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Hunting, human

R. M. Garrels, F. T. Mackenzie, and C. Hunt, Chemical Cycles and the Global Environment Assessing Human Influences, Kaufman, Inc., Los Altos, Calif, 1975 A. J. M. Schoot Uiterkamp, in P. M. Gresshoff, L. E. Roth, G. Stacey, and W. E. Newton, eds.. Nitrogen Eixation Achievements and Objectives, Chapman and Hall, London, 1990, p. 55. [Pg.93]

The impact of chemical pollution on the reproductive success and population sizes of wildlife species is often difficult to assess. In many cases, environmental factors such as habitat restriction, stress due to human intrusion and changes in natural food supplies owing to hunting, fishing and restocking policies may have a significant, even predominant, effect on population size. This makes it difficult to determine to what extent, if any, environmental endocrine disrupters may be contributing to observed effects on reproduction or population size in wildlife species. [Pg.9]

Human labor dominated all subsistence foraging activities, as the food acquired by gathering and hunting sufficed merely to maintain the essential metabolic functions and to support veiy slow population growth. Societies not very different from this ancestral archetype survived in some parts of the world (South Africa, Australia) well into the twentieth century Because they commanded veiy little energy beyond their subsistence food needs, they had very few material possessions and no permanent abodes. [Pg.622]

Hunt, S. and Grotf, J.L. 1990 Advanced Nutrition and Human Metabolism. St Paul, West Publishing Co. [Pg.209]

Deeks SG, Lu J, Hoh R, Neilands TB, Beatty G, Huang W, Liegler T, Hunt P, Martin JN, Kuritzkes DR (2007) Interruption of enfuvirtide in HIV-1 infected adults with incomplete viral suppression on an enfuvirtide-based regimen. J Infect Dis 195 387-391 Dejucq N, Simmons G, Clapham PR (2000) T-ceU line adaptation of human immunodeficiency virus type 1 strain SF162 effects on envelope, vpu and macrophage-tropism. J Gen Virol 81 2899-2904... [Pg.194]

Hunt GJ. 1998. Transfer across the human gut of environmental plutonium, americium, cobalt, caesium and technetium Studies with cockles (Cerastoderma edule) from the Irish Sea. J Radiol Prot 18(2) 101-109. [Pg.241]

Hunt GJ, Leonard DRP, Lovett MB. 1986a. Transfer of environmental plutonium and americium across the human gut. Lancet l(8478) 439-440. [Pg.241]

Lione LA, Carter RJ, Hunt MJ, Bates GP, Morton AJ, Dunnett SB. Selective discrimination learning impairments in mice expressing the human Huntington s disease mutation. J Neurosci 1999 19 10428— 10437. [Pg.281]

Hunt In the human body, for example, what is the normal range of nuclear to cytoplasmic volume ratios ... [Pg.36]

Jeunemaitre X, Soubrier F, Kotelevt-sev YV, Lifton RP, Williams CS, Char-ru A, Hunt SC, Hopkins N, Williams RR, Lajouel J-M, Corvol P. Molecular basis of human hypertension role of an-giotensinogen. Cell 1992 71 169-180. [Pg.264]

Hunt, S. L., Hsuan, J. J., Totty, N., and Jackson, R. J. (1999). Unr, a cellular cytoplasmic RNA-binding protein with five cold-shock domains, is required for internal initiation of translation of human rhinovirus RNA. Genes Dev. 13, 437—448. [Pg.352]

Pharmacologically, carbofuran inhibits cholinesterase, resulting in stimulation of the central, parasympathetic, and somatic motor systems. Sensitive biochemical tests have been developed to measure cholinesterase inhibition in avian and mammalian brain and plasma samples and are useful in the forensic assessment of carbamate exposure in human and wildlife pesticide incidents (Bal-lantyne and Marrs Hunt and Hooper 1993). Acute toxic clinical effects resulting from carbofuran exposure in animals and humans appear to be completely reversible and have been successfully treated with atropine sulfate. However, treatment should occur as soon as possible after exposure because acute carbofuran toxicosis can be fatal younger age groups of various species are more susceptible than adults (Finlayson et al. 1979). Carbofuran labels indicate that application is forbidden to streams, lakes, or ponds. In addition, manufacturers have stated that carbofuran is poisonous if swallowed, inhaled, or absorbed through the skin. Users are cautioned not to breathe carbofuran dust, fumes, or spray mist and treated areas should be avoided for at least 2 days (Anonymous 1971). Three points are emphasized at this juncture. First, some carbofuran degradation... [Pg.805]

Kupfer D. 1982. Studies on short and long-range estrogenic action of chlorinated hydrocarbon pesticides. In Hunt VR, Smith MK, Worth D, eds. Environmental factors in human growth and development. Banbury Report No. 1 1, Cold Spring Harbor Laboratory, 379-393. [Pg.268]


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See also in sourсe #XX -- [ Pg.163 ]




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