CN105016873A - Compound mixed biological bacterial fertilizer for restoring cadmium contaminated soil and preparation method and application thereof - Google Patents
Compound mixed biological bacterial fertilizer for restoring cadmium contaminated soil and preparation method and application thereof Download PDFInfo
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Abstract
The invention provides a compound mixed biological bacterial fertilizer for restoring cadmium contaminated soil; the compound mixed biological bacterial fertilizer includes NPK nutritious components and agricultural rare earth nitrate, a catalyst waste agent, a microbial agent, a humic acid mineral powder, sepiolite, plant ash, kaolin and zeolite with proper proportion; after the compound mixed biological bacterial fertilizer is applied to the cadmium contaminated soil, under the synergy of all the components, the contaminated soil is effectively restored while cadmium in the soil is effectively passivated and immobilized, the cadmium activity in the soil is decreased significantly, and the absorption of crops on cadmium is facilitated to be reduced, so as to make the cadmium content in the crops decreased significantly; the compound improver has relatively good stability and environmental friendly characteristic, does not produce secondary pollution, and is low in cost and prone to large-area promotion; when the compound mixed biological bacterial fertilizer is applied to the cadmium contaminated soil, the application amount is only 10-200 kg/hm<2>, the cadmium content in the crops can be significantly reduced, and the crops are allowed to meet national edible safety standards.
Description
Technical field
Compound bio-bacterial manure that the present invention relates to a kind of cadmium pollution soil repair and its preparation method and application, belongs to the technical field of contaminated soil remediation.
Background technology
Along with the fast development of industry and the continuous increase of countryside tax system intensity, the pollutents such as plurality of heavy metal enter edatope, thus have caused the heavy metal contamination of soil, and become one by the global problem of extensive concern.It is reported, nearly 2,000 ten thousand hm of cultivated area that current China pollutes by cadmium, mercury, arsenic, chromium, lead etc.
3, account for 20% of national total cultivated area, had a strong impact on modern agricultural development and social stablizing.
The pollution of heavy metal in soil, directly causes exceeding standard of agricultural-food heavy metal content, and then constitutes a serious threat to human health after entering human body by food chain.According to existing published documents and materials report, the exceeding standard rate of the suburbs, Hangzhou vegetables cadmium, copper, mercury, zinc is respectively 28%, 15%, 59% and 4%; The exceeding standard rate of Changsha vegetables heavy metal is 50%; The suburbs, Shenyang Chinese cabbage exceeding standard rate that is plumbous and cadmium is respectively 100% and 58%, and cucumber cadmium, mercury, lead doping rate are respectively 73%, 27% and 18%; Metal Contamination of Vegetables in Tianjin City as Derived by Principal Components cadmium exceeding standard rate is 40%; The exceeding standard rate of Nanning City's vegetables cadmium and mercury is respectively 92% and 50%; The exceeding standard rate of Baoshan District of Shanghai vegetables lead and cadmium is respectively up to 82% and 54%; The content of Wenzhou City's vegetables cadmium exceedes national standard 1.7 times, and fruit is 1.6 times; 9 kinds, Chengdu vegetables exceeding standard rate that is plumbous and cadmium is respectively 22% and 29%; Chongqing City's paddy rice cadmium, lead doping rate are 25-50%, and corn lead content exceeding standard rate is the exceeding standard rate of 22-66%, cadmium and mercury is 11%; Bulk vegetable cadmium, the lead doping rate of the domestic Xiangjiang River basin in Hunan have all exceeded 10%, and the exceeding standard rate of Tidal Flat Reclamation agriculture district, Pearl River Delta rice nickel, lead, chromium, cadmium reaches 48.3%, 28.9%, 12.3% and 2.6% respectively.According to another the measurement result of the units such as tealeaves institute of the Chinese Academy of Agricultural Sciences and the Ministry of Agriculture, the tealeaves lead doping rate in main Chan Cha district is increase trend in recent years.Within 1999, Tea Samples lead doping rate is 12.5%, and calendar year 2001 then rises to 25%.Therefore, the Pollution abatement of heavy metal-polluted soil is extremely urgent.
Chinese patent literature CN 104046361A discloses a kind of compound heavy metal contaminated soil conditioner, it comprises following component: plant ash, fused(calcium magnesium)phosphate, unslaked lime, zeolite and fertilizer, and the proportioning of its weight is plant ash: fused(calcium magnesium)phosphate: unslaked lime: zeolite: fertilizer=(0.3-1.1): (0.1-1.2): (0.4-2.1): (0.1-0.6): (0.008-0.06): (0.4-1.2).This soil improvement agent passes through the heavy metal in the inorganic component fixed-contamination soil such as the phosphoric acid salt in unslaked lime, fused(calcium magnesium)phosphate, hydroxyapatite, the salt of wormwood in plant ash, heavy metal activity is reduced, but, after above-mentioned soil improvement agent is applied to cadmium pollution soil, repairing effect is unsatisfactory, in farm crop, cadmium content is still higher, and needs disposablely to use in a large number, is generally 2250-4500kg/hm
2, transportation cost and to use cost all higher, peasant not easily accepts, and is difficult to spread.
Summary of the invention
After technical problem to be solved by this invention is that soil improvement agent of the prior art is applied to cadmium pollution soil, repairing effect is unsatisfactory, in farm crop, cadmium content is still higher, thus proposes a kind of effective and effectively can reduce the compound bio-bacterial manure of the cadmium pollution soil repair of cadmium content in farm crop to soil remediation.
For solving the problems of the technologies described above, technical scheme of the present invention is:
A compound bio-bacterial manure for cadmium pollution soil repair, its raw material composition comprises:
Nitrogenous fertilizer, 10-60 weight part;
Phosphate fertilizer, 10-60 weight part;
Potash fertilizer, 10-60 weight part;
Arsenic determination, 0.5-2 weight part;
Catalyzer gives up agent, 2-10 weight part;
Microbiobacterial agent, 2-10 weight part;
Humic acid breeze, 25-55 weight part;
Sepiolite, 15-25 weight part;
Plant ash, 3-11 weight part;
Kaolin, 0.5-1.1 weight part;
Zeolite, 0.3-1.2 weight part.
The give up active ingredient of agent of described catalyzer is cupric oxide and zinc oxide.
The agent of giving up of described catalyzer is be that the catalst for synthesis of methanol of carrier gives up agent with aluminum oxide.
Described microbiobacterial agent comprise in Azobacter, phosphorus decomposing mushroom, potassium decomposing mushroom one or more.
Described nitrogenous fertilizer is the mixture of one or more in urea, volatile salt, ammonium sulfate, ammonium chloride, nitrocalcite and ammonium nitrate, described phosphate fertilizer is the mixture of one or more in monoammonium phosphate, diammonium phosphate, calcium superphosphate, double superhosphate and fused(calcium magnesium)phosphate, and described potash fertilizer is the mixture of one or more in Repone K, potassium sulfate, potassium silicate and saltpetre.
The give up particle diameter of agent of described catalyzer is less than or equal to 10nm, the particle diameter of described humic acid breeze is 110-140 order, and the particle diameter of described sepiolite is 110-140 order, and the particle diameter of described plant ash is 110-140 order, described kaolinic particle diameter is 110-140 order, and the particle diameter of described zeolite is 110-140 order.
Also be added with at least one in unslaked lime, wilkinite, hydroxyapatite and fertilizer;
In described fertilizer, to dry quality of organic matter mark >=40% of base; To dry massfraction >=4.0% of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient; Massfraction≤30% of the moisture of fresh sample, potential of hydrogen pH value is 5.5-8.5.
The preparation method of the compound bio-bacterial manure of described cadmium pollution soil repair, its step is as follows:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
The application of compound bio-bacterial manure in heavy-metal contaminated soil is repaired of described cadmium pollution soil repair.
The application process of the compound bio-bacterial manure of described cadmium pollution soil repair, its step is as follows:
In the soil of heavy metal contamination, add the compound bio-bacterial manure of described cadmium pollution soil repair, addition is 10-200kg/hm
2, the balance improvement soil time is 7-14 days.
Technique scheme of the present invention has the following advantages compared to existing technology:
(1) the compound bio-bacterial manure of cadmium pollution soil repair of the present invention, comprise the arsenic determination of n p k nutrition component and applicable proportioning, catalyzer gives up agent, microbiobacterial agent, humic acid breeze, sepiolite, plant ash, kaolin and zeolite component, after being applied to heavy-metal contaminated soil, under the synergy of above-mentioned each component, realize heavy metal in soil being carried out effective passivation and effectively repairing polluted soil while fixing, thus make the active significantly reduction of the cadmium in soil on the one hand, be conducive to reducing farm crop to the absorption of cadmium, and then cadmium content in farm crop is significantly reduced, the n p k nutrition component contained on the other hand and plant ash etc. can provide nutrition to improve soil fertility for soil again, the microbiobacterial agent simultaneously contained is conducive to improving structure of soil microbial community, continue the repairing effect of strengthening to polluted soil, in addition, rare earth component in arsenic determination itself has antagonistic action to cadmium, be conducive to further reducing farm crop to the absorption of cadmium, composite modifying agent of the present invention has good stability and environment friendly, secondary pollution can not be produced, with low cost, be easy to spread, when being applied to cadmium pollution soil, amount of application is only 10-200kg/hm
2, just can significantly reduce cadmium content in farm crop, make it reach national edible safety standard, reach management goal.
(2) the compound bio-bacterial manure of cadmium pollution soil repair of the present invention, also be added with unslaked lime, wilkinite, hydroxyapatite and fertilizer, by the cadmium in the inorganic component fixed-contamination soil in unslaked lime, wilkinite, hydroxyapatite, and improve the fertility of soil in conjunction with fertilizer, thus the repair of strengthening to polluted soil while improving Cadmium in Soil fixed action.
Embodiment
1g is represented with 1 weight part in following examples.
Embodiment 1
The present embodiment provides a kind of compound bio-bacterial manure of cadmium pollution soil repair, and its raw material composition comprises:
Urea, 10 weight parts;
Monoammonium phosphate, 60 weight parts;
Repone K, 10 weight parts;
Arsenic determination, 2 weight parts;
Catalst for synthesis of methanol gives up agent, 2 weight parts;
Azobacter microbiobacterial agent, 2 weight parts;
Humic acid breeze, 55 weight parts;
Sepiolite, 15 weight parts;
Plant ash, 11 weight parts;
Kaolin, 0.5 weight part;
Zeolite, 1.2 weight parts.
The particle diameter of described arsenic determination is 10 orders, and the give up particle diameter of agent of described catalst for synthesis of methanol is 10nm; The particle diameter of described humic acid breeze, sepiolite, plant ash, kaolin and zeolite is 110 orders.
Further, the preparation method of the compound bio-bacterial manure of described cadmium pollution soil repair is provided, is specially:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
Embodiment 2
The present embodiment provides a kind of compound bio-bacterial manure of cadmium pollution soil repair, and its raw material composition comprises:
Volatile salt, 60 weight parts;
Diammonium phosphate, 10 weight parts;
Potassium sulfate, 60 weight parts;
Arsenic determination, 0.5 weight part;
Catalst for synthesis of methanol gives up agent, 10 weight parts;
Phosphate solubilizing bacteria quasi-microorganism microbial inoculum, 5 weight parts;
Humic acid breeze, 25 weight parts;
Sepiolite, 25 weight parts;
Plant ash, 3 weight parts;
Kaolin, 1.1 weight parts;
Zeolite, 0.3 weight part;
Unslaked lime, 10 weight parts;
Wilkinite, 15 weight parts;
Hydroxyapatite, 10 weight parts;
Fertilizer, 20 weight parts.
The particle diameter of described arsenic determination is 10 orders, and the give up particle diameter of agent of described catalst for synthesis of methanol is 9nm; The particle diameter of described humic acid breeze, sepiolite, plant ash, kaolin and zeolite is 140 orders.
The particle diameter of described unslaked lime, wilkinite, hydroxyapatite is 10 orders.
In described fertilizer, to dry the quality of organic matter mark of base for 40%; To dry the massfraction of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient for 4.0%; The massfraction of the moisture of fresh sample is 30%, and potential of hydrogen pH value is 5.5.
Further, the preparation method of the compound bio-bacterial manure of described cadmium pollution soil repair is provided, is specially:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
Embodiment 3
The present embodiment provides a kind of compound bio-bacterial manure of cadmium pollution soil repair, and its raw material composition comprises:
Ammonium sulfate, 40 weight parts;
Calcium superphosphate, 35 weight parts;
Potassium silicate, 50 weight parts;
Arsenic determination, 1.5 weight parts;
Catalst for synthesis of methanol gives up agent, 5 weight parts;
Potassium solubilizing bacteria quasi-microorganism microbial inoculum, 10 weight parts;
Humic acid breeze, 40 weight parts;
Sepiolite, 17 weight parts;
Plant ash, 8 weight parts;
Kaolin, 0.9 weight part;
Zeolite, 0.8 weight part;
Wilkinite, 10 weight parts;
Fertilizer, 20 weight parts.
The particle diameter of described arsenic determination is 10 orders, and the give up particle diameter of agent of described catalst for synthesis of methanol is 8nm; Described humic acid breeze, sepiolite, plant ash, kaolin, zeolite and bentonitic particle diameter are 140 orders.
In described fertilizer, to dry the quality of organic matter mark of base for 55%; To dry the massfraction of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient for 8.0%; The massfraction of the moisture of fresh sample is 18%, and potential of hydrogen pH value is 7.5.
Further, the preparation method of the compound bio-bacterial manure of described cadmium pollution soil repair is provided, is specially:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
Embodiment 4
The present embodiment provides a kind of compound bio-bacterial manure of cadmium pollution soil repair, and its raw material composition comprises:
The mixture that ammonium chloride, nitrocalcite and ammonium nitrate form according to mass ratio 1: 1: 1,45 weight parts;
The mixture that double superhosphate and fused(calcium magnesium)phosphate form according to mass ratio 1: 1,45 weight parts;
The mixture that potassium silicate and saltpetre form according to mass ratio 1: 1,45 weight parts;
Arsenic determination, 1.2 weight parts;
Catalyzer gives up agent, 6 weight parts;
Complex micro organism fungicide simultaneously containing Azobacter, phosphorus decomposing mushroom and potassium decomposing mushroom, 8 weight parts;
Humic acid breeze, 38 weight parts;
Sepiolite, 21 weight parts;
Plant ash, 10 weight parts;
Kaolin, 0.8 weight part;
Zeolite, 0.9 weight part;
Hydroxyapatite, 20 weight parts;
Fertilizer, 20 weight parts.
The particle diameter of described arsenic determination is 10 orders, and the give up particle diameter of agent of described catalyzer is 8nm; Described humic acid breeze, sepiolite, plant ash, kaolin, zeolite and bentonitic particle diameter are 140 orders.
Described catalyzer give up agent be take aluminum oxide as carrier, agent of giving up with cupric oxide and the zinc oxide catalyzer that is active ingredient.
In described fertilizer, to dry the quality of organic matter mark of base for 45%; To dry the massfraction of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient for 5.0%; The massfraction of the moisture of fresh sample is 20%, and potential of hydrogen pH value is 7.
Further, the preparation method of the compound bio-bacterial manure of described cadmium pollution soil repair is provided, is specially:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
Comparative example 1
This comparative example provides a kind of composite modifying agent of cadmium pollution soil repair, and its raw material composition comprises:
Plant ash, 3 weight parts;
Fused(calcium magnesium)phosphate, 12 weight parts;
Unslaked lime, 4 weight parts;
Zeolite, 1 weight part;
Wilkinite, 10 weight parts;
Hydroxyapatite, 0.08 weight part;
Fertilizer, 4 weight parts.
The particle diameter of described plant ash, unslaked lime, zeolite, wilkinite and hydroxyapatite is 110 orders.
In described fertilizer, to dry the quality of organic matter mark of base for 55%; To dry the massfraction of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient for 8.0%; The massfraction of the moisture of fresh sample is 18%, and potential of hydrogen pH value is 7.5.
Further, the preparation method of the composite modifying agent of described cadmium pollution soil repair is provided, is specially:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
The extruder grain technique that above-described embodiment and comparative example adopt can adopt extruder grain production technique general in prior art, and special compound fertilizer process flow process also can be adopted to carry out producing (see " agricultural modernization research " the 18th volume the 2nd phase the 108th page).
Experimental example
The compound bio-bacterial manure of the cadmium pollution soil repair described in embodiment 1-4 and comparative example 1 and modifying agent are numbered as A-D, E successively, select heavy metal Cd contaminated soil as subject, compound bio-bacterial manure and the modifying agent of described cadmium pollution soil repair is added in above-mentioned Cd contaminated soil, and cadmium content effective in soil after reparation is measured, concrete grammar is: claim 5.0g to cross the pedotheque of 100 mesh sieves in 100ml centrifuge tube, add the NH that 25ml concentration is 1mol/L
4cl solution, centrifugation after vibration 2h, filters and obtains extracting solution, adopts the soluble state metal content in aas determination extracting solution, is effective cadmium content.
What table 1 showed is the measurement result adopting sample A-E to carry out repairing rear effectively cadmium content to the soil being initially 7.23mg/kg containing Cd amount, and wherein, the addition of composite modifying agent is 10kg/hm
2, balance improvement soil 7 days;
Table 2 show for adopting sample A to being initially followed successively by 7.23 containing effective Cd amount, 7.56,8.05,6.53, the measurement result of the soil of 7.86mg/kg effective cadmium content after carrying out repairing;
The measurement result for adopting sample A soil (the initial Cd of containing amount is 7.23mg/kg) to be carried out to effective cadmium content after repairing under Different adding amount that table 3 shows;
What table 4 showed is adopt sample A at same addition 10kg/hm
2under, soil (initial be 7.23mg/kg containing Cd amount) is not carried out under homostasis improvement time to the measurement result of effectively cadmium content after repairing.
Table 1-initially containing Cd amount for the soil of 7.23mg/kg carry out repairing after the measurement result of effective cadmium content
Table 2-sample A is to the measurement result of cadmium content effective after Cd contaminated soil remediation
| Initial effectively Cd content/(mg/kg) | 7.23 | 7.56 | 8.05 | 6.53 | 7.86 |
| Addition/(the kg/hm of composite modifying agent 2) | 10 | 10 | 10 | 10 | 10 |
| Balance improvement soil time/(my god) | 15 | 15 | 15 | 15 | 15 |
| Effective Cd content/(mg/kg) after repairing | 1.02 | 1.19 | 1.51 | 0.95 | 1.22 |
| Effective Cd reduced rate in soil | 85.89％ | 84.26％ | 81.24％ | 85.45％ | 84.48％ |
Table 3-sample A under Different adding amount to soil remediation after the measurement result of effective cadmium content
Table 4-sample A under not homostasis improvement time to soil remediation after the measurement result of effective cadmium content
As can be seen from the test result of above-mentioned table 1-4, after adopting the compound bio-bacterial manure of cadmium pollution soil repair of the present invention to repair Cd contaminated soil, in soil, effective Cd reduced rate is all positioned at more than 80%, thus illustrate that composite modifying agent of the present invention can realize effective passivation of heavy metal in soil Cd and fixing and adopt modifying agent described in comparative example (see table 1) to repair effective Cd reduced rate in rear soil to soil to be only 55.04%, to illustrate that the repairing effect of modifying agent of the prior art to cadmium pollution soil is unsatisfactory.
Further, in order to study in soil Cd content to the impact of crop growth, in blank soil, add heavy metal Cd makes Cd content in soil be respectively 0, 1, 5, 10, 20mg/kg, for often organizing Cd content, control group and experimental group are set respectively, wherein, do not add the soil of composite modifying agent of the present invention (sample A) as a control group, soil after adopting sample A to repair is as experimental group, respectively in the culturing on soil Plantula Brassicae chinensis of above-mentioned experimental group and control group, adopt the biomass of weighting method after dried difference experiment with computing group and control group, calculate biomass increment rate further, adopt atomic absorption spectrophotometer to measure Cd content in Plantula Brassicae chinensis, result is as shown in table 5.
The table 5-impact that soil absorbs Growth of Cabbage and Cd after composite modifying agent is repaired
Test result as can be seen from above-mentioned table 5, in Plantula Brassicae chinensis, the detected result of Cd content shows, compared with control group, when the initial addition of soil Cd is respectively 1mg/kg, 5mg/kg, during 10mg/kg and 20mg/kg, after composite modifying agent of the present invention is repaired, biomass increment rate is respectively 53.88%, 64.2%, 11.76% and 12.5%, illustrate that described composite modifying agent effectively can promote the growth of Plantula Brassicae chinensis, in Plantula Brassicae chinensis, Cd content reduces by 27.66% respectively, 40.89%, 36.62% and 27.87%, illustrate that compound bio-bacterial manure of the present invention can make the active significantly reduction of the cadmium in soil, reduce farm crop to the absorption of cadmium, cadmium content in farm crop is significantly reduced.Even if for the soil (initial Cd content is 0mg/kg) not by cadmium pollution, use after composite modifying agent of the present invention repairs, biomass increment rate is up to 70.13%, illustrate that described composite modifying agent effectively can promote the growth of Plantula Brassicae chinensis, also make Cd content in Plantula Brassicae chinensis reduce by 8.3% simultaneously.
Obviously, above-described embodiment is only for clearly example being described, and the restriction not to embodiment.For those of ordinary skill in the field, can also make other changes in different forms on the basis of the above description.Here exhaustive without the need to also giving all embodiments.And thus the apparent change of extending out or variation be still among the protection domain of the invention.
Claims (10)
1. a compound bio-bacterial manure for cadmium pollution soil repair, is characterized in that, raw material composition comprises:
Nitrogenous fertilizer, 10-60 weight part;
Phosphate fertilizer, 10-60 weight part;
Potash fertilizer, 10-60 weight part;
Arsenic determination, 0.5-2 weight part;
Catalyzer gives up agent, 2-10 weight part;
Microbiobacterial agent, 2-10 weight part;
Humic acid breeze, 25-55 weight part;
Sepiolite, 15-25 weight part;
Plant ash, 3-11 weight part;
Kaolin, 0.5-1.1 weight part;
Zeolite, 0.3-1.2 weight part.
2. the compound bio-bacterial manure of cadmium pollution soil repair according to claim 1, is characterized in that, the give up active ingredient of agent of described catalyzer is cupric oxide and zinc oxide.
3. the compound bio-bacterial manure of cadmium pollution soil repair according to claim 1 and 2, is characterized in that, the agent of giving up of described catalyzer is be that the catalst for synthesis of methanol of carrier gives up agent with aluminum oxide.
4. the compound bio-bacterial manure of the cadmium pollution soil repair according to any one of claim 1-3, is characterized in that, described microbiobacterial agent comprise in Azobacter, phosphorus decomposing mushroom, potassium decomposing mushroom one or more.
5. the compound bio-bacterial manure of the cadmium pollution soil repair according to any one of claim 1-4, it is characterized in that, described nitrogenous fertilizer is the mixture of one or more in urea, volatile salt, ammonium sulfate, ammonium chloride, nitrocalcite and ammonium nitrate, described phosphate fertilizer is the mixture of one or more in monoammonium phosphate, diammonium phosphate, calcium superphosphate, double superhosphate and fused(calcium magnesium)phosphate, and described potash fertilizer is the mixture of one or more in Repone K, potassium sulfate, potassium silicate and saltpetre.
6. the compound bio-bacterial manure of the cadmium pollution soil repair according to any one of claim 1-5, it is characterized in that, the give up particle diameter of agent of described catalyzer is less than or equal to 10nm, the particle diameter of described humic acid breeze is 110-140 order, the particle diameter of described sepiolite is 110-140 order, the particle diameter of described plant ash is 110-140 order, and described kaolinic particle diameter is 110-140 order, and the particle diameter of described zeolite is 110-140 order.
7. the compound bio-bacterial manure of the cadmium pollution soil repair according to any one of claim 1-6, is characterized in that, is also added with at least one in unslaked lime, wilkinite, hydroxyapatite and fertilizer;
In described fertilizer, to dry quality of organic matter mark >=40% of base; To dry massfraction >=4.0% of the nitrogen of base, Vanadium Pentoxide in FLAKES and potassium oxide total nutrient; Massfraction≤30% of the moisture of fresh sample, potential of hydrogen pH value is 5.5-8.5.
8. the preparation method of the compound bio-bacterial manure of the cadmium pollution soil repair according to any one of claim 1-7, its step is as follows:
Get various feed composition according to above-mentioned weight part and mix, namely obtaining described composite modifying agent through extruder grain.
9. the application of compound bio-bacterial manure in cadmium pollution soil is repaired of the cadmium pollution soil repair described in any one of claim 1-7.
10. the application process of the compound bio-bacterial manure of the cadmium pollution soil repair described in any one of claim 1-7, its step is as follows:
In the soil of cadmium pollution, add the compound bio-bacterial manure of described cadmium pollution soil repair, addition is 10-200kg/hm
2, the balance improvement soil time is 7-14 days.
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| CN106045758A (en) * | 2016-05-26 | 2016-10-26 | 淄博出入境检验检疫局综合技术服务中心 | Amendment for heavy-metal contaminated soil and preparation method therefor |
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| CN107473849A (en) * | 2017-09-19 | 2017-12-15 | 南京仙草堂生物科技有限公司 | A kind of preparation method and application process of the biological organic fertilizer for improving Cadmium Pollution in Soils |
| CN107473847A (en) * | 2017-09-19 | 2017-12-15 | 南京仙草堂生物科技有限公司 | A kind of biological organic fertilizer for improving Cadmium Pollution in Soils |
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| CN109628099A (en) * | 2018-09-12 | 2019-04-16 | 扬州大学 | A kind of passivation stabilizer for agricultural land soil cadmium pollution reparation and preparation method thereof and application method |
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| CN110016350A (en) * | 2019-04-29 | 2019-07-16 | 深圳润康生态环境股份有限公司 | Arable land heavy-metal contaminated soil preparation for repairing and preparation method thereof |
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| CN105542788A (en) * | 2015-12-23 | 2016-05-04 | 江苏盖亚环境工程有限公司 | A composite material for soil in-situ remediation and a preparing method thereof |
| CN106045758A (en) * | 2016-05-26 | 2016-10-26 | 淄博出入境检验检疫局综合技术服务中心 | Amendment for heavy-metal contaminated soil and preparation method therefor |
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| CN107629798A (en) * | 2017-08-11 | 2018-01-26 | 湖南省土壤肥料研究所 | Acidic soil conditioner and application |
| CN107473849A (en) * | 2017-09-19 | 2017-12-15 | 南京仙草堂生物科技有限公司 | A kind of preparation method and application process of the biological organic fertilizer for improving Cadmium Pollution in Soils |
| CN107473847A (en) * | 2017-09-19 | 2017-12-15 | 南京仙草堂生物科技有限公司 | A kind of biological organic fertilizer for improving Cadmium Pollution in Soils |
| CN109628099A (en) * | 2018-09-12 | 2019-04-16 | 扬州大学 | A kind of passivation stabilizer for agricultural land soil cadmium pollution reparation and preparation method thereof and application method |
| CN109744102A (en) * | 2019-01-30 | 2019-05-14 | 湖南杂交水稻研究中心 | A kind of rice production method reducing heavy metal cadmium |
| CN110016350A (en) * | 2019-04-29 | 2019-07-16 | 深圳润康生态环境股份有限公司 | Arable land heavy-metal contaminated soil preparation for repairing and preparation method thereof |
| CN113800721A (en) * | 2021-09-30 | 2021-12-17 | 海南大学 | Treatment method for ecological restoration of water pollution of farmland water body |
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Application publication date: 20151104 |