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Morris, CD, Niederbuhl, JM and Mahr, JM (1993) Determining the capability of individuals with mental retardation to give informed consent American Journal on Mental Retardation, 98, 263 272 Morris, RG (1997) Cognition and ageing In R Jacoby and C Oppenheimer (eds), Psychiatry in the Elderly (2nd edn; pp 37 62) Oxford: Oxford University Press Mukherjee, S and Shah, A (2001) The prevalence and correlates of capacity to consent to a geriatric psychiatry admission Aging and Mental Health, 5, 335 339 Murphy, GH (1993) The use of aversive stimuli in treatment: the issue of consent Journal of Intellectual Disability Research, 37, 211 219 Murphy, G (2000) Justice denied Mental Health Care, 8, 256 257 Murphy, GH and Clare, ICH (1997) Consent issues In J O Hara and A Sperlinger (eds), Adults with Learning Disabilities: A Practical Approach for Health Professionals (pp.

similar to that predicted after ooding at our site. Martius (1997) reported that woody decay rates in the Central Amazon oodplain are enhanced by the seasonal oscillation between wetting and drying. Decay rates during the terrestrial phase of the ooding cycle were greatest for wood that had been immersed for one to four weeks, as compared with wood that had not been submerged or wood that had been submerged for six months (Martius, 1997). Microbial and fungal activity in uence the rates of wood decomposition (Harmon et al., 1986), and such activity in turn is affected by temperature, moisture, and aeration (Marra and Edmonds, 1994; Rayner and Todd, 1979). In our study, microbial and fungal activity generally increased with ooding (Molles et al., 1998). Responses included increased abundance of soil bacteria, fungi, and cellulose decomposers, higher mycorrhizal inoculum potential and root lengths colonized by mycorrhizal fungi, and increased dehydrogenase activity, indicating biological activity in the soil. We also used respiration chambers to measure forest oor respiration during the second two experimental oods, as well as during one natural ood.

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171 185) Chichester: John Wiley & Sons..

Physiological Reviews, 46, 323 357 De Flora, S & C Ramel (1988) Mechanisms of mutagenesis and carcinogenesis Classi cation and overview Mutation Research, 202, 285 306 De Flora, S, P Zanachi, C Bennicelli, A Camoirano, C Basso, M Bagnasco, A Izzotti & GS Badolati (1989) Genotoxicity, biotransformations, and interactions of marine pollutants as related to genetic and carcinogenic hazards In: (ed Grandjean, E) Carcinogenic, mutagenic, and teratogenic marine pollutants: impact on human health and the environment Vol 5 (Advances in Applied Biotechnology) Gulf Publishing Company, Houston, Texas, pp 3 31 De Flora, S, M Bagnasco & P Zanacchi (1991) Genotoxic, carcinogenic and teratogenic hazards in the marine environment, with special reference to the Mediterranean Sea Mutation Research, 258, 285 320 De Marini, DM (1991) Environmental mutagens/complex mixtures In: (eds Li, AP & RH He ich) Genetic toxicology.

so large that it requires thousands of sensors. Mathematical and computational methods and the software of the scenario must be capable of working with this extremely high number of nodes. The design should allow the system to work properly even when the number of sensors is increased. Fault tolerance: it is highly possible to lose some sensors of the network due to the environmental and operational conditions. However, the network should maintain its operation even if a few nodes fail to perform their task. That is, it should have a predetermined fault tolerance against possible errors. Node heterogenity: it is practically impossible to have all nodes identical in a wireless sensor network application. Some of them should be more powerful than the others. Also, some nodes may be mobile while others are static. For this precision agriculture application scenario, we need sink nodes that are more powerful than elementary sensor nodes. It also has various sensors measuring different parameters of the soil and food products. The system should support node heterogenity.

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