CN103878171A - Ecological treatment bed of chromium contaminated soil - Google Patents
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Abstract
Description
技术领域technical field
本发明涉及污染土壤治理技术领域,尤其是一种铬污染土壤的生态处理床。The invention relates to the technical field of contaminated soil treatment, in particular to an ecological treatment bed for chromium-contaminated soil.
背景技术Background technique
铬及其化合物在工业生产的各个领域应用广泛,是冶金、电镀、制革、印染等行业必不可少的原料,这些企业在生产过程中污染了土壤。铬的毒性主要来自六价铬,它对人体和环境危害极大。对铬污染的土壤进行治理是目前环境科学技术研究的热点。Chromium and its compounds are widely used in various fields of industrial production, and are essential raw materials for industries such as metallurgy, electroplating, tanning, printing and dyeing, etc. These enterprises pollute the soil during the production process. The toxicity of chromium mainly comes from hexavalent chromium, which is extremely harmful to the human body and the environment. Treatment of chromium-contaminated soil is a hot spot in environmental science and technology research.
煤矿等矿山企业在生产过程中产生大量的煤矸石等废弃物,堆放这些煤矸石也需要一定量的土地,煤矿企业的矿灯房、机械厂等会产生一定量的废酸,如何合理又经济地利用这些废弃的煤矸石和废酸成为各大煤矿企业的一个难题。Coal mines and other mining enterprises produce a large amount of coal gangue and other wastes in the production process, and a certain amount of land is required to stack these coal gangues. Miner's lamp houses and machinery factories of coal mining enterprises will produce a certain amount of waste acid. How to reasonably and economically Utilizing these abandoned coal gangue and waste acid has become a difficult problem for major coal mining enterprises.
发明内容Contents of the invention
本发明要解决的技术问题是:为了解决污染土壤中铬的去除问题和煤矸石的堆放占用土地与矿灯房产生的废酸的处理利用问题,提供一种操作简单、投资少的铬污染土壤的治理方法和生态处理床,利用酸处理后的煤矸石作为还原材料,对污染土壤进行原位治理,将煤矸石和废酸的处理利用与污染土壤的治理结合起来,走以废治废的道路。The technical problem to be solved by the present invention is: in order to solve the problem of chromium removal in polluted soil and the disposal and utilization of land occupied by coal gangue and the waste acid produced by miner's lamp house, to provide a chromium-contaminated soil with simple operation and low investment Treatment method and ecological treatment bed, using coal gangue after acid treatment as reducing material, in-situ treatment of polluted soil, combining the treatment and utilization of coal gangue and waste acid with the treatment of polluted soil, and taking the road of treating waste by waste .
本发明解决其技术问题所采用的技术方案是:本发明的一种铬污染土壤的生态处理床是按如下步骤建造实施的:The technical solution adopted by the present invention to solve its technical problems is: the ecological treatment bed of a kind of chromium-contaminated soil of the present invention is built and implemented according to the following steps:
(1)调查、实验、分析,确定污染土壤的范围、面积和深度。(1) Investigate, experiment and analyze to determine the scope, area and depth of polluted soil.
(2)根据调查结果,规划、确定污染土壤治理的位置、面积,计算充填的厚度、土方量;把治理目标区规划成方格网状结构,规划成边长为5-10米的矩形方块。(2) According to the survey results, plan and determine the location and area of contaminated soil treatment, and calculate the filling thickness and earth volume; plan the treatment target area into a grid structure, and plan it into a rectangular block with a side length of 5-10 meters .
(3)剥离污染的土壤层,把部分剥离土堆积在生态处理床的四周,形成生态处理床的围堰。(3) The contaminated soil layer is stripped, and part of the stripped soil is piled up around the ecological treatment bed to form a cofferdam for the ecological treatment bed.
(4)生态处理床的底部设计有1-3%的水流坡度。(4) The bottom of the ecological treatment bed is designed with a water flow gradient of 1-3%.
(5)生态处理床的底部防渗处理,采用铺设防渗薄膜,防渗薄膜可采用1.5-2毫米厚的塑料膜,搭接处要处理好,以提高防渗效果;进一步的,为防止防渗薄膜被破坏,需在防渗薄膜下部土层和防渗薄膜上表面铺设细砂,或以土工布加细砂作为保护层。(5) The anti-seepage treatment at the bottom of the ecological treatment bed adopts the laying of anti-seepage film, and the anti-seepage film can adopt a plastic film with a thickness of 1.5-2 millimeters, and the lap joint will be handled well to improve the anti-seepage effect; further, in order to prevent If the anti-seepage film is damaged, it is necessary to lay fine sand on the lower soil layer of the anti-seepage film and the upper surface of the anti-seepage film, or use geotextile plus fine sand as a protective layer.
(6)把煤矸石破碎、过100-300目筛。(6) Crushing the gangue and passing through a 100-300 mesh sieve.
(7)将筛分后的煤矸石浸入到废酸溶液中、保持pH值2-5,浸泡2-4小时后自然风干,废酸溶液来自煤矿企业的矿灯房、机械厂等单位。(7) Immerse the sieved coal gangue in the waste acid solution, keep the pH value at 2-5, let it dry naturally after soaking for 2-4 hours, and the waste acid solution comes from miner lamp houses and machinery factories of coal mining enterprises.
(8)在防渗薄膜的保护层上充填风干的煤矸石,煤矸石的充填厚度为0.5-0.8米。(8) Fill the air-dried coal gangue on the protective layer of the anti-seepage film, and the filling thickness of the coal gangue is 0.5-0.8 meters.
(9)再在煤矸石上覆盖剥离的污染土壤,污染土壤的覆盖厚度为1-1.5米。(9) Cover the stripped polluted soil on the coal gangue again, and the covering thickness of the polluted soil is 1-1.5 meters.
(10)在生态处理床上选种植物,选种的植物应满足以下几点要求:①对铬的吸收能力强;②采用乡土物种,因土种植,因地制宜;③抗病能力强;④易于收获、便于处置;⑤耐涝能力强;⑥根系发达,茎叶茂密。常用的植物有李氏禾、芦苇、狗牙根、灰绿藜、牛筋草等。(10) Select plants on the ecological treatment bed, and the selected plants should meet the following requirements: ① strong absorption capacity for chromium; ② use native species, plant according to soil, and adapt measures to local conditions; ③ strong disease resistance; ④ easy to harvest , easy to handle; ⑤ strong waterlogging tolerance; ⑥ well-developed root system, dense stems and leaves. Commonly used plants include Lishihe, reed, bermudagrass, gray green quinoa, goosegrass and so on.
(11)对生态处理床定期浇灌。一方面维持床上植物的成活,植物吸收土壤中的铬元素,通过植物的收割一部分铬得以去除。另一方面浇灌水或自然雨水对污染土壤进行淋滤,淋滤液含有一定量的六价铬,淋滤液渗透到生态处理床下部的矸石层,与酸性的煤矸石发生反应,六价铬被还原成三价铬等低毒低害物质。(11) Water the ecological treatment bed regularly. On the one hand, to maintain the survival of the plants on the bed, the plants absorb the chromium element in the soil, and part of the chromium can be removed through the harvest of the plants. On the other hand, irrigation water or natural rainwater leaches the polluted soil, the leachate contains a certain amount of hexavalent chromium, the leachate penetrates into the gangue layer at the bottom of the ecological treatment bed, reacts with the acidic coal gangue, and the hexavalent chromium is reduced into low-toxic and low-harm substances such as trivalent chromium.
(12)在生态处理床的下游设计有淋滤液的收集塘,用来收集处理后的浇灌水或自然雨水,实现达标排放。(12) A leachate collection pond is designed downstream of the ecological treatment bed to collect treated irrigation water or natural rainwater to achieve standard discharge.
(13)保持生态处理床运行6-12个月,无害化后的生态处理床可用于园林绿化、生态种植,或作为建设用地等。(13) Keep the ecological treatment bed running for 6-12 months. The harmless ecological treatment bed can be used for landscaping, ecological planting, or as construction land.
本发明的有益效果是,本发明利用煤矸石作为填充材料直接充填到待处理的污染土壤下部,利用酸处理后的煤矸石作为还原材料,土壤中的六价铬被还原成三价铬等低毒低害物质,原位治理铬污染的土壤;也解决了煤矸石存放的占地问题;该发明操作方便、投资少、运行成本低。The beneficial effect of the present invention is that the present invention uses coal gangue as filling material to directly fill the lower part of the polluted soil to be treated, and uses acid-treated coal gangue as a reducing material, so that the hexavalent chromium in the soil is reduced to trivalent chromium and other low Toxic and low-hazardous substances, in-situ treatment of chromium-contaminated soil; also solves the problem of land occupation for coal gangue storage; the invention is easy to operate, less investment, and low operating cost.
附图说明Description of drawings
下面结合附图和实施例对本发明进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and embodiments.
图1是本发明生态处理床的具体实施例的剖面图,图2是本发明生态处理床的具体实施例的平面图。Fig. 1 is a sectional view of a specific embodiment of an ecological treatment bed of the present invention, and Fig. 2 is a plan view of a specific embodiment of an ecological treatment bed of the present invention.
图中:1.防渗层,2.矸石层,3.污染土壤层,4.植物,5.围堰,6.矸石、土壤充填区,7.淋滤液排放口,8.淋滤液收集塘。In the figure: 1. anti-seepage layer, 2. gangue layer, 3. polluted soil layer, 4. plants, 5. cofferdam, 6. gangue and soil filling area, 7. leachate discharge port, 8. leachate collection pond .
具体实施方式Detailed ways
现在结合附图对本发明作进一步详细的说明。这些附图均为简化的示意图,仅以示意方式说明本发明的基本结构,因此其仅显示与本发明有关的构成。The present invention is described in further detail now in conjunction with accompanying drawing. These drawings are all simplified schematic diagrams, which only illustrate the basic structure of the present invention in a schematic manner, so they only show the configurations related to the present invention.
实施例1Example 1
苏南某企业搬迁后的工业厂地经调查、实验、分析,确定土壤为铬重度污染,根据调查结果,确定污染土壤治理的位置、面积,规划成边长为8米的矩形方块。After the relocation of an enterprise in southern Jiangsu, the industrial plant site was investigated, tested, and analyzed, and the soil was determined to be heavily polluted by chromium. According to the investigation results, the location and area of contaminated soil treatment were determined and planned into a rectangular square with a side length of 8 meters.
剥离污染的土壤层,把部分剥离土堆积在生态处理床的四周,形成生态处理床的围堰,生态处理床的底部设计有2%的水流坡度,生态处理床的底部铺设1.5毫米厚的塑料膜,在防渗薄膜下部土层和防渗薄膜上表面铺设细砂作为保护层。Strip the polluted soil layer, and pile up part of the stripped soil around the ecological treatment bed to form the cofferdam of the ecological treatment bed. The bottom of the ecological treatment bed is designed with a 2% water flow gradient, and the bottom of the ecological treatment bed is laid with 1.5 mm thick plastic For the anti-seepage membrane, fine sand is laid on the lower soil layer of the anti-seepage membrane and the upper surface of the anti-seepage membrane as a protective layer.
把煤矸石破碎、过200目筛,将筛分后的煤矸石浸入到废酸溶液中、保持pH值3,浸泡2小时后自然风干,废酸溶液来自煤矿企业的矿灯房、机械厂等单位。Crush the coal gangue and pass it through a 200-mesh sieve. Immerse the screened coal gangue in the waste acid solution, keep the pH value at 3, soak for 2 hours and then dry it naturally. .
在防渗薄膜的保护层上充填风干的煤矸石,煤矸石的充填厚度为0.6米,再在煤矸石上覆盖剥离的污染土壤,污染土壤的覆盖厚度为1.2米,在生态处理床上选种植物李氏禾。Fill the air-dried coal gangue on the protective layer of the anti-seepage film. The filling thickness of the coal gangue is 0.6 meters, and then cover the stripped polluted soil on the coal gangue. The covering thickness of the polluted soil is 1.2 meters. Plants are selected on the ecological treatment bed Li Shihe.
对生态处理床定期浇灌,维持床上植物李氏禾的正常生长,植物吸收土壤中的铬元素,通过李氏禾的收割一部分铬得以去除;另一方面浇灌水或自然雨水对污染土壤进行淋滤,淋滤液含有一定量的六价铬,淋滤液渗透到生态处理床下部的矸石层,与酸性的煤矸石发生反应,六价铬被还原成三价铬等低毒低害物质。Regularly water the ecological treatment bed to maintain the normal growth of the plants on the bed. The plants absorb the chromium in the soil, and a part of the chromium can be removed through the harvest of Li Shihe; on the other hand, the polluted soil is leached by irrigation water or natural rainwater , The leachate contains a certain amount of hexavalent chromium, the leachate penetrates into the gangue layer at the bottom of the ecological treatment bed, reacts with the acidic gangue, and the hexavalent chromium is reduced to trivalent chromium and other low-toxic and low-harm substances.
在生态处理床的下游设计有淋滤液的收集塘,用来收集处理后的浇灌水或自然雨水,实现达标排放。A leachate collection pond is designed downstream of the ecological treatment bed to collect treated irrigation water or natural rainwater to achieve standard discharge.
保持生态处理床运行8个月,无害化后的生态处理床用于园林绿化。Keep the ecological treatment bed running for 8 months, and the harmless ecological treatment bed is used for landscaping.
实施例2Example 2
苏北某企业搬迁后的工业厂地经调查、实验、分析,确定为土壤铬重度污染,根据调查结果,确定污染土壤治理的位置、面积,规划成边长为10米的矩形方块。After the relocation of an enterprise in northern Jiangsu, the industrial factory site was determined to be severely polluted by chromium in the soil after investigation, experimentation, and analysis. According to the investigation results, the location and area of contaminated soil treatment were determined, and the plan was made into a rectangular square with a side length of 10 meters.
剥离污染的土壤层,把部分剥离土堆积在生态处理床的四周,形成生态处理床的围堰,生态处理床的底部设计有3%的水流坡度,生态处理床的底部铺设2毫米厚的塑料膜,在防渗薄膜下部土层和防渗薄膜上表面铺设细砂作为保护层。Strip the polluted soil layer, and pile up part of the stripped soil around the ecological treatment bed to form the cofferdam of the ecological treatment bed. The bottom of the ecological treatment bed is designed with a 3% water flow gradient, and the bottom of the ecological treatment bed is laid with 2 mm thick plastic For the anti-seepage membrane, fine sand is laid on the lower soil layer of the anti-seepage membrane and the upper surface of the anti-seepage membrane as a protective layer.
把煤矸石破碎、过300目筛,将筛分后的煤矸石浸入到废酸溶液中、保持pH值4,浸泡4小时后自然风干,废酸溶液来自煤矿企业的矿灯房、机械厂等单位。Crush the coal gangue and pass it through a 300-mesh sieve. Immerse the screened coal gangue in the waste acid solution to keep the pH value at 4. After soaking for 4 hours, let it dry naturally. The waste acid solution comes from miner lamp houses and machinery factories of coal mining enterprises. .
在防渗薄膜的保护层上充填风干的煤矸石,煤矸石的充填厚度为0.8米,再在煤矸石上覆盖剥离的污染土壤,污染土壤的覆盖厚度为1.5米,在生态处理床上选种植物芦苇。Fill the air-dried coal gangue on the protective layer of the anti-seepage film. The filling thickness of the coal gangue is 0.8 meters, and then cover the peeled polluted soil on the coal gangue. The covering thickness of the polluted soil is 1.5 meters. Plants are selected on the ecological treatment bed reed.
对生态处理床定期浇灌,维持床上芦苇的正常生长,芦苇吸收土壤中的铬元素,通过芦苇的收割铬得以去除;另一方面浇灌水或自然雨水对污染土壤进行淋滤,淋滤液含有一定量的六价铬,淋滤液渗透到生态处理床下部的矸石层,与酸性的煤矸石发生反应,六价铬被还原成三价铬等低毒低害物质。Regularly water the ecological treatment bed to maintain the normal growth of the reeds on the bed. The reeds absorb the chromium in the soil and remove the chromium through the harvesting of the reeds. On the other hand, the irrigation water or natural rainwater leaches the polluted soil, and the leachate contains a certain amount The hexavalent chromium, the leachate penetrates into the gangue layer at the lower part of the ecological treatment bed, reacts with the acidic gangue, and the hexavalent chromium is reduced to trivalent chromium and other low-toxic and low-harm substances.
在生态处理床的下游设计有淋滤液的收集塘,用来收集处理后的浇灌水或自然雨水,实现达标排放。A leachate collection pond is designed downstream of the ecological treatment bed to collect treated irrigation water or natural rainwater to achieve standard discharge.
保持生态处理床运行12个月,无害化后的生态处理床用于建设用地。Keep the ecological treatment bed running for 12 months, and the harmless ecological treatment bed is used for construction land.
以上述依据本发明的理想实施例为启示,通过上述的说明内容,相关工作人员完全可以在不偏离本项发明技术思想的范围内,进行多样的变更以及修改。本项发明的技术性范围并不局限于说明书上的内容,必须要根据权利要求范围来确定其技术性范围。Inspired by the above-mentioned ideal embodiment according to the present invention, through the above-mentioned description content, relevant workers can make various changes and modifications within the scope of not departing from the technical idea of the present invention. The technical scope of the present invention is not limited to the content in the specification, but must be determined according to the scope of the claims.
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Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104941995A (en) * | 2015-06-09 | 2015-09-30 | 北京市环境保护科学研究院 | Repair method for chromium-polluted soil |
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CN105478465A (en) * | 2016-02-26 | 2016-04-13 | 东北师范大学 | Ecological restoration method for arid region heavy metal pollution site |
CN108043868A (en) * | 2017-12-08 | 2018-05-18 | 常州大学 | Soil with serious petroleum pollution repairs bed |
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CN110052483A (en) * | 2019-03-26 | 2019-07-26 | 山东省鲁南地质工程勘察院(山东省地勘局第二地质大队) | Dystopy wet reducing-stabilisation joint repairs chromium-polluted soil and underground water method |
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1810397A (en) * | 2006-02-21 | 2006-08-02 | 天津市大钧科技开发有限公司 | Technology of repairing chromium contaminated soil |
CN101224465A (en) * | 2008-01-25 | 2008-07-23 | 暨南大学 | A method for leaching and repairing cadmium-contaminated coastal saline soil |
CN101704016A (en) * | 2009-11-17 | 2010-05-12 | 上海市农业科学院 | Phytochemically combined remediation technology for soil contaminated by heavy metals, Mn, Pb, Cr and Zn |
CN102726187A (en) * | 2012-06-25 | 2012-10-17 | 西北综合勘察设计研究院 | Surface ecological management method for mining subsidence area of coal mine |
CN102919040A (en) * | 2012-11-21 | 2013-02-13 | 中国科学院亚热带农业生态研究所 | Method for planting ramie in middle-level heavy metal contaminated soils |
-
2014
- 2014-03-27 CN CN201410119490.7A patent/CN103878171B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1810397A (en) * | 2006-02-21 | 2006-08-02 | 天津市大钧科技开发有限公司 | Technology of repairing chromium contaminated soil |
CN101224465A (en) * | 2008-01-25 | 2008-07-23 | 暨南大学 | A method for leaching and repairing cadmium-contaminated coastal saline soil |
CN101704016A (en) * | 2009-11-17 | 2010-05-12 | 上海市农业科学院 | Phytochemically combined remediation technology for soil contaminated by heavy metals, Mn, Pb, Cr and Zn |
CN102726187A (en) * | 2012-06-25 | 2012-10-17 | 西北综合勘察设计研究院 | Surface ecological management method for mining subsidence area of coal mine |
CN102919040A (en) * | 2012-11-21 | 2013-02-13 | 中国科学院亚热带农业生态研究所 | Method for planting ramie in middle-level heavy metal contaminated soils |
Non-Patent Citations (3)
Title |
---|
侯新村等: "草本能源植物修复重金属污染土壤的潜力", 《中国草地学报》 * |
陶芨汛等: "李氏禾对电镀污泥污染土壤中铬铜镍的吸收和积累", 《桂林理工大学学报》 * |
黄慧等: "植物修复重金属汞、镉、铬污染土壤的研究进展", 《中国农学通报》 * |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104941995A (en) * | 2015-06-09 | 2015-09-30 | 北京市环境保护科学研究院 | Repair method for chromium-polluted soil |
CN104941995B (en) * | 2015-06-09 | 2018-01-19 | 北京市环境保护科学研究院 | A kind of restorative procedure for chromium-polluted soil |
CN105032912A (en) * | 2015-07-17 | 2015-11-11 | 中国科学院武汉岩土力学研究所 | In-situ repair method for shallow-buried heavy metal pollution site |
CN105478465A (en) * | 2016-02-26 | 2016-04-13 | 东北师范大学 | Ecological restoration method for arid region heavy metal pollution site |
CN105478465B (en) * | 2016-02-26 | 2017-12-19 | 东北师范大学 | A kind of ecological restoring method in arid biogeographic zone heavy metal pollution place |
CN108043868A (en) * | 2017-12-08 | 2018-05-18 | 常州大学 | Soil with serious petroleum pollution repairs bed |
CN108941174A (en) * | 2018-07-10 | 2018-12-07 | 常州大学 | A kind of solid waste dismantling contaminated soil remediation device |
CN109290333A (en) * | 2018-11-16 | 2019-02-01 | 梅州市华智星技术服务有限公司 | A kind of integrated application method of chromium slag landfill disposal |
CN110052483A (en) * | 2019-03-26 | 2019-07-26 | 山东省鲁南地质工程勘察院(山东省地勘局第二地质大队) | Dystopy wet reducing-stabilisation joint repairs chromium-polluted soil and underground water method |
CN112139227A (en) * | 2020-09-14 | 2020-12-29 | 常州大学 | System and method for restoring soil by using river |
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