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Discussion Hydropedology: Towards new insights into interactive pedologic and hydrologic processes across scales Henry Lin Dept. of Crop and Soil Sciences, Pennsylvania State Univ., University Park, PA, USA article info Article history: Available online 13 June 2011 Keywords: Hydropedology Hydrology Pedology Landscape Critical Zone summary Ó 2011 Elsevier B.V. All rights reserved. 1. Introduction Healthy academic debate provides beneficial clarifications of possible misunderstandings or misperceptions, so I welcome the invitation to address the concerns and challenges raised by Prof. Philippe Baveye (this issue). I will first make a brief remark on the difference between ‘‘compartmentalization of hydrology into sub-disciplines’’ that Prof. Baveye focused on in his comments vs. ‘‘synergies across scientific interfaces’’ that I would emphasize here. I will then highlight the problems in the classical study of soil hydrology, and explain why hydropedology is needed for a shift in our basic thinking and approach towards pore, pedon, landscape, and watershed scale analysis of interactive pedologic and hydro- logic processes. I believe the discussion here is about the art itself, rather than the label of visitors at an art museum as Prof. Baveye suggested. Prof. Baveye is right in cautioning the naming game in modern academia and in reminding us of the need for a holistic approach to the hydrologic science. His remarks, however, should be balanced by recognizing the tremendous synergies across the interfaces of scientific disciplines and by appreciating the unique contribution that pedology can make to the study of hydrologic processes. One might discern two questionable assumptions underlying Prof. Baveye’s remarks: (1) new names are merely combinations of words to create compartmentized sub-disciplines of hydrology; and (2) the way soil hydrology research has been done in the past is satisfactory. While I will leave it to more qualified colleagues to comment on other subjects raised in Prof. Baveye’s remarks, here I will focus on rebutting his incorrect statements about hydropedol- ogy. More extensive discussions on why hydropedology is needed and what hydropedology can contribute have been published by Lin et al. (2005, 2006, 2008), which were not cited in his remarks. 2. The true meaning of pedology To begin, I would ask the readers to ponder on a simple and yet revealing question: ‘‘What is the difference between a cow and the ground beef?’’ To illustrate the fundamental difference between naturally-formed soils in the landscape vs. ground-sieved soil mate- rials in the laboratory, Kubiena (1938) insightfully pointed out that a crushed sample of soil is as akin to a natural soil profile as a pile of debris is to a building. The ground beef is no longer a living en- tity and has no structure, while a cow is alive and has intricate internal architecture for its appropriate functioning. Hence, the tra- ditional way of studying soils using ground-sieved soil materials (or even beach sands or glass beads) and isolated soil cores or col- umns (especially repacked ones) create significant deviations from field soils where distinct pedogenic features (such as structure, macropores, horizons, and coatings) and open boundary conditions (with dynamic changes induced by climate, biota, and human activities) prevail. It is unfortunate that the term pedology continues to be misun- derstood or undervalued by many, including some fellow soil scien- tists and hydrologists. ‘‘Ped’’ (naturally-formed soil aggregates with various strengths, sizes, and shapes) is a unique term in soil science, and ‘‘pedology’’ captures that uniqueness well. Historically, the term pedology has evolved into two meanings in the earth science com- munity: one is the original – specifically referring to the integrated study of soils as natural or anthropogenically-modified landscape entities, including soil genesis, morphology, classification, survey, 0022-1694/$ - see front matter Ó 2011 Elsevier B.V. All rights reserved. doi:10.1016/j.jhydrol.2011.05.054 E-mail address: [email protected] Journal of Hydrology 406 (2011) 141–145 Contents lists available at ScienceDirect Journal of Hydrology journal homepage: www.elsevier.com/locate/jhydrol

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Page 1: Hydropedology: Towards new insights into interactive pedologic and hydrologic processes across scales

Journal of Hydrology 406 (2011) 141–145

Contents lists available at ScienceDirect

Journal of Hydrology

journal homepage: www.elsevier .com/ locate / jhydrol

Discussion

Hydropedology: Towards new insights into interactive pedologicand hydrologic processes across scales

Henry LinDept. of Crop and Soil Sciences, Pennsylvania State Univ., University Park, PA, USA

a r t i c l e i n f o s u m m a r y

Article history:Available online 13 June 2011

Keywords:HydropedologyHydrologyPedologyLandscapeCritical Zone

0022-1694/$ - see front matter � 2011 Elsevier B.V. Adoi:10.1016/j.jhydrol.2011.05.054

E-mail address: [email protected]

� 2011 Elsevier B.V. All rights reserved.

1. Introduction

Healthy academic debate provides beneficial clarifications ofpossible misunderstandings or misperceptions, so I welcome theinvitation to address the concerns and challenges raised by Prof.Philippe Baveye (this issue). I will first make a brief remark onthe difference between ‘‘compartmentalization of hydrology intosub-disciplines’’ that Prof. Baveye focused on in his comments vs.‘‘synergies across scientific interfaces’’ that I would emphasize here.I will then highlight the problems in the classical study of soilhydrology, and explain why hydropedology is needed for a shiftin our basic thinking and approach towards pore, pedon, landscape,and watershed scale analysis of interactive pedologic and hydro-logic processes. I believe the discussion here is about the art itself,rather than the label of visitors at an art museum as Prof. Baveyesuggested.

Prof. Baveye is right in cautioning the naming game in modernacademia and in reminding us of the need for a holistic approach tothe hydrologic science. His remarks, however, should be balancedby recognizing the tremendous synergies across the interfaces ofscientific disciplines and by appreciating the unique contributionthat pedology can make to the study of hydrologic processes.One might discern two questionable assumptions underlying Prof.Baveye’s remarks: (1) new names are merely combinations ofwords to create compartmentized sub-disciplines of hydrology;and (2) the way soil hydrology research has been done in the pastis satisfactory. While I will leave it to more qualified colleagues tocomment on other subjects raised in Prof. Baveye’s remarks, here Iwill focus on rebutting his incorrect statements about hydropedol-

ll rights reserved.

ogy. More extensive discussions on why hydropedology is neededand what hydropedology can contribute have been published byLin et al. (2005, 2006, 2008), which were not cited in his remarks.

2. The true meaning of pedology

To begin, I would ask the readers to ponder on a simple and yetrevealing question: ‘‘What is the difference between a cow and theground beef?’’ To illustrate the fundamental difference betweennaturally-formed soils in the landscape vs. ground-sieved soil mate-rials in the laboratory, Kubiena (1938) insightfully pointed out thata crushed sample of soil is as akin to a natural soil profile as a pileof debris is to a building. The ground beef is no longer a living en-tity and has no structure, while a cow is alive and has intricateinternal architecture for its appropriate functioning. Hence, the tra-ditional way of studying soils using ground-sieved soil materials(or even beach sands or glass beads) and isolated soil cores or col-umns (especially repacked ones) create significant deviations fromfield soils where distinct pedogenic features (such as structure,macropores, horizons, and coatings) and open boundary conditions(with dynamic changes induced by climate, biota, and humanactivities) prevail.

It is unfortunate that the term pedology continues to be misun-derstood or undervalued by many, including some fellow soil scien-tists and hydrologists. ‘‘Ped’’ (naturally-formed soil aggregates withvarious strengths, sizes, and shapes) is a unique term in soil science,and ‘‘pedology’’ captures that uniqueness well. Historically, the termpedology has evolved into two meanings in the earth science com-munity: one is the original – specifically referring to the integratedstudy of soils as natural or anthropogenically-modified landscapeentities, including soil genesis, morphology, classification, survey,

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mapping, interpretation, and modeling (Wilding, 2000; Buol et al.,2003; Minasny et al., 2008); while the other is synonymous withthe discipline of soil science. Hydropedology emphasizes the origi-nal meaning of pedology. It was Dokuchaev (1893) who formulatedthe theory of soil formation through extensive field investigationsacross wide geographic regions that gave birth to modern soil sci-ence. Up to this date, pedology remains a unique sub-discipline ofsoil science and earth science, while the other sub-disciplines of soilscience have been (for the most part) applied mathematics, physics,chemistry, biology, and others in the study of soils or, more oftenthan not, soil materials.

3. Problems in the classical study of soil hydrology

Some alarming statements from well-established scholars withwhom I have interacted serve here to illustrate fundamental prob-lems associated with classical soil hydrology.

During an interdisciplinary meeting of vadose zone hydrologyheld in 1995 at UC-Davis in honoring Donald Nielsen’s career, soilphysicist Bill Jury told the audience that ‘‘the foundation of our mod-els is shaky.’’ I wondered: without a solid foundation, how can webuild a reliable skyscraper? No matter how fancy a skyscraper(or a computer model) may look like, it will crash sooner or laterif it is built on a shaky foundation. As an example, 10 conceptuallydifferent hydrologic models all failed to predict catchmentdischarge in a 6-ha artificial catchment (called Chicken Creek) inGermany, given soil texture and topography data as inputs(Holländer et al., 2009). None of the model simulations came evenclose to predicting the observed water balance for the 3-year per-iod monitored. A key missing piece in all these models was signif-icant biological soil crusts emerged at the surface in the initialdevelopment of the ecosystem. Discharge was mainly predictedby these classical models as subsurface discharge with little directrunoff; in reality, surface runoff was a major flow component de-spite the fairly coarse soil texture throughout the entire catchment(Gerwin et al., 2011).

At a hydrology meeting held at Iowa State University in 2004(the purpose of which was to develop a vision paper for theConsortium of Universities for the Advancement of HydrologicSciences, Inc.), hydrologist Ken Potter commented that ‘‘the adventof computer has actually slowed down the advancement of hydrologicsciences.’’ In the past decades of computer modeling frenzy, the col-lection and analysis of field data has been undervalued. Previously,however, many publications were devoted to field data collection,analysis, and interpretation, and such publications have providedsome of the most fundamental insights into soils and hydrologicprocesses. For instance, Darcy’s Law (1856), Buckingham’s Law(1907), Jenny’s theory (1941), and Horton’s Law (1945) were alldeveloped prior to the advent of the computer. Yet decades there-after, no new theory has been solidly established in soil hydrology.

In a thought-provoking paper, hydrologist Keith Beven (2006)noted that ‘‘Nearly all hydrologic, water quality, and sediment trans-port models use the same small scale laboratory homogeneous domaintheory to represent integrated fluxes at the much larger scales of hill-slope and catchment. . . This is the root of many discrepancies betweenmodel predictions and the reality.’’ This view is now widely sharedacross the hydrology community (e.g., Uhlenbrook, 2006; Kirchner,2006; McDonnell et al., 2007). Among the challenged assumptionsin standard models of flow and transport in the real-world is un-known boundary condition (Beven, 2006).

In an interesting paper of flow configuration generation and evo-lution in nature, mechanical engineer Bejan (2007) challenged thehydrology community by stating that ‘‘Hydrology research is provingevery day that science has hit a wall.’’ The open, interactive discus-sions associated with this article revealed many controversies and

problems in the field (see http://www.hydrol-earth-syst-sci-discuss.net/3/1773/2006/hessd-3-1773-2006-discussion.html).

Finally, during the 11th National Congress of Chinese Soil Sci-ence in Beijing in 2008, pedologist Zitong Gong pointed out aninteresting paradox in the scientific community: ‘‘We now havemore and more people studying soils, but we have fewer and fewerpeople knowing what soil really is.’’ Many young and energeticresearchers who have been trained in various disciplines are tack-ling complex issues related to soils, but fewer and fewer of themhave ever touched a real soil profile in the field. This situation hin-ders their in-depth understanding and appreciation of the com-plexity and dynamics involved in soil processes, leading to theirsimplified and often unrealistic assumptions about real-worldsoils.

4. Scope and characteristics of hydropedology

Broadly speaking, hydropedology is the study of the interfacebetween the pedosphere and the hydrosphere, with an emphasison interactive pedologic and hydrologic processes across scalesin situ. Considerable synergies can be generated by bridging pedol-ogy with soil physics and hydrology, along with other related bio-and geo-sciences, to holistically address the following two basicquestions of hydropedology (Lin et al., 2005, 2006, 2008):

(1) How do soil architecture and the distribution of soils overthe landscape exert a first-order control on hydrologic pro-cesses (and associated biogeochemical and ecologicaldynamics) across spatio-temporal scales?

(2) How do landscape hydrologic processes (and the associatedtransport of energy, sediment, chemicals, and biomaterialsby flowing water) influence soil genesis, evolution, variabil-ity, and functions?

The first question calls for quantitative relationships betweensoil architecture and functions across scales. Soil architecture hererefers to the entirety of how the soil is structured from the micro-scopic to macroscopic levels, which encompasses (1) solid compo-nents (including soil texture, microfabric, aggregation, andhorizons), (2) pore space (size distribution, density, connectivity,and morphology of pores and their networks, as well as liquids,gases, and biota within the pore space) and (3) interfaces betweenthe solid component and the pore space (such as coatings on pedsor pore edges, and the interfaces of macropore–matrix, soil–root,microbe-aggregate, horizon–horizon, soil–rock, and others). Theseinterfaces are often active zones of biogeochemical reactions ortriggers of preferential flow of water, chemicals, gases, and mi-crobes. Numerous water-restricting subsoil horizons and featureshave been identified in Soil Taxonomy (Soil Survey Staff, 2006),which act as an aquitard or aquiclude to downward moving water,ultimately resulting in seasonal perched water table or water mov-ing laterally within the soil as subsurface throughflow (e.g., Freeret al., 2002; Gburek et al., 2006; McDaniel et al., 2008).

Whereas considerable knowledge on soil structure has beenamassed over decades, a comprehensive theory and an effectivemeans of quantifying soil architecture across scales remain elusive.To propel the field out of the stagnation, and to represent soilarchitecture in a manner that can be coupled into models of flow,scaling, and rate processes, considerable efforts remain needed, notleast non-invasive, continuous, and precision quantification of sub-surface structure, especially in situ. Encouragingly, non-invasiveinvestigations (e.g., through computing tomography and geophys-ical tools) and continuous mapping (e.g., using spectroscopy andremote sensing) are being employed increasingly to reveal soilarchitectural complexity across scales. However, how to enhance

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the resolution of field investigations and how to quantitatively linksoil structural parameters to hydrologic (and biogeochemical andecological) functions remains the challenge.

The second question has been ignored in traditional soil hydrol-ogy, but is a new arena for pedological research. It takes pedologyout of its traditional sphere by emphasizing the nature, origin,function, and significance of pore space at multiple scales. Howwater moves through soils – along with associated shrink-swell,freeze–thaw, dissolution–precipitation, oxidation-reduction, andother processes – dictates the dynamic evolution of soil heteroge-neity, the formation of soil structural features including pore space,and the feedback mechanisms of soil functions. Hydrology is a keyintegrating factor of soil formation and evolution, and is a maindriving force of soil change; hence hydrology may offer a unifyingtheme for monitoring, mapping, and modeling soil evolution andfunctions across scales.

It is becoming increasingly apparent that solid Earth is not acontinuous fluid; rather, it poses hierarchical heterogeneities withdiscrete flow networks embedded in the mosaics of the surface andsubsurface. For instance, there are a variety of networks in soils,such as crack and fissure networks, root branching networks,animal burrow networks, mycorrhizal mycelial networks, andman-made drainage networks (Lin, 2010b). These belowgroundnetworks can lead to threshold-like hydrologic responses as wellas hot spots or not moments in biogeochemical dynamics (e.g.,Tromp-van Meerveld and McDonnell, 2006; McClain et al., 2003).Enhanced partition of flow currents between more transitionalporous portion of the soil and the preferential flow domain couldlead to the next generation of hydrologic and biogeochemicalmodels.

5. Bridges that hydropedology builds

Lin (2003) and Lin et al. (2005) discussed the role that hydro-pedology plays in bridging disciplines, scales, data, and education.Lin (2010a) further described the opportunities in coupling hydro-pedology with related bio- and geo-sciences towards the holisticstudy of the Earth’s Critical Zone (e.g., coupling hydropedologywith ecohydrology to improve the linkage of belowground andaboveground processes, and coupling hydropedology with biogeo-chemistry to enhance the identification of hot spots and hot mo-ments in the landscape). In the following, three importantbridges that hydropedology is in a unique position to build arehighlighted, providing hopefully some compelling justificationsfor us to come together (rather than to be separated).

5.1. Bridging fast and slow processes

There are three types of soil change – irregular (or random) var-iability, cyclic fluctuations, and trend changes. Soil formation andevolution refer mostly to trend changes over long time periods,while random and periodical changes are more of concern for soilfunctions within shorter time periods. However, the short- andlong-time scale changes are intertwined, with interactions, feed-backs, thresholds, and accumulative effects (Lin, submitted forpublication). With growing interests in sustainability and globalchanges, both short- and long-term changes of soil systems shouldbe considered simultaneously.

Hydropedology encapsulates the co-evolution of fast (water)and slow (soil) changes in multiphase soil systems, where fastand cyclic soil functioning processes (SFPs) involve mostly liquids,gases, and biota (in which circulating water is a key), while slowand irreversible specific pedogenic processes (SPPs) involve predom-inantly solids (Targulian and Goryachkin, 2004). Each SPP is char-acterized by a set of solid-phase pedogenic features formed over

hundreds to thousands or more years, while SFPs are dominatedby diurnal, seasonal, and annual changes (Targulian, 2005). ManySFPs and related cycles are not completely closed, and manyinput–output fluxes are not necessarily balanced in the open,dissipative soil system (Rode, 1947; Targulian and Goryachkin,2004). Such non-closed cycles and off-balanced fluxes of SFPs gen-erate residual solid-phase products in the soil profile over time.Each single cycle may generate a micro amount of transformedor newly-formed solid products, which may hardly be detected;but being produced repeatedly over long time these microamounts gradually accumulate into macro amounts that aredetectable morphologically or analytically (Targulian and Goryach-kin, 2004). Such residual products generated in SPPs will feedbackto alter SFPs, mostly in a gradual manner, but some could lead tothreshold changes in the soil system (Lin, submitted forpublication).

5.2. Bridging stochastic variability and deterministic pattern

Pedologists are foremost among basic soil scientists who helpdevelop integrated systems approach to scale up knowledge fromsmall samples to global pedosphere (Sposito and Reginato, 1992).Pedologists have studied both the mechanisms and the magnitudesof spatial variability of soils and landforms as a basis for broad gen-eralizations about soils (especially pedogenesis, classification, andmapping). Whereas soil physicists and hydrologists have studiedscaling theories and spatial variability using similitudes, fractals,geostatistics, and other means. As noted by Nielsen and Wendroth(2003), while a versatile and powerful set of statistical tools existfor diagnosing spatially and temporally variable field observations,we have to explore the cause of variation and to improve and ex-pand soil classification concepts. However, the efforts made bypedologists, soil physicists, and hydrologists on soil variabilityand scaling have not converged well in the past.

Hydropedology can help make that convergence happen, andcan help de-mystify the seemly mind-boggling variability in fieldsoils via identifying myriads of soil patterns. This is because allprocesses in the soil are bound to an underlying structural controlthat exhibits a hierarchical organization (Vogel and Roth, 2003; Linet al., 2006). This organization can be used to discern deterministicand stochastic components at each scale. For instance, at micro-scales water flow is controlled by capillarity and laminar flowthrough individual soil pores and around peds. As scale increases,flow often becomes controlled by impeding layers in a soil profile,then accumulation of water downslope as dictated by soil catenaand associated bedrock geology, and finally routing of flow througha stream network that in itself is controlled by soil–landscapecharacteristics.

5.3. Bridging mapping with monitoring and modeling

Jenny (1941) noted, ‘‘The goal of soil geographer is the assemblageof soil knowledge in the form of a map. In contrast, the goal of the‘functionalist’ is the assemblage of soil knowledge in the form of acurve or an equation. . . Clearly, it is the union of the geographic andthe functional method that provides the most effective means of ped-ological research.’’ Hydropedology is intended to promote such aunion of soil maps and soil functions. This means that soil mappingmust go beyond the classical taxonomy-dominated exercises andshould consider soil functional characterizations as well as soil var-iability quantifications. A soil map can no longer be a static prod-uct; rather, soil changes (especially anthropogenic alternations)and functional units (such as soil hydrologic functions) should bedefined and mapped.

Bridging mapping with monitoring and modeling helps soil mapquantification and the inter- or extra-polation and upscaling of

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point-based data. Mapping can diagnose and stratify the soil–land-scape for optimal location and number of sites needed for monitor-ing or sampling, as well as facilitate spatially-distributed modeling.On the other hand, monitoring and/or modeling can permit dy-namic and functional mapping and ground truthing for maps. Thelink between mapping and monitoring/modeling is an importantone for integrating space and time and for developing a systems-based understanding, especially in an iterative fashion (Lin, 2010a).

6. Examples of funding opportunities related to hydropedology

The following multimillion-dollar funding cases illustrate theopportunities of integrated approach to landscape studies, ofwhich hydropedology is an integral part.

After spending billions of dollars, the US Army is still strugglingwith effective counter-landmine sensing technologies that areapplicable to real-world soils. Geophysical tools and many othersensing techniques have been developed in sophisticated waysbut often based on sand boxes. In 2003, the US Army Research Of-fice released a call for University Countermine Research Center to‘‘focus primarily on developing an in-depth understanding of the tophalf meter of the heterogeneous, complex, and dynamic terrestrialenvironment, the soil and soil–mine interaction phenomenology andon the geo-environmental factors that can affect mine detection andneutralization in different environmental settings within the contextof a variety of sensing modalities and neutralization approaches’’(http://www.arl.mil/aro/research/ucrc/). As described in the RFP,this effort includes descriptions of different soil types and their de-gree of heterogeneity under various environmental conditions; soilphysical properties that affect landmine sensors and their intrinsicinterrelationships, geospatial scaling behavior, and natural varia-tion in different soil types, environments, and climates; soil mois-ture spatial and temporal variability, and its impacts on sensingsignals. Another important aspect of this call for help is that allsensor work must be tied back to real soils and be integrated intothe overall functional system that can be used in the battle field.Such a call has a strong flavour of hydropedology – that is, theholistic understanding of the landscape–soil–water relationshipand its influence on soil–mine interaction under a wide range ofreal-world soil and environmental conditions.

In recognizing that processes occurring at and near the Earth’ssurface do not operate independently, a holistic framework forintegrated studies of water with soil, rock, air, and biotic resourcesin the terrestrial environment was called for by the US NationalResearch Council (NRC, 2001). In 2006, the US National ScienceFoundation solicited proposals and funded three Critical ZoneObservatories (CZOs) ‘‘that will operate at the watershed scale andthat will significantly advance our understanding of the integrationand coupling of Earth surface processes as mediated by the presenceand flux of fresh water’’ (http://www.nsf.gov/pubs/2006/nsf06588/nsf06588.pdf). In 2009, three additional CZOs were funded in theUS. In the meantime, German Helmholtz Association has estab-lished four Terrestrial Environmental Observatories (TERENO) in2008–2009 to investigate the consequences of global change forterrestrial ecosystems and the associated socioeconomic implica-tions (http://www.tereno.net/). In 2009, the EU 7th FrameworkProgramme funded four CZOs to study soil processes at the fieldscale and to describe from 1st principles how soil structure im-pacts processes and functions at the soil profile scale (http://www.soiltrec.eu/). As the landscape–soil–water interaction acrossscales is a key to understanding the Earth’s Critical Zone, hydro-pedology will be an important contributor to these observatories.Long-term health of the soil, through monitoring its ‘‘blood pres-sure’’ (soil water potential), temperature, respiration, carbon con-tent, structural dynamics, and other potentially key signs of

global land change, is essential to the sustainability of ecosystemservices, secure food production, lasting air and water quality,and a balanced growth of human society with natural systems.

7. Concluding remarks

The value of differentiating a cow and the ground beef is obvi-ous. Apparently, it is much more challenging to raise a cow than tokeep the ground beef. But to address the seminal question of ‘‘whatis soil,’’ one needs to have an in-depth understanding and appreci-ation of this unique gift from nature and its essential characteris-tics in the landscape. Kung (1990) summarized well: untilpedologists and sedimentologists can offer a more detaileddescription of the texture and structure of the vadose zone, simu-lated results of field-scale solute transport by models based on theclassical concept could be completely misleading. He also notedthat although flow pattern in soils could be extremely complex,it is not random. Thus, all transport parameters that are treatedas random variables in stochastic models probably will never beaccurately assessed unless the real flow paths can be estimated(Kung, 1990).

However, there are two bottlenecks in advancing hydropedolo-gy and hydrology in general. On the conceptual and theoreticalfront, going beyond small-scale physics and embracing a hierarchi-cal structural framework can provide a more meaningful connec-tion between point-based observations and landscape patterns aswell as guide the appropriate development and use of models.The disconnect between the Dokuchaev–Jenny’s theory of soil for-mation and the Darcy–Buckingham’s law of soil water movementneeds to be resolved, which offers a great opportunity for hydro-pedology to contribute to an improved theory of flow and transportin heterogeneous and structured field soils. On the technologicalfront, the emergence of real-time sensor networks, coupled withimproved non-invasive geophysical and remote sensing tools, canprovide increasingly spatially and temporally extensive datasetsabout the subsurface and flow dynamics. However, while land-forms and vegetation can now be mapped with high resolution(e.g., using LiDAR and the Worldview), non-invasive mapping ofthe subsurface with precision over space and time remains a signif-icant challenge. As Beven (2006) noted, the most important need toadvance hydrology of the 21st century is to provide techniquesthat can measure integrated fluxes and storages at useful scales,and the second one is the search for appropriate closure schemesat various scales.

Science advances through both integration and interfaces. Thusthe development of justified sub-disciplines of hydrology is notnecessarily in contradiction with the need for unity. A possibleway that Journal of Hydrology may move forward with its debateover sub-sections vs. unity is to perhaps provide a broad categori-cal grouping (e.g., physical vs. socio-economical dimensions ofhydrology), which may benefit those who like to scan over variousissues; however, online search engines nowadays can easily re-solve this issue by pulling out relevant papers regardless how theyare grouped in a journal.

References

Baveye, P., this issue. Hydropedology biohydrology and the compartmentalizationof hydrology into sub-disciplines: necessary evolution or dispersal of efforts? J.Hydrol.

Bejan, A., 2007. Constructal theory of pattern formation. Hydrol. Earth Syst. Sci. 11,753–768.

Beven, K., 2006. Searching for the holy grail of scientific hydrology: Qt=H(S

R Dt)A as

closure. Hydrol. Earth Syst. Sci. 10, 609–618.Buckingham, E., 1907. Studies on the movement of soil moisture. US Dept. Agric.

Bur. Soils Bull., 38.Buol, S.W., Southard, R.J., Graham, R.C., McDaniel, P.A., 2003. Soil Genesis and

Classification, fifth ed. Lowa State University Press, Ames, IA.

Page 5: Hydropedology: Towards new insights into interactive pedologic and hydrologic processes across scales

H. Lin / Journal of Hydrology 406 (2011) 141–145 145

Darcy, H., 1856. Les Fontaines Publiques de la Ville de Dijon, Dalmont, Paris (Englishtranslation by Patricia Bobeck)

Dokuchaev, V.V., 1893. The Russian steppes and study of soil in Russia, it is past andpresent (Translated by J.M. Crawford). Ministry of Crown Domains, St.Petersburg, Russia.

Freer, J., McDonnell, J.J., Beven, K.J., Peters, N.E., Burns, D.A., Hooper, R.P., Aulenbach,B., Kendall, C., 2002. The role of bedrock topography on subsurface storm flow.Water Resour. Res. 38 (12), 1269. doi:10.1029/2001WR000872.

Gburek, W.J., Needelman, B.A., Srinivasan, M.S., 2006. Fragipan controls on runoffgeneration: hydropedological implications at landscape and watershed scales.Geoderma 131, 330–344.

Gerwin, W., Schaaf, W., Biemelt, D., Winter, S., Fischer, A., Veste, M., Hüttl, R.F., 2011.Overview and first results of ecological monitoring at the artificial watershedChicken Creek (Germany). Phys. Chem. Earth 36, 61–73.

Holländer, H.M., Blume, T., Bormann, H., Buytaert, W., Chirico, G.B., Exbrayat, J.-F.,Gustafsson, D., Hölzel, H., Kraft, P., Stamm, C., Stoll, S., Blöschl, G., Flühler, H.,2009. Comparative predictions of discharge from an artificial catchment(Chicken Creek) using sparse data. Hydrol. Earth Syst. Sci. 13, 2069–2094.

Horton, R., 1945. Erosion development of streams and their drainage watersheds;hydrophysical approach to quantitative morphology. Geo. Soc. Am. Bull. 56,275–370.

Jenny, H., 1941. Factors of Soil Formation – A System of Quantitative Pedology.McGraw-Hill, NY.

Kirchner, J.W., 2006. Getting the right answers for the right reasons: linkingmeasurements, analyses and models to advance the science of hydrology.Water Resour. Res. 42, W03S04. doi:10.1029/2005WR004362.

Kubiena, W.L., 1938. Micropedology. Collegiate Press, Ames, IA.Kung, K.-J.S., 1990. Preferential flow in a sandy vadose zone: 1. Field observation.

Geoderma 46, 51–58.Lin, H.S., 2003. Hydropedology: bridging disciplines, scales and data. Vadose Zone J.

2, 1–11.Lin, H.S., 2010a. Earth’s critical zone and hydropedology: concepts, characteristics,

and advances. Hydrol. Earth Syst. Sci. 14, 25–45.Lin, H.S., 2010b. Linking principles of soil formation and flow regimes. J. Hydrol.

393, 3–19. doi:10.1016/j.jhydrol.2010.02.013.Lin, H.S., submitted for publication. Understanding soil change across time scales.

Soil Sci. Soc. Am. J.Lin, H.S., Bouma, J., Wilding, L., Richardson, J., Kutilek, M., Nielsen, D., 2005.

Advances in hydropedology. Adv. Agron. 85, 1–89.Lin, H., Bouma, J., Pachepsky, Y., Western, A., Thompson, J., van Genuchten, R., Vogel,

H.-J., Lilly, A., 2006. Hydropedology: synergistic integration of pedology andhydrology. Water Resour. Res. 42, W05301. doi:10.1029/2005WR004085.

Lin, H.S., Brook, E., McDaniel, P., Boll, L., 2008. Hydropedology and surface/subsurface runoff processes. In: Anderson, M.G. (Editor-in-Chief) Encyclopediaof Hydrologic Sciences. John Wiley & Sons Ltd. doi: 10.1002/0470848944.hsa306.

McClain, M.E., Boyer, E.W., Dent, C.L., Gergel, S.E., Grimm, N.B., Groffman, P.M., Hart,S.C., Harvey, J.W., Johnston, C.A., Mayorga, E., McDowell, W.H., Pinay, G., 2003.Biogeochemical hot spots and hot moments at the interface of terrestrial andaquatic ecosystems. Ecosystems 6, 301–312. doi:10.1007/s10021-003-0161-9.

McDaniel, P.A., Regan, M.P., Brooks, E., Boll, J., Barndt, S., Falen, A., Young, S.K.,Hammel, J.E., 2008. Linking fragipans, perched water tables and catchment-scale hydrological processes. Catena. doi:10.1016/j.catena.2007.05.011.

McDonnell, J.J., Sivapalan, M., Vache, K., Dunn, S., Grant, G., Haggerty, R., Hinz, C.,Hooper, R., Kirchner, J., Roderick, M.L., Selker, J., Weiler, M., 2007. Movingbeyond heterogeneity and process complexity: a new vision for watershedhydrology. Water Resour. Res. 43, W07301. doi:10.1029/2006WR005467.

Minasny, B., McBratney, A.B., Salvador-Blanes, S., 2008. Quantitative models forpedogenesis – a review. Geoderma 144, 140–157.

National Research Council (NRC), 2001. Basic research opportunities in earthscience. National Academy Press, Washington, D.C.

Nielsen, D.R., Wendroth, O., 2003. Spatial and Temporal Statistics: Sampling FieldSoils and Their Vegetation. Catena Verlag, Cremlingen, Destedt.

Rode, A.A., 1947. The Soil Forming Process and Soil Evolution. Israel Program forScientific Translations, Jerusalem (Translated by J.S. Joffe, 1961).

Soil Survey Staff, 2006. Keys to Soil Taxonomy. 10th ed. United States Department ofAgriculture – Natural Resources Conservation Service, Washington, DC.

Sposito, G., Reginato, R.J. (Eds.), 1992. Opportunities in Basic Soil Science Research.Soil Science Society of America, Inc., Madison, WI.

Targulian, V.O., 2005. Elementary pedogenic processes. Eurasian Soil Sci. 38, 1255–1264.

Targulian, V.O., Goryachkin, S.V., 2004. Soil memory: types of record, carriers,hierarchy and diversity. Rev. Mex. Cienc. Geol. 21, 1–8.

Tromp-van Meerveld, I., McDonnell, J.J., 2006. Threshold relations in subsurfacestormflow 1: a 147 storm analysis of the Panola hillslope trench. Water Resour.Res.. doi:10.1029/2004WR003778.

Uhlenbrook, 2006. Catchment hydrology – a science in which all processes arepreferential. HP Today. Hydrol. Process. 20, 3581–3585.

Vogel, H.J., Roth, K., 2003. Moving through scales of flow and transport in soil. J.Hydrol. 272, 95–106.

Wilding, L.P., 2000. Pedology. In: Sumner, M.E. (Ed.-in-Chief) Handbook of soilscience. p. E-1–E-4, CRC Press, Boca Raton, FL.