Indirect effects and distributed control in ecosystems: Comparative network environ analysis of a seven-compartment model of nitrogen storage in the Neuse River Estuary, USA: Time series analysis

Abstract Compartmental, or “stock-and-flow”, models describe the storage and transfer of conservative energy or matter entering and leaving open systems. The storages are the standing “stocks”, and the intra-system and boundary transfers are transactional “flows”. Network environ analysis (NEA) provides network methods and perspectives for the quantitative analysis of compartment models. These emphasize the distinction between direct and indirect relationships between the compartments, and also with their environments. In NEA, each compartment in a system has an incoming network that brings energy or matter to it from the system’s boundary inputs, and an outgoing network that takes substance from it to boundary outputs. These networks are, respectively, input and output environs. Individual pathways in environs have an identity not unlike spaghetti in a bowl, each strand of which originates at some boundary input and terminates at some boundary output. All strands originating at the j’th input collectively comprise, no matter where they terminate, the j’th output environ; similarly, all strands terminating at the i’th output comprise, no matter where they originate, the i’th input environ. Thus, any substance freely mixing in the system as a whole runs in pathways consigned to one and only one output environ traced forward from its compartment of entry, and also one and only one input environ traced backward from its compartment of exit. The environs are partition elements – they decompose the interior stocks and flow according to their input origins and output destinations. Moreover, each environ’s dynamics and other systems and network properties are unique, and sum over all the environs to give the aggregate dynamics and properties of the whole. It is this composite, aggregate whole that empirical methods measure; empiricism unaided by theoretical analysis is blind to the environ pathways that actually compose the wholes. A previous study of nitrogen dynamics in the Neuse River Estuary (NRE), North Carolina, USA ( Whipple et al., 2007 ) described within-environ transfers using a throughflow-based network analysis, NEA-T. Throughflow (Tin, Tout) is the sum of flows into or out of each compartment. This paper extends this work using a companion storage-based methodology, NEA-S, re-notated from its antecedent and originating contributions ( Barber, 1978a , Barber, 1978b , Barber, 1979 , Matis and Patten, 1981 ). Time-series data implementing 16 seasonal steady-state network models of nitrogen (N) storage and flow in the Neuse system were constructed for spring 1985 through winter 1989 by Christian and Thomas, 2000 , Christian and Thomas, 2003 . Network topology was constant over time, but the storage and transfer quantities changed. Environ analysis of this model showed that nitrogen storage and residence times differ within the different environs composing the compartments, and moreover, that these differences originate in the system’s interconnecting network as a whole. Thus, environs function within themselves as autonomous flow–storage units, but this individuality derives from, and at the same time contributes to the entire system’s properties. Environ autonomy is reflected in unique standing stocks and residence times, and whole empirical systems are formed as additive compositions of these. Because storage is durable and transfers ephemeral, storage environs revealed by NEA-S have more autonomy than flow environs computed using NEA-T. We quantified this autonomy by comparing the heterogeneity of extensive environs in models driven by actual inputs with intensive environs normalized to unit inputs. The former is more storage-heterogeneous than their unit reference counterparts, with dissolved nutrients NOx, DON, and NH4 exhibiting greatest heterogeneity. A previous NEA study of distributed control in this same model by Schramski et al. (2007) showed that NOx controls the system whereas sediment is controlled by the system. In the present study, NOx dominates storage in extensive environs, and therefore, is controlling in actuality. However, in the intensive unit, environs sediment accounted for most of the storage, reflecting greater control potential. This potential is expressed by the sediment acting like a capacitor for N, seasonally sequestering and releasing this element in the role of a biogeochemical regulator.

[1]  Stuart R. Borrett,et al.  Equivalence of the realized input and output oriented indirect effects metrics in Ecological Network Analysis , 2011, 1103.6276.

[2]  Wassily Leontief Input-Output Economics , 1966 .

[3]  Hans W. Paerl,et al.  Environmental controls of phytoplankton bloom dynamics in the Neuse River Estuary, North Carolina, U.S.A. , 1997 .

[4]  B. C. Patten,et al.  Systems approach to the concept of niche , 2004, Synthese.

[5]  Robert R. Christian,et al.  Significance of subtidal sediments to heterotrophically-mediated oxygen and nutrient dynamics in a temperate estuary , 1996 .

[6]  Robert R. Christian,et al.  CONSEQUENCES OF HYPOXIA ON ESTUARINE ECOSYSTEM FUNCTION: ENERGY DIVERSION FROM CONSUMERS TO MICROBES , 2004 .

[7]  John Schramski,et al.  Distributed control in the environ networks of a seven compartment model of nitrogen flow in the Neuse River Estuary, North Carolina, USA , 2006 .

[8]  R. Christian,et al.  Dynamics of NH4+ and NO3− uptake in the water column of the Neuse River Estuary, North Carolina , 1994 .

[9]  G. G. Parker,et al.  Hydrology of major estuaries and sounds of North Carolina , 1979 .

[10]  H. Paerl,et al.  Fish kills and bottom-water hypoxia in the Neuse River and Estuary: reply to Burkholder et al. , 1999 .

[11]  B. C. Patten Jakob von Uexküll and the theory of environs , 2001 .

[12]  M. C. Barber,et al.  A retrospective Markovian model for ecosystem resource flow , 1978 .

[13]  Patten Bc The biocoenetic process in an estuarine phytoplankton community. ORNL-3946. , 1966 .

[14]  Brian D. Fath,et al.  Quantifying resource homogenization using network flow analysis , 1999 .

[15]  Michael A. Mallin,et al.  Fish kills, bottom-water hypoxia, and the toxic Pfiesteria complex in the Neuse River and Estuary , 1999 .

[16]  W. Leontief Quantitative Input and Output Relations in the Economic Systems of the United States , 1936 .

[17]  B. C. Patten,et al.  Rapid development of indirect effects in ecological networks , 2010 .

[18]  Bernard C. Patten,et al.  ENERGY CYCLING IN THE ECOSYSTEM , 1985 .

[19]  Stuart R. Borrett,et al.  Equivalence of throughflow- and storage-based environs , 2007 .

[20]  J. Finn,et al.  Measures of ecosystem structure and function derived from analysis of flows. , 1976, Journal of theoretical biology.

[21]  M. C. Barber A note concerning time parameterization of Markovian models of ecosystem flow analysis , 1979 .

[22]  K. Bjorndal,et al.  Historical Overfishing and the Recent Collapse of Coastal Ecosystems , 2001, Science.

[23]  Hans W. Paerl,et al.  Ecosystem Responses to Internal and Watershed Organic Matter Loading: Consequences for Hypoxia in the Eutrophying Neuse River Estuary, North Carolina, USA , 1998 .

[24]  Richard A. Luettich,et al.  Neuse River Estuary Modeling and Monitoring Project Stage 1: Hydrography and Circulation, Water Column Nutrients and Productivity, Sedimentary Processes and Benthic-Pelagic Coupling, and Benthic Ecology , 2000 .

[25]  S. Borrett,et al.  Reconnecting environs to their environment , 2011 .

[26]  B. C. Patten Environs: Relativistic Elementary Particles for Ecology , 1982, The American Naturalist.

[27]  D. Bohm,et al.  Wholeness and the Implicate Order , 1981 .

[28]  R. Christian,et al.  Significance of euphotic sediments to oxygen and nutrient cycling in a temperate estuary , 1992 .

[29]  Caner Kazanci,et al.  How much of the storage in the ecosystem is due to cycling? , 2014, Journal of theoretical biology.

[30]  Stuart R. Borrett,et al.  Indirect effects and distributed control in ecosystems: Comparative network environ analysis of a seven-compartment model of nitrogen flow in the Neuse River estuary, USA—Time series analysis , 2007 .

[31]  Brian D. Fath,et al.  Indirect effects and distributed control in ecosystems:: Distributed control in the environ networks of a seven-compartment model of nitrogen flow in the Neuse River Estuary, USA—Steady-state analysis , 2006 .

[32]  Stuart R. Borrett,et al.  Indirect effects and distributed control in ecosystems Network environ analysis of a seven-compartment model of nitrogen flow in the Neuse River Estuary, USA-Steady-state analysis , 2006 .

[33]  J. Grinnell The Niche-Relationships of the California Thrasher , 1917 .

[34]  D. Corbett Resuspension and estuarine nutrient cycling: insights from the Neuse River Estuary , 2010 .

[35]  B. C. Patten Environs: The Superniches of Ecosystems , 1981 .

[36]  Bernard C. Patten,et al.  Further aspects of the analysis of indirect effects in ecosystems , 1986 .

[37]  H. Paerl Dynamics of Blue-Green Algal (Microcystis aeruginosa) Blooms in the Lower Neuse River, North Carolina: Cauative Factors and Potential Controls , 1987 .

[38]  Bernard C. Patten,et al.  System Theory of the Ecological Niche , 1981, The American Naturalist.

[39]  Stuart R. Borrett,et al.  Indirect effects and distributed control in ecosystems: Distributed control in the environ networks of a seven-compartment model of nitrogen flow in the Neuse River Estuary, USA—Time series analysis , 2007 .

[40]  Ernest W. Tollner,et al.  Cycling in ecosystems: An individual based approach , 2009 .

[41]  Robert R. Christian,et al.  Neuse River Estuary Modeling and Monitoring Project Stage 1: Network Analysis for Evaluating the Consequences of Nitrogen Loading , 2000 .

[42]  J. Burkholder,et al.  WATER QUALITY TRENDS AND MANAGEMENT IMPLICATIONS FROM A FIVE-YEAR STUDY OF A EUTROPHIC ESTUARY , 2000 .

[43]  W. Leontief,et al.  The Structure of American Economy, 1919-1939. , 1954 .

[44]  Andria K. Salas,et al.  Evidence for resource homogenization in 50 trophic ecosystem networks , 2010, 1104.0021.

[45]  R. Christian,et al.  A metabolism-based trophic index for comparing the ecological values of shallow-water sediment habitats , 1996 .

[46]  James H. Matis,et al.  The water environs of Okefenokee swamp: An application of static linear environ analysis , 1982 .

[47]  Stuart R. Borrett,et al.  Evidence for the dominance of indirect effects in 50 trophic ecosystem networks , 2010, 1009.1841.

[48]  W. Bryant,et al.  THE RELATIONSHIP BETWEEN RIVER FLOW AND MICROCYSTIS AERUGINOSA BLOOMS IN THE NEUSE RIVER, NORTH CAROLINA , 1986 .

[49]  Stuart R. Borrett,et al.  Indirect effects and distributed control in ecosystems: Temporal variation of indirect effects in a seven-compartment model of nitrogen flow in the Neuse River Estuary, USA—Time series analysis , 2006 .

[50]  Bernard C. Patten,et al.  Dominance of Indirect Causality in Ecosystems , 1989, The American Naturalist.

[51]  Ernest W. Tollner,et al.  Implications of network particle tracking (NPT) for ecological model interpretation , 2009 .

[52]  M. C. Barber,et al.  A Markovian model for ecosystem flow analysis , 1978 .

[53]  J. Burkholder,et al.  Pfiesteria piscicida and other Pfiesreria‐like dinoflagellates: Behavior, impacts, and environmental controls , 1997 .

[54]  Robert R. Christian,et al.  Network analysis of nitrogen inputs and cycling in the Neuse River estuary, North Carolina, USA , 2003 .

[55]  R. Christian,et al.  Multi-year distribution patterns of nutrients within the Neuse River Estuary, North Carolina , 1991 .

[56]  Joseph N. Boyer,et al.  Patterns of phytoplankton primary productivity in the Neuse River estuary, North Carolina, USA , 1993 .

[57]  Robert R. Christian,et al.  Ecological network analyses and their use for establishing reference domain in functional assessment of an estuary. , 2009 .

[58]  B. C. Patten,et al.  Throughflow analysis: A stochastic approach , 2009 .