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Suspended particle matter

Filtration is a fundamental unit operation that, within the context of this volume, separates suspended particle matter from water. Although industrial applications of this operation vary significantly, all filtration equipment operate by passing the solution or suspension through a porous membrane or medium, upon which the solid particles are retained on the medium s surface or within the pores of the medium, while the fluid, referred to as the filtrate, passes through. [Pg.62]

The solvent reservoir is a storage container made of a saterial resistant to chemical attack by the mobile diase. In its simplest fora a glass jug, solvent bottle or Erlenmeyer flask with a cap and a flexible hose connection to the pump is adequate. The PTFE connecting hose is terminated on the solvent side with a 2 micrometer pore size filter to prevent suspended particle matter from reaching the pump. In more sophisticated instruments the solvent reservoir may also be Cjquipped for solvent degassing, as... [Pg.794]

PMS APSS-200 Automated parenteral sampling system for pharmaceutical fluids is designed to size and count suspended particlate matter in a wide range of liquids. [Pg.485]

Various techniques of particle delivery are used to deduce pulmonary and systemic effects from the wide parameters of potential toxicological influences. The specific techniques that are currently employed in these studies include intratracheal instillation, intratracheal aspiration, and intratracheal inhalation. Of these different delivery techniques, intratracheal installation is a useful technique to assess the potential health effects of different particles efficiently and cost effectively. Intratracheal instillation is characterized by saline suspended particles administered directly into the trachea of the animal being tested. Intratracheal installation provides a relatively easy way to compare the toxicology between different materials. However intratracheal installation is not able to assess particle deposition. Intratracheal aspiration involves droplet administration of suspended particle matter in the form of a puff of air. Intratracheal inhalation is the most relevant for toxicity and risk assessment. Intratracheal inhalation involves nanoparticulate aerosol formation at constant concentrations during the exposure. [Pg.710]

The concentrations of suspended particle matter (SPM) near bottom waters at stations B1 and E3 were 9.6 14.2 and 19.3 24.0 mg/L with averages of 12.2 and 22.2 mg/L, respectively. The reciprocal of the SPM near bottom waters was 0.08 L/g at station B1 and 0.045 L/g at station E3. The annual variation of SPM between the BH98 and BH99 cruises was 25% and 11% at stations B1 and E3, respectively. This implied that the nutrient releases from sediments could be very close to the maximum release. In the experiment, the atom ratios of released nutrients were Si DIN P=40 25 l, which indicated that the phosphorus amount was relatively low compared to the Redfield ratio (Si N P 16 16 l). Fig. 2.45 (Liu et al., 2004) is the plot of time dependent desorption/release of phosphate and silicate from sediments. When surface sediment and seawater were mixed, they were released from sediments (Fig. [Pg.211]

Samples that contain suspended matter are among the most difficult types from which to obtain accurate pH readings because of the so-called suspension effect, ie, the suspended particles produce abnormal Hquid-junction potentials at the reference electrode (16). This effect is especially noticeable with soil slurries, pastes, and other types of colloidal suspensions. In the case of a slurry that separates into two layers, pH differences of several units may result, depending on the placement of the electrodes in the layers. Internal consistency is achieved by pH measurement using carefully prescribed measurement protocols, as has been used in the determination of soil pH (17). [Pg.467]

Mean Chemical Composition and Atmospheric Concentrations of Suspended Particulate Matter Sampled by the United States Environmental Protection Agency s Inhalable Particle and National Air Surveillance Networks—/rg/m and Percentage of Total Mass Sampled, 1980... [Pg.50]

The separation step requires (1) application of a force that produces a differential motion of the particles relative to the gas, and (2) sufficient gas-retention time for the particles to migrate to the collecting surface. Most dust-collections systems are comprised of a pneumatic-conveying system and some device that separates suspended particulate matter from the conveyed air stream. The more common systems use either filter media (e.g., fabric bags) or cyclonic separators to separate the particulate matter from air. [Pg.777]

In the recycle flow pressurization system (Figure 27.10), a portion (15-50%) of the clarified effluent from the flotation chamber is recycled, pressurized, and semisaturated with air in the air dissolving tube. The recycled flow is mixed with the unpressurized main influent stream just before admission to the flotation chamber, with the result that the air bubbles come out of aqueous phase in contact with suspended particulate matter at the inlet compartment of the flotation chamber. The system is usually employed in applications where preliminary chemical addition and flocculation are necessary and ahead of flotation. It eliminates the problems with shearing the flocculated particles since only the clarified effluent passes through the pressurizing pump and the friction valve. It should be noted, however, that the increased hydraulic flow on the flotation chamber due to the flow recirculation must be taken into account in the flotation chamber design. [Pg.1165]

In aquatic environments, radiocerium readily forms chemical complexes in seawater and associates with particles by adsorption (Mauch-line and Templeton, 1963). When radiocerium was added to natural seawater, it became associated with suspended matter, especially that with apparent particle diameters of 0.02 to 0.1 fim (Carpenter and Grant, 1967). When ionic radiocerium was added to filtered seawater at pH > 6.0, it hydrolyzed and formed complexes with hydroxide, chloride, or other anions in seawater and went on to form particles (Hirano et al., 1973). Adsorption of radiocerium onto suspended particles has also been noted after its release to freshwater ecosystems (Beninson et al., 1966). [Pg.12]

Particulate matter is a complex emission that is classified as either suspended particulate matter, total suspended particulate matter, or simply, particulate matter. For human health purposes, the fraction of particulate matter that has been shown to contribute to respiratory diseases is termed PMio (i.e., particulate matter with sizes less than 10 tim). From a control standpoint, particulate matter can be characterized as follows (1) particle size distribution and (2) particulate matter concentration in the emission (mg/m ). On occasion, physical property descriptions may also be employed when there are specific control applications. [Pg.244]

Sorption of pharmaceuticals onto the surface of particulate matter or their distribution between two phases (water and either sludge, sediment or soil) depends on many factors, the most important being liquid phase pH and redox potential, the stereochemical structure and chemical nature of both the pharmaceutical compound and the sorbent, the lipophilicity of the sorbed molecules (excellent sorption at log Kov > 4, low sorption at log < 2.4), the sludge-water distribution coefficient Kd Kd > 2 L g SS good sorption, < 0.3 L g SS low sorption), the extent of neutral and ioiuc species present in the wastewater and the characteristics of the suspended particles. Moreover, the presence of humic and fulvic substances may alter the surface properties of the sludge, as well as the number of sites available for sorption and reactions, thereby enhancing or suppressing sorption of PhCs [38, 55, 61]. [Pg.150]

Soil organic matter is found wherever organic matter is decomposed, mainly in the near surface. However soil organic matter may also be transported as suspended particles into deeper layers of the vadose zone or via surface- and groundwaterforming sediments. Although these components form a minor part of the total solid phase, they are of major importance in defining the surface properties of the solid phase and have a great impact on the chemical behavior. [Pg.14]


See other pages where Suspended particle matter is mentioned: [Pg.283]    [Pg.434]    [Pg.11]    [Pg.14]    [Pg.283]    [Pg.434]    [Pg.11]    [Pg.14]    [Pg.271]    [Pg.302]    [Pg.27]    [Pg.50]    [Pg.53]    [Pg.346]    [Pg.259]    [Pg.697]    [Pg.259]    [Pg.398]    [Pg.404]    [Pg.113]    [Pg.78]    [Pg.155]    [Pg.59]    [Pg.788]    [Pg.194]    [Pg.24]    [Pg.75]    [Pg.332]    [Pg.364]    [Pg.536]    [Pg.171]    [Pg.191]    [Pg.361]    [Pg.50]    [Pg.214]    [Pg.244]    [Pg.272]    [Pg.118]   
See also in sourсe #XX -- [ Pg.283 , Pg.330 ]




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Seawater suspended particle matter

Suspended particles

Suspending

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