JP2011072941A - Method for deciding state of soil - Google Patents

Method for deciding state of soil Download PDF

Info

Publication number
JP2011072941A
JP2011072941A JP2009228347A JP2009228347A JP2011072941A JP 2011072941 A JP2011072941 A JP 2011072941A JP 2009228347 A JP2009228347 A JP 2009228347A JP 2009228347 A JP2009228347 A JP 2009228347A JP 2011072941 A JP2011072941 A JP 2011072941A
Authority
JP
Japan
Prior art keywords
soil
plant
data
evaluation
evaluation target
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
JP2009228347A
Other languages
Japanese (ja)
Inventor
Satoshi Naito
敏 内藤
Nobuyuki Kadokura
伸行 門倉
Akihiko Horikawa
朗彦 堀川
Tomoki Yamamoto
知己 山本
Shiro Wakui
史郎 涌井
Kentaro Iijima
健太郎 飯島
Shigeo Morinaga
茂生 森永
Yuichi Sugano
菅野  裕一
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kumagai Gumi Co Ltd
Original Assignee
Kumagai Gumi Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kumagai Gumi Co Ltd filed Critical Kumagai Gumi Co Ltd
Priority to JP2009228347A priority Critical patent/JP2011072941A/en
Publication of JP2011072941A publication Critical patent/JP2011072941A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for deciding the state of soil which can alleviate the mental feeling of dislike of land owners of ground after cleaning, or neighboring residents by embodying in the actual fields whether the ground after cleaning is true cleaned or not by using plant. <P>SOLUTION: Soil 50 for evaluation under cleaning treatment, or plant 51 is planted in the soil 50 for evaluation under cleaning treatment is used as a sensor for deciding purifying effect of the soil 50 for evaluation. data of the plant concerned extracted after planting the plant 51 in the soil which is not polluted is taken as a sample data, data of the plant 51 concerned extracted after planting the plant 51 in the soil 50 for evaluation is taken for a soil evaluation data, the soil evaluation data and the sample data concerned are compared, and if close to each other, the soil 50 is decided to be purified. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、植物を利用した土壌の状態判定方法に関する。   The present invention relates to a soil state determination method using plants.

従来、例えば、汚染土壌に油を分解する微生物を供給することによって汚染土壌を浄化する方法が提案されている(例えば、特許文献1,2参照)。   Conventionally, for example, methods for purifying contaminated soil by supplying microorganisms that decompose oil to the contaminated soil have been proposed (see, for example, Patent Documents 1 and 2).

特開平9−276837号公報Japanese Patent Laid-Open No. 9-276837 特開平9−276840号公報JP-A-9-276840

汚染土壌を浄化する処理を行った後に、浄化の効果を確かめる方法としては、その浄化後の土壌の成分を調査することが一般的である。しかしながら、成分調査の場合、100m(10m×10m)に1地点の割合で土壌を採取し、その分析数値データによる証明だけであり、浄化処理を行った土地が本当に浄化されているのかどうかを当該現場で具現化する物体がなかったので、浄化処理を行った土地の地権者や近隣住民としては、本当に浄化されているのかどうか確信を得られない心理的な状況(心理的な嫌悪感)を払拭できないことが多いという問題点があった。
本発明は上記問題点に鑑みてなされたもので、浄化処理を行った土地が本当に浄化されているのかどうかを植物を用いて当該現場で具現化することにより、浄化処理を行った土地の地権者や近隣住民の心理的な嫌悪感を軽減可能な土壌の状態判定方法を提供することを目的とする。
As a method for confirming the effect of purification after the treatment for purifying the contaminated soil, it is common to investigate the components of the soil after the purification. However, in the case of component survey, soil is sampled at a rate of 100m 2 (10m × 10m), and it is only proof by the numerical analysis data, and whether the land that has undergone the purification process is really purified or not. Psychological situation (psychological disgust) in which there is no object to embody at the site, and as landowners and neighbors of the land that has undergone purification treatment, it is not possible to be sure whether it is really being purified. There was a problem that it was often impossible to wipe out.
The present invention has been made in view of the above-mentioned problems. By embodying whether or not the land subjected to the purification treatment is really purified at the site using the plant, the land right of the land subjected to the purification treatment is obtained. The purpose is to provide a soil condition determination method that can reduce the psychological disgust of the elderly and the neighboring residents.

本発明に係る土壌の状態判定方法は、浄化処理中の評価対象土壌、又は、浄化処理後の評価対象土壌に植物を植え、当該植物を当該評価対象土壌の浄化効果を判定するためのセンサーとして用いるので、浄化処理を行った土地が浄化されていることを植物によって当該現場で具現化できるので、浄化処理を行った土地の地権者や近隣住民の心理的な嫌悪感を軽減できる。
汚染されていない土壌に植物を植えた後に採取した当該植物のデータをサンプルデータとし、上記評価対象土壌に植物を植えた後に採取した当該植物のデータを土壌評価データとし、当該土壌評価データとサンプルデータとを比較し、近似していれば上記評価対象土壌が浄化されていると判定するので、浄化処理を行った土地が浄化されていることを植物によって当該現場で具現化できるとともに、データによっても裏付けできるので、浄化処理を行った土地の地権者や近隣住民の心理的な嫌悪感を軽減できる。
The soil state determination method according to the present invention is a sensor for determining a purification effect of the evaluation target soil by planting a plant in the evaluation target soil during the purification process or the evaluation target soil after the purification process. Since it uses, it can embody in the said field that the land which performed the purification process is purified by the said plant, Therefore The psychological disgust of the landowner of the land which performed the purification process, and a neighboring inhabitant can be reduced.
The data of the plant collected after planting the plant on uncontaminated soil is used as sample data, the data of the plant collected after planting the plant on the evaluation target soil is used as soil evaluation data, the soil evaluation data and the sample If the data is compared and approximated, it is determined that the evaluation target soil has been purified. Therefore, it is possible to embody the fact that the land subjected to the purification treatment has been purified by the plant, and the data Can also help to reduce the psychological disgust of landowners and neighbors of the land that has undergone the purification process.

当該評価対象土壌に植物を植えた状態を示す図。The figure which shows the state which planted the plant in the said evaluation object soil. サンプルデータを採取するための実験装置の平面図。The top view of the experimental apparatus for extract | collecting sample data. サンプルデータを採取するための実験装置の断面図。Sectional drawing of the experimental apparatus for extract | collecting sample data. 植物育成部の拡大断面図。The expanded sectional view of a plant growth part.

実施形態では、図1に示すように、浄化処理中の評価対象土壌50、又は、浄化処理後の評価対象土壌50に植物51を植え、当該植物51を当該評価対象土壌50の浄化効果を判定するためのセンサーとして用いる。
例えば、病院や工場等の土壌汚染源となっていた建物を解体した後の跡地の汚染土壌を浄化処理中に当該浄化処理中の評価対象土壌50に植物51を植えたり、上記汚染土壌を浄化処理した後の評価対象土壌50に植物51を植える。
植物51としては、土壌を汚染する土壌汚染物質に反応する植物51を用いる。例えば、土壌汚染物質に反応する植物51としては、土壌汚染物質としての油(重油など)に反応する植物51、土壌汚染物質としての水銀に反応する植物51、土壌汚染物質としての鉛に反応する植物51等を用いる。
土壌汚染物質に反応する植物51とは、土壌汚染物質に汚染された土壌に植えられた場合と、土壌汚染物質に汚染されていない土壌に植えられた場合とで、生育状態に差が表れる植物51を言う。例えば、葉や茎の彩度、色具合、植物51の温度、葉の形態などの生育状態に差が表れる植物51である。
In the embodiment, as shown in FIG. 1, a plant 51 is planted in the evaluation target soil 50 during the purification process or the evaluation target soil 50 after the purification process, and the purification effect of the evaluation target soil 50 is determined for the plant 51. It is used as a sensor for
For example, the plant 51 is planted in the evaluation target soil 50 during the purification process or the contaminated soil is purified during the purification process of the contaminated soil in the former site after dismantling a building that has become a soil contamination source such as a hospital or factory. The plant 51 is planted in the soil 50 to be evaluated after the evaluation.
As the plant 51, a plant 51 that reacts with a soil pollutant that contaminates the soil is used. For example, as the plant 51 that reacts with soil pollutants, the plant 51 reacts with oil (such as heavy oil) as soil pollutants, the plant 51 reacts with mercury as soil pollutants, and the lead as soil pollutants. Plant 51 etc. are used.
The plant 51 that reacts to soil pollutants is a plant that shows a difference in growth state between when planted in soil contaminated with soil pollutants and when planted in soil not contaminated with soil pollutants. Say 51. For example, the plant 51 shows a difference in the growth state such as the saturation and color of the leaves and stems, the temperature of the plant 51, and the leaf form.

上述した評価対象土壌50に植物51を植えて、当該植物51の生育変化を観察することにより当該評価対象土壌50の状態を判定する。判定は、サンプルデータと、観察データとを比較して行う。   A plant 51 is planted in the evaluation target soil 50 described above, and the state of the evaluation target soil 50 is determined by observing a growth change of the plant 51. The determination is made by comparing the sample data with the observation data.

図2を参照し、サンプルデータを採取するための実験装置を説明する。実験装置1は、複数の植物育成部2を備える。植物育成部2(2A;2B;2C;2D;2E)は、領域を区画する領域区画材3と、領域区画材3で囲まれた領域に設けられた土壌4と、土壌4に植えられた植物51とにより構成した。領域は、底面6と領域区画材3とにより区画された縦寸法a=60cm、横寸法b=60cm、深さ寸法c=90cmの立方体領域に形成される。図4に示すように、土壌4は、底面6の上に設けられた吸着層7と、吸着層7の上に設けられた下側良質土層8と、下側良質土層8の上に設けられた汚染土層9と、汚染土層9の上に設けられた上側良質土層10とにより構成される。
吸着層7の深さ寸法7aは30cm、下側良質土層8の深さ寸法8aは10cm、汚染土層9の深さ寸法9aは30cm、上側良質土層10の深さ寸法10aは15cmとした。尚、後述するアガサを植える土壌は、吸着層7の深さ寸法7aを20cm、下側良質土層8の深さ寸法8aを10cm、汚染土層9の深さ寸法9aを100cm、上側良質土層10の深さ寸法10aを50cmとした。これは、植物の根系の深さの違いによりモニタリング出来る深度を使い分けることを目的としている。
An experimental apparatus for collecting sample data will be described with reference to FIG. The experimental apparatus 1 includes a plurality of plant growing units 2. The plant growing section 2 (2A; 2B; 2C; 2D; 2E) is planted in the area partition material 3 for partitioning the area, the soil 4 provided in the area surrounded by the area partition material 3, and the soil 4 The plant 51 is comprised. The region is formed in a cubic region having a vertical dimension a = 60 cm, a horizontal dimension b = 60 cm, and a depth dimension c = 90 cm partitioned by the bottom surface 6 and the region partition material 3. As shown in FIG. 4, the soil 4 is formed on the adsorption layer 7 provided on the bottom surface 6, the lower quality soil layer 8 provided on the adsorption layer 7, and the lower quality soil layer 8. It is comprised by the contaminated soil layer 9 provided and the upper quality soil layer 10 provided on the contaminated soil layer 9.
The depth dimension 7a of the adsorption layer 7 is 30 cm, the depth dimension 8a of the lower quality soil layer 8 is 10 cm, the depth dimension 9a of the contaminated soil layer 9 is 30 cm, and the depth dimension 10a of the upper quality soil layer 10 is 15 cm. did. The soil for planting Agatha, which will be described later, has a depth dimension 7a of the adsorption layer 7 of 20 cm, a depth dimension 8a of the lower quality soil layer 8 of 10 cm, a depth dimension 9a of the contaminated soil layer 9 of 100 cm, and an upper quality soil. The depth dimension 10a of the layer 10 was 50 cm. The purpose is to use different depths that can be monitored depending on the depth of the root system of the plant.

汚染物質として鉛を含有した鉛汚染土層を備えた植物育成部2A、汚染物質として水銀を含有した水銀汚染土層を備えた植物育成部2B、汚染物質として油を含有した油汚染土層を備えた植物育成部2C、汚染物質として鉛と水銀と油とを含有した混合汚染土層を備えた植物育成部2Dを作製した。また、比較用として、汚染物質を含有しない良質土層のみの植物育成部2Eを作製した。
鉛汚染土層や水銀汚染土層や混合汚染土層を備えた植物育成部2A,2B,2Dの吸着層7は、重金属類吸着剤+砂質土とにより作製した。油汚染土層を備えた植物育成部2Cの吸着層7は、油吸着剤+砂質土とにより作製した。吸着層7は、汚染物質がほかの領域に移動するのを防止する。
Plant growth part 2A with a lead-contaminated soil layer containing lead as a pollutant, Plant growth part 2B with a mercury-contaminated soil layer containing mercury as a pollutant, and an oil-contaminated soil layer containing oil as a pollutant A plant growing part 2C provided with a mixed contaminated soil layer containing lead, mercury and oil as pollutants was prepared. Moreover, the plant growth part 2E only for the quality soil layer which does not contain a pollutant was produced for the comparison.
The adsorption layer 7 of the plant growing parts 2A, 2B, 2D provided with a lead-contaminated soil layer, a mercury-contaminated soil layer, or a mixed-contaminated soil layer was prepared with a heavy metal adsorbent + sandy soil. The adsorption layer 7 of the plant growing part 2C provided with the oil-contaminated soil layer was produced by using an oil adsorbent + sandy soil. The adsorption layer 7 prevents contaminants from moving to other areas.

植物育成部2に植える供試植物52としては、エニシダ20、ハマボウフウ21、ハマゴボウ22、ヨモギ23、ミソソバ24、キショウブ25、アガサ26、三種混合芝27を用いた。
つまり、鉛汚染土層を備えた植物育成部2A、水銀汚染土層を備えた植物育成部2B、油汚染土層を備えた植物育成部2C、混合汚染土層を備えた植物育成部2D、良質土層のみの植物育成部2Eを、それぞれ、供試植物52の種類毎に用意し、異なる土層を備えた植物育成部2にそれぞれ同じ種類の供試植物52を植えて、土層の違いによって同じ植物の生育にどのような違いが出るかを目視観察、触感観察できるような実験装置1とした。
As a test plant 52 to be planted in the plant breeding unit 2, a fern 20, a scallop 21, a sagebrush 22, a mugwort 23, a buckwheat 24, a kishibu 25, an agusa 26, and a three-type mixed turf 27 were used.
That is, a plant growing unit 2A having a lead contaminated soil layer, a plant growing unit 2B having a mercury contaminated soil layer, a plant growing unit 2C having an oil contaminated soil layer, a plant growing unit 2D having a mixed contaminated soil layer, A plant growing section 2E having only a good soil layer is prepared for each type of the test plant 52, and the same type of the test plant 52 is planted in each plant growing section 2 having a different soil layer. The experimental apparatus 1 was configured to allow visual observation and tactile observation of the difference in the growth of the same plant due to the difference.

上記実験装置1の各植物育成部2に植えた供試植物52のデータ、例えば、目視観察データ、触感観察データ、測定データなどを定期的(例えば、1週間毎、1ヶ月毎)に採取してサンプルデータとする。
目視観察データは、葉の斑点の有無や茎の太さなどのように、目で観察できるデータである。
触感観察データは、葉や茎を手で触った場合の異物の有無などのように、手で触って観察できるデータである。
測定データは、例えば、植物の撮像画像を解析して得られる彩度、色度合等の植物の色データ、サーモグラフィにより測定した植物の温度データ、植物に流れる微弱電流データなどである。
Data of the test plant 52 planted in each plant growing part 2 of the experimental apparatus 1 such as visual observation data, tactile sensation observation data, measurement data, etc. are collected periodically (for example, every week, every month). Sample data.
The visual observation data is data that can be observed with eyes, such as the presence or absence of leaf spots or the thickness of a stem.
The tactile sensation observation data is data that can be observed by touching with a hand such as the presence or absence of a foreign object when a leaf or stem is touched with the hand.
The measurement data is, for example, plant color data such as saturation and chromaticity obtained by analyzing a captured image of the plant, temperature data of the plant measured by thermography, weak current data flowing through the plant, and the like.

そして、上述したような、病院や工場等の土壌汚染源となっていた建物を解体した後の跡地の汚染土壌を浄化処理中に当該浄化処理中の評価対象土壌50、又は、上記汚染土壌を浄化処理した後の評価対象土壌50に植物51を植え、当該植物51が生育する過程で得られるデータ、例えば、目視観察データ、触感観察データ、測定データなどを定期的(例えば、1週間毎、1ヶ月毎)に採取して土壌評価データとする。   Then, the soil 50 to be evaluated during the purification process or the contaminated soil is purified during the purification process of the contaminated soil in the former site after dismantling the building that has been a soil contamination source such as a hospital or a factory as described above. The plant 51 is planted in the evaluation target soil 50 after the treatment, and data obtained in the process of growing the plant 51, for example, visual observation data, tactile observation data, measurement data, etc. are periodically (for example, every week, 1 Collected every month) as soil evaluation data.

同一種類の植物51に関する土壌評価データとサンプルデータとを比較することで、評価対象土壌50を適切に評価できる。つまり、土壌評価データが良質土層のみの植物育成部2Eで育てた供試植物52から採取されたサンプルデータと似ていれば、評価対象土壌50の土壌は浄化されていると判断する。
即ち、植物51を上記評価対象土壌50の浄化効果を判定するためのセンサーとして用いることができるようになる。
By comparing the soil evaluation data regarding the same type of plant 51 and the sample data, the evaluation target soil 50 can be appropriately evaluated. That is, if the soil evaluation data is similar to the sample data collected from the test plant 52 grown in the plant growing unit 2E having only a good quality soil layer, it is determined that the soil of the evaluation target soil 50 has been purified.
That is, the plant 51 can be used as a sensor for determining the purification effect of the evaluation target soil 50.

例えば、病院や工場等の土壌汚染源となっていた建物を解体した後の跡地の土壌を浄化している途中、又は、浄化した後に、当該跡地を地権者に返却する場合に、当該跡地が浄化されていて安全であることを当該跡地の地権者や近隣住民に説明する際、評価対象土壌50としての当該跡地に植えた植物51の外観変化を地権者や近隣住民に定期的に見せ、当該外観変化と良質土層のみの植物育成部2Eで育てた供試植物52の外観変化とが似ていることを地権者や近隣住民に提示することにより、地権者や近隣住民は、当該跡地の浄化効果を、当該跡地が浄化されていることを具現化している植物51によって現場で現状確認できることから、地権者や近隣住民の心理的な嫌悪感が払拭されるようになる。   For example, when the soil of the former site after demolition of a building that was a source of soil contamination such as a hospital or factory is being purified, or after it has been purified, the former site is purified. When explaining to the landowners and neighbors of the site that they have been safe, the appearance change of the plant 51 planted in the site as the evaluation target soil 50 is regularly shown to the landowners and neighbors. By presenting to the landowner and neighbors that the appearance change is similar to the appearance change of the test plant 52 grown in the plant breeding unit 2E having only the high quality soil layer, the landowner and neighbors Since the present condition can be confirmed on site by the plant 51 that embodies that the site is being purified, the purification effect can be wiped away from the psychological disgust of landowners and neighboring residents.

そして、当該外観変化と良質土層のみの植物育成部2Eで育てた供試植物52の外観変化とが似ていることを地権者や近隣住民に提示することに加え、土壌評価データと良質土層のみの植物育成部2Eで育てた供試植物52から採取されたサンプルデータとが似ていることを提示することにより、浄化効果を、データによっても裏付けできるので、浄化処理を行った土地の地権者や近隣住民の心理的な嫌悪感をより軽減できるようになる。   In addition to presenting the landowner and neighboring residents that the change in appearance is similar to the change in appearance of the test plant 52 grown in the plant growing section 2E having only the high-quality soil layer, the soil evaluation data and the high-quality soil By showing that the sample data collected from the test plant 52 grown in the layer-only plant growing section 2E is similar, the purification effect can be supported by the data, so that This will reduce the psychological disgust of landowners and neighbors.

また、同一種類の植物51に関する土壌評価データと植物育成部2A〜2Dで育てた供試植物52から採取されたサンプルデータとが近似していれば、評価対象土壌50が浄化されていないと判定する。当該判定により、再び浄化処理を行うことによって、浄化処理を行った土地の地権者や近隣住民の心理的な嫌悪感を軽減できる。この場合、土壌評価データが、どのような汚染物質を含有する汚染土層を備えた植物育成部2A〜2Dで育てた供試植物52から採取されたサンプルデータと似ているのかを判定することで、当該評価対象土壌50にどのような汚染物質が残留しているのかを判断できる。当該評価対象土壌50の汚染物質がわかれば、その汚染物質を効果的に除去できる浄化方法を用いて当該評価対象土壌50を浄化できるようになる。   Moreover, if the soil evaluation data regarding the same kind of plant 51 and the sample data collected from the test plant 52 grown in the plant growing parts 2A to 2D are approximate, it is determined that the evaluation target soil 50 is not purified. To do. By performing the purification process again by this determination, it is possible to reduce the psychological disgust of the landowner and the neighboring residents of the land that has performed the purification process. In this case, it is determined whether the soil evaluation data is similar to the sample data collected from the test plant 52 grown in the plant breeding units 2A to 2D having the contaminated soil layer containing the pollutant. Thus, it is possible to determine what contaminants remain in the evaluation target soil 50. If the pollutant of the said evaluation object soil 50 is known, the said evaluation object soil 50 can be purified now using the purification method which can remove the contaminant effectively.

実施形態によれば、植物51を評価対象土壌50の浄化処理後の浄化効果を判定するためのセンサーとして用いることができるようになり、評価対象土壌50の関係者は、評価対象土壌50の浄化効果を、当該評価対象土壌50が浄化されていることを具現化している植物51によって現場で現状確認できることから、評価対象土壌50の関係者の心理的な嫌悪感が払拭されるようになる。   According to the embodiment, the plant 51 can be used as a sensor for determining the purification effect after the purification treatment of the evaluation target soil 50, and the person concerned with the evaluation target soil 50 purifies the evaluation target soil 50. Since the effect can be confirmed on the spot by the plant 51 that embodies that the evaluation target soil 50 has been purified, the psychological disgust of the parties concerned with the evaluation target soil 50 is eliminated.

実施形態によれば、評価対象土壌50の浄化が不完全な場合に、当該評価対象土壌50に残っている汚染物質を判断できるようになるので、その汚染物質を効果的に除去できる浄化方法を用いて当該評価対象土壌50を浄化できるようになる。   According to the embodiment, when the purification of the evaluation target soil 50 is incomplete, the contaminant remaining in the evaluation target soil 50 can be determined. Therefore, a purification method that can effectively remove the contaminant is provided. It becomes possible to purify the soil 50 to be evaluated.

尚、評価対象土壌50としての汚染土壌に上述した各種の植物51を植えて、当該各種の植物51の土壌評価データを記録し、当該土壌評価データと上記サンプルデータとを比較することで、当該汚染土壌の汚染物質を特定することも可能となるので、その汚染土壌の汚染物質を効果的に除去できる浄化方法を用いて汚染土壌を浄化できるようになる。   In addition, by planting the various plants 51 described above in the contaminated soil as the evaluation target soil 50, recording the soil evaluation data of the various plants 51, and comparing the soil evaluation data with the sample data, Since it becomes possible to identify the pollutant in the contaminated soil, the contaminated soil can be purified using a purification method capable of effectively removing the pollutant in the contaminated soil.

50 評価対象土壌、51 植物。   50 soil to be evaluated, 51 plants.

Claims (2)

浄化処理中の評価対象土壌、又は、浄化処理後の評価対象土壌に植物を植え、当該植物を当該評価対象土壌の浄化効果を判定するためのセンサーとして用いることを特徴とする土壌の状態判定方法。   A soil state determination method characterized in that a plant is planted in the evaluation target soil during the purification treatment or the evaluation target soil after the purification treatment, and the plant is used as a sensor for determining the purification effect of the evaluation target soil. . 汚染されていない土壌に植物を植えた後に採取した当該植物のデータをサンプルデータとし、上記評価対象土壌に植物を植えた後に採取した当該植物のデータを土壌評価データとし、当該土壌評価データとサンプルデータとを比較し、近似していれば上記評価対象土壌が浄化されていると判定することを特徴とする請求項1に記載の土壌の状態判定方法。   The data of the plant collected after planting the plant on uncontaminated soil is used as sample data, the data of the plant collected after planting the plant on the evaluation target soil is used as soil evaluation data, the soil evaluation data and the sample 2. The soil state determination method according to claim 1, wherein the evaluation target soil is determined to be purified if the data is compared and approximated.
JP2009228347A 2009-09-30 2009-09-30 Method for deciding state of soil Pending JP2011072941A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2009228347A JP2011072941A (en) 2009-09-30 2009-09-30 Method for deciding state of soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2009228347A JP2011072941A (en) 2009-09-30 2009-09-30 Method for deciding state of soil

Publications (1)

Publication Number Publication Date
JP2011072941A true JP2011072941A (en) 2011-04-14

Family

ID=44017514

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2009228347A Pending JP2011072941A (en) 2009-09-30 2009-09-30 Method for deciding state of soil

Country Status (1)

Country Link
JP (1) JP2011072941A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102150568A (en) * 2010-11-29 2011-08-17 中国科学院新疆生态与地理研究所 Method for confirming soil plant toxicity
CN106771057A (en) * 2016-11-30 2017-05-31 湖南城市学院 A kind of method based on Atrichum undulatum accurate detection Lead Pollution in Soil degree
US10086417B2 (en) 2014-05-05 2018-10-02 Agri-Tech Producers, Llc Combined remediation biomass and bio-product production process
CN113182339A (en) * 2021-05-12 2021-07-30 谢非 Farmland is administered and is used novel soil treatment system
KR20230053867A (en) * 2021-10-15 2023-04-24 한국과학기술연구원 Method for analyzing soil contaminated by pollutants

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10123124A (en) * 1996-10-18 1998-05-15 Sumitomo Forestry Co Ltd Method for judging quality of earth generated from filtration plant used for plant-rearing culture medium
WO2007139100A1 (en) * 2006-05-29 2007-12-06 National University Corporation Hokkaido University Method of examining soil pollution and/or water pollution

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10123124A (en) * 1996-10-18 1998-05-15 Sumitomo Forestry Co Ltd Method for judging quality of earth generated from filtration plant used for plant-rearing culture medium
WO2007139100A1 (en) * 2006-05-29 2007-12-06 National University Corporation Hokkaido University Method of examining soil pollution and/or water pollution

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102150568A (en) * 2010-11-29 2011-08-17 中国科学院新疆生态与地理研究所 Method for confirming soil plant toxicity
US10086417B2 (en) 2014-05-05 2018-10-02 Agri-Tech Producers, Llc Combined remediation biomass and bio-product production process
CN106771057A (en) * 2016-11-30 2017-05-31 湖南城市学院 A kind of method based on Atrichum undulatum accurate detection Lead Pollution in Soil degree
CN106771057B (en) * 2016-11-30 2018-11-30 湖南城市学院 A method of accurately detecting Lead Pollution in Soil degree based on Atrichum undulatum
CN113182339A (en) * 2021-05-12 2021-07-30 谢非 Farmland is administered and is used novel soil treatment system
KR20230053867A (en) * 2021-10-15 2023-04-24 한국과학기술연구원 Method for analyzing soil contaminated by pollutants
KR102645223B1 (en) 2021-10-15 2024-03-11 한국과학기술연구원 Method for analyzing soil contaminated by pollutants

Similar Documents

Publication Publication Date Title
JP2011072941A (en) Method for deciding state of soil
Okorie et al. The application of in vitro gastrointestinal extraction to assess oral bioaccessibility of potentially toxic elements from an urban recreational site
Chandrasena et al. Evaluating Escherichia coli removal performance in stormwater biofilters: a laboratory-scale study
Janssens et al. Incorporation of iron and organic matter into young Antarctic sea ice during its initial growth stages
Mahlangu et al. A simplified cost-effective biosand filter (BSFZ) for removal of chemical contaminants from water
Michelutti et al. Assessing the effects of climate and volcanism on diatom and chironomid assemblages in an Andean lake near Quito, Ecuador
Bruland et al. Recent changes in soil total phosphorus in the Everglades: Water Conservation Area 3
Val-Peon et al. A taphonomic approach to the pollen assemblage from layer M of the Abric Romaní archaeological site (NE Iberian Peninsula)
He et al. Mass balance of metals during the phytoremediation process using Noccaea caerulescens: a pot study
Dalu et al. Emerging freshwater pollutants: analysis, Fate and Regulations
Trinh et al. Eco-friendly remediation of lampenflora on speleothems in tropical karst caves
Bada et al. Response of kenaf (Hibiscus Cannabinus L.) grown in different soil textures and lead concentrations
Mancin et al. The agglutinated foraminifera from the SW Pacific bathyal sediments of the last 550 kyr: Relationship with the deposition of tephra layers
KR101479254B1 (en) Environmentally-friendly remediation system and its application to remediate subsoil and ground water affected by the contamination source in association with appropriate monitoring system
Cuske et al. Ultrasonic cleaning of plant roots in their preparation for analysis on heavy metals
Reutova et al. Species of wild flora as indicators of environmental genotoxicity
Tavakoli et al. Lead and cadmium spatial pattern and risk assessment around coal mine in Hyrcanian Forest, North Iran
WO2006076475A3 (en) Treatment fluid disposal in chemical cleaning processes for drinking water facilities
Bhattarai et al. Modeling effect of cover condition and soil type on rotavirus transport in surface flow
Turg‘unovich et al. POLLUTION OF SOILS OF INDUSTRIAL TERRITORIES AND WAYS OF THEIR EFFICIENT CLEANING
Hebda Assessing wildfire risk to municipal drinking water using paleoecology
Janssens Incorporation mechanisms of iron and organic matter into newly-formed sea ice
Ajmone Marsan et al. Soils in urban areas
Matallah et al. First checklist of benthic macroinvertebrate communities from Chrea National Park, Blida province, Northern Algeria.
Myrstad Colonisation and growth of benthic algae in a recently deculverted urban stream

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20120703

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20121108

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20121113

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20130115

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20131105