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collector-to-emitter reverse bias current as a function of the collector-to-emitter voltage; collector-to-substrate reverse bias current as a function of the collector-to-substrate voltage Bipolar Transistor Ideality Transistor emitter-base ideality factor can be altered as a result of ESD stress Post-ESD stress, the transistor emitter-base ideality factor can be altered as a result of an increase in bulk or surface recombination centers in the emitter base junction Transistor emitter-base ideality factors can be observed from the following measurements: Gummel plot of base current as a function of the emitter-base voltage and extraction of the base current slope; Gummel plot ratio of collector-to-base current as a function of emitter-base voltage; extraction of the leakage current scaling with increased temperature; direct current bipolar gain characteristics; model extraction from Gummel-Poon model at low currents As an example, in the work of RL Minear and GA.



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Dodson, in a CBE bipolar homojunction transistor, it was observed that the pre-ESD stress collector and base ideality factors were n 1:02 and n 1:17 prior to ESD stress, respectively [41] Base and collector currents were measured for a base-emitter voltage from 03 to 10 V, with preforward bias current levels from 1 10 9 to 1 10 3 A levels After HBM ESD stress of the emitter base junction, the Gummel plot base characteristic (eg, log IB versus VBE ) showed a change in the slope with a new ideality factor of n 2:02; no change was observed in the Gummel plot collector current characteristic [41] In this result, the Gummel plot slope changed by 2 from an ideal device (eg, n 1); this indicates that the ESD stress generated mid-band gap recombination centers in the emitter base junction region.





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Previous studies on effects of pulp mill ef uents in sh clearly indicate endocrine disrupting responses by the ef uents, including reduced gonad growth, reduced sex steroid levels, reduced growth and impaired reproduction and recruitment (Andersson et al, 1988; Sandstr m et al, 1988; McMaster et al, 1991; van der Kraak et al, 1992; Gagnon et al, 1994; Munkittrick et al, 1994; Sandstr m, 1995; Sandstr m et al, 1997) Masculinising effects of pulp and paper mill ef uents include gonopodium formation of female poecilids (Howell et al, 1980; Cody & Burtone, 1997), testicular growth and enlarged eyes in eels (Caruso et al, 1988), spawning warts in female sh (Munkittrick et al, 1999) and more male embryos in viviparous eelpout close to a pulp mill (Larsson et al, 1999).

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The recombination centers can be associated with bulk recombination centers or surface recombination centers The recombination centers would satisfy a forward bias characteristic of qVBE IB / exp 2kT MOSFET Threshold Voltage Shifts In RF MOSFET devices, the evidence of ESD-induced degradation may be evident by an observation of the MOSFET threshold voltage shift In a MOSFET structure, MOSFET threshold voltage shifts can occur due to MOSFET gate dielectric surface state generation, MOSFET hot-electron injection, MOSFET negative bias temperature instability (NBTI), MOSFET gate-induced drain leakage (GIDL), and MOSFET parasitic current devices ESD-stress can lead to changes in the spatial location of xed charge in the isolation materials (eg, LOCOS isolation, or shallow trench isolation), or generate additional charge & '.

Endocrine disruption in sh near pulp mills seems not to have disappeared after introduction of chlorine free bleaching or secondary treatment Suggested responsible candidate compounds include plant sterols and/or other compounds endogenous to the wood raw material The repeated sh investigations in the receiving waters at Norrsundet pulp mill clearly show that a very positive but not complete recovery has occurred as a result of the internal process modi cation and improved treatment of the waste water Most individual organism effects previously observed in exposed sh have either disappeared or show a very limited response Additionally, investigations of the sh community in the receiving water outside Norrsundet pulp mill (Sandstr m, 1995) showed a much improved situation except for a disturbed recruitment and reduced abundance of sh.

2.0 g m 3 [1] and between 1.5 and 20 g m 3 in urban areas, whereas the concentration of EC in remote ocean areas is in the range 5 20 ng m 3 [1]. Studies concerning the size distribution and characteristics of EC aerosols are summarised in a report by EPA [1]. In polluted areas EC presents a bimodal size distribution with the rst mode between 0.05 and 0.12 m and the second mode between 0.5 and 1.0 m. Average EC concentrations are around 1.3 and 3.8 g m 3 for rural and urban sites, respectively, in the US. The ratio of EC to total carbon is in the range 0.15 0.20 in rural areas and 0.2 0.6 in urban areas. The OC is a complex mixture of thousands of different organic compounds [17, 29, 30] and a very small portion of its molecular structure has been characterised (around 10%). Combustion sources emit particles in the ne mode and the mass distribution has a mode at 0.1 0.2 m. Gas

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