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CN105230412A - Biological-physical control method for spartina alterniflora - Google Patents

Biological-physical control method for spartina alterniflora Download PDF

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CN105230412A
CN105230412A CN201510782852.5A CN201510782852A CN105230412A CN 105230412 A CN105230412 A CN 105230412A CN 201510782852 A CN201510782852 A CN 201510782852A CN 105230412 A CN105230412 A CN 105230412A
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spartina alterniflora
sunshade net
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physical
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CN105230412B (en
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沈浩
李婷
黄立新
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Research Center for Eco Environmental Sciences of CAS
South China Botanical Garden of CAS
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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
    • A01G13/00Protection of plants
    • A01G13/30Ground coverings
    • A01G13/32Mats; Nets; Sheets or films
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01MCATCHING, TRAPPING OR SCARING OF ANIMALS; APPARATUS FOR THE DESTRUCTION OF NOXIOUS ANIMALS OR NOXIOUS PLANTS
    • A01M99/00Subject matter not provided for in other groups of this subclass

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  • Insects & Arthropods (AREA)
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Abstract

本发明公开了一种互花米草生物-物理控制方法。本发明方法包括以下步骤:a、物理遮盖阶段:将塑料遮阳网遮盖并固定在有互花米草生长的滩涂上,待互花米草生长受抑制、地上生物量降低45%以上后,进入下一阶段;b、生物替代阶段:在塑料遮阳网上开孔种植无瓣海桑、秋茄、桐花、老鼠簕和卤蕨幼苗,封滩养护。本发明在物理覆盖手段的基础上引入生物替代技术实现对互花米草长久有效的综合治理,具有操作简单,成本低廉的优点,并且能实现真正意义上的“退草还林”。

The invention discloses a bio-physical control method of Spartina alterniflora. The method of the present invention comprises the following steps: a, physical covering stage: cover and fix the plastic sunshade net on the beach where Spartina alterniflora grows, and enter The next stage; b. Bio-substitution stage: Open holes on the plastic sunshade net to plant the seedlings of Sonnensis apetalum, Candela, Tung Flower, Mouse Bougainvillea and Brine Fern, and seal the beach for maintenance. The present invention introduces biological substitution technology on the basis of physical covering means to realize long-term and effective comprehensive management of Spartina alterniflora, has the advantages of simple operation and low cost, and can realize "returning grass to forest" in the true sense.

Description

一种互花米草生物-物理控制方法A kind of bio-physical control method of Spartina alterniflora

技术领域technical field

本发明属于生态环境保护技术领域,具体涉及一种互花米草生物-物理控制方法。The invention belongs to the technical field of ecological environment protection, and in particular relates to a bio-physical control method of Spartina alterniflora.

背景技术Background technique

互花米草(SpartinaalternifloraLoisel)为禾本科米草属多年生草本植物。自我国1979年引进以来生长、传播、蔓延,已经对沿海及全国各地的农牧渔产业及海岸带红树林生态环境造成了极大地破坏(王卿等,2006)。互花米草被世界公认为外来恶性杂草之一,也被我国列入首批16种外来入侵物种名录,并对其蔓延趋势进行监控(中科院和环保总局,2003)。目前国内外对互花米草的控制主要有物理控制、化学控制、生物防治和生物替代等方法(Hedgeetal.,2003)。物理控制主要采用人工拔除幼苗、织物或薄膜覆盖、连续刈割拔除、水淹、火烧和碾埋等。这类的物理控制效果明显,但人工及机械清除效率较低,成本也较高,往往需要定期重复治理,难以实现对互花米草的持续控制。覆盖法是物理方法种较常用的一种,即用致密的丝织布或塑料膜紧密地覆盖住互花米草斑块,连续覆盖一到两个生长季,该法对于控制小斑块的互花米草较为有效(DeniseandSanger,2004)。现有对互花米草的覆盖处理的研究表明:覆盖时间越长互花米草的死亡率越高,通常在覆盖8-10周后地面部分互花米草死亡率可达到100%(李贺鹏,2007)。化学控制是指采用有效的除草剂来进行防除。利用化学除草剂控制互花米草存在着一定的局限性,互花米草生长在海岸潮间带,滩涂周期性地被海水淹没,容易造成除草剂的散失,且常用除草剂通常只能清除地表以上部分,难以控制根系的生长和蔓延;除草剂通常具有一定的毒性,可能会对周围生态系统和人类健康造成一定的负面影响。生物替代技术是根据植物群落演替的自身规律,利用有本地植物取代外来入侵植物的一种生态学防治技术。中国科学院热带雨林研究所曾经于1999年在珠海淇澳岛引种无瓣海桑进行替代互花米草的实验,无瓣海桑由于生长速度快,种植1年后即可郁闭成林,成功替代互花米草(唐国玲等,2007)。无瓣海桑虽然可有效控制互花米草,但是大量栽植后造成华南沿海形成大面积无瓣海桑人工纯林,该林分结构单一,容易遭到病虫害;同时无瓣海桑属外来物种,无瓣海桑的大面积种植不利于乡土树种的生长,和本地红树林生态系统的恢复。Spartina alterniflora Loisel is a perennial herb of the genus Spartina alterniflora. Since the introduction in my country in 1979, the growth, spread and spread have caused great damage to the coastal and national agriculture, animal husbandry and fishery industries and the ecological environment of coastal mangroves (Wang Qing et al., 2006). Spartina alterniflora is recognized as one of the exotic weeds in the world, and it has also been included in the list of the first 16 invasive alien species in my country, and its spreading trend is monitored (Chinese Academy of Sciences and State Environmental Protection Administration, 2003). At present, the control of Spartina alterniflora at home and abroad mainly includes physical control, chemical control, biological control and biological substitution (Hedge et al., 2003). Physical control mainly adopts manual pulling out of seedlings, fabric or film covering, continuous cutting and pulling out, flooding, burning and crushing. This type of physical control has obvious effects, but the efficiency of manual and mechanical removal is low, and the cost is also high. Regular repeated treatments are often required, making it difficult to achieve continuous control of Spartina alterniflora. The mulching method is a more commonly used physical method, that is, densely woven silk cloth or plastic film is used to cover the patch of Spartina alterniflora tightly for one to two growing seasons. Spartina alterniflora is more effective (Denise and Sanger, 2004). Existing research on the mulching treatment of Spartina alterniflora shows that the longer the mulching time, the higher the mortality rate of Spartina alterniflora, and usually the mortality rate of Spartina alterniflora on the ground can reach 100% after covering 8-10 weeks (Li Hepeng , 2007). Chemical control refers to the use of effective herbicides for control. There are certain limitations in the use of chemical herbicides to control Spartina alterniflora. Spartina alterniflora grows in the coastal intertidal zone, and tidal flats are periodically flooded by seawater, which easily causes the loss of herbicides, and commonly used herbicides can only be removed Above the surface, it is difficult to control the growth and spread of the root system; herbicides are usually toxic to a certain extent, and may cause certain negative effects on the surrounding ecosystem and human health. Bio-replacement technology is an ecological control technology that uses native plants to replace invasive plants according to the law of plant community succession. The Institute of Tropical Rainforest of the Chinese Academy of Sciences once introduced S. apetalum in Qi’ao Island, Zhuhai in 1999 to replace Spartina alterniflora. Due to its fast growth, S. apetalum can be closed and formed into a forest after one year of planting. It was successful. Alternative to Spartina alterniflora (Tang Guoling et al., 2007). Although S. apetalum can effectively control Spartina alterniflora, large-scale plantation of S. apetalum has resulted in the formation of a large area of artificial pure forest of S. apetalum in the coastal areas of South China. The forest stand has a single structure and is easily attacked by diseases and insect pests. At the same time, S. apetalum is an alien species. , the large-scale planting of S. apetalum is not conducive to the growth of native tree species and the restoration of the local mangrove ecosystem.

在现有的互花米控制技术中,物理防治方法能在短时间内实现互花米草的清除,故在互花米草防治工作中占据重要地位,但需耗费大量劳动力,成本较高,且不能彻底根除互花米草的入侵。过去的覆盖手段中缺乏对地面部分互花米草枯死后的后续防治。生物竞争或生物替代法可以通过替代物种的生长对互花米草的生长造成持续有效的抑制,彻底根除互花米草,但替代物种的选择有较大的局限性,且周期较长。In the existing control technology of Spartina alterniflora, the physical control method can realize the removal of Spartina alterniflora in a short time, so it occupies an important position in the prevention and control of Spartina alterniflora, but it needs a lot of labor and the cost is high. And the invasion of Spartina alterniflora cannot be completely eradicated. In the past, the mulching methods lacked the follow-up control of the dead Spartina alterniflora on the ground. Biological competition or biological substitution can continuously and effectively inhibit the growth of Spartina alterniflora through the growth of substitute species, and completely eradicate Spartina alterniflora, but the selection of substitute species has great limitations and a long period.

发明内容Contents of the invention

本发明针对现有技术的不足,提供一种操作简单,成本相对低廉,并能彻底根除互花米草入侵的互花米草生物-物理控制方法,这种方法适宜在受互花米草入侵胁迫的红树林滩涂大面积推广。Aiming at the deficiencies of the prior art, the present invention provides a bio-physical control method of Spartina alterniflora that is simple in operation, relatively low in cost, and can completely eradicate the invasion of Spartina alterniflora. Threatening the spread of mangrove tidal flats.

本发明的互花米草生物-物理控制方法,包括以下步骤:Spartina alterniflora bio-physical control method of the present invention comprises the following steps:

a.物理遮盖阶段:将遮阳网遮盖并固定在有互花米草生长的滩涂上,待互花米草生长受抑制、地上生物量降低45%以上后,进入下一阶段;a. Physical covering stage: Cover and fix the sunshade net on the tidal flat where Spartina alterniflora grows, and enter the next stage after the growth of Spartina alterniflora is inhibited and the aboveground biomass is reduced by more than 45%;

b.生物替代阶段:在遮阳网上开孔,在孔相对应位置挖种植穴,然后在种植穴内种植无瓣海桑、秋茄、桐花、老鼠簕和卤蕨幼苗,封滩养护。b. Bio-replacement stage: Open holes on the sunshade net, dig planting holes at the corresponding positions of the holes, and then plant the seedlings of sea mulberry, candela, tung flower, mouse bougainvillea and halofern in the planting holes, and seal the beach for maintenance.

优选,所述的遮阳网为透光率为10%的黑色塑料遮阳网。Preferably, the sunshade net is a black plastic sunshade net with a light transmittance of 10%.

优选,所述的遮阳网遮盖时间为每年的6-9月;更优选的,为每年的7-8月;互花米草的一个生长季一般为6-9月,其中7-8月为互花米草生长最旺盛时期,在这一时期进行遮阴覆盖可缩短遮阴时间,取得同等的控制效果。Preferably, the shade net covering time is June-September every year; more preferably, July-August every year; a growing season of Spartina alterniflora is generally June-September, wherein July-August is During the most vigorous growth period of Spartina alterniflora, shading and covering during this period can shorten the shading time and achieve the same control effect.

优选,所述的种植穴的间距为1.5-2m。Preferably, the distance between the planting holes is 1.5-2m.

优选,所述的无瓣海桑、秋茄、桐花、老鼠簕和卤蕨幼苗为生长1-2年、茎高1-1.5m的幼苗。Preferably, the seedlings of Sangria apetalum, candela, tung flower, mouse bougainvillea and brine fern are 1-2 years old and have a stem height of 1-1.5m.

优选,封滩养护为封滩2年以上,及时补植,适时施肥和防治病虫害。Preferably, the beach sealing maintenance is more than 2 years, timely replanting, timely fertilization and prevention and control of diseases and insect pests.

本发明通过结合物理覆盖技术和生物替代手段彻底根除互花米草。研究表明光照条件对互花米草的生长具有很大影响,不同遮荫强度下互花米草的生长状况、光合能力及生物量等均存在显著差别,遮荫对互花米草的生长具有显著的抑制作用。通过物理覆盖虽然能控制互花米草生长,但往往只能在短时间内有成效,且影响自然景观,一旦覆盖物破损或摘除互花米草就会重新生长起来。本控制方法分为物理遮盖和生物替代两个阶段。阶段一,即物理遮盖期,将塑料遮阳网遮盖在有互花米草生长的滩涂上,遮盖期约为60天,使互花米草生长受到一定程度的抑制(地上生物量降低45%以上);阶段二,即生物替代期,在塑料遮阳网上开孔,挖种植穴,并在种植穴内种植无瓣海桑、桐花、老鼠簕和卤蕨等速生红树植物,进一步与互花米草竞争光资源并占据其生存空间,无瓣海桑是速生乔木,树高一般可达15-20m,一旦形成郁闭的林冠便可实现对互花米草的自然遮蔽,桐花、老鼠簕、卤蕨等乡土红树植物耐阴性较强,适宜在无瓣海桑林下生长。本发明在物理覆盖手段的基础上引入生物替代技术实现对互花米草长久有效的综合治理。本发明采用遮阳网而非不透气的塑料薄膜覆盖,无须预先对互花米草进行人工清除,且具有通透性,不会影响土壤生态环境和底栖生物的生长繁殖。The invention completely eradicates Spartina alterniflora by combining physical covering technology and biological alternative means. Studies have shown that light conditions have a great influence on the growth of Spartina alterniflora. There are significant differences in the growth status, photosynthetic capacity and biomass of Spartina alterniflora under different shading intensities. Shading has a significant effect on the growth of Spartina alterniflora. Significant inhibitory effect. Although the growth of Spartina alterniflora can be controlled by physical covering, it is often effective only in a short period of time and affects the natural landscape. Once the covering is damaged or removed, Spartina alterniflora will re-grow. This control method is divided into two stages of physical covering and biological substitution. Phase one, namely the physical covering period, covered the tidal flats with Spartina alterniflora growth with plastic sunshade nets, and the covering period was about 60 days, so that the growth of Spartina alterniflora was inhibited to a certain extent (aboveground biomass was reduced by more than 45%) ); stage two, namely the bio-replacement period, opening holes on plastic sunshade nets, digging planting holes, and planting fast-growing mangrove plants such as Apetalum sinensis, Tung flower, mouse bougainvillea and halofern, etc. Grass competes for light resources and occupies its living space. Sonnensis apetalum is a fast-growing tree, and the height of the tree can generally reach 15-20m. Once a canopy is formed, it can naturally shade Spartina alterniflora. Native mangrove plants such as mulberry and halofern have strong shade tolerance and are suitable for growing under sea mulberry forests. The invention introduces biological substitution technology on the basis of physical covering means to realize long-term and effective comprehensive management of Spartina alterniflora. The invention adopts a sunshade net instead of an airtight plastic film to cover, does not need to manually remove the Spartina alterniflora in advance, has permeability, and will not affect the soil ecological environment and the growth and reproduction of benthic organisms.

与现有技术相比,本发明的优点主要有:(1)通过不同透光率塑料遮阳网覆盖下互花米草生理生态和生长适应等指标的比较研究,确定互花米草致死的临界光强,以最低覆盖密度实现较低的投入产出比;(2)本技术无须对互花米草进行拔除或翻耕等物理操作,减小劳动力投入;(3)结合竞争替代的生物手段实现互花米草的彻底清除,实现真正意义上的“退草还林”。Compared with the prior art, the advantages of the present invention mainly include: (1) Through the comparative study of indicators such as the physiological ecology and growth adaptation of Spartina alterniflora under the coverage of plastic sunshade nets with different light transmittances, the lethal criticality of Spartina alterniflora is determined. Light intensity, with the lowest coverage density to achieve a lower input-output ratio; (2) This technology does not require physical operations such as pulling out or plowing Spartina alterniflora, reducing labor input; (3) Combining biological means of competition and substitution Realize the complete eradication of Spartina alterniflora, and realize the true sense of "returning grass to forest".

附图说明Description of drawings

图1是盆栽实验中不同遮阴条件下互花米草生长情况。Figure 1 shows the growth of Spartina alterniflora under different shading conditions in pot experiments.

图2是遮阴60天后每平方米互花米草的生长量。Figure 2 shows the growth of Spartina alterniflora per square meter after shading for 60 days.

图3是遮盖前的生长旺盛的互花米草。Figure 3 is the vigorous growth of Spartina alterniflora before covering.

图4是黑色塑料遮阳网遮盖并固定在互花米草生长旺盛的滩涂上。Figure 4 is a black plastic sunshade net covered and fixed on the tidal flat where Spartina alterniflora grows vigorously.

图5是封滩养护2年后红树群落替代互花米草效果。Figure 5 shows the effect of replacing Spartina alterniflora with mangrove communities after 2 years of beach sealing and maintenance.

具体实施方式detailed description

以下实施例是对本发明的进一步说明,而不是对本发明的限制。The following examples are to further illustrate the present invention, rather than limit the present invention.

实施例1Example 1

实施样地在广东珠海淇澳岛红树林自然保护区内,互花米草面积约300平方米。The implementation sample site is in the mangrove nature reserve of Qi'ao Island, Zhuhai, Guangdong, and the area of Spartina alterniflora is about 300 square meters.

1.预实验:选择遮阳网最佳透光率1. Pre-experiment: choose the best light transmittance of the sunshade net

互花米草遮阴盆栽实验:用不同透光度的黑色塑料遮阳网设置4种遮荫处理,其透光率分别为100%(无遮荫)、45%、30%和10%,其中后3个遮荫处理设在高2.5m铁架罩黑色尼龙网形成的遮荫棚内。将茎长10cm左右的互花米草幼苗种植于4种不同光照条件下,栽培基质为取自珠海淇澳岛的海泥,遮阴半年后对比各处理下互花米草的生长情况,结果表明10%透光率的遮阳网对互花米草生长的抑制效果最好(图1)。在透光率为100%(无遮荫)、45%和30%的情况下,互花米草均能保持一定的生长速率,且能正常开花结穗,遮阴的抑制效果并不显著(图1)。为达到良好的处理效果和较低的投入成本,采用透光率为10%的塑料遮阳网作为覆盖材料。Shading experiment of Spartina alterniflora shading potted plants: 4 kinds of shading treatments were set up with black plastic sunshade nets with different light transmittance, and the light transmittances were 100% (no shade), 45%, 30% and 10%, respectively. The last three shading treatments are located in a shade shed formed by a 2.5m high iron frame covered with a black nylon net. Spartina alterniflora seedlings with a stem length of about 10 cm were planted under four different light conditions, and the cultivation substrate was sea mud from Qi’ao Island, Zhuhai. After half a year of shading, the growth of Spartina alterniflora under each treatment was compared, and the results were It showed that the sunshade net with 10% light transmittance had the best inhibitory effect on the growth of Spartina alterniflora (Fig. 1). Under the conditions of light transmittance of 100% (no shading), 45% and 30%, Spartina alterniflora can maintain a certain growth rate, and can flower and set ears normally, and the inhibitory effect of shading is not significant ( figure 1). In order to achieve a good treatment effect and lower input costs, plastic sunshade nets with a light transmittance of 10% are used as covering materials.

2.遮阳网覆盖互花米草2. Shade net covered with Spartina alterniflora

将透光率为10%的黑色塑料遮阳网平铺于互花米草生长旺盛的滩涂上(图3和图4所示),遮阳网面积根据互花米草实际生长范围而定,此实施例中,遮阳网面积为10m*30m。遮阳网边缘每隔5m固定一根绳索,绳索另一端则用木桩固定于滩涂表面,使遮阳网尽可能与滩面接近,以压缩互花米草生长空间同时便于红树苗木的栽种。遮阴时间为2015年6月30日—2015年8月30日。Spread black plastic sunshade nets with a light transmittance of 10% on the tidal flats where Spartina alterniflora grows vigorously (as shown in Figures 3 and 4). The area of the sunshade nets is determined according to the actual growth range of Spartina alterniflora. In the example, the area of the sunshade net is 10m*30m. A rope is fixed every 5m on the edge of the sunshade net, and the other end of the rope is fixed on the tidal flat surface with wooden stakes, so that the sunshade net is as close as possible to the beach surface, so as to compress the growth space of Spartina alterniflora and facilitate the planting of mangrove seedlings. The shade time is from June 30, 2015 to August 30, 2015.

3.栽种红树苗木3. Planting mangrove seedlings

遮阳网覆盖2个月后,互花米草地上生物量下降46%(图2),这时进行第二阶段的红树苗木栽种,在遮阳网上按照一定的间隔(1.5-2m,可根据苗木种类和种植的适宜间距而定)剪出直径为0.3m孔,在孔相对应处的滩涂上挖出种植穴(穴规格为直径30cm,深40cm),在种植穴中种植无瓣海桑、秋茄、桐花树、老鼠簕和卤蕨等红树植物,都选用生长1-2年,茎高1-1.5m的幼苗。将无瓣海桑与耐阴性较强的桐花树和老鼠簕、卤蕨混合种植可使红树群落配置更优,对互花米草的抑制效果更佳。After 2 months of covering with the shade net, the biomass of S. alterniflora decreased by 46% (Fig. 2). The type and the suitable spacing for planting are determined) to cut out a hole with a diameter of 0.3m, dig out a planting hole on the tidal flat corresponding to the hole (the size of the hole is 30cm in diameter, 40cm in depth), and plant sea mulberry, Mangrove plants such as candela, tung flower tree, mouse bougainvillea and halogen fern all use seedlings that have grown for 1-2 years and have a stem height of 1-1.5m. The mixed planting of S. apetalum with strong shade-tolerant tung flower, agaricus, and halofern can make the mangrove community configuration better, and the inhibitory effect on Spartina alterniflora is better.

4.栽后管理4. Management after planting

红树种植以后需要加强管护:1)封滩2年以上,并且要专人管护,防止人类和动物践踏;2)要防治病虫害;3)要及时补植,适时施肥,确保造林成效,最终实现以本土红树林竞争替代互花米草,恢复受损红树林群落。After mangrove planting, management and protection need to be strengthened: 1) The beach should be closed for more than 2 years, and special personnel should be managed and protected to prevent human and animal trampling; 2) Diseases and insect pests should be prevented; 3) Timely replanting and timely fertilization should be carried out to ensure the effectiveness of afforestation. Realize the replacement of Spartina alterniflora with native mangroves and restore damaged mangrove communities.

5.实施效果5. Implementation effect

本技术已在珠海淇澳红树林自然保护区试验地取得了良好的实施效果(图5所示),红树群落替代互花米草以初见成效,互花米草清除率80%以上,红树林造林成活率80%以上。适合进行更大范围的推广。This technology has achieved good implementation results in the test site of Zhuhai Qi'ao Mangrove Nature Reserve (as shown in Figure 5). The mangrove community has replaced Spartina alterniflora to achieve initial results. The removal rate of Spartina alterniflora is over 80%. The survival rate of mangrove afforestation is over 80%. Suitable for wider promotion.

Claims (7)

1.一种互花米草生物-物理控制方法,其特征在于,包括以下步骤:1. a kind of Spartina alterniflora bio-physical control method, is characterized in that, comprises the following steps: a.物理遮盖阶段:将遮阳网遮盖并固定在有互花米草生长的滩涂上,待互花米草生长受抑制、地上生物量降低45%以上后,进入下一阶段;a. Physical covering stage: Cover and fix the sunshade net on the tidal flat where Spartina alterniflora grows, and enter the next stage after the growth of Spartina alterniflora is inhibited and the aboveground biomass is reduced by more than 45%; b.生物替代阶段:在遮阳网上开孔,在孔相对应位置挖种植穴,然后在种植穴内种植无瓣海桑、秋茄、桐花、老鼠簕和卤蕨幼苗,封滩养护。b. Bio-replacement stage: Open holes on the sunshade net, dig planting holes at the corresponding positions of the holes, and then plant the seedlings of sea mulberry, candela, tung flower, mouse bougainvillea and halofern in the planting holes, and seal the beach for maintenance. 2.根据权利要求1所述的方法,其特征在于,所述的遮阳网为透光率为10%的黑色塑料遮阳网。2. The method according to claim 1, wherein said sunshade net is a black plastic sunshade net with a light transmittance of 10%. 3.根据权利要求1所述的方法,其特征在于,所述的遮阳网遮盖时间为每年的6-9月。3. The method according to claim 1, characterized in that, the covering time of the sunshade net is June-September every year. 4.根据权利要求1所述的方法,其特征在于,所述的遮阳网遮盖时间为每年的7-8月。4. The method according to claim 1, characterized in that, the covering time of the sunshade net is July-August every year. 5.根据权利要求1所述的方法,其特征在于,所述的种植穴的间距为1.5-2m。5. The method according to claim 1, characterized in that the distance between the planting holes is 1.5-2m. 6.根据权利要求1所述的方法,其特征在于,所述的无瓣海桑、秋茄、桐花、老鼠簕和卤蕨幼苗为生长1-2年、茎高1-1.5m的幼苗。6 . The method according to claim 1 , characterized in that, the seedlings of Sangria apetalum , Candela , Tung Flower , Mouse Bougainvillea , and Brine Fern are 1-2 years old and have a stem height of 1-1.5m. 7.根据权利要求1所述的方法,其特征在于,所述的封滩养护为封滩2年以上,及时补植,适时施肥和防治病虫害。7. The method according to claim 1, characterized in that, the maintenance of the beach sealing is more than 2 years, timely replanting, timely fertilization and prevention and control of diseases and insect pests.
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CN108293534A (en) * 2018-01-18 2018-07-20 华南农业大学 A kind of black careless method of net covering control that do not absorb water of the permeable fertilizer of energy
CN108293353A (en) * 2018-03-15 2018-07-20 钱咏梅 A kind of ecological effective technology making mutual spartina natural death
CN110073932A (en) * 2019-05-27 2019-08-02 遵义衡中中药材科技开发有限公司 One kind covering web, high efficiency planting technology method
CN111328493A (en) * 2020-04-27 2020-06-26 广东湛江红树林国家级自然保护区管理局 A method of removing Spartina alterniflora
CN111418466A (en) * 2020-05-09 2020-07-17 贵州省植物园 Efficient bletilla striata weeding method
CN112673875A (en) * 2020-12-29 2021-04-20 广东如春生态集团有限公司 Method for treating spartina alterniflora by using ecological succession measures for restoring habitat
CN113712018A (en) * 2021-09-16 2021-11-30 江苏盐城国家级珍禽自然保护区管理处 Comprehensive method for treating spartina alterniflora by flooding with fresh water
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CN114342720A (en) * 2022-01-28 2022-04-15 上海市嘉定区农业技术推广服务中心(上海市嘉定区蔬菜技术推广站、上海市嘉定区农产品检测中心) A two-color sunshade net and a method for using the two-color sunshade net in strawberry seedling propagation
CN116250439A (en) * 2023-02-16 2023-06-13 海南省林业科学研究院(海南省红树林研究院) A method for systematic management of Spartina alterniflora
CN116250439B (en) * 2023-02-16 2024-05-31 海南省林业科学研究院(海南省红树林研究院) Method for managing spartina alterniflora system

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