CN105850419A - Artificial restoration method for saltmarsh vegetation - Google Patents

Artificial restoration method for saltmarsh vegetation Download PDF

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Publication number
CN105850419A
CN105850419A CN201610210687.0A CN201610210687A CN105850419A CN 105850419 A CN105850419 A CN 105850419A CN 201610210687 A CN201610210687 A CN 201610210687A CN 105850419 A CN105850419 A CN 105850419A
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CN
China
Prior art keywords
cylinder
vegetation
saltmarsh
salt marsh
marsh vegetation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201610210687.0A
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Chinese (zh)
Inventor
张群
崔心红
朱义
何小丽
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Shanghai Academy of Landscape Architecture Science and Planning
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Shanghai Academy of Landscape Architecture Science and Planning
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Publication date
Application filed by Shanghai Academy of Landscape Architecture Science and Planning filed Critical Shanghai Academy of Landscape Architecture Science and Planning
Priority to CN201610210687.0A priority Critical patent/CN105850419A/en
Publication of CN105850419A publication Critical patent/CN105850419A/en
Pending legal-status Critical Current

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Classifications

    • 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

Abstract

The invention discloses an artificial restoration method for saltmarsh vegetation. The method includes the steps that the saltmarsh vegetation is artificially cultured; seedlings start to be transplanted when 15-20 cm high; the saltmarsh vegetation is planted in a planting utensil and then planted in a wet land or a mud flat, wherein the planting utensil comprises a cylinder, the upper end and the lower end of the cylinder are open, the height of the cylinder ranges from 18 cm to 25 cm, an insertion plate is arranged at the lower end of the cylinder, and a plurality of through holes are formed in the side wall of the cylinder and located in the zone with the distance of 5-20 cm to the top end of the cylinder. The saltmarsh vegetation is planted in the cylinder of the planting utensil, the cylinder and the insertion plate are made perpendicular, then the saltmarsh vegetation is completely planted in sediment in an intertidal zone, and the upper end of the cylinder is flush with the surface of the sediment, so that planting of the saltmarsh vegetation in the intertidal zone is reinforced, the tide scour resisting capacity of the saltmarsh vegetation in planting restoration is improved, planting growth of the saltmarsh vegetation is promoted, the survival rate of the saltmarsh vegetation is increased, and the reproductive capacity of the saltmarsh vegetation is improved.

Description

A kind of method of manual reversion salt marsh vegetation
Technical field
The present invention relates to ecological environmental protection field, particularly relate to salt marsh vegetation, particularly a kind of manual reversion salt The method of natural pond vegetation.
Background technology
Scirpus mariqueter (Scirpus mariqueter Tang&F.T.Wang) is that Cyperaceae grass belongs to one Plant herbaceos perennial, be the endemic species really with Shanghai characteristic, be also entrance of Changjiang River wetlands ecosystems The primary producer of middle most critical, status is special, function is extensive, has the effect that can not be substituted.But it is near Over 30 years, the impact invaded due to human activity interference and alien species Spartina alterniflora, Scirpus mariqueter etc. The existence of endemic species receives serious threat, and its distribution area is from about 135km2Fall sharply to 40km2Hereinafter, Through badly influence the integrity of Chongming Wetland ecosystem, health and service function (Li B, Liao CZ, Zhang XD,Chen HL,Wang Q,Chen ZY,Gan XJ,Wu JH,Zhao B,Ma ZJ,Cheng XL,Jiang LF&Chen JK.2009.Spartina alterniflora invasions in the Yangtze River estuary,China:an overview of current status and ecosystem effects.Ecological Engineering,35:511-520.).This trend is not as obtained effectively Containment, these species of Scirpus mariqueter likely move towards overall extinction, estuary wetland ecosystem in entrance of Changjiang River Also (present situation of the peculiar salt-marsh plants Scirpus mariqueter of Chen Xiuzhi, Sun Ying .2011. China and guarantor can be collapsed Protect utilization [J]. Wetland Science and management, 1:60-63.).In view of Scirpus mariqueter is at entrance of Changjiang River Wetland ecological Importance in system and the threat faced at present, we must strengthen the research to these species and protection Work, the group of the indigenous species such as reconstruction and rejuvenation Scirpus mariqueter.
It is ecological that Shanghai City started Shanghai Chongming Dong Tan Birds National Nature Reserve Spartina alterniflora in 2013 Controlling to optimize engineering with Studies on Avian Habitat, this engineering is the important component part that Chongming eco-island is built, and reach Above-mentioned purpose, after removing the Spartina alterniflora of invasion, it is necessary to control the expansion again of Spartina alterniflora, rebuild and answer The group of the indigenous species such as strong Scirpus mariqueter.Resume work and be divided in Engineering Zone and Intertidal zone wetland outside region (being called for short " dike is outer ").The latter is owing to being washed away by sea water persistence, and it has complicated change in water and sand and fortune Dynamic, the field planting rate directly transplanting the Scirpus mariqueter seedling planted outside dike is less than 30% after 30 days, recovers work It is abnormal difficult to make.
Summary of the invention
A kind of method that it is an object of the invention to provide manual reversion salt marsh vegetation, described this manual reversion The method of salt marsh vegetation to solve to recover difficult, easily outside the salt marsh vegetation dikes such as Scirpus mariqueter of the prior art By periodically tidewater is washed away, colonization ability is low, growth and the technical problem of fertility difference.
A kind of method that the invention provides manual reversion salt marsh vegetation, comprises the steps:
1) step of artificial culture's salt marsh vegetation;After seedling plant height 15~20cm, start to transplant;
2) salt marsh vegetation is planted in a field planting utensil, then plant in wetland or beach, described Field planting utensil includes a cylinder, the upper and lower end opening of described cylinder, described cylinder Height between 18~25cm, the diameter of described cylinder between 8~10cm, described cylinder Lower end be provided with a plate, plate to the lower section of cylinder extend, the height of described plate Between 20~30cm, the sidewall of described cylinder is provided with plurality of through holes, through hole number No less than 30, described through hole is arranged on the region between the top 5~20cm of distance cylinder In.
Further, described salt marsh vegetation is Scirpus mariqueter.
Further, described plate and described cylinder are integrally formed.
Further, described plate is wedge structure.
Further, described cylinder is cylindrical structural.
Further, a diameter of 1.5cm of described through hole.
Further, the distance between the through hole that any two is adjacent is 3cm.
The present invention can recover salt marsh vegetation, improves the vegetation erosion resistibility to tide, and can be effectively improved calmly Plant the diffusion of the salt marsh vegetation such as Scirpus mariqueter, fertility, salt marsh vegetation planted in specific utensil, The salt marsh vegetation such as described utensil divides upper and lower two parts, and upper end is tubular structure, plantation Scirpus mariqueter, and open Hole is beneficial to rhizome and the growth of bulb and breeding dispersal, and the lower end of cylinder is not closed, and is beneficial to processing and root system Growth, plate is processed as wedge shape, inserts in Wetland Sediments, is beneficial to plantation and reinforces, perforate a diameter of 1.5cm, upper and lower and left and right hole back gauge is 3 centimetres, 15 between top down 5 centimetres to 20 centimetres The salt marsh vegetation diffusions such as cm section open interior, beneficially Scirpus mariqueter, not perforate topmost, does not reduce device Mechanical strength and moisture resistance nighttide scouring capability.
The present invention compares with prior art, and it has the technical effect that positive and obvious.The present invention is by Scirpus mariqueter Plant in specific cylinder etc. salt marsh vegetation, then by vertical with plate for cylinder and plant completely in Intertidal zone deposit In thing, cylinder upper end is contour with deposit surface, strengthens the salt marsh vegetation such as the Scirpus mariqueter kind in Intertidal zone Plant, contribute to the field planting growth of the salt marsh vegetation such as Scirpus mariqueter, improve the salt marsh vegetation such as Scirpus mariqueter Survival rate and diffusion fertility.
Accompanying drawing explanation
Fig. 1 is the side view of a kind of field planting utensil for manual reversion salt marsh vegetation of the present invention.
Fig. 2 is the front view of a kind of field planting utensil for manual reversion salt marsh vegetation of the present invention.
Detailed description of the invention
Embodiment 1
The invention provides a kind of field planting utensil for manual reversion salt marsh vegetation, including a cylinder 1, institute The upper and lower end opening of the cylinder 1 stated, the height of described cylinder 1 is 20cm, and the diameter of described cylinder 1 exists Between 8~10cm, the lower end of described cylinder 1 is provided with a plate 2, and plate 2 extends to the lower section of cylinder 1, The height of described plate 2, between 20~30cm, the sidewall of described cylinder 1 is provided with plurality of through holes 3, Through hole number is no less than 30, and described through hole 3 is arranged on the region between the top 5~20cm of distance cylinder 1 In, described plate 2 and described cylinder 1 are integrally formed, and described plate 2 is wedge structure, described A diameter of 1.5cm of through hole 3, the distance between the through hole 3 that any two is adjacent is 3cm.
(1) under artificial condition, Scirpus mariqueter is cultivated;After seedling plant height 15~20cm, start to transplant.
(2) for improving erosion resistibility to tide, and can be effectively improved the diffusion of Scirpus mariqueter after field planting, Fertility, (L represents the device of a length of 50 centimetres, H to design Scirpus mariqueter planting unit 2 kinds Represent the device of a length of 40 centimetres), utilize thick bamboo tube to process planting unit 600.
(3) outside the dike of Chongming Dongtan new embankment southern side, at new embankment 50m, the outer Scirpus mariqueter of selected dike Rejuvenate species demonstration pilot project, utilizes field planting utensil (thick bamboo tube planting unit) and the seedling of the present invention, completes dike outer 600 m2Demonstration plant, planting density is 10 strains (1 field planting utensil)/m2, 1 field planting utensil/m2
(4) growth and the survival rate that continue to monitor Scirpus mariqueter in the erosion resistibility of device and device (are deposited Motility rate is the number/total device number retained having survival Scirpus mariqueter in device).
Following data are obtained by experiment:
Table Scirpus mariqueter plant height and survival rate
After testing 60 days, the survival rate of Scirpus mariqueter and the anti-impact of thick bamboo tube rinse ability, 2 kinds of device length Process under, without obvious difference, for saving material usage, convenient transport and plantation, can be selected for total length is The planting unit of 40cm.

Claims (8)

1. the method for a manual reversion salt marsh vegetation, it is characterised in that comprise the steps:
1) step of artificial culture's salt marsh vegetation;After seedling plant height 15 ~ 20cm, start to transplant;
2) salt marsh vegetation is planted in a field planting utensil, plant in wetland or beach again, described field planting utensil includes a cylinder, described cylinder upper, lower ending opening, the height of described cylinder is between 18 ~ 25cm, the diameter of described cylinder is between 8 ~ 10cm, the lower end of described cylinder is provided with a plate, plate extends to the lower section of cylinder, the height of described plate is between 20 ~ 30cm, it is provided with plurality of through holes on the sidewall of described cylinder, through hole number is no less than 30, described through hole is arranged in the region between the top 5 ~ 20cm of distance cylinder, planting density is 1 ~ 2 field planting utensil/m2
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: described salt marsh vegetation is Scirpus mariqueter.
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: described plate and described cylinder are integrally formed.
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: described plate is wedge structure.
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: described cylinder is cylindrical structural.
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: a diameter of 1.5cm of described through hole.
The method of a kind of manual reversion salt marsh vegetation the most according to claim 1, it is characterised in that: the distance between the through hole that any two is adjacent is 3cm.
8. the field planting utensil for manual reversion salt marsh vegetation, it is characterized in that: include a cylinder, the upper and lower end opening of described cylinder, the height of described cylinder is between 18 ~ 25cm, the diameter of described cylinder is between 8 ~ 10cm, the lower end of described cylinder is provided with a plate, plate extends to the lower section of cylinder, the height of described plate is between 20 ~ 30cm, it is provided with plurality of through holes on the sidewall of described cylinder, through hole number is no less than 30, and described through hole is arranged in the region between the top 5 ~ 20cm of distance cylinder.
CN201610210687.0A 2016-04-06 2016-04-06 Artificial restoration method for saltmarsh vegetation Pending CN105850419A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109005750A (en) * 2018-08-01 2018-12-18 华东师范大学 A kind of intertidal belt submarine scirpus scirpus natural community ecological recovery method
CN109168737A (en) * 2018-08-31 2019-01-11 吉林省方水土贸易有限公司 A kind of plantation carrier and implantation methods

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1038744A (en) * 1988-03-04 1990-01-17 伊藤嘉英 The method for planting of seedling
CN2061366U (en) * 1989-03-13 1990-09-05 杨承庄 Sapling-cultivating pot and young tree transplanting device
CN101213920A (en) * 2008-01-15 2008-07-09 陈礼斌 Plant cultivation method and using planting apparatus
CN203120593U (en) * 2012-12-26 2013-08-14 华南师范大学 Large mangrove plant seedling planting protection cover
JP2014076013A (en) * 2012-10-11 2014-05-01 Takanori Kihara Plant growing device
CN103999666A (en) * 2014-05-12 2014-08-27 中国科学院东北地理与农业生态研究所 Method for effectively controlling wet land non-target seeds and promoting natural vegetation recovery
CN105409748A (en) * 2015-12-08 2016-03-23 上海市园林科学研究所 Fast breeding method for scirpus mariqueter
CN205454892U (en) * 2016-04-06 2016-08-17 上海市园林科学规划研究院 A field planting utensil that is used for artifical sabkha vegetation that resumes

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1038744A (en) * 1988-03-04 1990-01-17 伊藤嘉英 The method for planting of seedling
CN2061366U (en) * 1989-03-13 1990-09-05 杨承庄 Sapling-cultivating pot and young tree transplanting device
CN101213920A (en) * 2008-01-15 2008-07-09 陈礼斌 Plant cultivation method and using planting apparatus
JP2014076013A (en) * 2012-10-11 2014-05-01 Takanori Kihara Plant growing device
CN203120593U (en) * 2012-12-26 2013-08-14 华南师范大学 Large mangrove plant seedling planting protection cover
CN103999666A (en) * 2014-05-12 2014-08-27 中国科学院东北地理与农业生态研究所 Method for effectively controlling wet land non-target seeds and promoting natural vegetation recovery
CN105409748A (en) * 2015-12-08 2016-03-23 上海市园林科学研究所 Fast breeding method for scirpus mariqueter
CN205454892U (en) * 2016-04-06 2016-08-17 上海市园林科学规划研究院 A field planting utensil that is used for artifical sabkha vegetation that resumes

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
赵冬至等: "《入海河口湿地生态系统空间评价理论与实践》", 31 July 2013, 海洋出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109005750A (en) * 2018-08-01 2018-12-18 华东师范大学 A kind of intertidal belt submarine scirpus scirpus natural community ecological recovery method
CN109005750B (en) * 2018-08-01 2020-11-03 华东师范大学 Ecological restoration method for natural community of scirpus in intertidal zone
CN109168737A (en) * 2018-08-31 2019-01-11 吉林省方水土贸易有限公司 A kind of plantation carrier and implantation methods

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Application publication date: 20160817