Ecosystem Productivity and Diversity Primary Focus of Ecosystem Ecology
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7.014 Handout PRODUCTIVITY: the “METABOLISM” of ECOSYSTEMS
7.014 Handout PRODUCTIVITY: THE “METABOLISM” OF ECOSYSTEMS Ecologists use the term “productivity” to refer to the process through which an assemblage of organisms (e.g. a trophic level or ecosystem assimilates carbon. Primary producers (autotrophs) do this through photosynthesis; Secondary producers (heterotrophs) do it through the assimilation of the organic carbon in their food. Remember that all organic carbon in the food web is ultimately derived from primary production. DEFINITIONS Primary Productivity: Rate of conversion of CO2 to organic carbon (photosynthesis) per unit surface area of the earth, expressed either in terns of weight of carbon, or the equivalent calories e.g., g C m-2 year-1 Kcal m-2 year-1 Primary Production: Same as primary productivity, but usually expressed for a whole ecosystem e.g., tons year-1 for a lake, cornfield, forest, etc. NET vs. GROSS: For plants: Some of the organic carbon generated in plants through photosynthesis (using solar energy) is oxidized back to CO2 (releasing energy) through the respiration of the plants – RA. Gross Primary Production: (GPP) = Total amount of CO2 reduced to organic carbon by the plants per unit time Autotrophic Respiration: (RA) = Total amount of organic carbon that is respired (oxidized to CO2) by plants per unit time Net Primary Production (NPP) = GPP – RA The amount of organic carbon produced by plants that is not consumed by their own respiration. It is the increase in the plant biomass in the absence of herbivores. For an entire ecosystem: Some of the NPP of the plants is consumed (and respired) by herbivores and decomposers and oxidized back to CO2 (RH). -
Thermophilic Lithotrophy and Phototrophy in an Intertidal, Iron-Rich, Geothermal Spring 2 3 Lewis M
bioRxiv preprint doi: https://doi.org/10.1101/428698; this version posted September 27, 2018. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Thermophilic Lithotrophy and Phototrophy in an Intertidal, Iron-rich, Geothermal Spring 2 3 Lewis M. Ward1,2,3*, Airi Idei4, Mayuko Nakagawa2,5, Yuichiro Ueno2,5,6, Woodward W. 4 Fischer3, Shawn E. McGlynn2* 5 6 1. Department of Earth and Planetary Sciences, Harvard University, Cambridge, MA 02138 USA 7 2. Earth-Life Science Institute, Tokyo Institute of Technology, Meguro, Tokyo, 152-8550, Japan 8 3. Division of Geological and Planetary Sciences, California Institute of Technology, Pasadena, CA 9 91125 USA 10 4. Department of Biological Sciences, Tokyo Metropolitan University, Hachioji, Tokyo 192-0397, 11 Japan 12 5. Department of Earth and Planetary Sciences, Tokyo Institute of Technology, Meguro, Tokyo, 13 152-8551, Japan 14 6. Department of Subsurface Geobiological Analysis and Research, Japan Agency for Marine-Earth 15 Science and Technology, Natsushima-cho, Yokosuka 237-0061, Japan 16 Correspondence: [email protected] or [email protected] 17 18 Abstract 19 Hydrothermal systems, including terrestrial hot springs, contain diverse and systematic 20 arrays of geochemical conditions that vary over short spatial scales due to progressive interaction 21 between the reducing hydrothermal fluids, the oxygenated atmosphere, and in some cases 22 seawater. At Jinata Onsen, on Shikinejima Island, Japan, an intertidal, anoxic, iron- and 23 hydrogen-rich hot spring mixes with the oxygenated atmosphere and sulfate-rich seawater over 24 short spatial scales, creating an enormous range of redox environments over a distance ~10 m. -
Relationships Between Net Primary Production, Water Transparency, Chlorophyll A, and Total Phosphorus in Oak Lake, Brookings County, South Dakota
Proceedings of the South Dakota Academy of Science, Vol. 92 (2013) 67 RELATIONSHIPS BETWEEN NET PRIMARY PRODUCTION, WATER TRANSPARENCY, CHLOROPHYLL A, AND TOTAL PHOSPHORUS IN OAK LAKE, BROOKINGS COUNTY, SOUTH DAKOTA Lyntausha C. Kuehl and Nels H. Troelstrup, Jr.* Department of Natural Resource Management South Dakota State University Brookings, SD 57007 *Corresponding author email: [email protected] ABSTRACT Lake trophic state is of primary concern for water resource managers and is used as a measure of water quality and classification for beneficial uses. Secchi transparency, total phosphorus and chlorophyll a are surrogate measurements used in the calculation of trophic state indices (TSI) which classify waters as oligotrophic, mesotrophic, eutrophic or hypereutrophic. Yet the relationships between these surrogate measurements and direct measures of lake productivity vary regionally and may be influenced by external factors such as non-algal tur- bidity. Prairie pothole basins, common throughout eastern South Dakota and southwestern Minnesota, are shallow glacial lakes subject to frequent winds and sediment resuspension. Light-dark oxygen bottle methodology was employed to evaluate vertical planktonic production within an eastern South Dakota pothole basin. Secchi transparency, total phosphorus and planktonic chlorophyll a were also measured from each of three basin sites at biweekly intervals throughout the 2012 growing season. Secchi transparencies ranged between 0.13 and 0.25 meters, corresponding to an average TSISD value of 84.4 (hypereutrophy). Total phosphorus concentrations ranged between 178 and 858 ug/L, corresponding to an average TSITP of 86.7 (hypereutrophy). Chlorophyll a values corresponded to an average TSIChla value of 69.4 (transitional between eutrophy and hypereutro- phy) and vertical production profiles yielded areal net primary productivity val- ues averaging 288.3 mg C∙m-2∙d-1 (mesotrophy). -
Analysis of Habitat Fragmentation and Ecosystem Connectivity Within the Castle Parks, Alberta, Canada by Breanna Beaver Submit
Analysis of Habitat Fragmentation and Ecosystem Connectivity within The Castle Parks, Alberta, Canada by Breanna Beaver Submitted in Partial Fulfillment of the Requirements for the Degree of Master of Science in the Environmental Science Program YOUNGSTOWN STATE UNIVERSITY December, 2017 Analysis of Habitat Fragmentation and Ecosystem Connectivity within The Castle Parks, Alberta, Canada Breanna Beaver I hereby release this thesis to the public. I understand that this thesis will be made available from the OhioLINK ETD Center and the Maag Library Circulation Desk for public access. I also authorize the University or other individuals to make copies of this thesis as needed for scholarly research. Signature: Breanna Beaver, Student Date Approvals: Dawna Cerney, Thesis Advisor Date Peter Kimosop, Committee Member Date Felicia Armstrong, Committee Member Date Clayton Whitesides, Committee Member Date Dr. Salvatore A. Sanders, Dean of Graduate Studies Date Abstract Habitat fragmentation is an important subject of research needed by park management planners, particularly for conservation management. The Castle Parks, in southwest Alberta, Canada, exhibit extensive habitat fragmentation from recreational and resource use activities. Umbrella and keystone species within The Castle Parks include grizzly bears, wolverines, cougars, and elk which are important animals used for conservation agendas to help protect the matrix of the ecosystem. This study identified and analyzed the nature of habitat fragmentation within The Castle Parks for these species, and has identified geographic areas of habitat fragmentation concern. This was accomplished using remote sensing, ArcGIS, and statistical analyses, to develop models of fragmentation for ecosystem cover type and Digital Elevation Models of slope, which acted as proxies for species habitat suitability. -
Ecological Systems of the United States a Working Classification of U.S
ECOLOGICAL SYSTEMS OF THE UNITED STATES A WORKING CLASSIFICATION OF U.S. TERRESTRIAL SYSTEMS NatureServe is a non-profit organization dedicated to providing the scientific knowledge that forms the basis for effective conservation action. Citation: Comer, P., D. Faber-Langendoen, R. Evans, S. Gawler, C. Josse, G. Kittel, S. Menard, M. Pyne, M. Reid, K. Schulz, K. Snow, and J. Teague. 2003. Ecological Systems of the United States: A Working Classification of U.S. Terrestrial Systems. NatureServe, Arlington, Virginia. © NatureServe 2003 Ecological Systems of the United States is a component of NatureServe’s International Terrestrial Ecological Systems Classification. Á Funding for this report was provided by a grant from The Nature Conservancy. Front cover: Maroon Bells Wilderness, Colorado. Photo © Patrick Comer NatureServe 1101 Wilson Boulevard, 15th Floor Arlington, VA 22209 (703) 908-1800 www.natureserve.org ECOLOGICAL SYSTEMS OF THE UNITED STATES A WORKING CLASSIFICATION OF U.S. TERRESTRIAL SYSTEMS Á Á Á Á Á Patrick Comer Don Faber-Langendoen Rob Evans Sue Gawler Carmen Josse Gwen Kittel Shannon Menard Milo Pyne Marion Reid Keith Schulz Kristin Snow Judy Teague June 2003 Acknowledgements We wish to acknowledge the generous support provided by The Nature Conservancy for this effort to classify and characterize the ecological systems of the United States. We are particularly grateful to the late John Sawhill, past President of The Nature Conservancy, who was an early supporter of this concept, and who made this funding possible through an allocation from the President’s Discretionary Fund. Many of the concepts and approaches for defining and applying ecological systems have greatly benefited from collaborations with Conservancy staff, and the classification has been refined during its application in Conservancy-sponsored conservation assessments. -
Interactions Between Photosynthesis and Respiration in an Aquatic Ecosystem
Interactions between Photosynthesis and Respiration in an Aquatic Ecosystem Jane E. Caldwell and Kristi Teagarden 53 Campus Drive, P.O. Box 6057 Dept. of Biology West Virginia University Morgantown, WV 26506 [email protected] (304)293-5201 extension 31459 [email protected] (304)293-5201 extension 31542 Abstract: Students measure the results of respiration and photosynthesis separately, combined, and in comparison to a non-living control “ecosystem”. The living ecosystem uses only snails and water plants. Oxygen, carbon dioxide, and ammonia nitrogen concentrations are measured with simple colorimetric and titration water tests using commercially available kits. The exercise is designed for large enrollment non-majors labs, but modifications for large and small classrooms are described. Introduction This lab exercise was developed for a freshman course for non-science majors at West Virginia University. The exercise asks students to apply their knowledge of basic metabolic processes to a series of simple aquatic ecosystems, which students monitor through water testing. These ecosystems consist of aquaria containing plants and/or snails with or without light exposure, and are compared against a non-living control system (an aquarium with water, light, and gravel). As they analyze their results, students observe the interplay of respiration, photosynthesis, protein digestion (or waste excretion), and decomposition through their effects on dissolved oxygen, carbon dioxide, and ammonia. Students synthesize these observations into written explanations of their results. During the course of the lab, students: • predict the relative levels of oxygen, carbon dioxide, and ammonia for various aquaria compared to a control aquarium. • observe and conduct titrimetric and colorimetric tests for dissolved compounds in water. -
Productivity Is Defined As the Ratio of Output to Input(S)
Institute for Development Policy and Management (IDPM) Development Economics and Public Policy Working Paper Series WP No. 31/2011 Published by: Development Economics and Public Policy Cluster, Institute of Development Policy and Management, School of Environment and Development, University of Manchester, Manchester M13 9PL, UK; email: [email protected]. PRODUCTIVITY MEASUREMENT IN INDIAN MANUFACTURING: A COMPARISON OF ALTERNATIVE METHODS Vinish Kathuria SJMSOM, Indian Institute of Technology Bombay [email protected] Rajesh S N Raj * Centre for Multi-Disciplinary Development Research, Dharwad [email protected] Kunal Sen IDPM, University of Manchester [email protected] Abstract Very few other issues in explaining economic growth has generated so much debate than the measurement of total factor productivity (TFP) growth. The concept of TFP and its measurement and interpretation have offered a fertile ground for researchers for more than half a century. This paper attempts to provide a review of different issues in the measurement of TFP including the choice of inputs and outputs. The paper then gives a brief review of different techniques used to compute TFP growth. Using three different techniques – growth accounting (non-parametric), production function accounting for endogeniety (semi-parametric) and stochastic production frontier (parametric) – the paper computes the TFP growth of Indian manufacturing for both formal and informal sectors from 1989-90 to 2005-06. The results indicate that the TFP growth of formal and informal sector has differed greatly during this 16-year period but that the estimates are sensitive to the technique used. This suggests that any inference on productivity growth in India since the economic reforms of 1991 is conditional on the method of measurement used, and that there is no unambiguous picture emerging on the direction of change in TFP growth in post-reform India. -
Structure and Distribution of Cold Seep Communities Along the Peruvian Active Margin: Relationship to Geological and Fluid Patterns
MARINE ECOLOGY PROGRESS SERIES Vol. 132: 109-125, 1996 Published February 29 Mar Ecol Prog Ser l Structure and distribution of cold seep communities along the Peruvian active margin: relationship to geological and fluid patterns 'Laboratoire Ecologie Abyssale, DROIEP, IFREMER Centre de Brest, BP 70, F-29280 Plouzane, France '~epartementdes Sciences de la Terre, UBO, 6 ave. Le Gorgeu, F-29287 Brest cedex, France 3~aboratoireEnvironnements Sedimentaires, DROIGM, IFREMER Centre de Brest, BP 70, F-29280 Plouzane, France "niversite P. et M. Curie, Observatoire Oceanologique de Banyuls, F-66650 Banyuls-sur-Mer, France ABSTRACT Exploration of the northern Peruvian subduction zone with the French submersible 'Nau- tile' has revealed benthlc communities dominated by new species of vesicomyid bivalves (Calyptogena spp and Ves~comyasp ) sustained by methane-nch fluid expulsion all along the continental margin, between depths of 5140 and 2630 m Videoscoplc studies of 25 dives ('Nautiperc cruise 1991) allowed us to describe the distribution of these biological conlnlunities at different spahal scales At large scale the communities are associated with fluid expuls~onalong the major tectonic features (scarps, canyons) of the margln At a smaller scale on the scarps, the distribuhon of the communities appears to be con- trolled by fluid expulsion along local fracturatlon features such as joints, faults and small-scale scars Elght dlves were made at one particular geological structure the Middle Slope Scarp (the scar of a large debns avalanche) where numerous -
Carlson's Trophic State Index
Carlson's Trophic State Index The cloudiness of lake water and how far down you can see is often related to the amount of nutrients in the water. Nutrients promote growth of microscopic plant cells (phytoplankton) that are fed upon by microscopic animals (zooplankton). The more the nutrients, the more the plants and animals and the cloudier the water is. This is a common, but indirect, way to roughly estimate the condition of the lake. This condition, called eutrophication, is a natural aging process of lakes, but which is unnaturally accelerated by too many nutrients. A Secchi disk is commonly used to measure the depth to which you can easily see through the water, also called its transparency. Secchi disk transparency, chlorophyll a (an indirect measure of phytoplankton), and total phosphorus (an important nutrient and potential pollutant) are often used to define the degree of eutrophication, or trophic status of a lake. The concept of trophic status is based on the fact that changes in nutrient levels (measured by total phosphorus) causes changes in algal biomass (measured by chlorophyll a) which in turn causes changes in lake clarity (measured by Secchi disk transparency). A trophic state index is a convenient way to quantify this relationship. One popular index was developed by Dr. Robert Carlson of Kent State University. Trophic State Index Carlson's index uses a log transformation of Secchi disk values as a measure of algal biomass on a scale from 0 - 110. Each increase of ten units on the scale represents a doubling of algal biomass. Because chlorophyll a and total phosphorus are usually closely correlated to Secchi disk measurements, these parameters can also be assigned trophic state index values. -
Biodiversity Implications Is Biogeography: For
FEATURE BIODIVERSITY IS BIOGEOGRAPHY: IMPLICATIONS FOR CONSERVATION By G. Carleton Ray THREE THEMES DOMINATEthis review. The first is similarities, as is apparent within the coastal zone, that biodiversity is biogeography. Or, as Nelson the biodiversity of which depends on land-sea in- and Ladiges (1990) put it: "Indeed, what beyond teractions. biogeography is "biodiversity' about?" Second, "Characteristic Biodiversity"--a Static View watershed and seashed patterns and their scale-re- A complete species inventory for any biogeo- lated dynamics are major modifiers of biogeo- graphic province on Earth is virtually impossible. graphic pattern. And, third, concepts of biodiver- In fact, species lists, absent a biogeographic frame sity and biogeography are essential guides for of reference, can be ecologically meaningless, be- conservation and management of coastal-marine cause such lists say little about the dynamics of systems, especially for MACPAs (MArine and environmental change. To address such dynamics, Coastal Protected Areas). biodiversity is best expressed at a hierarchy of Conservation and conservation bioecology have scales, which this discussion follows. entered into an era of self-awareness of their suc- cesses. Proponents of "biodiversity" have achieved Global Patterns worldwide recognition. Nevertheless: "Like so Hayden el al. (1984) attempted a summary of the many buzz words, biodiversity has many shades of state-of-the-art of global, coastal-marine biogeogra- • . the coastal zone, meaning and is often used to express vague and phy at the behest of UNESCO's Man and the Bios- which is the most bio- ill-thought-out concepts" (Angel, 1991), as phere Programme (MAB) and the International reflected by various biodiversity "strategies" Union for the Conservation of Nature (IUCN). -
Forest Production Ecology • Objectives – Overview of Forest Production Ecology • C Cycling – Primary Productivity of Trees and Forest Ecosystems
Forest Production Ecology • Objectives – Overview of forest production ecology • C cycling – Primary productivity of trees and forest ecosystems … ecologists and ecosystem managers are unlikely to achieve desired management objectives unless they are familiar with the distribution and movements of energy that are responsible for the character and productivity of ecosystems under their management. (Kimmins 2004) – First: questions, take-home points, things you learned, etc. from reading assignment 1 Forest Production Ecology • Why should you care about C cycling? – C is the energy currency of all ecosystems • Plant (autotrophic) production is the base of almost all food/energy pyramids • Underlies all ecosystem goods & services – Plant C cycling, to a large extent, controls atmospheric CO2 concentrations (i.e., climate) • 3-4x as much C in terrestrial ecosystems as the atmosphere • Forests account for ~80% of global plant biomass and ~50% of global terrestrial productivity – C is fundamental to soil processes (i.e., SOM) • Belowground resources are a primary control over all ecosystem processes 2 Forest Production Ecology •Global Carbon Cycle ≈ “Breathing” of Earth 3 Forest Production Ecology • C enters via photosynthesis The C Bank Account 1. Gross Primary Production (GPP) •Total C input via photosynthesis 2. Accumulates in ecosystems (C pools/storage) as: (a) plant biomass; (b) SOM & microbial biomass; or (c) animal biomass 3. Returned to the atmosphere via: (a) respiration (R; auto- or hetero-trophic); (b) VOC emissions; or (c) disturbance Chapin et al. (2011) 4. Leached from or transferred laterally to another ecosystem Forest Production Ecology • Keys to understanding biological C cycling 1. Pools (storage) vs. fluxes (flows) of C • Live and dead (detrital) biomass • Above- and belowground 2. -
Productivity Significant Ideas
2.3 Flows of Energy & Matter - Productivity Significant Ideas • Ecosystems are linked together by energy and matter flow • The Sun’s energy drives these flows and humans are impacting the flows of energy and matter both locally and globally Knowledge & Understandings • As solar radiation (insolation) enters the Earth’s atmosphere some energy becomes unavailable for ecosystems as the energy absorbed by inorganic matter or reflected back into the atmosphere. • Pathways of radiation through the atmosphere involve the loss of radiation through reflection and absorption • Pathways of energy through an ecosystem include: • Conversion of light to chemical energy • Transfer of chemical energy from one trophic level to another with varying efficiencies • Overall conversion of UB and visible light to heat energy by the ecosystem • Re-radiation of heat energy to the atmosphere. Knowledge & Understandings • The conversion of energy into biomass for a given period of time is measured by productivity • Net primary productivity (NPP) is calculated by subtracting respiratory losses (R) from gross primary productivity (GPP) NPP = GPP – R • Gross secondary productivity (GSP) is the total energy/biomass assimulated by consumers and is calculated by subtracting the mass of fecal loss from the mass of food eaten. GSP = food eaten – fecal loss • Net secondary productivity (NSP) is calculated by subtracting the respiratory losses (R) from GSP. NSP=GSP - R Applications and Skills • Analyze quantitative models of flows of energy and matter • Construct quantitative