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Dethlefsen, V, H von Westernhagen & P Cameron (1996) Malformations in North Sea pelagic sh embryos during the period 1984 1995 ICES Journal of Marine Science, 53 (6), 1024 1035 Devos, E, P Devos & M Cornet (1998) Effect of cadmium on the cytoskeleton and morphology of gill chloride cells in parr and smolt Atlantic salmon (Salmo salar) Fish Physiology and Biochemistry, 18, 15 27 Dexiang, C & AJ Ainsworth (1991) Effect of temperature on the immune system of channel cat sh (Ictalurus punctatus) II Adaptation of anterior kidney phagocytes to 10 C Comparative Biochemistry and Physiology, 100A, 913 918 Donaldson, EM (1981) The piturary-interrenal axis as an indicator of stress in sh In: (ed Pickering, AD) Stress in Fish Academic Press, London, New York, pp 11 47 Ellis, AE (1981) Stress and the modulation of defence mechanisms in sh In: (ed.

In both cases, Eq. (7.6) is modified to Eq. (7.7) by using Z S Kc 1=2 KI 3=2 : T Z 1 KA cc2 K I I 2 K T Z K K In the case of Fuoss-Kraus, T Z F Z 1 Z 1 Z 1 : : : 1=2 1=2 and in the case of Shedlovsky, 1 Z2 Z3 ::: S Z 1 Z T Z 2 8 Values of F(Z) and S(Z) are listed in the literature [15, 16]. From Eq. (7.7), the T(Z)/K vs cc2K/T(Z) relation is linear, with an intercept of 1=KI and a slope of KA/ KI 2 , from which we can obtain the values of KI and KA. These KI and KA values are also used in data analyses by Eq. (7.5). The values of KA obtainable by Eqs (7.6) and (7.7) range from 103 to 107 mol 1 l. If KA 107 mol 1 l, the slope of the linear relation is too large to obtain reliable I K (or KA) values. In these cases, we obtain the value of KI separately, either by use of Walden s rule or from the known values of ionic molar conductivities kI , i and use it to obtain KA. 7:7

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The medium access control (MAC) layer in Release 99 focuses on mapping between the logical channels and handling the priorities, as well as selection of the data rates being used i.e., selection of the transport format (TF) being applied. Transport channel switching is also a MAC layer functionality. Both HSDPA and HSUPA introduce new elements in the architecture. The MAC layer functionalities for HSDPA and HSUPA can operate independently of Release 99 s DCH operation, but takes into account the overall resource limitations of the air interface. Figure 3.4 illustrates the overall radio interface architecture for HSDPA and HSUPA user data, highlighting the new protocol entities dealing with user data. Control plane signalling omitted in Figure 3.4 would simply connect to the RLC and then have

Pickering, AD) Stress in Fish Academic Press, London, pp 147 169 Evans, MR, SJ Larsen, GHM Riekerk & KG Burnett (1997) Patterns of immune response to environmental bacteria in natural populations of the red drum, Sciaenops ocellatus (Linnaeus) Journal of Experimental Marine Biology and Ecology, 208, 87 105 Faisal, M & RJ Huggett (1993) Effects of polycyclic aromatic hydrocarbons on the lymphocyte mitogenic response in spot, Leistomus xanthurus Marine Environmental Research, 35, 121 124 Fitzsimons, JD (1995) A critical-review of the effects of contaminants on early-life stage (ELS) mortality of Lake trout in the Great-Lakes Journal of Great Lakes Research, 21 (S1), 267 276 Fitzsimons, JD, SB Brown, DC Honey eld & JG Hnath (1999) A review of early mortality syndrome (EMS) in Great Lake salmonids: Relationship with thiamine de ciency Ambio, 28, 9 15.

Q 0 0 U U 0 U: U 0 S 0:142

F rlin, L, T Andersson, C Haux, PE Olsson & Larsson (1986) Physiological methods in sh toxicology: Laboratory and eld studies In: (eds Nilsson & Holmgren) Fish Physiology: Recent Advances Croom Helm, London, pp 158 169 F rlin, L, T Andersson, L Balk & Larsson (1991) Biochemical and physiological effects of pulp mill ef uents on sh In: (ed S dergren, A) Environmental Fate and Effects of Bleached Pulp Mill Ef uents Swedish EPA Report (4031), Sweden, pp 235 243 F rlin, L, T Andersson, L Balk & Larsson (1995) Biochemical and physiological effects of bleached pulp mill ef uents in sh Ecotoxicology and Environmental Safety, 30, 164 170 Fragoso, NM, JL Parrott, ME Hahn & PV Hodson (1998) Chronic retene exposure causes sustained induction of CYP1A activity and protein in rainbow trout (Oncorhynchus mykiss).

FIGURE 5.12 Histograms of posterior samples with MLE (vertical line) for 0 and 1 of Example 5.5, modeling the time to kidney failure.

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