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The complex system of inter-relationships among organisms, materials, and environment that results in the biodeterioration of materials. It explains the differences between biodeterioration and biodegradation and how autotrophs and heterotrophs play a role in the biological colonization of a material. The document also covers ecological factors that can influence the life of an organism and how they can be limiting factors.
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1st SEMESTER: Principles of Conservation (Foundation Course) National Museum Institute, Delhi Topic: Understanding Biodeterioration and Biodegradation in Art Conservation Studies The term Biodeterioration was first defined as “ any undesirable change in the properties of a material caused by the vital activities of organisms ” (Hueck, 1965, 1968), and the microorganism or organism that causes damage to the materials are called Biodeteriogen. The term biodeterioration and biodegradation tends to be used interchangeably, but hold distant differences. As biodegradation refers to the biological processes through which organic macromolecules are decomposed, with particular reference to the transformation, by means of microorganism, of toxic compounds into less toxic or harmless compounds. Therefore, while biodeterioration has a negative connotation of damage, biodegradation generally implies a beneficial or positive process. The process of biodeterioration of materials is a complex system of inter-relationships among organisms, materials and environment. Different phenomena acting together results in the biodeterioration of materials: physical or mechanical processes leading to cases such as loss of cohesion, rupture, or disaggregation and chemical processes that leads to degradation, transformation, or decomposition of the substrate. These processes usually occur simultaneously, but one type can predominate over the other depending on the kind of substrate and the biotic community, as well as environmental condition. It should be noted that there is no clear separation between the chemical and physical causes of deterioration on one side and the biological ones on the other, since any physical or chemical process can induce or influence the activity of organisms (Pinna & Salvadori, 2008).
To understand the processes of biodeterioration, it should be understood that the biological colonization of a material may involve: i. The utilization of the substrate as a food source; and ii. The use of the material solely as a support for the colony’s development. It is therefore important to distinguish between autotrophs and heterotrophs: autotrophs are the organisms that can manufacture foods for themselves in the organic materials necessary for their development, while the heterotrophs must extract these organic materials from the substrate to survive. Thus, the autotrophs (i.e., some bacteria, lichens, mosses, and vascular plants) can colonize inorganic substrates, while heterotrophs (i.e., numerous bacteria and fungi) are only able to grow on such substrates if organic substances are available to them from external sources. To study these correlations, it is vital to realize the underlying notions of the ecological requirements of diverse organisms (producers, destroyers and consumers) and the influences that environmental parameters may accept on them. Ecological factors are those physical, chemical, or biological factors in the environment that can influence the life of an organism. Liebig’s law (Law of the minimum, 1840) states that under conditions of stationary equilibrium, essential substances become limiting factors if their quantity is close to the minimum. In other words, the growth of an organism depends on the factor present in minimal quantity with respect to its needs and not by substances required in a greater quantity. While Shelford’s Law (Law of Tolerance,1913) as the extension of the Liebig’s Law, states that organisms not only have an ecological minimum but also a maximum, which together define an interval representing the limits of tolerance. This range contains the optimal value of each species (Figure 1.1). Thus, not only the minimum value but also the maximum value can be a critical factor. Consequently, any ecological factor can be a limiting factor based on the proximity of its value to the minimum or the maximum limits of tolerance, thus
References Hueck, H.J. (1965). The biodeterioration of materials as a part of Hylobiology. Material und Organismen,1 (1):5-34. Hueck, H.J. (1968). The biodeterioration of materials-An appraisal. In: Biodeterioration of materials. Elsevier, London: 6-12. Pinna, D., & Salvadori, O. (2008). Stone and related materials. In: Plant biology for Cultural Heritage , The Getty Conservation Institute, pp. 128-149. Caneva, G., & Ceschin, S. (2008). Ecology of Biodeterioration. In: Caneva G., Nugari, M.P., Salvadori, O. (Eds.), Plant Biology for Cultural Heritage Biodeterioration and Conservation. Getty Publication: 36-37.