CN103669282A - Method for disposing river or lake bottom mud on site - Google Patents
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- CN103669282A CN103669282A CN201310727843.7A CN201310727843A CN103669282A CN 103669282 A CN103669282 A CN 103669282A CN 201310727843 A CN201310727843 A CN 201310727843A CN 103669282 A CN103669282 A CN 103669282A
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- 238000000034 method Methods 0.000 title claims description 12
- 239000013049 sediment Substances 0.000 claims abstract description 40
- 239000011159 matrix material Substances 0.000 claims abstract description 21
- 241000196324 Embryophyta Species 0.000 claims abstract description 20
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 13
- 231100000719 pollutant Toxicity 0.000 claims abstract description 13
- 241000722731 Carex Species 0.000 claims abstract description 6
- 239000000203 mixture Substances 0.000 claims abstract description 3
- 239000000463 material Substances 0.000 claims description 21
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- 241000124033 Salix Species 0.000 claims description 8
- 239000002893 slag Substances 0.000 claims description 8
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 4
- 239000010451 perlite Substances 0.000 claims description 4
- 235000019362 perlite Nutrition 0.000 claims description 4
- 239000000758 substrate Substances 0.000 claims description 4
- 241001290610 Abildgaardia Species 0.000 claims description 3
- 229910000831 Steel Inorganic materials 0.000 claims description 3
- 229910021536 Zeolite Inorganic materials 0.000 claims description 3
- 239000010959 steel Substances 0.000 claims description 3
- 239000010455 vermiculite Substances 0.000 claims description 3
- 235000019354 vermiculite Nutrition 0.000 claims description 3
- 229910052902 vermiculite Inorganic materials 0.000 claims description 3
- 239000010457 zeolite Substances 0.000 claims description 3
- 230000007797 corrosion Effects 0.000 claims description 2
- 238000005260 corrosion Methods 0.000 claims description 2
- 238000011065 in-situ storage Methods 0.000 abstract description 8
- 230000007613 environmental effect Effects 0.000 abstract description 6
- 238000005516 engineering process Methods 0.000 abstract description 2
- 239000004568 cement Substances 0.000 abstract 1
- 239000002131 composite material Substances 0.000 abstract 1
- 238000010276 construction Methods 0.000 abstract 1
- 230000000813 microbial effect Effects 0.000 abstract 1
- 238000004064 recycling Methods 0.000 abstract 1
- 239000000126 substance Substances 0.000 description 4
- 230000006378 damage Effects 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000009412 basement excavation Methods 0.000 description 1
- 239000003818 cinder Substances 0.000 description 1
- 230000002301 combined effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000010297 mechanical methods and process Methods 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000008439 repair process Effects 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000004162 soil erosion Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A10/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE at coastal zones; at river basins
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Abstract
本发明涉及一种河(湖)底泥就地处理构建生态护岸的生态工程技术。是将城市区域河(湖)底泥与颗粒组分物填充生态袋,用于在水泥硬质化河湖岸边构建生态堤,在生态袋与原岸带间填充底泥和其他组分的混合物,然后种植灌丛和苔草等高净化能力植物,构建底泥就地处理系统。本发明是实现城市污染的河湖底泥就地处理,减少运输成本,减少环境影响,利用构建的底泥基质、植物和微生物复合系统,实现底泥的生态无害化处理与循环利用。形成的近自然植物生态带可以拦截、吸收地表径流携带入河(湖)的面源污染物,消减污染水平。
The invention relates to an ecological engineering technology for in-situ treatment of river (lake) bottom mud and construction of ecological revetment. It is an ecological bag filled with river (lake) sediment and granular components in urban areas, used to build ecological dikes on the banks of cement hardened rivers and lakes, and filled with sediment and other components between the ecological bag and the original shore zone. Mixture, and then plant high-purifying plants such as shrubs and sedges to build an in-situ sediment treatment system. The invention realizes in-situ treatment of river and lake bottom mud polluted by cities, reduces transportation costs, reduces environmental impact, and realizes ecologically harmless treatment and recycling of bottom mud by using a constructed bottom mud matrix, plant and microbial composite system. The formed near-natural plant ecological zone can intercept and absorb non-point source pollutants brought into rivers (lakes) by surface runoff and reduce pollution levels.
Description
技术领域 technical field
本发明属于环保技术领域,具体是涉及一种河湖底泥就地处理的方法。 The invention belongs to the technical field of environmental protection, and in particular relates to a method for treating river and lake bottom mud on site.
背景技术 Background technique
伴随经济的高速发展,城市规模的不断扩大,河湖水系的污染问题日益严重。流域内由于农田开垦、植被破坏等原因,水土流失加剧。城市为了维持明水景观,构建堤坝等设施,导致河湖底泥积累速度加快,影响了城市蓄水防洪等生态安全问题。因此,城市区河湖区积蓄有大量污染物的底泥处理就成为当前政府和社会迫在眉睫的问题。大量的有机质碎屑、有毒难降解物质、重金属等在河湖底泥中沉积,导致底泥污染加剧。在点源污染和面源污染较大时,底泥对这些污染物起到富集作用;而当点源污染和面源污染得到控制后,这些沉积于底泥中的污染物在物理、化学和生物的作用下,在底泥中发生复杂的变化,继而向水体释放污染物,对水生生态系统构成威胁乃至破坏,进而威胁人类的身体健康。 With the rapid development of the economy and the continuous expansion of the city scale, the pollution of rivers and lakes is becoming more and more serious. Due to farmland reclamation and vegetation destruction in the watershed, soil erosion has intensified. In order to maintain the clear water landscape, the city builds dams and other facilities, which accelerates the accumulation of sediment in rivers and lakes, and affects ecological security issues such as urban water storage and flood control. Therefore, the disposal of sediments with a large amount of pollutants accumulated in rivers and lakes in urban areas has become an urgent problem for the current government and society. A large amount of organic debris, toxic and refractory substances, heavy metals, etc. are deposited in the bottom mud of rivers and lakes, resulting in aggravated bottom mud pollution. When the point source pollution and non-point source pollution are relatively large, the sediment can enrich these pollutants; and when the point source pollution and non-point source pollution are controlled, the pollutants deposited in the bottom mud can be physically and chemically Under the action of organic matter and organisms, complex changes occur in the sediment, and then pollutants are released into the water body, posing a threat or even damage to the aquatic ecosystem, and thus threatening human health.
针对污染河湖底泥的处理,目前多采用疏浚后集中处理,通过水力或机械方法挖除湖泊底泥表层的污染物,再进行输移处理,减少底泥污染物的释放。虽然疏浚可以较为有效的解决河流的污染状况,但由于疏浚后的底泥依然需要进行后续处理,挖掘相应的弃料坑进行填埋,运费与挖掘费用也加大了底泥疏浚的成本;而底泥中蕴含的大量污染物也会进入土壤造成二次污染,形成新的环境问题。现有专利中针对河湖底泥处理方法的描述也有很多,例如一种利用改性沸石原位控制底泥磷释放的方法(CN103408209A)、一种河湖清淤污泥脱水干化一体化试验装置及方法(CN103408207A)、适用于浅窄型混杂水河道的多级水质生态净化系统(CN103351084A)、用于中心城区河道污染底泥清除的处理系统及处理工艺(CN103334469A)、受污染底泥处理装置(CN203307188U)但多局限于通过物理、化学的方法改变底泥的理化性质,忽视了生物与生态的联合作用,且都需要进行异地处理,无形间增加了运输的成本。 For the treatment of polluted river and lake sediments, centralized treatment after dredging is mostly used at present. The pollutants on the surface of lake sediments are excavated by hydraulic or mechanical methods, and then transported to reduce the release of sediment pollutants. Although dredging can effectively solve the pollution situation of rivers, since the dredged sediment still needs to be followed up, excavating corresponding waste pits for landfill, transportation and excavation costs also increase the cost of sediment dredging; and A large number of pollutants contained in the sediment will also enter the soil to cause secondary pollution and form new environmental problems. There are also many descriptions of river and lake sediment treatment methods in existing patents, such as a method of using modified zeolite to control the release of phosphorus from sediment in situ (CN103408209A), an integrated test device for river and lake dredging and sludge dehydration and drying And method (CN103408207A), multi-stage water quality ecological purification system suitable for shallow and narrow mixed water channels (CN103351084A), treatment system and treatment process for removing polluted sediment from rivers in central urban areas (CN103334469A), contaminated sediment treatment device (CN203307188U) However, most of them are limited to changing the physical and chemical properties of the sediment through physical and chemical methods, ignoring the combined effect of biology and ecology, and all need to be treated in different places, which invisibly increases the cost of transportation.
随着我国经济快速发展,城市规模的不断扩大,河流与湖泊的水污染问题的日趋加重,污染底泥的处理也成为热点问题,如何对底泥低成本,无害化与资源化处理将是政府和社会关注的重点。 With the rapid development of my country's economy, the continuous expansion of the city scale, the increasing water pollution of rivers and lakes, the treatment of polluted sediment has also become a hot issue, how to deal with the sediment at low cost, harmless and resourceful will be The focus of government and society's attention.
发明内容 Invention content
本发明针对以上底泥疏浚后处理技术方面的不足,依据河湖生态系统的特殊性,提出一种河湖底泥就地处理的方法。 The present invention aims at the above deficiencies in the bottom mud dredging post-treatment technology, and according to the particularity of river and lake ecosystems, proposes a method for treating river and lake bottom mud in situ.
本发明采用的技术方案: The technical scheme adopted in the present invention:
将河(湖)底泥疏浚输送到河湖岸边,并与粗、细材料组分按一定比例均匀混合构成底泥混合基质,将该底泥混合基质充填到耐腐蚀,永久不可降解,并且具有良好透水性性能的生态袋中,在距离河(湖)岸1-2米处堆积该生态袋,并利用锚固桩锚固构建成生态堤,生态堤面高于水面约50-80cm,在生态堤与原河(湖)岸带间填充底泥混合基质,并在底泥混合基质上种植高效去除污染物并具有环境美化功能的植物,植物可为灌丛植物和草本植物。实现对岸带地表径流携带面源污染的截留,底泥与水体中的污染物的去除,同时具有景观美化、生态护岸等多种功能,实现底泥低成本、无害化与资源化处理的目标。 The river (lake) sediment is dredged and transported to the bank of the river and lake, and mixed evenly with the coarse and fine material components in a certain proportion to form a mixed matrix of sediment, and the mixed matrix of sediment is filled to a corrosion-resistant, permanent non-degradable, and In the ecological bag with good water permeability, the ecological bag is piled up at a distance of 1-2 meters from the bank of the river (lake), and anchored by anchor piles to form an ecological embankment. The ecological embankment is about 50-80cm above the water surface. Fill the bottom mud mixed matrix between the embankment and the original river (lake) bank, and plant plants on the bottom mud mixed matrix that can efficiently remove pollutants and have the function of beautifying the environment. The plants can be shrub plants and herbaceous plants. Realize the interception of non-point source pollution carried by surface runoff in the opposite shore zone, and the removal of pollutants in sediment and water bodies. At the same time, it has multiple functions such as landscaping and ecological revetment, and realizes the goal of low-cost, harmless and resource-based treatment of sediment .
底泥和粗、细材料组分组成底泥混合基质按重量比例为: Bottom mud and coarse and fine material components make up the bottom mud mixed matrix by weight ratio:
粗材料组分 20%-40% Coarse material component 20%-40%
细材料组分 20%-40% Fine material composition 20%-40%
底泥组分 40% Sediment Components 40%
各组分之和为100%; The sum of each component is 100%;
所述的粗材料组分为钢渣、火山渣、炉灰渣、砾石其中的一种或几种,可以以任意比例混合; The coarse material component is one or more of steel slag, volcanic slag, furnace ash and gravel, which can be mixed in any proportion;
所述的细材料组分为珍珠岩、沸石、蛭石、火山灰其中的一种或几种,可以以任意比例混合; The fine material component is one or more of perlite, zeolite, vermiculite and volcanic ash, which can be mixed in any proportion;
所述的细材料组分直径小于5 mm,粗材料组分直径大于10 mm ; The diameter of the fine material component is less than 5 mm, and the diameter of the coarse material component is greater than 10 mm;
所述的在混合基质上种植高效去除污染物并具有环境美化功能的植物,可为灌丛柳和苔草,两者的种植密度为:灌丛柳1株/m2,苔草5株/m2, The plants that can efficiently remove pollutants and have the function of beautifying the environment planted on the mixed substrate can be shrub willow and sedge, and the planting density of both is: 1 shrub willow/m 2 and 5 sedge/m 2 ,
本发明与现有技术相比,具有以下优点: Compared with the prior art, the present invention has the following advantages:
1 、本发明实现了城市河湖底泥疏浚后的低成本、无害化处理,减少运输成本,减轻对其它环境的影响。通过利用底泥与其它组分构建的就地处理系统,生长的植物与微生物可对底泥物理化学特性有较好的改良作用,通过物理、化学、生物的协同作用,可以消减去除底泥中的污染物,一定程度上实现对底泥结构组分的修复,实现无害化目标; 1. The present invention realizes low-cost and harmless treatment of urban river and lake sediment after dredging, reduces transportation costs, and reduces impact on other environments. Through the in-situ treatment system constructed by using the sediment and other components, the growing plants and microorganisms can improve the physical and chemical properties of the sediment, and through the synergistic effect of physics, chemistry and biology, it can reduce and remove the sediment in the sediment. Pollutants, to a certain extent, to achieve the restoration of the structural components of the sediment, to achieve the goal of harmlessness;
2 、河湖底泥构建的就地处理系统在针对底泥进行修复的同时,一定程度改善了河流水质,同时对汇入河湖的径流污染有着一定程度的截留作用; 2. The in-situ treatment system built for river and lake sediments not only repairs the sediment, but also improves the river water quality to a certain extent, and at the same time has a certain degree of interception effect on the runoff pollution flowing into rivers and lakes;
3、利用河湖底泥构建的近自然护岸就地处理系统,还可实现生态护岸,城市休闲娱乐区景观美化等功能,同时具有良好的环境宣传教育功能,有助于提高居民的环保意识和环境知识。 3. The near-natural revetment on-site treatment system constructed by using river and lake bottom mud can also realize functions such as ecological revetment, urban leisure and entertainment area landscape beautification, etc. At the same time, it has a good environmental publicity and education function, which helps to improve residents' environmental protection awareness and environmental protection. Knowledge.
附图说明 Description of drawings
附图为一种河湖底泥就地处理方法的示意图 The accompanying drawing is a schematic diagram of an in-situ treatment method for river and lake sediment
图中:1.生态堤,2.植物,3.底泥混合基质,4.锚固桩。 In the figure: 1. Ecological embankment, 2. Plants, 3. Sediment mixed matrix, 4. Anchorage piles.
具体实施方式Detailed ways
实施例1:Example 1:
在水体深度为1m的人工湖,取底泥混合基质装入生态袋,距离湖岸2米处堆积生态袋形成生态堤,堤面高于水面50cm,并锚固。底泥混合基质为底泥与粗材料组分炉渣、细材料组分蛭石按40%:40%:20%的重量比例均匀混合而成,再将底泥混合基质充填于原湖岸和生态堤之间,然后每平米种植1株灌丛柳,5株苔草。 In an artificial lake with a water depth of 1m, take the mixed substrate of sediment and put it into an ecological bag, and pile up the ecological bag at a distance of 2 meters from the lake shore to form an ecological embankment. The embankment surface is 50cm above the water surface and anchored. The bottom mud mixed matrix is uniformly mixed with bottom mud, coarse material component slag, and fine material component vermiculite at a weight ratio of 40%: 40%: 20%, and then the bottom mud mixed matrix is filled in the original lakeshore and ecological embankment Between, and then plant 1 shrub willow and 5 carex per square meter.
实施例2: Example 2:
在水体深度为2 m的河岸,将底泥与粗材料组分炉渣和砾石,细组分珍珠岩按40%:20%:40%的重量比例均匀混合成底泥混合基质,取底泥混合基质入生态袋,距离河岸1米处堆积生态袋形成生态堤,并锚固,堤面高于水面60cm。再将底泥混合基质充填于原河岸和生态堤之间,然后每平米种植1株灌丛柳,5株苔草。 On the river bank with a water body depth of 2 m, the bottom mud is uniformly mixed with the coarse material components slag and gravel, and the fine component perlite at a weight ratio of 40%:20%:40% to form a bottom mud mixed matrix, and the bottom mud is mixed The matrix is put into the ecological bag, and the ecological bag is piled up 1 meter away from the river bank to form an ecological embankment, which is anchored, and the embankment surface is 60cm above the water surface. Then fill the bottom mud mixed matrix between the original river bank and the ecological embankment, and then plant 1 shrub willow and 5 carex per square meter.
the
实施例3:Example 3:
在水体深度为3 m的河岸,将底泥与粗材料组分钢渣和砾石,细材料组分珍珠岩和火山灰按40%:30%:30%的重量比例均匀混合成底泥混合基质,取底泥混合基质装入生态袋,距离河岸1.5米处堆积生态袋形成生态堤,并锚固,堤面高于水面70cm。再将底泥混合基质充填于原河岸和生态堤之间,然后每平米种植1株灌丛柳,5株苔草。 On a river bank with a water depth of 3 m, the bottom mud, coarse material components, steel slag and gravel, and fine material components, perlite and volcanic ash, were uniformly mixed at a weight ratio of 40%:30%:30% to form a bottom mud mixed matrix. The bottom mud mixed matrix is put into an ecological bag, and the ecological bag is piled up 1.5 meters away from the river bank to form an ecological embankment, which is anchored, and the embankment surface is 70cm above the water surface. Then fill the bottom mud mixed matrix between the original river bank and the ecological embankment, and then plant 1 shrub willow and 5 carex per square meter.
实施例4:Example 4:
在水体深度为3m的湖岸,将底泥与粗组分炉渣和火山渣,细组分沸石按40%:25%:35%的比例均匀混合成底泥混合基质,取底泥混合基质装入生态袋,距离湖岸1米处堆积生态袋形成生态堤,并锚固,堤面高于水面80cm。再将底泥混合基质充填于原湖岸和生态堤之间,然后每平米种植1株灌丛柳,5株苔草。
On the shore of the lake with a water depth of 3m, the bottom mud, the coarse component slag and volcanic cinder, and the fine component zeolite are uniformly mixed at a ratio of 40%:25%:35% to form a bottom mud mixed matrix, and the bottom mud mixed matrix is loaded into the Ecological bags, stacking
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Cited By (12)
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CN104119175A (en) * | 2014-08-12 | 2014-10-29 | 许盛英 | Production method of volcanic ash compressed nutritional soil |
CN104404917A (en) * | 2014-11-03 | 2015-03-11 | 江苏龙腾工程设计有限公司 | Taihu lake ecological dam revetment construction method |
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CN105442491A (en) * | 2015-11-12 | 2016-03-30 | 东北师范大学 | Bottom silt on-site treatment and ecological slope protection method for river/lake |
CN105648974A (en) * | 2014-12-02 | 2016-06-08 | 中国科学院烟台海岸带研究所 | In-situ desilting, oxygen aeration and landscape construction method of polluted riverway |
CN109024479A (en) * | 2018-07-24 | 2018-12-18 | 上海海洋大学 | Structure, manufacture craft and the seashore wetland landforms of Wetland ecological brick regulate and control method |
CN110857236A (en) * | 2018-08-15 | 2020-03-03 | 四川达沃斯生态环保科技股份有限公司 | Ecological river lake underwater forest construction method |
CN111576339A (en) * | 2020-05-12 | 2020-08-25 | 中国城市建设研究院有限公司 | Ecological revetment for strengthening treatment of black and odorous water body by microorganisms |
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CN104119175A (en) * | 2014-08-12 | 2014-10-29 | 许盛英 | Production method of volcanic ash compressed nutritional soil |
CN104119175B (en) * | 2014-08-12 | 2016-05-18 | 许盛英 | The production method of volcanic ash compression Nutrition Soil |
CN104404917A (en) * | 2014-11-03 | 2015-03-11 | 江苏龙腾工程设计有限公司 | Taihu lake ecological dam revetment construction method |
CN105648974B (en) * | 2014-12-02 | 2017-12-19 | 中国科学院烟台海岸带研究所 | Desilting in situ, oxygenation and the Scene construction method of a kind of polluted river channel |
CN105648974A (en) * | 2014-12-02 | 2016-06-08 | 中国科学院烟台海岸带研究所 | In-situ desilting, oxygen aeration and landscape construction method of polluted riverway |
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CN105442491A (en) * | 2015-11-12 | 2016-03-30 | 东北师范大学 | Bottom silt on-site treatment and ecological slope protection method for river/lake |
CN105350489A (en) * | 2015-11-23 | 2016-02-24 | 东北师范大学 | Ecological anti-pollution bank slope construction method for river and lake |
CN105417905A (en) * | 2015-12-08 | 2016-03-23 | 上海水源地建设发展有限公司 | Method for treating in situ sludge of lake and river channel based on underwater lawn module system |
CN109024479A (en) * | 2018-07-24 | 2018-12-18 | 上海海洋大学 | Structure, manufacture craft and the seashore wetland landforms of Wetland ecological brick regulate and control method |
CN109024479B (en) * | 2018-07-24 | 2020-08-18 | 上海海洋大学 | Manufacturing process of wetland ecological brick and coastal wetland landform regulation and control method |
CN110857236A (en) * | 2018-08-15 | 2020-03-03 | 四川达沃斯生态环保科技股份有限公司 | Ecological river lake underwater forest construction method |
CN111576339A (en) * | 2020-05-12 | 2020-08-25 | 中国城市建设研究院有限公司 | Ecological revetment for strengthening treatment of black and odorous water body by microorganisms |
CN112715316A (en) * | 2020-12-25 | 2021-04-30 | 中煤浙江生态环境发展有限公司 | Re-greening restoration backfill planting material and application thereof |
CN112715316B (en) * | 2020-12-25 | 2024-02-20 | 中煤浙江生态环境发展有限公司 | Restoring and backfilling planting material and application thereof |
CN118343965A (en) * | 2024-05-10 | 2024-07-16 | 中国科学院水生生物研究所 | Substrate improving material and method for reducing emission of greenhouse gases in lake sediments |
CN118343965B (en) * | 2024-05-10 | 2025-02-07 | 中国科学院水生生物研究所 | A bottom improvement material and a method for reducing greenhouse gas emissions from lake sediments |
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