JP2005296941A - Method for cleaning lead-contaminated soil - Google Patents
Method for cleaning lead-contaminated soil Download PDFInfo
- Publication number
- JP2005296941A JP2005296941A JP2005066610A JP2005066610A JP2005296941A JP 2005296941 A JP2005296941 A JP 2005296941A JP 2005066610 A JP2005066610 A JP 2005066610A JP 2005066610 A JP2005066610 A JP 2005066610A JP 2005296941 A JP2005296941 A JP 2005296941A
- Authority
- JP
- Japan
- Prior art keywords
- lead
- plant
- soil
- oxalic acid
- contaminated
- 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.)
- Granted
Links
- 239000002689 soil Substances 0.000 title claims abstract description 47
- 238000000034 method Methods 0.000 title claims description 29
- 238000004140 cleaning Methods 0.000 title abstract 2
- 241000196324 Embryophyta Species 0.000 claims abstract description 65
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 claims abstract description 63
- 235000006408 oxalic acid Nutrition 0.000 claims abstract description 21
- 150000001875 compounds Chemical class 0.000 claims abstract description 14
- 238000009825 accumulation Methods 0.000 claims description 4
- 238000003306 harvesting Methods 0.000 claims description 4
- 238000010521 absorption reaction Methods 0.000 claims description 3
- 238000009331 sowing Methods 0.000 claims description 3
- 241000207834 Oleaceae Species 0.000 claims description 2
- 241001107098 Rubiaceae Species 0.000 claims description 2
- 241000208165 Oxalidaceae Species 0.000 abstract description 2
- 241000219050 Polygonaceae Species 0.000 abstract description 2
- 241000219317 Amaranthaceae Species 0.000 abstract 1
- 241000209524 Araceae Species 0.000 abstract 1
- 241000218999 Begoniaceae Species 0.000 abstract 1
- 241000234615 Musaceae Species 0.000 abstract 1
- 238000010899 nucleation Methods 0.000 abstract 1
- 229910001385 heavy metal Inorganic materials 0.000 description 23
- 238000000746 purification Methods 0.000 description 8
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 6
- 238000011109 contamination Methods 0.000 description 5
- 230000007613 environmental effect Effects 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 3
- 240000007019 Oxalis corniculata Species 0.000 description 3
- 229910052793 cadmium Inorganic materials 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 150000007524 organic acids Chemical class 0.000 description 3
- 235000005985 organic acids Nutrition 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 241000218993 Begonia Species 0.000 description 2
- 235000016499 Oxalis corniculata Nutrition 0.000 description 2
- 235000018167 Reynoutria japonica Nutrition 0.000 description 2
- 240000001341 Reynoutria japonica Species 0.000 description 2
- 244000300264 Spinacia oleracea Species 0.000 description 2
- 235000009337 Spinacia oleracea Nutrition 0.000 description 2
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052725 zinc Inorganic materials 0.000 description 2
- 239000011701 zinc Substances 0.000 description 2
- VCVKIIDXVWEWSZ-YFKPBYRVSA-N (2s)-2-[bis(carboxymethyl)amino]pentanedioic acid Chemical compound OC(=O)CC[C@@H](C(O)=O)N(CC(O)=O)CC(O)=O VCVKIIDXVWEWSZ-YFKPBYRVSA-N 0.000 description 1
- BJEPYKJPYRNKOW-REOHCLBHSA-N (S)-malic acid Chemical compound OC(=O)[C@@H](O)CC(O)=O BJEPYKJPYRNKOW-REOHCLBHSA-N 0.000 description 1
- 241000208838 Asteraceae Species 0.000 description 1
- 241000871189 Chenopodiaceae Species 0.000 description 1
- 235000006481 Colocasia esculenta Nutrition 0.000 description 1
- 244000205754 Colocasia esculenta Species 0.000 description 1
- 241000221079 Euphorbia <genus> Species 0.000 description 1
- 241000221017 Euphorbiaceae Species 0.000 description 1
- 241000220485 Fabaceae Species 0.000 description 1
- 240000008620 Fagopyrum esculentum Species 0.000 description 1
- 235000009419 Fagopyrum esculentum Nutrition 0.000 description 1
- 241000222336 Ganoderma Species 0.000 description 1
- 241000234321 Heliconia Species 0.000 description 1
- 241000169101 Hyacinthaceae Species 0.000 description 1
- 240000000249 Morus alba Species 0.000 description 1
- 235000008708 Morus alba Nutrition 0.000 description 1
- 235000000139 Musa basjoo Nutrition 0.000 description 1
- 240000000569 Musa basjoo Species 0.000 description 1
- 241000209504 Poaceae Species 0.000 description 1
- 241000589180 Rhizobium Species 0.000 description 1
- 241000681978 Rhododendron japonicum Species 0.000 description 1
- 235000005247 Rumex japonicus Nutrition 0.000 description 1
- 244000189123 Rumex japonicus Species 0.000 description 1
- 244000061456 Solanum tuberosum Species 0.000 description 1
- 235000002595 Solanum tuberosum Nutrition 0.000 description 1
- 241000234267 Strelitzia Species 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- BJEPYKJPYRNKOW-UHFFFAOYSA-N alpha-hydroxysuccinic acid Natural products OC(=O)C(O)CC(O)=O BJEPYKJPYRNKOW-UHFFFAOYSA-N 0.000 description 1
- 238000009412 basement excavation Methods 0.000 description 1
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000002738 chelating agent Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- IRXRGVFLQOSHOH-UHFFFAOYSA-L dipotassium;oxalate Chemical compound [K+].[K+].[O-]C(=O)C([O-])=O IRXRGVFLQOSHOH-UHFFFAOYSA-L 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 229930182470 glycoside Natural products 0.000 description 1
- -1 glycoside compound Chemical class 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 229940046892 lead acetate Drugs 0.000 description 1
- RLJMLMKIBZAXJO-UHFFFAOYSA-N lead nitrate Chemical compound [O-][N+](=O)O[Pb]O[N+]([O-])=O RLJMLMKIBZAXJO-UHFFFAOYSA-N 0.000 description 1
- 239000001630 malic acid Substances 0.000 description 1
- 235000011090 malic acid Nutrition 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- JMTCDHVHZSGGJA-UHFFFAOYSA-M potassium hydrogenoxalate Chemical compound [K+].OC(=O)C([O-])=O JMTCDHVHZSGGJA-UHFFFAOYSA-M 0.000 description 1
- 235000012015 potatoes Nutrition 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- ZNCPFRVNHGOPAG-UHFFFAOYSA-L sodium oxalate Chemical compound [Na+].[Na+].[O-]C(=O)C([O-])=O ZNCPFRVNHGOPAG-UHFFFAOYSA-L 0.000 description 1
- 229940039790 sodium oxalate Drugs 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 230000007928 solubilization Effects 0.000 description 1
- 238000005063 solubilization Methods 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
- Cultivation Of Plants (AREA)
Abstract
Description
本発明は、植物によって重金属によって汚染された土壌の浄化を図る手法(ファイトレメディエーション)の内、特に鉛によって汚染された土壌の浄化を図る鉛汚染土壌の浄化方法に関する。 The present invention relates to a method for purifying lead-contaminated soil, particularly for purifying soil contaminated with lead, among methods (phytoremediation) for purifying soil contaminated with heavy metals by plants.
近年、経済的及び環境に対する負荷などの問題から、新たな土壌汚染浄化技術として、重金属によって汚染された土壌に重金属を吸収・蓄積する植物を生育させ、この植物を収穫・除去することにより環境中の重金属を除去しようとする手法(ファイトレメディエーション)が注目されている。 In recent years, due to problems such as economic and environmental burdens, as a new soil contamination purification technology, plants that absorb and accumulate heavy metals in soil contaminated by heavy metals are grown, and these plants are harvested and removed to the environment. The technique (Phytoremediation) that attempts to remove heavy metals is attracting attention.
例えば、下記特許文献に示される各種のファイトレメディエーションが提案されている。 For example, various phytoremediations shown in the following patent documents have been proposed.
下記特許文献1では、アオイ科フヨウ属に属する植物を重金属によって汚染された媒体上で栽培し、該重金属を吸収・蓄積させた後、該植物を収穫する浄化方法が提案されている。 Patent Document 1 below proposes a purification method for cultivating a plant belonging to the genus Hyacinthaceae on a medium contaminated with heavy metals, absorbing and accumulating the heavy metals, and then harvesting the plants.
下記特許文献2では、アカザ科アカザ属、アカザ科ホウレンソウ属、アカザ科タヌキマメ属に属する植物を重金属によって汚染された媒体上で栽培し、該重金属を吸収・蓄積させた後、該植物を収穫する浄化方法が提案されている。 In the following Patent Document 2, a plant belonging to the genus Akaza, Azaza, spinach, and Rhizobium is cultivated on a medium contaminated with heavy metals, and after the heavy metals are absorbed and accumulated, the plants are harvested. A purification method has been proposed.
下記特許文献3では、アオイ科トロロアオイ属に属する植物を重金属によって汚染された媒体上で栽培し、該重金属を吸収・蓄積させた後、該植物を収穫する浄化方法が提案されている。 Patent Document 3 below proposes a purification method for cultivating a plant belonging to the genus Trolloaoi on a medium contaminated with heavy metals, absorbing and accumulating the heavy metals, and then harvesting the plants.
下記特許文献4では、土壌中の重金属を植物に吸収させ、該植物体内に蓄積させることにより、土壌を浄化する方法において、土壌中にL−グルタミン酸2酢酸を共存させるようにした土壌の浄化方法が提案されている。 In the following Patent Document 4, a soil purification method in which L-glutamic acid diacetic acid is allowed to coexist in the soil in a method for purifying the soil by absorbing heavy metals in the soil and accumulating them in the plant body. Has been proposed.
下記特許文献5では、重金属類含有土壌に、重金属類を吸収する能力を有し、生育特性が異なる少なくとも2種類以上の植物を組み合わせて植栽するようにした重金属類含有土壌の浄化方法が提案されている。 In the following Patent Document 5, a method for purifying heavy metal-containing soil is proposed in which heavy metal-containing soil is planted in combination with at least two kinds of plants having the ability to absorb heavy metals and having different growth characteristics. Has been.
さらに、下記特許文献6では、カドミウム等の金属類で汚染された土壌に配糖体系化合物型植物(アオキ類、タデ類、ソバ類、センブリ類)又はその他の化合物型植物(アシ類、シダ類、ヘビノネゴザ類、ススキ類)を栽培し、ある程度生育した後、上記植物を上記土壌より採取除去処理することにより、土壌中の重金属類を除去する汚染土壌の浄化方法が提案されている。
ところで、近年射撃場における鉛汚染が社会的な問題となっている。飛散した鉛散弾の鉛分が溶出し土壌汚染を引き起こしているとともに、この鉛成分が河川に流出し、生活水を汚染する問題が深刻化しており、射撃場の一部では鉛撤去のために一時閉鎖が相次いでいる。 By the way, in recent years, lead contamination in shooting ranges has become a social problem. The lead content of the scattered lead shots eluted and caused soil contamination, and this lead component leaked into the river and the problem of contaminating living water became serious, and in some shooting ranges, lead removal There are many temporary closures.
鉛を除去する方法としては、例えば汚染された土壌部分を掘削し、客土によって埋立する方法(客土埋立法)、セメント系固化材により地盤を固化し鉛成分を固形化する方法(地盤改良法)、微生物を用いたバイオレメディエーションなどが採用されている。 As a method for removing lead, for example, excavating contaminated soil and landfilling with soil (customer land reclamation method), solidifying the ground with cement-based solidification material and solidifying the lead component (soil improvement) Method), bioremediation using microorganisms, etc. are employed.
しかし、前記客土埋立法の場合には、掘削及び埋立に多くの時間と手間が掛かる。前記地盤改良法の場合には、土壌環境が大きく変化するとともに、改良工事に膨大な費用と時間が掛かるなどの問題があった。さらに、微生物を用いたバイオレメディエーションの場合には、微生物の管理が困難であるとともに、鉛除去に対して実効性が小さいなどの問題があった。 However, in the case of the above-mentioned landfill method, it takes a lot of time and labor for excavation and landfill. In the case of the ground improvement method, there are problems that the soil environment changes greatly and the improvement work takes enormous costs and time. Furthermore, in the case of bioremediation using microorganisms, there are problems such as difficulty in managing microorganisms and low effectiveness in removing lead.
一方、上記植物によって重金属類による汚染土壌の浄化を図るファイトレメディエーションの場合には、経済的及び環境に対する負荷が少ないなどの理由によって有望視できるものの、上記特許文献1〜6に開示された各ファイトレメディエーションは、主としてカドミウムや亜鉛などの重金属類を主たる対象とするものであり、特に除去対象を鉛とするものではなく、鉛に対してはその除去効果が小さいなどの問題があった。例えば、重金属類の浄化に利用される植物種としては、イネ科、キク科、マメ科などの植物が多いが、これらの植物種では鉛の吸収・蓄積は見られない。 On the other hand, in the case of phytoremediation for purifying contaminated soil with heavy metals by the plant, each of the methods disclosed in Patent Documents 1 to 6 can be considered promising for reasons such as low economic and environmental burdens. Phytoremediation is mainly intended for heavy metals such as cadmium and zinc. In particular, phytoremediation is not intended for removal of lead, and there is a problem that its removal effect is small for lead. For example, many plant species such as Gramineae, Asteraceae, and Leguminosae are used for purification of heavy metals, but lead absorption and accumulation are not observed in these plant species.
鉛は、重金属元素の中でも原子量が大きく、重金属類の中で特に重い元素であり、通常の土環境条件(物理的・化学的条件)下では、水に溶解し難い化学的特性を有する。鉛化合物で水に溶け易い塩は、硝酸鉛(Pb(NO3)2)と酢酸鉛(Pb(CH3COO)2)のみである。植物による重金属の浄化では、まず溶解性の形態に変化させ、根から吸収させることが重要であるが、鉛を対象とした場合には、前記のような化学特性から、植物根から吸収され難く、鉛を選択的にかつ効果的に吸収する植物は確認されていなかった。 Lead has a large atomic weight among heavy metal elements and is a particularly heavy element among heavy metals, and has chemical characteristics that are difficult to dissolve in water under normal soil environmental conditions (physical and chemical conditions). The only lead-soluble salts that are soluble in water are lead nitrate (Pb (NO 3 ) 2 ) and lead acetate (Pb (CH 3 COO) 2 ). In the purification of heavy metals by plants, it is important to first change to a soluble form and absorb from the roots. However, when lead is the target, it is difficult to absorb from the plant roots due to the above chemical characteristics. No plant has been identified that selectively and effectively absorbs lead.
他方で、重金属類を植物に効果的に吸収・蓄積させるために、EDTAやクエン酸などの薬剤を溶化促進剤として土壌に混合することも行われている(上記非特許文献7、8参照)。しかしながら、これらの薬剤を土壌中に人工的に混合することは、EDTAの土壌中における生分解性が遅いため、永く土壌中に残存する虞があるとともに、他の陽イオン類と強く結合し、土壌が本来持つ機能を破壊したり、特性を変化させてしまう虞がある。また、キレート剤の散布によって鉛溶出量が数十倍になるため、排水処理を誤ると、かえって鉛汚染を拡散させる虞があるなどの問題があった。 On the other hand, in order to effectively absorb and accumulate heavy metals in plants, it is also performed to mix a chemical such as EDTA or citric acid into soil as a solubilization accelerator (see Non-Patent Documents 7 and 8 above). . However, artificially mixing these drugs into the soil, because EDTA has a slow biodegradability in the soil, it may remain in the soil for a long time and binds strongly to other cations, There is a risk of destroying the inherent function of the soil or changing its properties. In addition, since the amount of lead elution is increased several tens of times by spreading the chelating agent, there is a problem that lead contamination may be diffused if the wastewater treatment is mistaken.
そこで本発明の主たる課題は、除去対象を鉛及びその化合物に限定し、特定の植物種を利用することによって格段の鉛除去効果が得られるようにするとともに、周辺環境の二次汚染を招くことが無い鉛汚染土壌の浄化方法を提供することにある。 Therefore, the main problem of the present invention is to limit the removal target to lead and its compounds, and to obtain a remarkable lead removal effect by using a specific plant species, and to cause secondary contamination of the surrounding environment. The object is to provide a method for remediating lead-contaminated soil that is free from waste.
前記課題を解決するために本発明者等は鋭意研究を行った結果、シュウ酸を多く含有する植物種、具体的には、タデ科、カタバミ科、アカザ科、サトイモ科、シュウカイドウ科、バショウ科の植物は、根から分泌されるシュウ酸等の有機酸によって鉛を溶化し、効果的に根から吸収することができるとの知見を得るに至った。本発明はこの知見に基づくものである。 In order to solve the above-mentioned problems, the present inventors have conducted intensive research. As a result, plant species containing a large amount of oxalic acid, specifically, aceae, oxaceae, akazaceae, taroceae, euphorbiaceae, and salmonaceae The plant has obtained the knowledge that lead can be solubilized by organic acids such as oxalic acid secreted from the roots and effectively absorbed from the roots. The present invention is based on this finding.
その結果、請求項1に係る本発明として、鉛及び/又はその化合物によって汚染された土壌に、シュウ酸を多く含有する植物種を播種、或いは幼苗を移植することにより栽培し、前記シュウ酸を多く含有する植物種に鉛及び/又は化合物を吸収・蓄積させた後、収穫・除去することを特徴とする鉛汚染土壌の浄化方法が提供される。 As a result, the present invention according to claim 1 is cultivated by sowing a plant species containing a large amount of oxalic acid in a soil contaminated with lead and / or a compound thereof, or transplanting young seedlings, Provided is a method for remediating lead-contaminated soil, characterized by absorbing and accumulating lead and / or compounds in a plant species containing a large amount and then harvesting and removing it.
請求項2に係る本発明として、前記シュウ酸を多く含有する植物として、タデ科、カタバミ科、アカザ科、サトイモ科、シュウカイドウ科、バショウ科の植物のいずれかを又は組み合わせて用いる請求項1記載の鉛汚染土壌の浄化方法が提供される。 As the present invention according to claim 2, as the plant containing a large amount of oxalic acid, any one of a plant belonging to the family Taceae, Oleaceae, Rubiaceae, Taroceae, Scalyceae, Ganoderma is used in combination. A method for remediating lead-contaminated soil is provided.
以上詳説のとおり本発明によれば、シュウ酸を多く含有する植物種を利用し、ファイトレメディエーションを行うため、土壌中の鉛成分を効果的に根から吸収し、土壌から除去することが可能となる。 As described above in detail, according to the present invention, phytoremediation is performed using a plant species containing a large amount of oxalic acid, so that the lead component in the soil can be effectively absorbed from the root and removed from the soil. It becomes.
以下、本発明の実施の形態について詳述する。 Hereinafter, embodiments of the present invention will be described in detail.
本鉛汚染土壌の浄化方法は、鉛及び/又はその化合物によって汚染された土壌に、シュウ酸を多く含有する植物種(以下、シュウ酸高含有植物という。)を播種、或いは幼苗を移植することにより栽培し、前記シュウ酸を多く含有する植物種に鉛及び/又は化合物を吸収・蓄積させた後、収穫・取除去するものである。 In this method of remediating lead-contaminated soil, sowing a plant species containing a large amount of oxalic acid (hereinafter referred to as a plant containing a high amount of oxalic acid) or transplanting a young seedling into soil contaminated with lead and / or a compound thereof. The plant species containing a large amount of oxalic acid is cultivated in accordance with the above, and after the lead and / or compound is absorbed and accumulated, it is harvested and removed.
前記シュウ酸高含有植物としては、イヌタデ、イタドリ、ギシギシに代表されるタデ科植物、カタバミに代表されるカタバミ科植物、シロザ、ホウレンソウなどに代表されるアカザ科植物、サトイモ、クワズイモなどに代表されるサトイモ科植物、ベゴニア、木立ベゴニア、ヨウラクソウ、センパフローレンスなどに代表されるシュウカイドウ科植物、ストレリチア、ヘリコニア、バショウ、ヒメバショウ、オオギバショウなどに代表されるバショウ科植物のいずれか又は組み合わせて用いることができる。前記カタバミ科(Oxalidaceae)、タデ科(Polygonaceae)の植物は、全草に可溶性シュウ酸カリウム(シュウ酸水素カリウム KHC2O4)を10%程度、或いはそれ以上含有している。また、アカザ科(Chenopodiaceae)の植物には可溶性のシュウ酸(シュウ酸ナトリウム(CO2Na)2)が10%以上含有されている。 Examples of the high oxalic acid-containing plants include podaceae plants represented by Inuta, Itadori, Gishigishi, oxalis plants represented by Oxalis, red crustaceae plants represented by Shiroza, spinach, taros, mulberry potatoes, etc. Can be used in combination with any one or a combination of the taroaceae plants, begonia, grove begonia, euphorbia, sempaflorences, and the like, or strelitzia, heliconia, basho, himebasho, ogibasho, etc. it can. The plant of the family Oxalidaceae and Polygonaceae contains about 10% or more of soluble potassium oxalate (potassium hydrogen oxalate KHC 2 O 4 ) in the whole plant. In addition, plants of the genus Chenopodiaceae contain 10% or more of soluble oxalic acid (sodium oxalate (CO 2 Na) 2 ).
適用対象となる土壌は、鉛及び/又はその化合物によって汚染された土壌、具体的には射撃場などである。 The soil to be applied is soil contaminated with lead and / or a compound thereof, specifically a shooting range.
シュウ酸や各種の有機酸(クエン酸、リンゴ酸など)は、植物根から分泌されることは一般に知られており、これらの有機酸類は、いずれも分子構造中にカルボキシル基を有するものである。 Oxalic acid and various organic acids (citric acid, malic acid, etc.) are generally known to be secreted from plant roots, and these organic acids all have a carboxyl group in the molecular structure. .
本発明では、シュウ酸高含有植物から分泌されるシュウ酸によって鉛及び/又はその化合物が水溶性の形態となり、植物根から吸収し体内に蓄積されることで、土壌中の鉛及び/又はその化合物が土壌中から除去される。 In the present invention, lead and / or a compound thereof is made into a water-soluble form by oxalic acid secreted from a plant containing a high amount of oxalic acid, and is absorbed from the plant root and accumulated in the body. Compounds are removed from the soil.
前述したシュウ酸高含有植物を鉛及び/又はその化合物を吸収するのに適した期間で栽培し、茎及び葉を含む植物の地上部ないし根を含む地下根を適当な方法で採取する。採取方法としては、例えば地上部のみを刈り取り、再び生育したら刈り取る繰り返しによって採取する方法、植物の地上部と地下根とを一緒に刈り取る方法など任意である。 The above-mentioned oxalic acid-rich plant is cultivated for a period suitable for absorbing lead and / or its compounds, and the above-ground part of the plant including the stem and leaves or the underground root including the root is collected by an appropriate method. As a collection method, for example, a method of cutting only the above-ground part, and a method of collecting by repeatedly cutting when growing again, a method of cutting together the above-ground part of the plant and the underground root are arbitrary.
刈り取った植物は、焼却、粉砕、融解処理等で処理した後、鉛を回収したり、その焼却灰は例えばコンクリート又は樹脂等により固化封入し無害化することができる。 The harvested plant is treated by incineration, pulverization, melting treatment, etc., and then lead is collected, or the incineration ash can be solidified and sealed with, for example, concrete or resin to make it harmless.
一時閉鎖した某射撃場を借用し、土壌中の鉛含有量が比較的一定しているフィールドを選定し、本発明に係る浄化方法で用いられる植物種として、イヌタデ(タデ科植物)、イタドリ(タデ科植物)、ギシギシ(タデ科植物)、カタバミ(カタバミ科植物)、シロザ(アカザ科植物)の5種を生育するとともに、比較例として、下表1に示す植物群を生育し、6ヶ月後に地上部及び地下根を一緒に収穫し、その鉛含有量を調べた。 By borrowing the temporarily closed dredging range, selecting a field where the lead content in the soil is relatively constant, plant species used in the purification method according to the present invention are the Japanese azalea (Turaceae), Itadori ( The plant group shown in Table 1 below is grown as a comparative example for 6 months, while the plant grows 5 species of (Taceae plant), Shigegi (Tapaceae plant), Oxalis (Oxaeaceae plant), and Shiroza (Acariaceae plant). Later, the aerial part and the underground root were harvested together and their lead content was examined.
上記表1の結果より、本発明で使用されるシュウ酸高含有植物種の場合には、鉛の吸収・蓄積能力が他の植物と比較すると格段に高いことが判明した。 From the results of Table 1 above, it was found that the high oxalic acid content plant species used in the present invention has a significantly higher lead absorption / accumulation ability than other plants.
Claims (2)
The method for purifying lead-contaminated soil according to claim 1, wherein the plant containing a large amount of oxalic acid is any one of or a combination of a plant belonging to the family Taceae, Oleaceae, Rubiaceae, Taroceae, Scalyceae, and Glyceae.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2005066610A JP4431072B2 (en) | 2004-03-17 | 2005-03-10 | Purification method for lead-contaminated soil |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2004075765 | 2004-03-17 | ||
JP2005066610A JP4431072B2 (en) | 2004-03-17 | 2005-03-10 | Purification method for lead-contaminated soil |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2005296941A true JP2005296941A (en) | 2005-10-27 |
JP4431072B2 JP4431072B2 (en) | 2010-03-10 |
Family
ID=35329128
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2005066610A Active JP4431072B2 (en) | 2004-03-17 | 2005-03-10 | Purification method for lead-contaminated soil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP4431072B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008043221A (en) * | 2006-08-11 | 2008-02-28 | Taisei Corp | Greening base material, greening structure and greening method |
CN100457300C (en) * | 2006-07-27 | 2009-02-04 | 云南省环境科学研究院 | Method for repairing lead polluted soil using super enriching plant Tephrosia candida |
CN103949465A (en) * | 2014-05-07 | 2014-07-30 | 湖南省林业科学院 | Application of peruvian groundcherry herb in repairing heavy metal lead polluted soil |
JP2014172026A (en) * | 2013-03-13 | 2014-09-22 | Bio System Consulting:Kk | Heavy metal removal/recovery method |
-
2005
- 2005-03-10 JP JP2005066610A patent/JP4431072B2/en active Active
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100457300C (en) * | 2006-07-27 | 2009-02-04 | 云南省环境科学研究院 | Method for repairing lead polluted soil using super enriching plant Tephrosia candida |
JP2008043221A (en) * | 2006-08-11 | 2008-02-28 | Taisei Corp | Greening base material, greening structure and greening method |
JP2014172026A (en) * | 2013-03-13 | 2014-09-22 | Bio System Consulting:Kk | Heavy metal removal/recovery method |
CN103949465A (en) * | 2014-05-07 | 2014-07-30 | 湖南省林业科学院 | Application of peruvian groundcherry herb in repairing heavy metal lead polluted soil |
Also Published As
Publication number | Publication date |
---|---|
JP4431072B2 (en) | 2010-03-10 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Robinson et al. | The potential of the high-biomass nickel hyperaccumulator Berkheya coddii for phytoremediation and phytomining | |
JP5021861B2 (en) | How to remove pollutants from contaminated soil using fern plants | |
CN102372406B (en) | Heavy-metal-polluted substrate sludge ex-situ repairing method | |
JP4898085B2 (en) | Method for removing contaminants from contaminated media | |
JP4431072B2 (en) | Purification method for lead-contaminated soil | |
Chantachon et al. | Phytoextraction and accumulation of lead from contaminated soil by vetiver grass: laboratory and simulated field study | |
WO2010130730A1 (en) | Use of cistus libanotis to clean heavy metals containing soils | |
WO2005087399A1 (en) | Method of cleaning up lead-contaminated soil | |
Soto Carrión et al. | Potential phytoremediator of native species in soils contaminated by heavy metals in the garbage dump Quitasol-Imponeda Abancay | |
CN102310074A (en) | Method for repairing cadmium polluted soil by compositae plants | |
JP2007203146A (en) | Purification method of medium polluted by heavy metal | |
JP2008296181A (en) | Purification method of harmful heavy metal polluted medium | |
Comis | Metal-scavenging plants to cleanse the soil | |
CN105032907A (en) | Method of combinedly-reinforced repairing pyrene-and-lead combinedly-polluted soil with scripus triqueter | |
Lam et al. | Mine tailings phytoremediation in arid and semiarid environments | |
JP5216967B2 (en) | Method for purifying media contaminated with heavy metals | |
Aremu et al. | Phytoextraction potential of Vetiveria zizanioides on heavy metals | |
Ranjan et al. | Remediation Measures for Arsenic Pollution of Soil | |
Truong | Research and development of the Vetiver system for treatment of polluted water and contaminated land | |
Sigua et al. | Enhancing cleanup of heavy metal polluted landfill soils and improving soil microbial activity using green technology with ferrous sulfate | |
JP2010193882A (en) | Cultivation member for heavy metal hyperaccumulator plant and method of recovering heavy metal | |
US7069690B2 (en) | Compositions and methods for removing pollutants from contaminated wafer with a fern plant | |
Indelicato | The Use of Plants and Wildflowers as Bioremediation for Contaminated Soils in the Hong Kong SAR | |
JP2006102689A (en) | Cleaning method for contaminated medium | |
CN108941182A (en) | A kind of heavy metals in farmland pollution amelioration agent and restorative procedure |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20050701 |
|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20070314 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20090525 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20090528 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20090717 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20090807 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20091005 |
|
TRDD | Decision of grant or rejection written | ||
RD03 | Notification of appointment of power of attorney |
Free format text: JAPANESE INTERMEDIATE CODE: A7423 Effective date: 20091020 |
|
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20091215 |
|
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20091218 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20121225 Year of fee payment: 3 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 4431072 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |