态系统修复的具体步骤如下:The specific steps to restore the damaged ecosystem in the steep slope area of the water-fluctuation zone are as follows:
1)对丹江口水库蓄水水位最低时为5月,故选择在5月,对消落带迎水坡面进行修理平整,清理石块、杂草、垃圾,并进行适当的人工夯实。图中,下线即为夏汛限制水位线8,上线即为正常蓄水位线9。1) The water level of Danjiangkou Reservoir is the lowest in May, so May is chosen to repair and level the facing slope of the water-fluctuation zone, clean up stones, weeds, and garbage, and perform appropriate manual compaction. In the figure, the lower line is the summer flood
2)在消落区外坡面顶部,即水位170m以上区域,采用鱼鳞坑整地方式开挖种植穴。消落区外坡面顶部的种植穴,穴宽50-80cm、穴长70-100cm、穴深40-60cm、穴距200-300cm。开挖种植穴时,表土堆放在穴的上方,熟土堆放在穴的下方,捡出的石块在穴的下沿垒成一个堰,堰高20-25cm,在穴的上方左右两角各斜开一道引蓄雨水的小沟。种植穴内种植马尾松2或其他适宜树种,栽植时要分级栽植,不窝根,不吊空,根系舒展,扶正苗木,踩实捶紧。马尾松2或其他适宜树种在坡顶形成具有保持水土、涵养水源、改善水质等作用的多功能防护林带1。2) On the top of the outer slope of the water-fluctuation area, that is, the area above the water level of 170m, excavate planting holes by means of fish-scale pit preparation. The planting holes on the top of the outer slope of the sinking area are 50-80cm wide, 70-100cm long, 40-60cm deep, and 200-300cm apart. When excavating the planting hole, the topsoil is piled above the hole, the mellow soil is piled under the hole, and the picked stones are built on the lower edge of the hole to form a weir with a height of 20-25cm. Dig a small ditch to divert and store rainwater.
3)在消落深度2m以内区域,采用沿水平等高线带状整地方式开挖种植槽,种植槽宽20-25cm、行距40-60cm、深为20-30cm。消落深度2-10m之间区域采用穴状、鱼鳞坑整地方式开挖种植穴,种植穴为“V”状,穴距30-40cm、穴行距80-100cm、穴深20-30cm。3) In the area within 2m of the water level depth, the planting grooves are excavated along the horizontal contour strips. The width of the planting grooves is 20-25cm, the row spacing is 40-60cm, and the depth is 20-30cm. The area between the sinking depth of 2-10m adopts the method of pit-like and fish-scale pit preparation to excavate the planting holes. The planting holes are "V" shaped, the hole spacing is 30-40cm, the hole spacing is 80-100cm, and the hole depth is 20-30cm.
在种植穴外区域采用切茎撤压法种植狗牙根5。种植方法是,将狗牙根5的匍匐茎和根茎切成6-10cm的小段,混土撒于该区域内,及时镇压,使其与土壤接触。Bermudagrass was planted in the area outside the planting hole by cutting the stem and withdrawing pressure5. The planting method is to cut the stolons and rhizomes of
因狗牙根5覆盖性强,耐践踏,故布设黄麻土工布6及种植香根草3对其生长不会有太大的影响。Because
4)沿消落带迎水坡面铺设一层黄麻土工布6,黄麻土工布6是由低等黄红麻原料和麻纺下脚料织成的一种可生物降解的开口网眼织物,规格为:重量不低于200g/km2,经纬密度:每10cm×10cm为4-6根。黄麻土工布6的上端和下端均采用U形锚钉固定在土基中,使黄麻土工布6格网张拉紧,U形锚钉的间距不大于2m,相邻黄麻土工布的搭接长度不小于15cm,叠加处用可降解无害材料呈之字形穿绑。4) Lay one deck of
本发明采用黄麻土工布6进行坡面防护,黄麻土工布6是一种可快速控制坡面侵蚀的新型材料,在国际水土保持领域,它被誉为“土壤抢救物”和“防流失物”。其在调温、保湿、有益于植物生长方面的优点为人工合成材料制成的土工布所无法比拟。原因在于:The present invention adopts
黄麻土工布可灵活地覆盖并附着于土壤表面,有效地减小雨滴溅蚀,拦截坡面水流,控制土粒移动,从而有效地控制水土流失;黄麻纤维吸水性强,自然纤维结构使之在一定程度上改变了土壤孔隙结构,增加了土壤吸水能力,再加上其网状结构还能阻挡雨水,促进水分向土壤渗透,提高土壤的导水率,从而具有调节土壤温度,改善土壤湿度等生态微环境的特性,为植物提供较好的生长环境,从而促进植物发芽出苗、栽植成活及生长发育,提高出苗率、成活率,并且对地上部与地下部的生长都有明显促进作用。随使用时间的延长,黄麻土工布逐渐降解,并可改良培肥土壤,对于需要以植物作为长期护坡措施的坡面具有很好的生态效益。Jute geotextiles can flexibly cover and attach to the soil surface, effectively reduce raindrop splash erosion, intercept slope water flow, control soil particle movement, and effectively control soil erosion; jute fiber has strong water absorption and natural fiber structure. To a certain extent, it changes the soil pore structure, increases the water absorption capacity of the soil, and its mesh structure can also block rainwater, promote water penetration into the soil, and improve the hydraulic conductivity of the soil, thereby regulating soil temperature and improving soil humidity. The characteristics of the ecological microenvironment provide plants with a better growth environment, thereby promoting plant germination, planting survival, growth and development, increasing the rate of emergence and survival, and significantly promoting the growth of aboveground and underground parts. With the prolongation of the use time, the jute geotextile will gradually degrade and can improve the soil. It has good ecological benefits for slopes that need plants as long-term slope protection measures.
再加上其有独特的网眼结构。网眼结构能使植物有足够的生长空间,并可固定种子,使幼苗免受风雨袭击;组成网眼的每一根线绳都像一个微型水库,能够吸收和积蓄雨水,在干旱时能减缓水分蒸发。Plus it has a unique mesh structure. The mesh structure allows plants to have enough space to grow, and can fix the seeds to protect the seedlings from wind and rain; each thread that makes up the mesh is like a miniature reservoir, which can absorb and store rainwater and slow down water evaporation during drought .
总之,采用黄麻土工布6可使坡面流水流速变慢,推迟初始产流时间,增加土壤渗水量,减少径流量;覆盖地表,增加地面覆盖度,减少溅蚀,阻挡和减少水流、抬高浸湿基准面、降低坡面流速,防止沟蚀产生,保土效益高。In short, the use of
5)在消落深度2m以内区域的种植槽内移植香根草3,消落深度2-10m之间区域的种植穴中移植香根草3。在种植槽和种植穴内按丛种植,每丛种植3-4株。种植前,将香根草3地上部分剪至25-35cm,根系剪至5-15cm,种植时将植株斜靠在一侧,植株与地面保持60°-45°的角度,从另一侧覆土压实。种植槽内的丛距20-30cm。5)
在消落深度2m以内区域的种植槽内移植香根草3,构成香根草植物篱带4。
香根草3是一种两栖植物,具有极强生态适应性的抗逆(旱、湿、寒、热、酸、碱)能力,能抵抗长期干旱或渍水;对土壤的要求很低,光合能力强,生长快,易种植、易成活、易管理、极少传播病虫害。其根呈网状,根系纵深发达,可深达2-3m,甚至5m,能较牢固的固持土壤,而且根系的抗张力十分强大,是同等直径软钢的1/6。茎叶部分在长期淹水的情况下亦能存活。香根草植物篱带4可改善土壤肥力和土壤性质,有效地减少地表径流和土壤侵蚀,可把径流中的泥沙拦积在草篱之前,并有效地减少地表径流。
消落深度2-10m之间区域种植穴中移植香根草3,上下行香根草3纵向错开,成“品”字型种植。
在消落深度2-10m之间区域,本发明将香根草与狗牙根混合种植,充分利用香根草3根系发达、护坡固土能力强的特点以及狗牙根5匍匐茎和根茎快速扩展蔓延、覆盖性强,耐践踏的特点,建立起一个复合植被恢复带7,其与多功能防护林带1和香根草植物篱带4共同构成一个立体恢复空间,保证其在消落带陡坡上生根恢复,大面积恢复植被,实现生态修复,有效地控制水土流失,对水库起到一定的保护作用。In the area between 2-10m depth of water fall, the present invention mixes vetiver and bermudagrass to plant, fully utilizes the characteristics of
6)植物种植后及时浇灌定根水。6) Water the fixed root water in time after planting.
7)常规护理。7) Routine care.
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CN114508073A (en) * | 2022-03-17 | 2022-05-17 | 中电建华东勘测设计研究院(郑州)有限公司 | Fluctuation zone structure of a reservoir |
CN117502070A (en) * | 2023-11-30 | 2024-02-06 | 广东柏辉生态环境建设有限公司 | A method of restoring forestry ecological environment |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1990959A (en) * | 2005-12-27 | 2007-07-04 | 胡孟春 | Hydro-fluctuation belt grass vegetation constructing method |
CN101218873A (en) * | 2008-01-22 | 2008-07-16 | 同济大学 | Method of Restoring Damaged Ecosystem in Fluctuation Zone and Riparian Zone of Reservoir with Bermudagrass |
CN101580305A (en) * | 2009-06-04 | 2009-11-18 | 中国水电顾问集团华东勘测设计研究院 | Wetland governance method for improving ecological environmental in reservoir falling zone |
-
2010
- 2010-01-29 CN CN2010101027304A patent/CN101790931B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1990959A (en) * | 2005-12-27 | 2007-07-04 | 胡孟春 | Hydro-fluctuation belt grass vegetation constructing method |
CN101218873A (en) * | 2008-01-22 | 2008-07-16 | 同济大学 | Method of Restoring Damaged Ecosystem in Fluctuation Zone and Riparian Zone of Reservoir with Bermudagrass |
CN101580305A (en) * | 2009-06-04 | 2009-11-18 | 中国水电顾问集团华东勘测设计研究院 | Wetland governance method for improving ecological environmental in reservoir falling zone |
Non-Patent Citations (2)
Title |
---|
戴方喜等.对三峡水库消落区生态系统与其生态修复的思考.《中国水土保持》.2006,(第12期),6-7. * |
程龙飞,易忠玖.绿维护岸结构在三峡库岸消落带的应用研究.《自主创新与持续增长第十一届中国科协年会论文集(1)》.2009,580-584. * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
RU2787050C1 (en) * | 2022-01-10 | 2022-12-28 | Федеральное государственное бюджетное научное учреждение "Курский федеральный аграрный научный центр" | Method for creating a water-regulating forest strip on a slope |
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