A
ABSORPTION Cross-references Agrophysics: Physics Applied to Agriculture The process by which one substance, such as solid or liq- uid, takes up another substance, such as liquid or gas, through minute pores or spaces between its molecules. ADAPTABLE TILLAGE Clay minerals can take water and ions by absorption. See Tillage, Impacts on Soil and Environment ABSORPTIVITY ADHESION Absorbed part of incoming radiation/total incoming radiation. The attraction between different substances, acting at sur- faces of contact between the substances e.g., water and solid, water films and organo-mineral surfaces, soil and ACOUSTIC EMISSION the metal cutting surface.
The phenomenon of transient elastic-wave generation due to a rapid release of strain energy caused by a structural ADSORPTION alteration in a solid material. Also known as stress-wave emission. A phenomenon occurring at the boundary between phases, where cohesive and adhesive forces cause the con- Bibliography centration or density of a substance to be greater or smaller McGraw-Hill Dictionary of Scientific & Technical Terms, 6E, than in the interior of the separate phases. Copyright © 2003 by The McGraw-Hill Companies, Inc. Bibliography Introduction to Environmental Soil Physics (First Edition). 2003. ACOUSTIC TOMOGRAPHY Elsevier Inc. Daniel Hillel (ed.) http://www.sciencedirect.com/ science/book/9780123486554 A form of tomography in which information is collected from beams of acoustic radiation that have passed through Cross-references an object (e.g., soil). One can speak of thermo-acoustic Adsorption Energy and Surface Heterogeneity in Soils tomography when the heating is realized by means of Adsorption Energy of Water on Biological Materials microwaves, and of photo-acoustic tomography when Solute Transport in Soils optical heating is used. Surface Properties and Related Phenomena in Soils and Plants
Jan Gliński, Józef Horabik & Jerzy Lipiec (eds.), Encyclopedia of Agrophysics, DOI 10.1007/978-90-481-3585-1, # Springer Science+Business Media B.V. 2011 2 ADSORPTION COMPLEX
Energetically heterogeneous surfaces can be next clas- ADSORPTION COMPLEX sified into several groups, among which we can distin- guish patchwise and random surfaces. In the case of Collection of organic and inorganic substances in soil that random surfaces e ðx; yÞ varies quite randomly with are capable of adsorbing (absorbing) ions or molecules. ad x; y; for patchwise surfaces eadðx; yÞ¼constant for x; y within consecutive regions Di. Both random and Cross-references patchwise surfaces are two limiting cases of surface topog- Adsorption Energy and Surface Heterogeneity in Soils raphy that is defined by spatial correlations between the Surface Properties and Related Phenomena in Soils and Plants points xi; yi with given values of the energy ead;i. We can distinguish correlations between pairs of sites, triples of sites, and so on (Bulnes et al., 2001). The variation of the energy of adsorption results from ADSORPTION ENERGY AND SURFACE several factors: the presence of different atoms or groups HETEROGENEITY IN SOILS of atoms on the surface; geometrical irregularities includ- ing the presence of pores of different shape and dimen- Zofia Sokołowska1, Stefan Sokołowski2 sions, and so on. Of course, geometrical and energetic 1Institute of Agrophysics, Polish Academy of Sciences, nonuniformities are correlated and the former is one of Lublin, Poland principal sources of energetic heterogeneity. Moreover, 2Department for the Modeling of Physico-Chemical a given adsorbent may be a quite complex mixture of sev- Processes, MCS University, Lublin, Poland eral interacting chemical species. Both energetic and geo- metric heterogeneities have a great impact on the Generalities adsorption process. The potential energy of interaction of a single adsorbate molecule with a solid adsorbent can be described by the Description of adsorption on energetically function UðRÞ, where fRg is a set of coordinates neces- heterogeneous surfaces sary to define the position of the adsorbate molecule. Accurate modeling adsorption on geometrically Assuming that the adsorbate molecule is a sphere of diam- nonuniform surfaces is difficult and only in some cases it eter s, its position is given by the Cartesian coordinates of ; ; is possible to construct an adequate model for a solid. its center, R ¼ r ¼ðx y zÞ. For molecules composed of When it is possible, then computer simulations can be several atoms, one needs to specify a multidimensional employed. However, the structure of great majority of vector fRg that determines the coordinates of all the atoms environmental adsorbents, and soils in particular (see Clay (or groups of atoms) building a given molecule. Formally, Minerals and Organo-Mineral Associates; Organic according to the classical statistical thermodynamics Matter, Effects on Soil Physical Properties and Processes; UðRÞ is the sum of the interactions of Na interaction cen- Parent Material and Soil Physical Properties; Soil ters located within a given adsorbate molecule, with Ns Phases) is extremely complex due to diversified mineral, interaction centers located within a solid, X X organic, and ionic composition. Therefore, the application of approximate approaches is necessary. The most widely UðRÞ¼ uðr Þ; (1) ij used methods are based on the so-called integral adsorp- i2Ns j2Na tion isotherm equation. ; where rij is the distance between the interacting centers. Of Suppose we know the function ylð p eÞ that describes course, when quantum-mechanical treatment is employed, the isotherm (surface coverage) on a uniform surface with UðRÞ is the difference of ground state energies between the adsorption energy e. Then, the isotherm on the molecule at the position fRg and the ground state of a heterogeneous surface can be approximated as a separated molecule. Z emax For a selected adsorbate molecule, say a spherical mol- yð pÞ¼Nm ylð p; eÞwðeÞde; (2) ecule, the potential UðrÞ can be used to characterize the emin surface. For a given set of coordinates x; y in the plane par- allel (or tangential) to the solid the minimum of the func- where p is the pressure, yðp; eÞ is the global (measured) tion UðrÞ with respect to the third coordinate, z, is often adsorption isotherm, N is the monolayer capacity, and called “the adsorption energy,” e .Ife is independent m ad ad w e is the energy distribution function that yields of x; y, the corresponding surface is energetically uniform ð Þ a fraction of the surface characterized by the adsorption (or homogeneous). For crystalline surfaces e (and, of ad energy e. The latter function satisfies the normalization course, UðrÞ) is a periodic function of x; y. However, there condition exists a variety of surfaces that are neither uniform nor ; Z crystalline. In those cases, eadðx yÞ may vary in a quite emax complicated manner with x; y and we call such surfaces de ¼ 1; (3) energetically heterogeneous. emin ADSORPTION ENERGY AND SURFACE HETEROGENEITY IN SOILS 3 where ½emin; emax are the lower and upper integration meaningful results are to be obtained, special care and limits. In many cases, these limits are assumed to be the quality of experimental data are required (Jaroniec ½e0; ?Þ, where e0 is the liquefaction energy of the adsor- and Bräuer, 1986) The easiest way to obtain an approxi- bate. Equation 2 states that the total adsorption is just mate solution of Equation 2 goes through the so-called a weighted average of the isotherms on model, homoge- condensation approximation, according to which neous surfaces, characterized by different values of e. (Rudziński and Everett, 1992) However, it means that the adsorption on each homoge- wðeÞ¼ @y½ pðeÞ =@e: (5) neous surface occurs independently of the adsorption on other surfaces. The last assumption is satisfied only for The condensation approximation replaces the local a patchwise topography, or when the interactions between adsorption isotherm by a step function, i.e., every pressure adsorbed particles are negligibly small. Despite of the is associated with the value of the adsorption energy, above quoted limitations, Equation 2 has been widely p=p0 ¼ expðe=kTÞ, that corresponds to one half of the used to describe adsorption on heterogeneous surfaces. coverage of a given homotattic patch. The basic difficulty Note that a quite similar approach is usually used to in this method is associated with an appropriate numerical describe adsorption by porous solids. In the latter case, differentiation of the total adsorption isotherm, y½pðeÞ . the weight function is just the pore size distribution One of the methods that has been widely used for that pur- function. pose relies on the approximation of the experimental data If the local adsorption isotherm and the energy distribu- by the so-called exponential adsorption isotherm (Jaroniec tion function are given by analytical expressions, Equation 2 and Bräuer, 1986) can be integrated to yield an equation for the total adsorption "# isotherm. For example, if the local isotherm is just given by XN = n ; the Langmuir equation, ylðp; eÞ¼pKðeÞ=½1 þ pKðeÞ , yð pÞ¼exp Bn ðÞkTlnðp pmÞ (6) n 1 where KðeÞ¼K0 exp½ e=kT , k is the Boltzmann constant, ¼ T is the temperature, and K0 is a constant, then one can g show that the Temkin isotherm, yðpÞ¼lnð1 þ KpÞ , corre- where fBng are the coefficients and the pressure pm sponds to a constant energy distribution function; the is associated with the minimum adsorption energy via Freundlich isotherm is associated with an exponential emin ¼ kTlnðpmÞ. The distribution function resulting from distribution and the Langmuir–Freundlich isotherm, Equations 5 and 6 is yð pÞ¼Cpg=½1 þ Cpg – with a quasi-Gaussian distribu- "#"# tion (Xia et al., 2006). In the above C; K and g are constants. XN XN n 1 n : Numerous analytical expressions for the total adsorption wðeÞ¼ nBnðe emÞ exp Bnðe emÞ isotherms obtained from Equation 2 can be found in the n¼1 n¼1 monographs of Rudziński and Everett (1992)andJaroniec (7) and Madey (1988). The above method of derivation of isotherm equations Approximation of the experimental data using Equa- can be also extended to the case of a multilayer adsorption. tion 6 must be carried out under constraint that the func- The multilayer local adsorption isotherm on tion wðeÞ is nonnegative for the energies corresponding a homogeneous surface can be described by the Brunauer, to the interval of pressures at which the isotherm was mea- Emmet and Teller (BET) equation (Brunauer et al., 1938) sured. Note that the above described method has been next extended to the case of adsorption on fractal surfaces 1 cðeÞx (Sokołowska and Sokołowski, 2008). y ðp; eÞ¼ ; (4) l 1 x 1 þ½cðeÞ 1 x The steps that lead to an appropriate solution of Equa- tion 2 must involve a correct choice of the local adsorption where x ¼ p=ps is the relative vapor pressure, ps is the isotherm and initial analysis of experimental data with saturated vapor pressure, and cðeÞ¼exp½ ðe e0Þ=kT . respect to elimination of systematic and random experi- For a quasi-Gaussian energy distribution, we obtain mental errors. Several numerical procedures for the evalu- then the multilayer Langmuir–Freundlich isotherm ation of wðeÞ from experimental adsorption data have been of the form yðxÞ¼½1=ð1 xÞf~cxg=½1 þ ~cxg g with proposed; numerous of them have been outlined by ~c ¼ exp ½ ðemin e0Þ=kT (Rudziński and Everett, 1992). Jaroniec and Bräuer (1986) and Jaroniec and Madey (1988). One of the most accurate methods is the so-called Evaluation of the energy distribution functions regularization method (von Szombathely et al., 1992). from the experimental adsorption isotherms Note that a quite analogous method was also employed When the total adsorption yðxÞ is measured experimen- to calculate the pore size distribution from experimental tally and the local adsorption model is assumed, Equa- adsorption isotherms (Kowalczyk et al., 2003). Another tion 2 can be solved (analytically or numerically) with quite accurate and numerically simple method was devel- respect to the distribution function wðeÞ. The main diffi- oped by Stanley and Guiochon (1993), who employed an culty in evaluating wðeÞ is the ill-posed nature of Equa- expectation–maximization method of parameter estima- tion 2 for some of its kernels ylð p; eÞ. Therefore, if tion to calculate adsorption energy distributions from 4 ADSORPTION ENERGY AND SURFACE HETEROGENEITY IN SOILS experimental adsorption isotherms. The method does not require any prior knowledge of the distribution function, c or the analytical expression for the experimental isotherm, 4 H O requires no smoothing of the isotherm data, and converges c 2 with high stability toward the maximum-likelihood esti- N2 mate. The method is therefore robust and accurate at high iteration numbers. The test calculations carried out by 3 b Stanley and Guiochon proved that their method is more
accurate than several previous approaches (Jaroniec and )
e a (
Madey, 1988). c One should also mention about an alternative theoreti- 2 cal approach to model adsorption by heterogeneous adsor- a bents that is based on the concept of quenched–annealed mixtures (Pizio, 2000). In the case of one-component b adsorbate, the adsorption system is considered as a two- 1 component mixture, in which one component (adsorbent) is frozen. The application of the so-called replica method- ology (Pizio, 2000) allows them to calculate adsorption isotherms. Similarly, a planar heterogeneous surface can 0 be modeled by “quenching” an imaginary “fluid of 012345 . (e−e ) adsorbing centers” (Rzysko et al., 1999). This approach, 0 /kT although theoretically promising, has been not employed to model experimental data adsorption on environmental Adsorption Energy and Surface Heterogeneity in Soils, materials so far. Figure 1 Examples of the energy distribution functions vs. dimensionless energy obtained from adsorption isotherms of nitrogen and water vapor on a sample of alluvial soil by Energetic heterogeneity of soils Sokołowska et al. (2002). Labels (a), (b), and (c) denote horizons. The concepts of adsorbent heterogeneity and the integral (Reprinted from Sokołowska et al. (2002). Copyright (2002), with adsorption equation in particular have been widely used permission from Elsevier). to study adsorption of vapors by soils (Bottero et al., 1993; Pachepsky et al., 1995; Józefaciuk and Bowanko, characteristic of a given surface. In order to associate its 2002; Sokołowska et al., 1999; 2002; Villiéras et al., particular peaks to really existing adsorption centers, addi- 2002). The energy distribution functions and the average tional studies, e.g., spectroscopic measurements of values of the energy of adsorption, < e >, adsorbed molecules, are necessary. Z < > e ¼ deewðeÞ (8) Bibliography Bottero, J. Y., Arnaud, M., Villiéras, F., Michot, L. J., de Dobato, P., obtained from experimental adsorption isotherms have and François, M., 1993. Surface and textural heterogeneity of been proved to be useful while discussing the mechanism fresh hydrous ferric oxides in water and in the dry state. Journal of adsorption, the role played by selected constituents of of Colloid and Interface Science, 159,45–52. soils and soil minerals in the adsorption process, to get Brunauer, S., Emmett, P. H., and Teller, E., 1938. Adsorption of insights into the changes in the soils caused by chemical gases in multimolecular layers. Journal of the American Chemi- cal Society, 60, 309–319. and/or treatment, and so on. Bulnes, F., Ramirez-Pastor, A. J., and Zgrablich, G., 2001. Scaling Figure 1 shows exemplary energy distribution func- behavior in adsorption on bivariate surfaces and the determina- tions obtained from the numerical solution of Equation 2 tion of energetic topography. The Journal of Chemical Physics, applied experimental data of nitrogen and water vapor 115, 1513–1521. adsorption on alluvial soils (for details see Sokołowska Jaroniec, M., and Bräuer, P., 1986. Recent progress in determination et al., 2002). Of course, the energy of interaction of of energetic heterogeneity of solids from adsorption data. Surface Science Reports, 8,65–117. a single adsorbate particle with adsorbing surface depends Jaroniec, M., and Madey, R., 1988. Physical Adsorption on Hetero- on its chemical nature. Consequently, the results for both geneous Solids. Amsterdam: Elsevier. adsorbates are different. However, the energy distribution Józefaciuk, G., and Bowanko, G., 2002. Effect of acid and alkali functions for nitrogen, as well as for water are described treatment on surface areas and adsorption energies of selected by narrow, Gaussian-like peaks. Such peaks indicate the minerals. Clays and Clay Minerals, 50, 771–783. existence of one major kind of adsorbing centers. Kowalczyk, P., Terzyk, A. P., Gauden, P. A., Leboda, R., Szmechtig-Gauden, E., Rychlicki, G., Ryu, Z., and Rong, H., The energy distribution functions and their changes 2003. Estimation of the pore-size distribution function from the due to the changes or modifications of soils depend on nitrogen adsorption isotherm. Comparison of density functional the individual soil properties, but one should remember theory and the method of do and co-workers. Carbon, 41, that function wðeÞ provides only a global energetic 1113–1125. ADSORPTION ENERGY OF WATER ON BIOLOGICAL MATERIALS 5
Pachepsky, Y. A., Polubesova, T. A., Hajnos, M., Sokołowska, Z., Definition and Józefaciuk, G., 1995. Parameters of surface heterogeneity from laboratory experiments on soil degradation. Soil Science Adsorption energy (heat) represents the difference Society American Journal, 59,68–75. between the heat of evaporation the unit quantity of Pizio, O., 2000. Adsorption in random porous media. In Borówko, a substance from the product and the heat of evaporation M. (ed.), Computational Methods in Surface and Colloid the unit quantity substance from the pure liquid state in Science. New York: M. Dekker, pp. 293–346. the same conditions (temperature, external pressure, prod- Rudziński, W., and Everett, D. H., 1992. Adsorption of Gases on uct composition, etc.). The SI unit of adsorption energy is Heterogeneous Surfaces. London: Academic. Chapters 5–10. 1 . Rzysko, W., Pizio, O., Sokołowski, S., and Sokołowska, Z., 1999. J.mol . Application of the Replica Ornstein–Zernike equations to study The adsorption energy (heat) of water is usually calcu- submonolayer adsorption on energetically heterogeneous sur- lated at constant moisture content (isosteric heat of faces. Journal of Colloid and Interface Science, 219, 184–189. adsorption). Sokołowska, Z., Hajnos, M., Borówko, M., and Sokołowski, S., 1999. Adsorption of nitrogen on thermally treated peat soils: the role of energetic and geometric heterogeneity. Journal of Introduction 219 – Colloid and Interface Science, ,1 10. The biological materials are not simple substances and/or Sokołowska, Z., Borówko, M., Reszko-Zygmunt, J., and Sokołowski, S., 2002. Adsorption of nitrogen and water vapor simple mixtures. Substances in biological materials form by alluvial soils. Geoderma, 107,33–54. aggregates in which they bond one to the other (Physical Sokołowska, Z., and Sokołowski, S., 2008. Fractal approach to Properties of Raw Materials and Agricultural Products). adsorption/desorption processes on environmental surfaces. In The consequence is that molecules of the individual sub- Senesi, N., and Wilkinson, K. J. (eds.), Biophysical Chemistry stances have lower energy in the aggregates than in pure of Fractal Structures and Processes in Environmental Systems. substance. These interactions of the individual substances New York: Willey, pp. 179–220. Stanley, B. J., and Guiochon, C., 1993. Numerical estimation of in the aggregate are described by the chemical potentials adsorption energy distributions from adsorption isotherm data (Daniels and Alberty, 1961). with the expectation-maximization method. The Journal of For biological materials, the most important component Physical Chemistry, 97, 8098–8104. is water (See also Water Effects on Physical Properties of von Szombathely, M., Bräuer, P., and Jaroniec, M., 1992. The solu- Raw Materials and Foods; Water in Forming Agricultural tion of adsorption integral–equations by means of the regulariza- Products; Drying of Agricultural Products) and that is tion method. Journal of Computational Chemistry, 13,17–32. Villiéras, F., Michot, L. J., Bardot, F., Chamerois, M., Eypert- why we deal here only with the adsorption of water. Water Blaison, C., François, M., Gérard, G., and Cases, L.-M., 2002. vapor in the surrounding air depends on the state of water Surface heterogeneity of minerals. Geoscience, 334, 597–609. inside the material. Water from the material can evaporate Xia, X., Litvinov, S., and Mühler, M., 2006. Consistent approach to into the surrounding air or water can condense on the sur- adsorption thermodynamics on heterogeneous surfaces using face of the material. Both processes, evaporation and different empirical energy distribution models. Langmuir, 22, – condensation, lead to equilibrium after some time. In this 8063 8070. state, the properties of water inside a material can be described by the properties of water vapor. This equilib- Cross-references rium is related only to the “surface,” most available water Adsorption Energy of Water on Biological Materials being in contact with water vapor; the product usually Clay Minerals and Organo-Mineral Associates contains more water that is not in contact with the vapor. Estimation of Quartz Content in Mineral Soils This water is usually more bond than the above mentioned Organic Matter, Effects on Soil Physical Properties and Processes more available “surface” water. Different mechanisms of Parent Material and Soil Physical Properties water bonding in biological materials were observed. Soil Phases The most important are participation in solution, adsorp- Specific Surface Area of Soils and Plants tion on surfaces (internal and external), adsorption in bio- logical cells, and pore adsorption. Adsorption is not usually very strong when chemical adsorption is excluded. The state of internal water can be expressed by the ADSORPTION ENERGY OF WATER ON BIOLOGICAL relative chemical potential that is termed water potential MATERIALS (Oertli, 1976; Moore, 1972). This term is in direct relation to the adsorption enthalpy. The state of water vapor in the surrounding air is well described by the relative pressure ř Ji í Blahovec that is termed water activity (Daniels and Alberty, 1961). Department of Physics, Czech University of Life Sciences, Prague 6-Suchdol, Czech Republic Water potential: adsorption enthalpy Water potential (C) is directly given by the difference Synonyms between the chemical potential of water in the material Adsorption enthalpy; Adsorption heat; Isosteric heat of (mm) and the chemical potential of pure water (m0) in the sorption same conditions: 6 ADSORPTION ENERGY OF WATER ON BIOLOGICAL MATERIALS
C ¼ m m (1) materials, this relation is more complicated. It can be m 0 obtained experimentally at constant temperature in the The water potential can be expressed either in the usual SI form of a sorption isotherm that is the plot of moisture units (J.mol 1) or it could be recalculated into another SI content (usually on dry basis) versus water activity at expression, frequently into pressure (in Pa). The chemical equilibrium and constant temperature. In most cases, the potential is the relative Gibbs potential so that its value material is in solid and/or semisolid state (Rheology in represents also the adsorption enthalpy in conditions that Agricultural Products and Foods); in this case, the adsorp- the difference between entropy of water in the material tion of water is understood and theoretically analyzed as and entropy of water in the pure state can be omitted a surface controlled process, that is, process based on (Daniels and Alberty, 1961). Water potential is frequently water deposition on the (internal surface) of the material. used to describe the status of water in living organisms Van den Berg and Bruin (1981) gave 77 types of different (See Water Effects on Physical Properties of Raw Mate- equations that can be used to describe water sorption iso- rials and Foods) (Oertli, 1976) and in soil (Blahovec, therms in foodstuffs; more than 22 of them are theoreti- 2008). Binding of water in the product is expressed by cally based on water surface sorption. The most frequent the negative value of water potential. are the Langmuir’s isotherm, BET isotherm, and GAB isotherm. Water activity The most frequent way to obtain the sorption isotherm at a sample consists in finding individual points of the Dimensionless term, water activity (aw) of water solutions can be simply estimated by the formula (Daniels and sorption isotherm. Each point is obtained by determining Alberty, 1961) the moisture content of a sample (by a gravimetric method) that was kept for long time, up to equilibrium, C at constant temperature close to an oversaturated water aw ¼ eRT (2) solution of known water activity (Karel, 1975b). where R is the universal gas constant (8.3145 J.K 1. mol 1) and T absolute temperature. Water activity then changes from 0 to 1 for water potentials from ? to 0. Isosteric heat of sorption In more complicated materials, water activity can be sim- A set of sorption isotherms obtained at different tempera- ply expressed as the ratio of fugacities of the material tures is the usual basis for determining the isosteric heat of water ( fm) and pure water ( f0): sorption DH, that is, the difference between the heat of evaporation unit quantity of water from the product and fm pm aw ¼ (3) the heat of evaporation of a unit quantity of water from f0 p0 the pure water in the same conditions. Isosteric heat of that could be approximated by the ratio of the partial water sorption of water is given by formula (Daniels and Alberty, 1961, Blahovec, 2008) vapor pressures ( pm and p0) above the corresponding water states (Daniels and Alberty, 1961). The definition ! dðln a Þ of water activity by the pressure ratio is fully correct for DH ¼ R w (4) water vapor described as an ideal gas; the water activity d 1 of the material is then given directly by the air humidity T MC being in equilibrium with the material. The difference where MC denotes that the derivative is calculated at con- between water activity based on the fugacity and on the stant moisture content. The experimental values of water pressure increases with deviations of the water vapor activity are usually well given by an exponential function properties from properties of the ideal gas, for example, of reciprocal absolute temperature (see Equation 2) so that with increasing moisture content of the material. the isosteric heat of sorption is nearly independent of Water activity is a crucial parameter for the living activ- temperature. ity of agroproducts and the activity of their components – The isosteric heat of sorption in real biological mate- (enzymes, microorganisms, etc. see Karel, 1975b, rials increases with decreasing water activity (decreasing Fennema, 1976). This is very important for storage of agri- moisture content) similarly as the absolute value of the cultural products (See also Physical Phenomena and water potential in Equation 2 at least at moisture contents Properties Important for Storage of Agricultural Prod- higher than approximately 10% w. b. At lower moisture ucts; Physical Properties as Indicators of Food Quality). contents, Equation 2 loses its validity for real biological materials: Sorption isotherm The vapor pressure of the solvent in a solution can be DHR CR DHT CT (5) expressed by Raoult’s Law (Daniels and Alberty, 1961; Karel, 1975a, Moore, 1972) and the relation between where index R denotes water in real biological moisture content and water activity can be estimated on materials and index T denotes data based on water vapor this base. In real water solutions and/or more complex as an ideal gas. AERATION OF AGRICULTURAL PRODUCTS 7
Direct and indirect methods for determination Principles of Food Science, Karel, M., Fennema, O.R., and Lund, of the heat of adsorption D. B. (eds.), Part II Physical Principles of Food Preservation,New York: Marcel Dekker, pp. 219–236. Direct methods for the determination of the heat of adsorp- Karel, M., 1975b. Water activity and food preservation. In tion meet experimental difficulties when they are applied Fennema, O. R. (ed.), Principles of Food Science, Karel, M., to biological experimental materials (Heiss, 1968). The Fennema, O.R., and Lund, D. B. (eds.), Part II Physical Princi- biological materials are sensitive to changes of external ples of Food Preservation, New York: Marcel Dekker, parameters (temperature, pressure, see also Stomatal Con- pp. 237–263. Moore, W. J., 1972. Physical Chemistry. Englewood Cliffs, USA: ductance, Photosynthesis, and Transpiration, Modeling) Prentice Hall. that usually lead to changes of the physical state of the bio- Nelson, S. O., and Trabelsi, S., 2005. Permittivity measurements logical material. Hence, the direct experimental methods and agricultural applications. In Kupfer, K. (ed.), Electromag- have only limited application in the determination of the netic Aquametry. Berlin: Springer Verlag, pp. 419–442. heat of adsorption of biological materials. Oertli, J. J., 1976. The states of water in the plant. Theoretical Among indirect methods, the most frequent is the considerations. In Lange, O. L., Kappen, L., and Schulze, E.-D. above mentioned method based on the sorption isotherms. (eds.), Water and Plant Life. Problems and Modern Approaches. Berlin: Springer-Verlag, pp. 19–31. From the others, the methods based on the determination Van den Berg, C., and Bruin, S., 1981. Water activity and its estima- of the points of melting and evaporation can be also tion in food systems: theoretical aspects. In Rockland, L. B., and applied (Daniels and Alberty, 1961; Heiss, 1968). New Stuards, G. F. (eds.), Water activity. Influence on Food Quality. ways for studying water sorption in biological materials New York: Academic Press, pp. 1–61. have been developed (e.g., Nelson and Trabelsi, 2005). The highest values of the isosteric heat of adsorption Cross-references (20–30 kJ.mol 1) are observed in biological materials at Drying of Agricultural Products low moisture contents (lower than about 5% w.b.). These Physical Phenomena and Properties Important for Storage of values are about one half of the heat of vaporization of Agricultural Products water (Water in Forming Agricultural Products; Blahovec, Physical Properties as Indicators of Food Quality Physical Properties of Raw Materials and Agricultural Products 2007; 2008). Rheology in Agricultural Products and Foods Stomatal Conductance, Photosynthesis, and Transpiration, Modeling Conclusion Water Effects on Physical Properties of Raw Materials and Foods The adsorption energy of water (AEW) on biological Water in Forming Agricultural Products materials depends on the material moisture content. At higher moisture contents, AEW increases with decreasing moisture content in a similar manner as the absolute value of water potential increases with decreasing water activity. ADVECTION At the lowest moisture contents (less than 5%), the AEW reaches in many cases nearly constant values 20–30 kJ. See DNA in Soils: Mobility by Capillarity mol 1 that represent about half of the heat of evaporation of water. Cross-references The AEW is well described by isosteric heat of sorption Soil–Plant–Atmosphere Continuum that could be easily obtained from sorption isotherms measured at different temperatures. Direct methods for measurement of AEW are difficult to apply to AEW of biological materials. Application of physical chemistry AERATION OF AGRICULTURAL PRODUCTS to the calculation of AEW usually fails either due to the limited applicability of ideal gas conception or compli- Marek Molenda cated aggregate structure of biological materials. Institute of Agrophysics, Polish Academy of Sciences, Lublin, Poland Bibliography Blahovec, J., 2007. Role of water in food and product texture. Inter- Definition 21 – national Agrophysics, , 209 215. Aeration, that is, forced ventilation of ambient or refriger- Blahovec, J., 2008. Agromaterials. Study Guide. Prague: Czech University of Life Sciences. ated air through stored products is necessary to maintain Daniels, F., and Alberty, R. A., 1961. Physical Chemistry. their quality. The main purpose of aeration is to minimize New York: Wiley. a risk of storage losses through equalizing temperatures in Fennema, O. R., 1976. Water and ice. In Fennema, O. R. (ed.), a bedding in order to minimize moisture movement, to Principles of Food Science, Part II Physical Principles of Food cool product for pest control, and to stop product heating. Preservation, New York: Marcel Dekker, pp. 13–38. Heiss, R., 1968. Haltbarkeit und Sorptionsverhalten wassearmer Background Lebensmittel. Berlin: Springer-Verlag. Karel, M., 1975a. Equilibrium and rate considerations in processes Certain biological reactions generate heat and often it is for food concentration and dehydrations. In Fennema, O. R. (ed.), necessary to remove it, that is, to cool the product. Heating 8 AERATION OF SOILS AND PLANTS and cooling (see Heat Diffusion) large amounts of biolog- the activity of typical storage fungi is very low below ical material require energy and time so the knowledge this temperature. In spring, warming of grain is necessary about the process is necessary to optimize operations. if extended storage (post June) is required or if the temper- Heating or cooling is not an uniform inside the volume ature of grain is below 0 C. Typical aeration airflow rates of layer of material, rather heating or cooling front passes range from 1 to 2 L of air per second per cubic meter through the material. The velocity and thickness of the of grain (1–2 L/(s m3)). Higher rates should be used front are dependent on the air velocity (see Air Flux (2–6 L/(s m3)) if grain is stored at higher moisture levels (Resistance) in Plants and Agricultural Products), the or if a large variance in incoming moisture levels exist. evaporation rate, the temperature difference, and the sizes An aeration system cannot be considered a drying (see of particles (see Pore Size Distribution). Usually, the air Drying of Agricultural Products) system since natural air velocity is a crucial factor. In design of processes or equip- drying rates are at least 10 times longer. ment mathematical equations describing heating or cooling are used that are derived with necessary simplify- ing assumptions. Usually, the most important assumptions Conclusion are as follows: the material is isotropic (see Isotropy and Aeration and controlled atmosphere storage are still under Anisotropy in Agricultural Products and Foods) in terms development to elaborate efficient methods for control of of thermal and mass diffusivity; the temperature, moisture temperature and moisture of product, as well as for elabo- content, and porosity of the layer are initially identical in ration of optimum strategies specific for crop, storage the volume and porosity does not change during the pro- structure, and climatic conditions. Currently, investiga- cess; the temperature of the moving air does not change tions are conducted on characterization of bedding anisot- observably, walls limiting the considered volume are iso- ropy and including this into strategies of aeration control lated, and fluctuations of external temperature are negligi- (Navarro and Noyes, 2001). ble. Differential equations are formulated and solved numerically that allow to estimate movement of heat front. Bibliography Loewer, O. J., Bridges, T. C., and Bucklin, R. A., 1994. On-Farm Grain aeration Drying and Storage Systems. St. Joseph: American Society of Agricultural Engineers. The process of aeration of grain will be described below as Navarro, S., and Noyes, R. T., 2001. The mechanics and Physics of probably the most common at the farm. Grain is good Modern Grain Aeration Management. Boca Raton: CRC Press. insulator (see Grain Physics) and heat loss from it is rela- tively low as compared to other materials. Grain is usually Cross-references placed in a storage silo in the fall and its portion near the Air Flux (Resistance) in Plants and Agricultural Products center tends to remain near the temperature at which it Drying of Agricultural Products came from the dryer or field. The grain near the silo wall Grain Physics tends to cool to near the average outside temperature. With Heat Diffusion a decrease in the ambient temperature, the difference Isotropy and Anisotropy in Agricultural Products and Foods between the temperature in the center and near the wall Pore Size Distribution produces air currents inside the grain mass. The colder Water Effects on Physical Properties of Raw Materials and Foods air near the wall is denser and tends to fall, while warmer air flows up through the center of grain mass. Warmer air contains more moisture and when it reaches top center of the silo fill it cools to a point at which it cannot hold all AERATION OF SOILS AND PLANTS moisture it had absorbed. The excess moisture condenses at the top layer of grain and creates an environment Witold Stępniewski enhancing mold and insect growth. The opposite situation Department of Land Surface Protection Engineering, occurs in warmer periods, the moisture condenses near the Lublin University of Technology, Lublin, Poland bottom center of grain mass. The problem of air currents within the grain mass may Synonyms be minimized by keeping the temperatures near the center Gas exchange in soils; Oxygenation of soils and plants; close to the average temperature near the wall of the stor- Oxygenology of soils and plants age silo (Loewer et al., 1994). To accomplish this aeration fans may be used that pull air down through the grain until the temperature of grain mass is within 5 C of the average Definition monthly temperature. Aeration air can move either up or Aeration of soils and plants is a term used in wide sense as down through the grain mass. Most fans have the ability a name of complex issues related to air transport and dis- to either push or pull, however, airflow volumes and tribution in soil and its effect on processes occurring in soil power requirements will often change due to direction. It and plants. Sometimes it is used in a narrow sense to is not necessary to cool the grain mass below 5 C, because denote gas exchange between soil and atmosphere, or only AERATION OF SOILS AND PLANTS 9 oxygen content in soil air or even as a name for a process is without plants, the downward transport of gases practi- of artificially forcing air into the soil (Gliński and cally ceases while the gases generated in the soil such as Stępniewski, 1985). CO2 and CH4 are released to the atmosphere by ebullition. Between these two pathways, there are numerous inter- Introduction mediate situations with different contributions of soil- and In soil medium intensive production, transformations, and plant-mediated transport of gases dependently on the land consumption of a number of gases, which are transported use and tillage influencing air-filled porosity, gas diffusion to and from the atmosphere, take place. These processes coefficient, and air permeability of soil (Stępniewski and are not only important for the production of plant biomass Stępniewska, 2009). Agricultural land use is connected but also play an important environmental role. mainly with dryland conditions as wetland rice cultivation The most important soil gasses are oxygen (indispens- produces about 20% of food calories (IRRI, 2005). There able for root respiration and important for microbial are also examples of intermediate systems such as metabolism and for numerous biochemical and chemical midseason drainage of paddy fields to prevent toxicity of processes) and carbon dioxide (product of oxic respira- sulfides (Kanno et al., 1997), combining cultivation of tion of plant roots, microorganisms, and mezo- and lowland rice with dry season crops (So and Ringrose- macrofauna, as well as anoxic microbial respiration and Voase, 2000) as well as so-called system of rice intensifi- fermentation). Nitrogen, important for its fixation by some cation characterized by change from permanent flooding microbes, draws less attention because it is considered as to intermittent irrigation (Dobermann, 2004) to improve non-limiting due to its abundance. the oxygen supply to rice roots (Stoop et al., 2002). Soil air contains, moreover, a number of gases occur- ring in trace amounts such as nitrous oxide (N2O), nitro- Mechanism of gas exchange gen oxide (NO) and dioxide (NO2), ethylene, ammonia There are two essential mechanisms of gas exchange in (NH3), and hydrogen sulfide (H2S). An intermediate posi- soil medium: mass flow or advection (convection) and tion occupies methane which under dryland conditions molecular diffusion. Both these mechanisms can take occurs in trace amounts but under wetland conditions place in soil pores as well as in plant tissues. The relative and under landfill conditions can occupy a substantial contribution of both mechanisms of gas exchange can fraction of the soil air. Dependently on the aeration status, vary within wide limits dependently on the conditions. the soil can be a source or a sink of greenhouse gasses such as CH4 and N2O. Mass flow The driving force of mass flow is pressure gradients Pathways of gas exchange appearing within soil or plants due to fluctuations of atmo- There are two essential pathways of the gas transport in spheric pressure, variability of temperature, changes of the soil–plant–atmosphere continuum (see Soil–Plant– groundwater depth, infiltration of rainwater, as well as Atmosphere Continuum): the soil pathway and the internal humidity-induced convection in leaves and Venturi con- pathway through the plant tissues (Figure 1). The first one vection caused by wind action (Armstrong et al., 1996). prevails in soils cultivated under dryland conditions, while Of these drivers only fluctuations of atmospheric pressure the plant pathway dominates in natural and constructed may be of importance in the soils with very deep impervi- wetlands and paddy fields (e.g., Yan et al., 2000). If the soil ous layer.
N2 CH CO O2 4 2 N2O CO NO 2 Water O2
NH3 Oxic H2S CH4 O2 Anaerobic CO2 CO2 CO CH 2 Ebullition 4 Anoxic
Ground water Dryland Wetland
Aeration of Soils and Plants, Figure 1 Model of the two pathways of gas exchange in the atmosphere–plant–soil continuum. Dryland conditions – oxygen is supplied to the plant roots via the soil. Wetland conditions – oxygen is transported through the tissues of the plant itself. 10 AERATION OF SOILS AND PLANTS
In case of laminar flow (see Laminar Flow) usually Diffusion occurring in soil, when the Reynolds’s number < 1 The basic mechanism of gas exchange in the soil medium (Currie, 1970) the movement of gases is described by and within the plant tissues is the concentration diffusion Darcy’s equation: induced by concentration gradients. dV k dp The diffusive flow fx of a gas within a porous medium is ¼ A (1) described by the first Fick’s law. dt dx = where dV/dt is the volumetric rate of gas flow, m3 s 1, A is fx ¼ DdC dx (2) the cross-sectional area of the porous medium, m2; is the 1 1 The above equation says that the uniaxial diffusion flow dynamic viscosity of the gas, kg m s ;dp/dx is the 1 2 2 (f ) of an agent through a unit cross-section, in a unit of pressure gradient, Pa m =kgm s ; and k is the air x 2 time, is proportional to the concentration gradient (dC/ permeability, m . dx) and to the diffusion coefficient D characterizing the According to Gliński and Stępniewski (1985), the mobility of the agent in a given medium. values of air permeability in soil are within the range of Coefficient of gas diffusion in soil depends on the 0.01–500 10 12 m2. Air permeability depends in gen- kind of gas, its temperature, and pressure, and also on eral terms on the quantity and quality of air-filled pores. the amount of air-filled pores, their continuity, and The latter term relates to the pore size distribution, conti- shape which depend on the spatial arrangement of soil nuity, and tortuosity, which, in turn depend on the arrange- particles and on distribution of water. The diffusive ment of soil particles, on soil bulk density, and water properties of a soil medium are usually characterized content. Advective gas flow depends on the fourth power by the relative diffusion coefficient D/D , being the ratio of the pore size. o of gas diffusion coefficient in soil D, to that of the same Morphological changes within plants are very impor- gas in atmospheric air D , under the same pressure and tant adaptation to flood conditions. They include develop- o temperature conditions. The D/D value does not ment of a shallow root system, formation of adventitious o depend on the temperature, pressure, or the kind of the roots of high porosity, formation of aerenchyma within diffusing gas. roots (Gliński and Stępniewski, 1985), and development The influence of soil bulk density and soil moisture ten- of aerial roots or pneumatophores (e.g., Purnobasuki and sion on D/D is presented in Figure 3. The value of D/D Suzuki, 2005). o o in soil is usually below 0.2. It increases with soil moisture The internal air flux ability of the plant tissues can be tension, and rapidly decreases with soil bulk density. It a permanent feature or it may become apparent or should be stressed out that gas diffusion coefficient in enhanced under oxygen deficiency conditions (Figure 2). porous media does not depend on the size of the pores, Internal transport of oxygen via plant roots can cover not as long as the pore diameters are greater than the mean free only oxygen demand of the plant roots, but also can pro- 2+ path of the molecules of the gas under consideration. tect the plants against Fe and H S toxicity (Jayakumar 2 (Gliński and Stępniewski, 1985). This limit is the pore et al., 2005). It should be emphasized that an increase of diameter of 0.10 mm. In the case of soil, pores of that size internal porosity of root tissues increases both air perme- are emptied of water at soil moisture tension levels over ability as well as gas diffusion coefficient. 3 MPa (pF > 4.5), i.e., at moisture contents lower than the permanent wilting point. Thus, gas diffusion within macropores (above 30 mm) as well in the mezopores (30–0.2 mm) containing usually plant available water does 0.30 not depend on the pore size.
0.25 D/Do usually shows a curvilinear relationship versus Eg, as shown in Figure 4. It can be described by an empir- 0.20 ical power model in the following form:
0.15 D m ¼ g Eg (3) 0.10 Do
0.05 where g and m are empirical coefficients characterizing the porous material.
Root porosity, fraction of root volume fraction Root porosity, 0.00 0255075100125 150 The author was unable to find literature data related to ODR, μg m−2 s−1 direct measurements of gas diffusion coefficients within living plant tissues. Aeration of Soils and Plants, Figure 2 The relationship It should be underlined that the composition of air between oxygen availability in soil medium as characterized by within the intra-aggregate pores may differ from that oxygen diffusion rate (ODR) and the internal porosity of rice in the inter-aggregate pores due to soil heterogeneity. roots. (Modified from Ghildyal [1982].) The former pores contain less oxygen and more AERATION OF SOILS AND PLANTS 11
D/D0 0.18 d (Mg m−3) D/D0 1.00 0.16 0.16 1.22 1.37 1.40 0.14 0.14
0.12 0.12
0.10 0.10
0.08 0.08
0.06 0.06
0.04 0.04
0.02 0.02 D/D0 = 0.02
0.10 0.20 0.30 0.40 1.07 3 −3 B. density (Mg.m 100 Eg (m m ) 1.27 D/D0 = 0.005 50 Aeration of Soils and Plants, Figure 4 Relationship of D/Do 1.48 30 to air-filled porosity E , of silt Fluvisol at different bulk 1.51 g − 10 densities d. (Modified from Ste˛pniewski [1981].) 3 1.61 S.m. tension (kPa) ) 1.64
Aeration of Soils and Plants, Figure 3 Dependence of relative With respect to oxygen requirements, soil microbes are gas diffusion coefficient in a loamy textured Phaeozem (Kock, divided into obligate oxic, facultative anoxic, and obligate Poland) on soil moisture tension and bulk density. (Modified anoxic organisms (obligate anaerobes). A special group of from Ste˛pniewski [1981].) microorganisms constitute microaerophiles characterized by oxygen optimum of order 2–10% by volume (Black, 1996). Oxic microorganisms utilize oxygen as a terminal carbon dioxide compared to the inter-aggregate pores electron acceptor from the cytochrome oxidase. (e.g., Zausig et al., 1993; Højberg et al., 1994; Horn, 1994; Soil microbial activity depends both on oxygen and Horn and Smucker, 2005). carbon dioxide concentration, independently. Carbon dioxide is a carbon source for autotrophic microflora. Dommergues and Mangenot (1970) reported 2–14% Oxygen CO2 as the optimal range for the growth of these bacteria. Oxygen is taken up by the soil due to respiration of micro- For other microorganisms, carbon dioxide is an inhibitor organisms and plant roots. Respiration of soil microorgan- of respiration and growth although some microorganisms isms depends on the availability of oxygen, organic display metabolic stimulation by low CO2 concentration carbon, and nutrients as well on temperature and water and inhibition above a certain CO2 concentration (Dixon content. The temperature interval for microbial growth et al., 1998; Sierra and Renault, 1995). ranges from 12 Cto110 C. Microorganisms with The dependence of microbial respiration on water respect to their temperature requirements are divided into content shows a maximum corresponding to the range of psychrophilic, mesophilic, and termophilic (Paul and optimal availability of oxygen and water. With respect to Clark, 1998). A new term “hypertermophiles” denotes water requirements, the soil microorganisms are divided extreme thermopiles growing in the temperature range (Gliński and Stępniewski, 1985) into hydrophilic (disap- from 60 Cto110 C. Soil contains a mixture of different pearance of activity at pore water pressure > 7.1 MPa), groups of microorganisms and its respiration rate mesophilic (disappearance of activity within the pore increases two to three times with the increase of tempera- water pressure interval from 7.1 to 30 MPa), and ture by 10 C until the temperatures of break of metabo- xerophilic (disappearance of activity at pore water pres- lism (at about 60–70 C). sures < 30 MPa). Under field conditions, the rate of soil 12 AERATION OF SOILS AND PLANTS
5
4 ) 1 − 2 day 2
− 3 m 3
2 uptake (dm uptake
2 1 O Aeration of Soils and Plants, Figure 5 Diurnal dynamics of soil 1 respiration rate as measured by oxygen uptake and temperature. (Modified from Currie [1975].)
0 microbial respiration is usually within the range from J 1970D J 1971 O 0.1 to 10 mg m 3s 1 (Gliński and Stępniewski, 1985). The root respiration rate depends on plant internal fac- Aeration of Soils and Plants, Figure 6 Annual dynamics of tors such as plant type and development stage, root mass soil respiration as measured by oxygen uptake rate in an uncropped (1) and cropped (2) soil under moderate climate distribution, dimensions, and physiological age of the conditions of England. (Modified from Currie [1975].) tissue, as well as on external factors such as temperature and the availability of water and nutrients. It should be emphasized that soil microbial activity increases in the presence of plant roots due to production of root exudates Carbon dioxide and other gases being a source of easily available carbon for microorgan- Production of carbon dioxide in soil under oxic conditions isms. Respiration rate of the root tissues is about two is directly related to oxygen uptake and all the factors orders of magnitude of that of the soil itself and ranges influencing oxygen uptake affect also the emission of from 10 to 50 mg m 3s 1 (Gliński and Stępniewski, carbon dioxide. 1985). Because of complementary character of oxygen uptake Oxygen uptake by a cropped field is a sum of microbial and carbon dioxide production their sum in soil air is and root respiration and under field conditions is of order usually about 20% by volume (cf. Figure 7). It means that of several tons of oxygen per hectare and year (Gliński and also their fluxes between soil and the atmosphere are Stępniewski, 1985). Soil respiration under field conditions approximately equal. Concentration of oxygen in soil air (Figure 5) shows a maximum in the afternoon and mini- decreases with depth and that of CO2 increases. The com- mum before sunrise. In the moderate climate zone, the position of soil air is a decisive factor for microbial and annual dynamics of oxygen uptake under field conditions plant metabolism, for many oxidation–reduction reactions is characterized by a summer maximum (Figure 6). and oxidation state of numerous soil nutrients, as well as It should be emphasized that the presence of plants may for soil fertility and crop productivity. It should be kept elevate the oxygen uptake more than twice. in mind that under anoxia CO2 can be produced without The oxygen deficiency in soil affects the plant perfor- oxygen consumption (sum of O2 and CO2 >20%) and mance directly by limitation of root respiration, of energy the emission of CO2 from the soil exceeds the volume of supply, and changing the metabolism in the root tissue oxygen taken up. However, long-term CO2 emission itself, as well as indirectly by inducing chemical and under anoxia is reduced, what leads to carbon accumula- biological changes in the surrounding soil (e.g., oxida- tion in soil. tion–reduction reactions (see Oxidation–Reduction Reac- Soil aeration state effects not only global turnover of tions in the Environment), accumulation of phytotoxic oxygen and fluxes of greenhouse gases (see Greenhouse substances, changes of pH and ion exchange equilibria). Gas Fluxes: Effects of Physical Conditions) such as car- Effects of deficient aeration can be manifested in plant bon dioxide, methane, and nitrous oxide but also the emis- roots in the form of ethanol and ethylene generation, sion of ammonia, NOx, and ethylene. Methane emission reduced water permeability, growth inhibition, and necro- increases under anoxic conditions. Ethylene is generated sis. The shoot response comprises stomatal closure, within plants under moderate hypoxia. Nitrous oxide is chlorosis, epinasty, leaf senescence and abscission, partial formed and is stabile under moderate hypoxia and or complete suppression of photosynthesis (see Photosyn- undergoes decomposition both under oxic conditions thesis), and growth leading to reduction of biomass and and under severe anoxia. Ammonia under oxic condi- yield (Glinski and Stępniewski, 1985). tions undergoes oxidation to nitrates. AERODYNAMICS 13
Value (%) Horn, R., 1994. Effect of aggregation of soils on water, gas and heat transport. In Schulze, E. E. (ed.), Flux Control in Biological 0 5 50 15 20 Systems. San Diego: Academic, Vol. 10, pp. 335–361. 0 Horn, R., and Smucker, A., 2005. Structure formation and its CO2 O 2 consequences for gas and water transport in unsaturated arable and forest soils. Soil and Tillage Research, 82,5–14. IRRI, 2005. World Rice Statistics. http://www.rri.org/science/ 20 ricestat. Jayakumar, B., Subathra, C., Velu, V., and Ramanathan, S., 2005. Effect of integrated crop management practices on rice (Oryza sativa L.) root volume and rhizosphere redox potential. Agron- omy Journal, 4,311–314. 40 H = 85 cm Kanno, T., Miura, Y., Tsuruta, H., and Minami, K., 1997. Methane emission form rice paddy fields in all of Japanese prefecture. Nutrient Cycling in Agroecosystems, 49, 147–151. Paul, E. A., and Clark, F. E., 1998. Soil Microbiology and Biochem-
Depth (cm) istry. San Diego: Academic. 60 Purnobasuki, H., and Suzuki, M., 2005. Functional anatomy of air conducting network on the pneumatophores of a mangrove plant, Avicennia marina (Forsc.) Vierh. Asian Journal of Plant Sciences, 4, 334–347. 80 Sierra, J., and Renault, P., 1995. Oxygen consumption by soil microorganisms as affected by oxygen and carbon dioxide H = 150 cm levels. Applied Soil Ecology, 2, 175–184. So, H. B., and Ringrose-Voase, A. J., 2000. Management of clay soils for rain fed lowland rice-based cropping systems: an over- 100 view. Soil and Tillage Research, 56,3–14. Stępniewski, W., 1981. Oxygen diffusion and strength as related to Aeration of Soils and Plants, Figure 7 Distribution of oxygen soil compaction. II. Oxygen diffusion coefficient. Polish Journal 14 – and carbon dioxide concentration in a gley meadow soil of Soil Science, ,3 13. ę ę – (Garbow, near Lublin, Poland) at two levels of ground water St pniewski, W., and St pniewska, Z., 2009. Selected oxygen – on 1971.06.19 (ground water level H = 85 cm) and the same dependent processes response to soil management and tillage. 102 – point on 1971.09.04 (H = 150 cm). (From unpublished data Soil and Tillage Research, , 193 200. of Ste˛pniewski.) Stoop, W. A., Uphoff, N., and Kassam, A., 2002. A review of agri- cultural research issues raised by the systems for resource-poor farmers. Agricultural Systems, 71, 249–272. Yan, X., Shi, S., Du, L., and Xing, G., 2000. Pathways of N2O Bibliography emission from rice paddy soil. Soil Biology and Biochemistry, Armstrong, J., Armstrong, W., Beckett, P. M., Halder, J. E., Lythe, 32, 437–440. S., Holt, R., and Sinclair, A., 1996. Pathways of aeration and Zausig, J., Stępniewski, W., and Horn, R., 1993. Oxygen concentra- the mechanisms and beneficial effects of humidity – and Ven- tion and redox potential gradients in different model soil aggre- turi-induced convections in Phragmites australis (Cav.) Trin. gates at a range of low moisture tensions. Soil Science Society ex Steud. Aquatic Botany, 54, 177–197. of America Journal, 57, 906–916. Black, J. G., 1996. Microbiology. Principles and Applications, 3rd edn. Upper Saddle River: Prentice Hall, pp. 144–148. Currie, J. A., 1970. Movement of gases in soil respiration. In Sorp- Cross-references tion and Transport Processes in Soil. S.C.I. Monograph No. 37, Air Flux (Resistance) in Plants and Agricultural Products London: Society of Chemical Industry. Bulk Density of Soils and Impact on Their Hydraulic Properties Currie, J. A., 1975. Soil respiration. Ministry of Agriculture, Fisher- 29 – Climate Change: Environmental Effects ies and Food. Technical Bulletin, , 461 468. Greenhouse Gas Fluxes: Effects of Physical Conditions Dixon, N. M., Lovitt, R. W., Morris, J. G., and Dell, D. B., 1998. Greenhouse Gases Sink in Soils Growth energetic of Clostridium sporogenes NCIB 8053: modu- 65 – Laminar and Turbulent Flow in Soils lation by CO2. Journal of Applied Bacteriology, ,119 133. Oxidation–Reduction Reactions in the Environment Dobermann, A., 2004. A critical assessment of the system of rice 79 – Oxygenology intensification (SRI). Agricultural Systems, , 261 281. Soil–Plant–Atmosphere Continuum Dommergues, Y., and Mangenot, F., 1970. Ecologie Microbienne Stomatal Conductance, Photosynthesis, and Transpiration, du Sol. Paris: Mason. Modeling Ghildyal, B. P., 1982. Nature, physical properties and management of submerged rice soils, Transections of the 12th International Congress of Soil Science, New Delhi, India. In Vertisols and Rice Soils of the Tropics, Symposium papers II, Shri S.N. Mehta, New Delhi, India. AERODYNAMICS Gliński, J., and Stępniewski, W., 1985. Soil Aeration and Its Role for Plants. Boca Raton: CRC Press. Højberg,O.,Revsbech,N.P.,andTiedje,J.M.,1994.Denitrificationin See Cultivation Under Screens, Aerodynamics of Bound- soilaggregatesanalyzedwithmicrosensorsfornitrousoxideandoxy- ary Layers; Grains, Aerodynamic and Geometric gen.SoilScienceSocietyofAmericaJournal,58,1691–1698. Features 14 AFTER HARVEST TECHNOLOGY
Design is an intellectual activity; it is the oldest mental AFTER HARVEST TECHNOLOGY process engaged in by man to solve complex problems, develop and improve technical systems, including farm- See Mechanical Impacts at Harvest and After Harvest ing and food processing machines. Design is a process Technologies of drawing logical conclusions from empirical observa- tions. It enables man to create artificial objects that support his existence and to introduce technical systems into the AGGREGATE STABILITY natural environment. A machine is a set of interconnected elements that per- form a given set of operations, carry the load and the See Cropping Systems, Effects on Soil Physical Properties moment of force to perform useful work as an energetic Cross-references effect, and transform any type of energy into mechanical energy or mechanical energy into a different type of Soil Aggregates, Structure, and Stability energy. Motion is transferred by mechanisms.
Introduction AGGREGATION INDICES The primary goal of physics is to examine the material world and search for the truth and the fundamental proper- Soil aggregation may be determined through the following ties of matter on the assumption that the laws of physics indices: dispersion ratio, Wischmeier’s erodibility index, are consistent and universal. Physics studies natural clay dispersion index, clay flocculation index, geometric objects with the application of universal methods, con- mean diameter and mean -weigh diameter. cepts, and laws. Physical sciences support the design of farming and food processing machines by solving com- plex problems relating to the physical properties of soil, Bibliography organic materials, and food products with the use of Igwe, C. A., Akamigbo, F. O. R., and Mbagwu, J. S. C., 1995. The methods that involve the determination of physical quan- use of some soil aggregate indices to assess potential soil loss tities and process descriptions, based on the principles of in soils of South-Eastern Nigeria. International Agrophysics, 9, mechanics, thermodynamics, optics, electrodynamics, 95–100. electronics, acoustics, and nuclear, molecular, and solid- state physics, as well as the principles of other modern fields of physics. AGRICULTURAL PRODUCTS Rising competition in food production requires product quality growth and production costs reduction. Physical prosperities of raw materials make designing agricultural See Agrophysical Objects (Soils, Plants, Agricultural machinery and food processing machinery difficult. Products, and Foods); Agrophysics: Physics Applied to Precise knowledge of raw material prosperities is Agriculture a condition to create appropriate food processing technol- ogies and machinery. There are many problems to solve in machine designing, e.g., soil degradation, excessive AGRICULTURAL RAW MATERIALS chemicalization, food safety, etc. Sciences as agrophysics, agricultural engineering, food engineering, and other See Physical Properties of Raw Materials and Agricul- related sciences as mechanics, mechatronics, computer tural Products sciences, genetic engineering are used to help with gather- ing and receiving information for machine designing. Changing rapidly global economy uses robots on a big scale in food production. Today human work in food pro- AGRICULTURE AND FOOD MACHINERY, duction is replaced by machinery with complicated mech- APPLICATION OF PHYSICS FOR IMPROVING anisms, working units, sensors, and board computers. In current mechanical production dynamic development of Leszek Mieszkalski mechanization, atomization and robotics takes place. Department of Agricultural Engineering and Natural Raw Materials, University of Varmia and Mazury in Olsztyn, The importance of the physical properties of raw Olsztyn, Poland materials and food products in machines designing Definition Animate and inanimate matter differs as regards the values Physics is the science concerned with the study of matter of state parameters such as temperature, pressure, radia- and natural forces, such as light, heat, movement. tion field intensity, and humidity. Live cells of animate AGRICULTURE AND FOOD MACHINERY, APPLICATION OF PHYSICS FOR IMPROVING 15 matter used in the production of food have a highly com- Measurement precision determines the quality of physical plex microstructure, and its specific attributes, the observation. The results of measurements in a discrete sys- observed chemical and biological processes reflect the tem are expressed in the form of a finite set of numbers to universal laws of physics. The laws of physics attributed which quantitative data are attributed. The studied pro- to complex systems imply various characteristic proper- cesses involve recurring phenomena and phenomena that ties that have to be taken into account when designing constitute the laws of physics. Those phenomena can be food processing machines. Raw materials and food prod- used to formulate theoretical structures and design many ucts have unique physical characteristics such as stretch, practical applications. The laws of physics are expressed location, velocity, mass, momentum, temperature, color, in the form of mathematical relations between symbols and chemical and biological attributes. The raw materials representing different quantities. The discovery of new, used in the production of foodstuffs are examined with validated laws of physics expressed by equations and the use of physical methods to select the appropriate work- inequations supports the examination of the resulting con- ing parameters of the designed farming and food sequences. The application of physics theories in engi- processing machines. The study of physical phenomena neering and machine construction, including farming and occurring in plant and animal material, i.e., anisotropic food processing equipment, is important for the process objects, in an unstable and an unpredictable environment of designing processing technologies. The physical prop- poses a challenge for contemporary physics which, in erties of raw materials are transformed during processing addition to investigating the occurring processes, accumu- into food products. The principal physical quantities lating data and expanding our knowledge base, also aims describing a particle of the studied raw material or product to expand the intellectual capacity of technical sciences are particle mass, vectors of position, and forces applied to and offers solutions to specific problems. Scientific those particles. If those quantities are known at a given knowledge should have a practical dimension, and it time, then the velocity and acceleration of particle mass should satisfy man’s nutritional needs. Physical phenom- moved by that force is also known. Other quantities ena are described with the involvement of measurable include momentum, angular momentum, and torque. properties, referred to as physical quantities. The process Newton’s laws of dynamics, described as a system of three of examining the physical phenomena attributed to raw quadratic differential equations for unknown time func- materials for the food industry can be divided into several tions, support an infinite number of solutions. A fixed stages. The first stage involves the selection of parameters solution can be obtained only by determining the initial that support the investigation of the studied object’s suit- conditions. ability for processing and its description. The method of In the process of building farming and food processing measuring the selected parameters is determined at the machines with the use of laws of physics that describe the second stage. At the third stage, researchers develop the general relationships associated with an infinite number of general concept and the structure of measuring equipment; physically admissible solutions, a specific physical situa- they select the units of measurement and calibrate tools. tion at a given point in time should be determined and At the following stage, measurements are performed at implemented. Food engineering deals with various the required level of precision, the results are analyzed, objects, including elementary particles, atoms, cells, tis- and conclusions are formulated. At successive stages, the sues, ions, molecules, systems of microscopic and macro- obtained results are applied to design and upgrade farming scopic particles as well as fields. One of the many goals of and food processing machines. food engineering is the use of physics theories, namely the The relationship between motion and the force of raw laws of physics written down in mathematical form, in material and food product molecules at the microstructure a strictly defined environment. The above also applies to level is very important during the construction of farming farming and food processing equipment, raw materials and food processing machines. Motion is described with of plant and animal origin, and end products. For the use of parameters such as the components of a physics theory to be useful in the process of solving tech- a position vector that changes over time, which are attrib- nical problems, the number of predictions has to be consis- uted to the discrete morphological elements of a biological tent with experimental results. Established physics object. The measured quantities include distance, angle, theories are not always fit for use in farming and food and time. The correlation between the above quantities is engineering. Despite their universal character, the applica- investigated with the use of mathematical formulas. The bility and precision of those theories may be limited in this human senses do not respond to many physical phenom- particular context. If this is the case, a theory has to be ena, including field and radiation. Such phenomena are adapted to a given situation to ensure a higher level of often encountered in food processing technology. They accuracy and consistency with the experiment. Experi- are measured with the application of detectors that convert ments support the discovery of new physical phenomena various pulses into observable signals. Detectors are and new attributes of technical and biological objects clocks, weighing scales, thermoscopes, baroscopes, elec- (Shao et al., 2009), and they are of paramount importance troscopes, spectroscopes, microscopes, etc. A measuring in the process of solving technical problems in agriculture, device is closely interrelated with the physical quantity food engineering, and production. The measurements that is being measured at a given level of precision. used to determine the physical quantities of the studied 16 AGRICULTURE AND FOOD MACHINERY, APPLICATION OF PHYSICS FOR IMPROVING raw materials and food products contribute to the discov- heavily on mathematical modeling, which will develop ery of rules, correlations, structures, and dependencies. as new advances are made in IT and computer systems. These experimental and intellectual methodological oper- A preferred mathematical model for describing physical ations support the development of new concepts, concep- processes in farming and food engineering should have tual structures and theories, the discovery of important the widest possible range of applications, it should phenomena for biological objects and dynamic causal deliver a high degree of precision and, above all, it relationships. The acquired knowledge on raw materials should support the prediction of experimentally vali- and food products, expressed in mathematical form, dated events. enables researchers to examine and determine the effect Many discoveries have been made as regards measur- of changes in the physical qualities of the studied objects ing devices for observing the structure of biological owing to different factors (conditions), to subject their objects of plant and animal origin. Small objects in the findings to a critical evaluation and formulate logical con- structure of the studied raw materials are investigated with clusions. A physics theory that is free of logical and math- the use of microscopes. Vast advancements have been ematical contradictions is a venture point for explaining made in the field of microscopy, leading to the develop- causally connected facts, and it supports the prediction ment of electron and confocal microscopes (Entwistle, of new, unknown facts. 2000; Danilatos and Postle, 1982; Inoue, 1986). New Many problems in agricultural and food engineering solutions simplifying the observation of the spatial struc- may be solved with the use of data in the existing knowl- tures of those objects are likely to be introduced in the edge database. Scientists developing new farming and future. Empirical knowledge on the spatial distribution food processing machines rely on information describing of particles with a complex shape will contribute to the the physical properties of raw materials and food products development of more accurate particle models as well as as well as established scientific theories and laws of phys- theories that offer practical implications for farming and ics. Biological objects have a complex structure. The attri- food engineering. butes of complex objects are determined by the laws and properties applicable to their components. Their geomet- ric form follows from the surface structure of the morpho- Testing raw materials and food products logical components of a biological object. Physics and its laws are closely related to natural sciences, which is why There is a need to isolate a field of physics dealing exclu- the laws of science have many applications in agricultural sively with physical relations in the natural environment, and food engineering, in particular in describing working soil, water, air, plants, animals, raw materials of plant and animal origin, and food products. This field – processes and developing new technologies and – machines. A sound theory of elementary particles should agrophysics should have its own conceptual system cov- support the discovery of new phenomena and laws that ering a specific field of study. may be applied in designing new technologies for Agrophysics studies the ecosystem and biological processing a given type of raw materials into food prod- objects that participate in the food production process, ucts with the anticipated properties. As a rational science which are processed by human activity and whose mathe- supporting the development of formal languages for the matical, physical, and chemical attributes are described precise description of abstract concepts and relations, with the use of scientific methods. Agrophysics could fur- mathematics plays an important role in the physical ther the development of food research by: description of the actual condition of farming and food Introducing universal standards applicable to biological processing machines. From among a variety of mathemat- objects for food production ical equations describing a given phenomenon, scientists Promoting the development of high-precision research have to choose the propositions, concepts, and statements methods investigating the phenomena and properties that are fit for use in the process of building models of encountered in the food production process farming and food processing machines and modeling Describing physical processes in food production working processes in food production (Mieszkalski, Examining the physical properties of farming produce 1996; Hardin and Searcy, 2009). Many biological objects used for food processing with technical applications can be described with the use Investigating mutual relations in the natural environ- of geometric and mechanical models as discrete struc- ment relating to food production tures. A system of spatially distributed mass particles Designing new methods that restrict the degradation of may serve as a model of raw materials and food products. the environment where raw materials and food are The distance between mass particles is modified under the produced influence of the applied force. The physical quantities Monitoring and storing data on changes in physical indicating displacement over time are described with the quantities characteristic of raw materials and food prod- use of mechanics, thermodynamics, and other existing ucts during processing theories. Developing mathematical models of the processes The design of new farming and food processing observed in biological objects that are marked by high machines as well as food processing technologies relies variability and anisotropicity during food production AGRICULTURE AND FOOD MACHINERY, APPLICATION OF PHYSICS FOR IMPROVING 17