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Drugs and the pharmaceutical sciences

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270 Meltzer<br />

Extents of adsorption differ same organism / different Ros<br />

polyamide vs. cellulose acetate<br />

Bound radioactivity (CPM)<br />

(thous<strong>and</strong>s)<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

<strong>the</strong> attachments. This latter quality is a result, if not a cause, of hydrophobic adsorptions,<br />

as will be discussed. From <strong>the</strong> foregoing, it seems <strong>the</strong>re is a degree of commonality<br />

between biofilm formation <strong>and</strong> protein adsorption.<br />

The adsorption of organisms from <strong>the</strong>ir suspensions onto solid surfaces would<br />

involve <strong>the</strong> same forces of attraction <strong>and</strong> repulsion that regulate <strong>the</strong> adsorptive joining of<br />

one colloidal particle’s surface to that of ano<strong>the</strong>r. The process involving organisms would<br />

manifest itself in <strong>the</strong>ir adsorptive retention to <strong>the</strong> filter surfaces.<br />

Marshall (1992) points out that bacteria, as also particles in general, are kept from<br />

contact with surfaces by electrostatic forces. This includes <strong>the</strong> surfaces of o<strong>the</strong>r<br />

organisms. The repulsive forces involved are effective at long range, <strong>and</strong> prevail over <strong>the</strong><br />

weaker attractive forces that are simultaneously present. As will be described in <strong>the</strong><br />

forthcoming discussion of <strong>the</strong> electric double layer, <strong>the</strong> repulsions are attenuated by<br />

higher electrolyte concentrations. The attractive forces, albeit weaker, can <strong>the</strong>n assert<br />

<strong>the</strong>ir influence. The adsorptive interactions that follow would result in <strong>the</strong> formation of a<br />

biofilm.<br />

Fuoss Effect<br />

0 40 80 120 160 200 240 280<br />

Time (seconds)<br />

FIGURE 5 Upper<br />

line: Micobacterium<br />

adsorbed to polyamide<br />

RO membrane.<br />

Lower line: Micobacterium<br />

adsorbed to<br />

cellulose acetate RO<br />

membrane. Source:<br />

From Ridgway<br />

et al., 1984a;<br />

In suggesting a similarity between protein adsorptions to polymeric filter surfaces <strong>and</strong><br />

organism attachments to <strong>the</strong> same type surfaces, it is speculated that <strong>the</strong> term<br />

“adsorption” as used in <strong>the</strong> phrase “protein adsorption” includes a more varied<br />

expression of <strong>the</strong> same mechanisms that fixedly bond o<strong>the</strong>r surfaces to one ano<strong>the</strong>r. The<br />

bonding to activated carbon of organic molecular substances, whe<strong>the</strong>r in <strong>the</strong> form of<br />

vapors, liquids or particles, as utilized in gas masks or in water purification contexts, is a<br />

classical example of adsorption. As will be seen, <strong>the</strong> ionic strengths of <strong>the</strong> aqueous<br />

solutions from which proteins may be adsorbed also govern <strong>the</strong> adsorptive bonding of <strong>the</strong><br />

organics to <strong>the</strong> surfaces of <strong>the</strong> activated carbon particles. In this instance as well, <strong>the</strong>re is<br />

an apparent similarity in cause <strong>and</strong> effect. It is speculated that <strong>the</strong> adsorption of organic<br />

compounds including proteins to activated carbon surfaces is part of a like operation.<br />

The positive effect of ionic strengths on adsorptive sequestrations is forthcoming<br />

from <strong>the</strong> field of water treatment <strong>and</strong> involves <strong>the</strong> adsorption of organic substances by

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