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Assimilator

To decrease the contact surface (to assimilate it to a point) by the focalization of the magnetic field. [Pg.291]

It is a probe whose the coil support is a small circular sticks with a straiglit section. The aim of our study is to assimilate the resulting magnetic field to a material point, hi order to minimize the lateral field, we have chosen the construction of conical coil where the lateral field at a contact point in respect to a straight configuration is decreased with an exponential factor. The results obtained from the curves are as follow ... [Pg.292]

The resulting field at the contact point with the material to be tested can be assimilated to a material point. The influence of the lateral field is considerably minimized. [Pg.295]

Gr. iodes, violet) Discovered by Courtois in 1811, Iodine, a halogen, occurs sparingly in the form of iodides in sea water from which it is assimilated by seaweeds, in Chilean saltpeter and nitrate-bearing earth, known as caliche in brines from old sea deposits, and in brackish waters from oil and salt wells. [Pg.122]

To determine the feasibiUty of, or need for, fertilization requires knowing (/) which of the required elements, if any, are deficient in the soil (2) what chemical forms of the deficient elements are assimilable by the plants and thus suitable as fertilizers (5) what quantity of fertilizer material is required to meet the needs of the crop and (4) whether the crop yield increase resulting from fertilizer appHcation would warrant the cost of the fertilizer production and appHcation. [Pg.213]

Generally, soluble materials are more effective as micronutrient sources than are insoluble ones. For this reason, many soil minerals that contain the micronutrient elements are ineffective sources for plants. Some principal micronutrient sources and uses are summarized below. In this discussion the term frits refers to a fused, pulverized siUceous material manufactured and marketed commercially for incorporation in fertilizers. Chelates refers to metaHoorganic complexes specially prepared and marketed as especially soluble, highly assimilable sources of micronutrient elements (see CHELATING agents). [Pg.242]

Significant differences in net photosynthetic assimilation of carbon dioxide are apparent between C, C, and CAM biomass species. One of the principal reasons for the generally lower yields of C biomass is its higher rate of photorespiration if the photorespiration rate could be reduced, the net yield of biomass would increase. Considerable research is in progress (ca 1992) to achieve this rate reduction by chemical and genetic methods, but as yet, only limited yield improvements have been made. Such an achievement with C biomass would be expected to be very beneficial for foodstuff production and biomass energy appHcations. [Pg.29]

On ornamental plants CCC is appHed to a2aleas, geraniums, and hibiscus (Hibiscus sp] to make compact plants, and to poinsettias to reduce stem height and increase the red color of the bracts. A considerable amount of work has been carried out on cereals with CCC to reduce stem length and inhibit lodging. In Europe, the effect of CCC on shortening the culms of cereals is dependent upon the genotype. It has been demonstrated that the effect is as follows wheat > triticale > durum wheat > rye > oats > barley > corn = millet = rice (37). In barley, culms are initially inhibited but later the plant overcomes the inhibition (37). This has been attributed to poor assimilation, translocation, and rapid breakdown in wheat (38). [Pg.424]

The process of pulverized cuUet reduction yields a product having near-batch equivalent sizing (—12 mesh (<1.7 mm mm)) and in a furnace-ready condition. Foil-backed paper, lead and other metals, and some tableware ceramics can be removed in an oversized scalping operation after the first pass through the system. Other contaminants are reduced to a fine particle size that can be assimilated into the glass composition during melting. [Pg.569]

These appHcations require withdrawal of water from a source and subsequent treatment and conveyance to the point of use. Water is also used without being withdrawn from a source, eg, for navigation, recreation, wild and aquatic life propagation, hydroelectric-power generation, and waste assimilation and transport. The principal types of withdrawal uses and their average rates are given in Table 2. Some of these withdrawal rates represent multiple uses of the same water along main rivers in metropoHtan and industrialized areas. [Pg.220]

Although stream standards are the most reaUstic in light of the use of the assimilative capacity of the receiving water, they are difficult to administer and control in an expanding industrial and urban area. The equitable allocation of poUutional loads for many industrial and municipal complexes also poses pohtical and economic difficulties. A stream standard based on minimum dissolved oxygen at low stream flow intuitively implies a minimum degree of treatment. One variation of stream standards is the specification of a maximum concentration of a poUutant (ie, the BOD) in the stream after mixing at a specified low flow condition. [Pg.221]

The importance of the final settling, or humus, tank can be seen by an examination of what occurs in the trickling filter itself. A new filter is broken in by applying settled sewage as in the normal operation. After a period of time the microbial, or zoogleal, mass forms on the filter medium and stabilizes the waste. Waste material is first adsorbed, and then assimilated by the microorganisms. [Pg.283]

Although the antibacterial and antifungal activities of bialaphos and phosphinothricin were not found to be usehil, the two agents were later used as biodegradeable, relatively nonselective, postemergent herbicides. Glutamine synthetase inhibition is toxic to plants because the enzyme is key to ammonia assimilation. There is some selectivity for individual plant species as shown by the LD for bialaphos ranging from 0.125 to 8.5 kg/ha (301—303). [Pg.159]

The balance between animal and plant life cycles as affected by the solubiHty of carbon dioxide ia the earth s water results ia the carbon dioxide content ia the atmosphere of about 0.03 vol %. However, carbon dioxide content of the atmosphere seems to be increa sing as iacreased amounts of fossil fuels are burned. There is some evidence that the rate of release of carbon dioxide to the atmosphere may be greater than the earth s abiHty to assimilate it. Measurements from the U.S. Water Bureau show an iacrease of 1.36% ia the CO2 content of the atmosphere ia a five-year period and predictions iadicate that by the year 2000 the content may have iacreased by 25% (see Airpollution). [Pg.20]

Agriculture ndNutrition. Cobalt salts, soluble in water or stomach acid, are added to soils and animal feeds to correct cobalt deficiencies. In soil apphcation the cobalt is readily assimilated into the plants and subsequendy made available to the animals (56). Plants do not seem to be affected by the cobalt uptake from the soil. Cobalt salts are also added to salt blocks or pellets (see Feeds and feed additives). [Pg.382]

The body excretes tritium with a biological half-life of 8—14 d (10.5 d average) (75), which can be reduced significantly with forced fluid intake. For humans, the estimated maximum permissible total body burden is 37 MBq (1 mCi). The median lethal dose (LD q) of tritium assimilated by the body is estimated to be 370 GBq (10 Ci). Higher doses can be tolerated with forced fluid intake to reduce the biological half-life. [Pg.16]

The radiological hazard of tritium to operating personnel and the general population is controlled by limiting the rates of exposure and release of material. Maximum permissible concentrations (MPC) of radionucHdes were specified in 1959 by the International Commission on Radiological Protection (79). For purposes of control all tritium is assumed to be tritiated water, the most readily assimilated form. The MPC of tritium ia breathing air (continuous exposure for 40 h/wk) is specified as 185 kBq/mL (5 p.Ci/mL) and the MPC for tritium in drinking water is set at 3.7 GBq/mL (0.1 Ci/mL) (79). The maximum permitted body burden is 37 MBq (one millicurie). Whenever bioassay indicates this value has been exceeded, the individual is withdrawn from further work with tritium until the level of tritium is reduced. [Pg.16]

This section covers only the tests that are essential on a completed motor, irrespective of the manufacturing procedure and stage quality checks. If ISO 9000 guidelines are assimilated, practised and enforced by a manufacturer so that a customer s trust is obtained, a final pre-despatch inspection by the customer may not be necessary. The customer, having gained confidence in the practices and Quality Assurance Systems of the manufacturer, may issue an authorization to the manufacturer to despatch the material under their own inspection certificate, rather than an inspection by the customer. We discuss below the test requirements procedure and the acceptance norms prescribed by various national and international standards for such machines and adopted by various manufacturers. [Pg.250]


See other pages where Assimilator is mentioned: [Pg.475]    [Pg.35]    [Pg.213]    [Pg.219]    [Pg.478]    [Pg.28]    [Pg.45]    [Pg.477]    [Pg.482]    [Pg.524]    [Pg.476]    [Pg.82]    [Pg.82]    [Pg.93]    [Pg.285]    [Pg.285]    [Pg.304]    [Pg.569]    [Pg.286]    [Pg.463]    [Pg.78]    [Pg.78]    [Pg.171]    [Pg.216]    [Pg.223]    [Pg.389]    [Pg.391]    [Pg.384]    [Pg.130]    [Pg.15]    [Pg.509]    [Pg.389]    [Pg.49]   


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Absorption and Assimilation

Actinide assimilation

Algae, sulfate assimilation

Algal assimilation, nitrate

Amino acids assimilation

Amino acids assimilation mechanisms

Ammonia assimilation

Ammonia assimilation algae

Ammonia assimilation bacteroids

Ammonia assimilation control

Ammonia assimilation enzyme

Ammonia assimilation evidence

Ammonia assimilation genetics

Ammonia assimilation inhibitors

Ammonia assimilation leaves

Ammonia assimilation pathways

Ammonia assimilation roots

Ammonia assimilation table

Ammonia assimilation yeasts

Ammonium assimilation

Ammonium assimilation mechanisms

Ammonium assimilation pathways

Approach to Studying Nitrogen Assimilation

Assimilable organic carbon

Assimilable organic carbon, dissolved

Assimilate Allocation Strategy

Assimilate Allocation and Redistribution

Assimilate nitrate reduction

Assimilated food, conversion

Assimilated food, conversion efficiency

Assimilates

Assimilates

Assimilates accumulation

Assimilates acquisition

Assimilates allocation

Assimilates carbon

Assimilates distribution

Assimilates factors affecting

Assimilates hierarchy

Assimilates lateral transport

Assimilates macronutrients

Assimilates micronutrients

Assimilates mineral nutrients

Assimilates of carbon

Assimilates partitioning

Assimilates stem storage

Assimilates strategy

Assimilates tuber storage

Assimilation

Assimilation

Assimilation Pathways

Assimilation and fractional crystallization

Assimilation animal types

Assimilation capacity

Assimilation constituents

Assimilation effect

Assimilation efficiency

Assimilation efficiency models

Assimilation from Intestine

Assimilation in Bacteria

Assimilation in Fungi and Plants

Assimilation in Mammals

Assimilation mean values

Assimilation number

Assimilation of Atmospheric Nitrogen

Assimilation of Carbon and Nitrogen

Assimilation of Crustal Rocks

Assimilation of Trace Elements in Crystals

Assimilation of Trace Elements in Silicate Melts

Assimilation of lipids by the body

Assimilation of the Breakdown Products

Assimilation process

Assimilation ratio

Assimilation test

Assimilation, Mixing

Assimilation, microbial iron

Assimilation-fractional Crystallization

Assimilation-fractional crystallization (AFC)

Assimilative

Assimilative

Assimilative capacity

Bacteria metal assimilation

Bacteria, carbon dioxide assimilation

C02 assimilation

CO2, assimilation rate

Calcium assimilation

Carbohydrates assimilation

Carbon and Nitrogen Assimilation Tests

Carbon assimilation

Carbon assimilation tests

Carbon dioxide assimilation

Carbon dioxide assimilation, rate

Carbon dioxide, assimilation in animal labelled with

Carbon global assimilation rate

Chloroplasts reductive sulfate assimilation

Colour assimilation

Control of Assimilate Production

Cultural assimilator

Cultural assimilator Subject

Culture assimilator

DCP assimilating

DCP assimilating bacterium

Dark reaction carbon dioxide assimilation

Data assimilation

Delocalization process, communal entropy and assimilation

Diatom nitrogen assimilation

Differences in abilities to assimilate different nutrients

Dioxide Assimilation in Microorganisms

Dioxide Assimilation in Plants

Dissolved organic nitrogen assimilation

Enteric bacteria assimilation

Fermentative assimilation

Fibroblast galactosidase assimilation

Fixed nitrogen assimilation

Flux assimilation

Four-dimensional data assimilation

Gastrointestinal tract, assimilation

Glutamate ammonia assimilation

Iron assimilation

Iron phytoplankton assimilation

Learning assimilating

Maximum Assimilation Rate

Metal assimilation

Metal assimilation metals

Microbial assimilation

Microorganisms, carbon dioxide assimilation

Modeling data assimilation

Modifying Carbon Assimilation

N2 assimilation

Net assimilation rate

Nitrate assimilation

Nitrate assimilation pathway

Nitrite assimilation

Nitrite reductase Nitrogen assimilation

Nitrogen Assimilation by Vegetation

Nitrogen Uptake and Assimilation

Nitrogen assimilation

Nitrogen assimilation by plants

Nitrogen assimilation control protein

Nitrogen assimilation during photosynthesis

Nitrogen assimilation tests

Nitrogen cycle assimilation

Nitrogen fixation and assimilation

Nutrient assimilation

Oxidative assimilation

Phosphorus assimilation

Photosynthesis carbon dioxide assimilation

Photosynthesis nutrients assimilation

Phytoplankton nitrate assimilation

Phytoplankton nitrogen assimilation

Plant growth regulation assimilate production

Productivity assimilation rate

S, Assimilation

Self-regulation of nutrient assimilation

Serine pathway one-carbon compound assimilation

Soil Reduction Capacity Effects on Carbon Assimilation and Radial Oxygen Loss

Source of Assimilates for Starch Formation

Starch assimilation

Sucrose assimilation

Sulfate assimilation

Sulfate assimilation bound pathway

Sulfate assimilation free pathway

Sulfate assimilation regulation

Sulfate assimilative reduction

Sulfur assimilation (peculiarities)

Sulfur dioxide assimilation

Sulphur assimilation

Tannin assimilation

The dynamics of CO2 assimilation by plants in Russia

Thermodynamics of mixing and assimilation in ideal-gas systems

Two-Way Assimilation

Yeast assimilable nitrogen

Yeasts assimilation tests

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