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146results about How to "Strong ion exchange performance" patented technology

Sludge treatment process

InactiveCN105859068AEfficient removalAchieve homogeneous mixingSludge treatmentSludgeThree stage
The invention belongs to the field of environmental protection, and in particular relates to a sludge treatment process. The sludge treatment process comprises the following steps: 1) impurity removal: use multi-stage grille to filter out the garbage in the sludge; 2) pretreatment: utilize the three-stage sludge settling tank to pretreat the sludge to obtain the first, second, and The sludge in the three-stage sludge settling tank, the sludge slurry and the supernatant after being settled in the three-stage sludge settling tank; 3) solidification treatment: respectively adopt mixing solidification and dehydration solidification methods for the first, second, and third-stage sludge sedimentation The silt and silt slurry in the pond are dehydrated and solidified to obtain silt-solidified soils A and B; 4) stacking and aging: transport the silt-solidified soils A and B to a temporary storage yard and age them for 3 to 7 days to complete the treatment. The sludge treatment process of the present invention can simultaneously process particles and sludge with high viscosity and low water content, as well as sludge slurry with fine particles, organic matter and high water content, and is especially suitable for river courses with complex components, wide particle distribution, and large water content differences silt.
Owner:GUANGZHOU WATER CONSERVANCY & HYDROPOWER STATION CONSTR ENG

Heavy metal cadmium, lead and arsenic compound contaminated soil restorative agent and preparation method thereof

The invention provides a heavy metal cadmium, lead and arsenic compound contaminated soil restorative agent. The heavy metal cadmium, lead and arsenic compound contaminated soil restorative agent is prepared from the following components in percentage by weight: 30-50 percent of biomass charcoal, 5-10 percent of diatomite, 5-10 percent of sodium bentonite, 5-10 percent of activated aluminum oxide, 10-20 percent of dithiocar-bamate, 5-10 percent of ethylenediaminetetraacetic acid, 5-10 percent of tartaric acid, 5-10 percent of polyacrylamide and 5-10 percent of sodium dodecyl sulfate. A preparation method for the heavy metal cadmium, lead and arsenic compound contaminated soil restorative agent comprises the following steps: mixing the biomass charcoal, diatomite, sodium bentonite, activated aluminum oxide, ethylenediaminetetraacetic acid, tartaric acid, polyacrylamide and sodium dodecyl sulfate in mass proportion to obtain a mixture; and adding the dithiocar-bamate into the mixture in corresponding mass proportion to sufficiently mix uniformly, thereby obtaining the prepared soil restorative agent. The prepared soil restorative agent has good effect in restoring the cadmium, lead and arsenic compound contaminated soil.
Owner:CHANGSHA HUIJU ENVIRONMENTAL TECH CO LTD

Organic-inorganic compound bacterial fertilizer and preparation method of compound bacterial fertilizer

The invention provides an organic-inorganic compound bacterial fertilizer and a preparation method of the compound bacterial fertilizer. The compound bacterial fertilizer is prepared from the following materials in parts by weight: 20-80 parts of an inorganic fertilizer, 10-40 parts of organic matter, 2-20 parts of a soil conditioner, 0.01-2 parts of microelements and 0.001-0.04 part of microbial bacteria. The preparation method of the compound bacterial fertilizer comprises the following steps: (1) detecting macroelements, microelements and the organic matter in the soil; (2) separating, screening, identifying, culturing and compounding strains; (3) taking flour as a carrier of microbial bacteria, uniformly stirring and drying at a low temperature to prepare bacterial powder; (4) mixing and stirring the bacterial powder with the organic matter and the microelements according to a certain ratio to prepare a mixture; and (5) adding the mixture, the inorganic fertilizer and the soil conditioner into a small quantity of water, prilling, drying at the low temperature and bagging to prepare the compound bacterial fertilizer. The bacterial fertilizer has the effects of remarkably increasing effective microbial communities needed by the crops, decomposing slowly-available nutrient in the soil, improving fertilizer efficiency of the soil, increasing the yield of the crops, increasing the utilization rate of the fertilizer, effectively relieving soil hardness and detoxifying heavy metals.
Owner:南阳奇伟微生态基因科技开发有限公司

Comprehensive utilization method for coal ash solid waste

InactiveCN103420384AGood adsorption and cation exchange capacityHigh application prospectAlkaline-earth metal silicatesSilicon oxidesChemistryAluminium
A comprehensive utilization method for coal ash solid waste comprises the following steps: grinding and sieving coal ash after being calcined, and soaking in a hydrochloric acid of 20-30% mass concentration to respectively obtain ferro-aluminium chlorination liquor and solid residue; adding Ca(OH)2 and Al(OH)3 in the ferro-aluminium chlorination liquor, and adjusting the basicity to 45-55%, controlling the pH value at 3.5-5.0 through the hydrochloric acid, performing water thermal polymerization at the temperature of 105-110 DEG C, and obtaining a poly ferro-aluminium chlorination liquor after concentration and drying; washing and drying the solid residue, adding Ca(OH)2 at the molar ratio of n(Ca)to n(Si) of 5:6, adding NaOH at the molar ratio of n[Ca(OH)2] to n(NaOH) of 1:(0.5-1.5), and performing thermal reaction at the temperature of 180-220 DEG C to obtain a tobermorite sewage disposal material. According to the method, a comprehensive solution that aluminium oxide and a small amount of ferric oxide and calcium oxide in the coal ash are adopted to prepare poly ferro-aluminium chlorination purifying agent, and the components of silicon dioxide are adopted to prepare the tobermorite sewage disposal material is offered, so that the purpose that the coal ash is comprehensively used to prepare the environment material with higher added value is achieved.
Owner:SHAANXI UNIV OF SCI & TECH

Soil column combination matrix composite flow artificial wetland treatment system

InactiveCN102633407ARich habitat typeStrong nitrogen adsorption capacityMultistage water/sewage treatmentConstructed wetlandSoil science
The invention relates to a soil column combination matrix composite flow artificial wetland treatment system, which uses a composite underflow artificial wetland mode and comprises an artificial wetland pool, a soil column combination matrix system, an artificial wetland plant system and a water distribution system. The soil column combination matrix system is the core of the whole artificial wetland system and comprises a prefiltering unit, a combination matrix denitrification unit, a combination matrix dephosphorization unit and a fine filtering unit, and soil columns are arranged in the combination matrix denitrification unit and the combination matrix dephosphorization unit. The artificial wetland plant system is formed by aquatic plants such as reeds, cattails, cane shoots and the like by mixed planting and planted onto the combination matrix denitrification unit and the combination matrix dephosphorization unit after earthing. The artificial wetland pool is matched with the water distribution system to construct the artificial wetland system having multiple flow regimes including vertical downward flow, vertical upward flow, horizontal underflow and the like. The soil column combination matrix composite flow artificial wetland treatment system is reasonable in design of each portion, scientific in structure, small in occupied space, low in operation cost and convenient in management, and is a novel artificial wetland technique which can effectively purifying polluted water body.
Owner:TONGJI UNIV

Combined set for treating micro-polluted source water in counties and towns

The invention relates to a combined set for treating a micro-polluted source water in counties and towns, and the combined set comprises an inclined tube sedimentation tank, an aeration biozeolite filter column and an activated carbon filter column, wherein the inclined tube sedimentation tank consists of a water inlet region, a sloped tube region and a water collection region, the water inlet region is provided with turbulent stones and a baffle, the water collection region discharges water through a perforated water collection tank, the aeration biozeolite filter column consists of a water/gas inlet region, a filter material region and a water collection region, aeration is carried out in a blast aeration mode, gas is mixed in the water inlet region and enters the filter material region through a long-handle filter head, the filter material consists of coarse-grain zeolite and common-grain zeolite, the effluent water of the aeration biozeolite filter column enters the activated carbon column in a hydraulic drop mode, and the activated carbon filter column consists of a filter material region and a water outlet region. The inclined tube sedimentation tank water inlet region is provided with the turbulent stones and baffle to enhance the flocculation effect of the coagulant and the removal effect of the sedimentation tank. The activated carbon filter column connected to the aeration biozeolite filter column performs a two-stage biochemical synergistic action, and implements advantage complementation, thereby enhancing the water quality of the effluent water and lowering the treatment cost. The combined set can effectively remove ammonia nitrogen, organic substances, manganese and other pollutants in the micro-polluted source water, has the advantages of compact technical linkage, low investment and operating cost and stable quality of effluent water, and is suitable for being used in small-scale water generation occasions, such as water supply to counties and towns.
Owner:TONGJI UNIV

Planting method for organic high-yield rice

The invention discloses a planting method for organic high-yield rice. The method comprises: planting broad beans in a rice field, after harvesting the broad beans, performing green manure dressing and retting, and applying base fertilizer; performing water-controlling harden-seedling on rice seedlings whose seedling age is 15-20 days for 2-3 days; performing rotary tillage, ridge dividing, irrigation on the rice field, and then transplanting rice seedlings; after the rice seedlings survive, dressing a compound fertilizer to promote rice seedling tiller; 13-18 days after rice transplanting, putting newly-hatched ducklings whose day-age is 12-20 in the rice field according to amount of 8-15 per mu, 25-40 days after putting the ducks in the rice field, driving the ducks out of the rice field, spraying biopesticide, performing field draining for 7-10 days, topdressing a nitrogen-phosphorus-potassium composite fertilizer according to amount of 20-50 kg per mu, and then irrigating to 8-10 cm, and driving the ducks in the rice field, 15-20 days before the rice is mature, taking back the ducks, and cutting off water and drying the field. The planting method for organic high-yield rice is high in yield, and obtained rice is good in quality, and high-quality duck meat is obtained.
Owner:ANHUI MUMAHU AGRI DEV GRP

Method for preparing montmorillonite/graphene oxide aerogel/epoxy resin composite material

The invention provides a method for preparing a montmorillonite/graphene oxide aerogel/epoxy resin composite material and relates to a study on single-aspect performance of a double-phase composite material or epoxy resin. The method for preparing the montmorillonite/graphene oxide aerogel/epoxy resin composite material comprises the following steps: after adding expanded graphite to a container under a condition of ice-water bath, adding a mixed solution of concentrated sulfuric acid and concentrated nitric acid to the container; adding potassium permanganate to the container; stirring and heating an obtained mixture; after adding hydrogen peroxide to the mixture till a solution becomes luminous yellow, adjusting the PH value of the solution to 7; centrifuging the solution; freezing and drying the solution to obtain graphene oxide aerogel; taking the graphene oxide aerogel and adding the graphene oxide aerogel to acetone solution; carrying out ultrasonic treatment on an obtained mixture to obtain modified graphene oxide under the nitrogen protection; adding acetone to the modified graphene oxide and modified montmorillonite mixture; adding pre-heated epoxy resin to the modified graphene oxide and modified montmorillonite mixture in advance; and ultrasonically stirring, vacuumizing, heating, curing and cooling an obtained mixture to obtain a three-phase composite material. Themethod for preparing the montmorillonite/graphene oxide aerogel/epoxy resin composite material is used for preparing the montmorillonite/graphene oxide aerogel/epoxy resin composite material.
Owner:HARBIN UNIV OF SCI & TECH
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