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Adverse level

Injury to plants and vegetation is caused by a variety of factors, of which air pollution is only one. Drought, too much water, heat and cold, hail, insects, animals, disease, and poor soil conditions are some of the other causes of plant injury and possible plant damage (3). Estimates suggest that less than 5% of total crop losses are related to air pollution. Air pollution has a much greater impact on some geographic areas and crops than others. Crop failure can be caused by fumigation from a local air pollution source or by more widespread and more frequent exposure to adverse levels of pollution. [Pg.112]

LD50 = lethal dose, 50% kill LOAEL = lowest-observed-adverse-effect level NOAEL = no-observed-adverse-level NS = not specified... [Pg.104]

During the sampling step, ionic analytes are continuously transferred to the acceptor solution through the membrane. Unless the analytes are immediately replenished at the membrane interface, their concentration falls to an adverse level affecting dramatically the dialysis efficiency. By the use of probes, this problem can be avoided by keeping the unknown solution under convective mixing (e.g. with a magnetic stirrer) in order to ensure a constant supply to the membrane surface. [Pg.94]

Oral LD q levels have been deterrnined in the mouse at 470 mg/kg (21) and the guinea pig at 7750 mg/kg (22). Several other studies (23—25) have shown that large quantities of both synthetic and natural glycerol can be adniinistered orally to experimental animals and humans without the appearance of adverse effects. Intravenous adniinistration of solutions containing 5% glycerol to animals and humans has been found to cause no toxic or otherwise undesirable effects (26). [Pg.349]

The toxicity of 2,4-pentanedione is shown in Tables 3 and 11 to be similar to mesityl oxide, and greater than most other 1,2- or 1,4-diketones or monoketones. Inhalation of low levels of 2,4-pentanedione can cause nausea, eye contact can induce stinging, and recurrent exposure to high concentrations (300—400 ppm) can adversely affect the central nervous system and immune system (325). [Pg.499]

Tin. The widespread use of caimed foods results in a daily intake of tin that is ca 1—17 mg for an adult male (154). At this level it has not been shown to be toxic. Some grains also contain tin. Too much tin can adversely affect 2inc balance and iron metaboHsm. EssentiaUty has not been confirmed for humans. It has been shown for the rat. An enhanced growth rate results from tin supplementation of low tin diets (85). Animals on deficient diets exhibit poor growth and decreased feed efficiency (155). [Pg.388]

The 1994—1995 threshold limit values as recommended by the American Conference of Governmental Industrial Hygienists (ACGIH) are given in Table 8. These time-weighted average values are those levels to which nearly all workers may be exposed for an 8-h workday and a 40-h work week without adverse effect (99). [Pg.103]

National Ambient Air Quality Standards. Under the Clean Air Act, six criterion pollutants, ie, pollutants of special concern, have been estabhshed by the EPA sulfur oxides (SO ), particulates, carbon monoxide (CO), nitrogen oxides (NO ), o2one (photochemical oxidants), and lead. National Ambient Air QuaUty Standards (NAAQS) were developed by EPA based on threshold levels of air pollution below which no adverse effects could be experienced on human health or the environment. [Pg.77]

Latex compound viscosity obviously forms an important aspect of dipped product manufacture. Accurate measurement by a Brookfield or similar viscometer is desirable to estabhsh the fundamental viscosity of a compound, but Flow-Cup viscometers (Ford B.3 Cup) are more commonly used for day-to-day control of latex compounds during compounding and product manufacture. It is necessary to ensure that only stainless steel flow cups are used, if the measured latex is allowed to return to the production tanks brass cups yield an unacceptable level of copper contamination, which adversely affects aging properties of products made from copper-contaminated mbber compound. [Pg.261]

Bakery Products. Sorbates are used in and/or on yeast-raised and chemically leavened bakery products. The internal use of sorbates in yeast-raised products at one-fourth the amount of calcium—sodium propionate that is normally added provides a shelf life equal to that of propionate without adversely affecting the yeast fermentation. Sorbates added at one-tenth the propionate level reduce the mix time by 30% (126). This internal treatment combined with an external spray of potassium sorbate can provide the same or an increased shelf life of pan breads, hamburger and hot-dog buns, English muffins, brown-and-serve roUs, and tortillas. The total sorbate useful in or on these baked goods ranges from 0.03 wt % for pan breads to 0.5 wt % for tortillas 0.2—0.3 wt % sorbic acid protects chemically leavened yellow and chocolate cakes (127). Emit-pie fillings and icings can be protected with 0.03—0.1 wt % sorbates. [Pg.287]

Side Effects and Toxicity. Adverse effects to the tricycHc antidepressants, primarily the result of the actions of these compounds on either the autonomic, cardiovascular, or central nervous systems, are summarized in Table 3. The most serious side effects of the tricycHcs concern the cardiovascular system. Arrhythmias, which are dose-dependent and rarely occur at therapeutic plasma levels, can be life-threatening. In order to prevent adverse effects, as weU as to be certain that the patient has taken enough dmg to be effective, the steady-state semm levels of tricycHc antidepressant dmgs are monitored as a matter of good practice. A comprehensive review of stmcture—activity relationships among the tricycHc antidepressants is available (42). [Pg.468]

Acute Toxicity Studies. These studies should provide the following information the nature of any local or systemic adverse effects occurring as a consequence of a single exposure to the test material an indication of the exposure conditions producing the adverse effects, in particular, information on dose—response relationships, including minimum and no-effects exposure levels and data of use in the design of short-term repeated exposure studies. [Pg.236]


See other pages where Adverse level is mentioned: [Pg.319]    [Pg.417]    [Pg.414]    [Pg.475]    [Pg.319]    [Pg.417]    [Pg.414]    [Pg.475]    [Pg.26]    [Pg.231]    [Pg.336]    [Pg.98]    [Pg.322]    [Pg.245]    [Pg.475]    [Pg.42]    [Pg.302]    [Pg.309]    [Pg.77]    [Pg.199]    [Pg.343]    [Pg.525]    [Pg.466]    [Pg.355]    [Pg.146]    [Pg.181]    [Pg.458]    [Pg.41]    [Pg.319]    [Pg.305]    [Pg.481]    [Pg.463]    [Pg.466]    [Pg.508]    [Pg.121]    [Pg.91]    [Pg.180]    [Pg.214]    [Pg.301]    [Pg.469]    [Pg.136]    [Pg.270]    [Pg.318]   
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Adverse drug reactions levels

Adverse events levels

Lower lowest observable adverse effect level

Lowest Observable Adverse Effect Level

Lowest Observed Adverse Effect Level

Lowest adverse effect level

Lowest observed adverse effect level LOAEL)

Lowest-observed-adverse-effect level LOAEL) benchmark

Minimum-observed-adverse-effect-level

Minimum-observed-adverse-effect-level MOAEL)

No Observable Adverse Effect Levels NOAELs)

No Observed Adverse Effect Level

No adverse effect level

No observable adverse effect level NOAEL)

No observed adverse effect level NOAEL)

No-observable-adverse-effect level

Non-observable adverse effect level

Suggested No Adverse Response Level

Suggested-No-Adverse-Response Levels SNARL)

The no observed adverse effect level

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