Producers, Consumers and Food Webs 4.9AB
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Backyard Food
Suggested Grades: 2nd - 5th BACKYARD FOOD WEB Wildlife Champions at Home Science Experiment 2-LS4-1: Make observations of plants and animals to compare the diversity of life in different habitats. What is a food web? All living things on earth are either producers, consumers or decomposers. Producers are organisms that create their own food through the process of photosynthesis. Photosynthesis is when a living thing uses sunlight, water and nutrients from the soil to create its food. Most plants are producers. Consumers get their energy by eating other living things. Consumers can be either herbivores (eat only plants – like deer), carnivores (eat only meat – like wolves) or omnivores (eat both plants and meat - like humans!) Decomposers are organisms that get their energy by eating dead plants or animals. After a living thing dies, decomposers will break down the body and turn it into nutritious soil for plants to use. Mushrooms, worms and bacteria are all examples of decomposers. A food web is a picture that shows how energy (food) passes through an ecosystem. The easiest way to build a food web is by starting with the producers. Every ecosystem has plants that make their own food through photosynthesis. These plants are eaten by herbivorous consumers. These herbivores are then hunted by carnivorous consumers. Eventually, these carnivores die of illness or old age and become food for decomposers. As decomposers break down the carnivore’s body, they create delicious nutrients in the soil which plants will use to live and grow! When drawing a food web, it is important to show the flow of energy (food) using arrows. -
Body Size and Biomass Distributions of Carrion Visiting Beetles: Do Cities Host Smaller Species?
Ecol Res (2008) 23: 241–248 DOI 10.1007/s11284-007-0369-9 ORIGINAL ARTICLE Werner Ulrich Æ Karol Komosin´ski Æ Marcin Zalewski Body size and biomass distributions of carrion visiting beetles: do cities host smaller species? Received: 15 November 2006 / Accepted: 14 February 2007 / Published online: 28 March 2007 Ó The Ecological Society of Japan 2007 Abstract The question how animal body size changes Introduction along urban–rural gradients has received much attention from carabidologists, who noticed that cities harbour Animal and plant body size is correlated with many smaller species than natural sites. For Carabidae this aspects of life history traits and species interactions pattern is frequently connected with increasing distur- (dispersal, reproduction, energy intake, competition; bance regimes towards cities, which favour smaller Brown et al. 2004; Brose et al. 2006). Therefore, species winged species of higher dispersal ability. However, body size distributions (here understood as the fre- whether changes in body size distributions can be gen- quency distribution of log body size classes, SSDs) are eralised and whether common patterns exist are largely often used to infer patterns of species assembly and unknown. Here we report on body size distributions of energy use (Peters 1983; Calder 1984; Holling 1992; carcass-visiting beetles along an urban–rural gradient in Gotelli and Graves 1996; Etienne and Olff 2004; Ulrich northern Poland. Based on samplings of 58 necrophages 2005a, 2006). and 43 predatory beetle species, mainly of the families Many of the studies on local SSDs focused on the Catopidae, Silphidae, and Staphylinidae, we found number of modes and the shape. -
Fisheries in Large Marine Ecosystems: Descriptions and Diagnoses
Fisheries in Large Marine Ecosystems: Descriptions and Diagnoses D. Pauly, J. Alder, S. Booth, W.W.L. Cheung, V. Christensen, C. Close, U.R. Sumaila, W. Swartz, A. Tavakolie, R. Watson, L. Wood and D. Zeller Abstract We present a rationale for the description and diagnosis of fisheries at the level of Large Marine Ecosystems (LMEs), which is relatively new, and encompasses a series of concepts and indicators different from those typically used to describe fisheries at the stock level. We then document how catch data, which are usually available on a smaller scale, are mapped by the Sea Around Us Project (see www.seaaroundus.org) on a worldwide grid of half-degree lat.-long. cells. The time series of catches thus obtained for over 180,000 half-degree cells can be regrouped on any larger scale, here that of LMEs. This yields catch time series by species (groups) and LME, which began in 1950 when the FAO started collecting global fisheries statistics, and ends in 2004 with the last update of these datasets. The catch data by species, multiplied by ex-vessel price data and then summed, yield the value of the fishery for each LME, here presented as time series by higher (i.e., commercial) groups. Also, these catch data can be used to evaluate the primary production required (PPR) to sustain fisheries catches. PPR, when related to observed primary production, provides another index for assessing the impact of the countries fishing in LMEs. The mean trophic level of species caught by fisheries (or ‘Marine Trophic Index’) is also used, in conjunction with a related indicator, the Fishing-in-Balance Index (FiB), to assess changes in the species composition of the fisheries in LMEs. -
Plants Are Producers! Draw the Different Producers Below
Name: ______________________________ The Unique Producer Every food chain begins with a producer. Plants are producers. They make their own food, which creates energy for them to grow, reproduce and survive. Being able to make their own food makes them unique; they are the only living things on Earth that can make their own source of food energy. Of course, they require sun, water and air to thrive. Given these three essential ingredients, you will have a healthy plant to begin the food chain. All plants are producers! Draw the different producers below. Apple Tree Rose Bushes Watermelon Grasses Plant Blueberry Flower Fern Daisy Bush List the three essential needs that every producer must have in order to live. © 2009 by Heather Motley Name: ______________________________ Producers can make their own food and energy, but consumers are different. Living things that have to hunt, gather and eat their food are called consumers. Consumers have to eat to gain energy or they will die. There are four types of consumers: omnivores, carnivores, herbivores and decomposers. Herbivores are living things that only eat plants to get the food and energy they need. Animals like whales, elephants, cows, pigs, rabbits, and horses are herbivores. Carnivores are living things that only eat meat. Animals like owls, tigers, sharks and cougars are carnivores. You would not catch a plant in these animals’ mouths. Then, we have the omnivores. Omnivores will eat both plants and animals to get energy. Whichever food source is abundant or available is what they will eat. Animals like the brown bear, dogs, turtles, raccoons and even some people are omnivores. -
The Soil Food Web
THE SOIL FOOD WEB HEALTHY SOIL HEALTHY ENVIRONMENT The Soil Food Web Alan Sundermeier Extension Educator and Program Leader, Wood County Extension, The Ohio State University. Vinayak Shedekar Postdoctural Researcher, The Ohio State University. A healthy soil depends on the interaction of many organisms that make up the soil food web. These organisms live all or part of their life cycle in the soil and are respon- sible for converting energy as one organism consumes another. Source: Soil Biology Primer The phospholipid fatty acid (PLFA) test can be used to measure the activity of the soil food web. The following chart shows that mi-crobial activity peaks in early summer when soil is warm and moisture is adequate. Soil sampling for detecting soil microbes should follow this timetable to better capture soil microbe activity. The soil food web begins with the ener- gy from the sun, which triggers photo- synthesis in plants. Photosynthesis re- sults in plants using the sun’s energy to fix carbon dioxide from the atmosphere. This process creates the carbon and organic compounds contained in plant material. This is the first trophic level. Then begins building of soil organic matter, which contains both long-last- ing humus, and active organic matter. Active organic matter contains readily available energy, which can be used by simple soil organisms in the second trophic level of the soil food web. Source: Soil Biology Primer SOILHEALTH.OSU.EDU THE SOIL FOOD WEB - PAGE 2 The second trophic level contains simple soil organisms, which Agriculture can enhance the soil food web to create more decompose plant material. -
Can More K-Selected Species Be Better Invaders?
Diversity and Distributions, (Diversity Distrib.) (2007) 13, 535–543 Blackwell Publishing Ltd BIODIVERSITY Can more K-selected species be better RESEARCH invaders? A case study of fruit flies in La Réunion Pierre-François Duyck1*, Patrice David2 and Serge Quilici1 1UMR 53 Ӷ Peuplements Végétaux et ABSTRACT Bio-agresseurs en Milieu Tropical ӷ CIRAD Invasive species are often said to be r-selected. However, invaders must sometimes Pôle de Protection des Plantes (3P), 7 chemin de l’IRAT, 97410 St Pierre, La Réunion, France, compete with related resident species. In this case invaders should present combina- 2UMR 5175, CNRS Centre d’Ecologie tions of life-history traits that give them higher competitive ability than residents, Fonctionnelle et Evolutive (CEFE), 1919 route de even at the expense of lower colonization ability. We test this prediction by compar- Mende, 34293 Montpellier Cedex, France ing life-history traits among four fruit fly species, one endemic and three successive invaders, in La Réunion Island. Recent invaders tend to produce fewer, but larger, juveniles, delay the onset but increase the duration of reproduction, survive longer, and senesce more slowly than earlier ones. These traits are associated with higher ranks in a competitive hierarchy established in a previous study. However, the endemic species, now nearly extinct in the island, is inferior to the other three with respect to both competition and colonization traits, violating the trade-off assumption. Our results overall suggest that the key traits for invasion in this system were those that *Correspondence: Pierre-François Duyck, favoured competition rather than colonization. CIRAD 3P, 7, chemin de l’IRAT, 97410, Keywords St Pierre, La Réunion Island, France. -
Nocturnal Rodents
Nocturnal Rodents Peter Holm Objectives (Chaetodipus spp. and Perognathus spp.) and The monitoring protocol handbook (Petryszyn kangaroo rats (Dipodomys spp.) belong to the 1995) states: “to document general trends in family Heteromyidae (heteromyids), while the nocturnal rodent population size on an annual white-throated woodrats (Neotoma albigula), basis across a representative sample of habitat Arizona cotton rat (Sigmodon arizonae), cactus types present in the monument”. mouse (Peromyscus eremicus), and grasshopper mouse (Onychomys torridus), belong to the family Introduction Muridae. Sigmodon arizonae, a native riparian Nocturnal rodents constitute the prey base for species relatively new to OPCNM, has been many snakes, owls, and carnivorous mammals. recorded at the Dos Lomitas and Salsola EMP All nocturnal rodents, except for the grasshopper sites, adjacent to Mexican agricultural fields. mouse, are primary consumers. Whereas Botta’s pocket gopher (Thomomys bottae) is the heteromyids constitute an important guild lone representative of the family Geomyidae. See of granivores, murids feed primarily on fruit Petryszyn and Russ (1996), Hoffmeister (1986), and foliage. Rodents are also responsible for Petterson (1999), Rosen (2000), and references considerable excavation and mixing of soil layers therein, for a thorough review. (bioturbation), “predation” on plants and seeds, as well as the dispersal and caching of plant seeds. As part of the Sensitive Ecosystems Project, Petryszyn and Russ (1996) conducted a baseline Rodents are common in all monument habitats, study originally titled, Special Status Mammals are easily captured and identified, have small of Organ Pipe Cactus National Monument. They home ranges, have high fecundity, and respond surveyed for nocturnal rodents and other quickly to changes in primary productivity and mammals in various habitats throughout the disturbance (Petryszyn 1995, Petryszyn and Russ monument and found that murids dominated 1996, Petterson 1999). -
Introduction to the Special Issue on Spatial Ecology
International Journal of Geo-Information Editorial Space-Ruled Ecological Processes: Introduction to the Special Issue on Spatial Ecology Duccio Rocchini 1,2,3 1 University of Trento, Center Agriculture Food Environment, Via E. Mach 1, 38010 S. Michele all’Adige (TN), Italy; [email protected] 2 University of Trento, Centre for Integrative Biology, Via Sommarive, 14, 38123 Povo (TN), Italy 3 Fondazione Edmund Mach, Department of Biodiversity and Molecular Ecology, Research and Innovation Centre, Via E. Mach 1, 38010 S. Michele all’Adige (TN), Italy Received: 12 December 2017; Accepted: 23 December 2017; Published: 2 January 2018 This special issue explores most of the scientific issues related to spatial ecology and its integration with geographical information at different spatial and temporal scales. Papers are mainly related to challenging aspects of species variability over space and landscape dynamics, providing a benchmark for future exploration on this theme. The need for a spatial view in Ecology is a fact. Dealing with ecological changes over space and time represents a long-lasting theme, now faced by means of innovative techniques and modelling approaches (e.g., Chaudhary et al. [1], Palmer [2], Rocchini [3]). This special issue explores some of them, with challenging ideas facing different components of spatial patterns related to ecological processes, such as: (i) species variability over space [4–11]; and (ii) landscape dynamics [12,13]. Concerning biodiversity variability over space, key spatial datasets are needed to fully investigate biodiversity change in space and time, as shown by Geri et al. [7], who carried out innovative procedures to recover and properly map historical floristic and vegetation data for biodiversity monitoring. -
Urban Food Webs: Predators, Prey, and the People Who Feed Them
Urban Food Webs: Predators, Prey, and the People Who Feed Them A prevailing image of the city is of the steel and ships and energy flows through natural habitats, they concrete downtown skyline. The more common ex‑ have not been applied to urban ecosystems until re‑ perience of urban residents, however, is a place of cently (Faeth et al. 2005). irrigated and fertilized green spaces, such as yards, gardens, and parks, surrounding homes and business‑ At a symposium presented at the 2006 Ecological es where people commonly feed birds, squirrels, and Society of America meeting, 10 speakers assembled other wildlife. Within these highly human-modified to present and discuss “The Urban Food Web: How environments, researchers are becoming increasingly Humans Alter the State and Interactions of Trophic curious about how fundamental ecological phenom‑ Dynamics,” in a symposium organized by Paige War‑ ena play out, such as the feeding relationships among ren, Chris Tripler, Chris Lepczyk, and Jason Walker. species. While food webs have long provided a tool A key feature of urban environments, as described in for organizing information about feeding relation‑ the symposium, is that human influence may be en‑ Fig. 1. A generalized model of trophic dynamics in urban vs. non-urban terrestrial systems (modified from Faeth et al. 2005). Humans alter both systems, but in urban environments, human influences are more profound and include (a) enhancement of basal resources like water and fertilizer, and (b) direct control of plant species diversity and primary productivity, leading to strong bottom-up controls. Humans also (c) directly subsidize resources for herbivores and predators either through intentional feeding or unintended consequences of other activities (e.g., garbage, landscape plantings), leading to enhanced top-down control for some taxa and reduced top-down controls on others (see Fig. -
Models of the World's Large Marine Ecosystems: GEF/LME Global
Intergovernmental Oceanographic Commission technical series 80 Models of the World’s Large Marine Ecosystems UNESCO Intergovernmental Oceanographic Commission technical series 80 Models of the World’s Large Marine Ecosystems* GEF/LME global project Promoting Ecosystem-based Approaches to Fisheries Conservation and Large Marine Ecosystems UNESCO 2008 * As submitted to IOC Technical Series, UNESCO, 22 October 2008 IOC Technical Series No. 80 Paris, 20 October 2008 English only The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariats of UNESCO and IOC concerning the legal status of any country or territory, or its authorities, or concerning the delimitation of the frontiers of any country or territory. For bibliographic purposes, this document should be cited as follows: Models of the World’s Large Marine Ecosystems GEF/LME global project Promoting Ecosystem-based Approaches to Fisheries Conservation and Large Marine Ecosystems IOC Technical Series No. 80. UNESCO, 2008 (English) Editors: Villy Christensen1, Carl J. Walters1, Robert Ahrens1, Jackie Alder2, Joe Buszowski1, Line Bang Christensen1, William W.L. Cheung1, John Dunne3, Rainer Froese4, Vasiliki Karpouzi1, Kristin Kastner5, Kelly Kearney6, Sherman Lai1, Vicki Lam1, Maria L.D. Palomares1,7, Aja Peters-Mason8, Chiara Piroddi1, Jorge L. Sarmiento6, Jeroen Steenbeek1, Rashid Sumaila1, Reg Watson1, Dirk Zeller1, and Daniel Pauly1. Technical Editor: Jair Torres 1 Fisheries Centre, -
Soil Food Web: Implications to Soil Health
Soil Food Web: Implications to Soil Health Dr. Sajeemas “Mint” Pasakdee, Soil Scientist/Agronomist Advisor, Student Operated Organic Farm CIT-Jordan College of Agri. Sci. & Tech., Fresno State 1 Outline • Soil organisms and their interactions • What do soil organisms do? • Where do soil organisms live? • Food web structure • When are soil organisms active? • How is the food web measured? • Living soils—Bacteria; Fungi; Earthworms • Soil Environment 2 Organisms & Their Interaction 3 4 What do soil organisms do? Soil organisms support plant health as • decompose organic matter, • cycle nutrients, • enhance soil structure, • control the populations of soil organisms including crop pests. 5 Organic Matter • Food sources for soil organisms • Agricultural top soil ~1-6% (In CA, ~1-3% SOM) 6 Where do soil organisms live? • Around roots(rhizosphere) • Plant litter (C sources) • Humus (stabilized organic matter) • Surface of soil aggregates 7 Typical Food Web Structure • bacterial-dominated food webs o Grassland & Agri Soils o Ratio of fungi to bacteria, ~1:1 for productive agri. soils • fungal-dominated food webs o Ratio of fungal to bacterial, ~5:1 to 10:1 in a deciduous forest and 100:1 to 1000:1 in a coniferous forest 8 9 When are soil organisms active? 10 How is the food web measured? • Counting. Organism groups (bacteria, protozoa, arthropods, etc.); or subgroups (bacterial-feeding, fungal-feeding, and predatory nematodes), are counted and through calculations, can be converted to biomass. • Measuring activity levels. The amount of by-products, i.e., respiration (CO2); nitrification and decomposition rates • Measuring cellular constituents. Biomass carbon, nitrogen, or phosphorus; Enzymes; Phospholipids and other lipids; DNA and RNA 11 12 Soil Bacteria • One-celled organisms – generally 4/100,000 of an inch wide (1 µm) • A teaspoon of productive soil generally contains between 100 million and 1 billion bacteria (~two cows per acre). -
7.014 Lectures 16 &17: the Biosphere & Carbon and Energy Metabolism
MIT Department of Biology 7.014 Introductory Biology, Spring 2005 7.014 Lectures 16 &17: The Biosphere & Carbon and Energy Metabolism Simplified Summary of Microbial Metabolism The metabolism of different types of organisms drives the biogeochemical cycles of the biosphere. Balanced oxidation and reduction reactions keep the system from “running down”. All living organisms can be ordered into two groups1, autotrophs and heterotrophs, according to what they use as their carbon source. Within these groups the metabolism of organisms can be further classified according to their source of energy and electrons. Autotrophs: Those organisms get their energy from light (photoautotrophs) or reduced inorganic compounds (chemoautotrophs), and their carbon from CO2 through one of the following processes: Photosynthesis (aerobic) — Light energy used to reduce CO2 to organic carbon using H2O as a source of electrons. O2 evolved from splitting H2O. (Plants, algae, cyanobacteria) Bacterial Photosynthesis (anaerobic) — Light energy used to reduce CO2 to organic carbon (same as photosynthesis). H2S is used as the electron donor instead of H2O. (e.g. purple sulfur bacteria) Chemosynthesis (aerobic) — Energy from the oxidation of inorganic molecules is used to reduce CO2 to organic carbon (bacteria only). -2 e.g. sulfur oxidizing bacteria H2S → S → SO4 + - • nitrifying bacteria NH4 → NO2 → NO3 iron oxidizing bacteria Fe+2 → Fe+3 methane oxidizing bacteria (methanotrophs) CH4 → CO2 Heterotrophs: These organisms get their energy and carbon from organic compounds (supplied by autotrophs through the food web) through one or more of the following processes: Aerobic Respiration (aerobic) ⎯ Oxidation of organic compounds to CO2 and H2O, yielding energy for biological work.