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1

Moore, Ralph L. Environmental protection by the neutralization of wastewater using pH control. Research Triangle Park, N.C., U.S.A: Instrument Society of America, 1995.

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2

Price, Cynthia B. Transformation of RDX and HMX under controlled Eh/pH conditions. Vicksburg, Miss: U.S. Army Engineer Waterways Experiment Station, 1998.

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3

Paur, Richard J. Development and evaluation of a real-time pH and conductivity rain monitor. Research Triangle Park, NC: U.S. Environmental Protection Agency, Environmental Monitoring Systems Laboratory, 1987.

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4

Lytle, Darren A. Stagnation time, composition, pH, and orthophosphate effects on metal leaching from brass. Cincinnati, Ohio: National Risk Management Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, 1996.

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5

Swanson, Trevor. Walla Walla River Basin fecal coliform bacteria and pH total maximum daily load study, data summary report. Olympia, WA: Washington State Dept. of Ecology, 2005.

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6

Swanson, Trevor. Walla Walla River Basin fecal coliform bacteria and pH total maximum daily load study, data summary report. Olympia, WA: Washington State Dept. of Ecology, 2005.

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7

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, Or: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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8

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, Or: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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9

Fiske, Steven. Macroinvertebrate survey of 25 soft water-pH sensitive lakes in Vermont. [Waterbury, Vt.?]: Special Studies & Surveillance Unit, Dept. of Environmental Conservation, 1987.

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10

Schroder, L. J. Precision of the measurement of pH and specific conductance at National Atmospheric Deposition Program monitoring sites, October 1981 - November 1983. Lakewood, Colo: U.S. Dept. of the Interior, Geological Survey ; Denver, CO, 1985.

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11

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, OR: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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12

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, Or: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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13

Joy, Joe. Stillaguamish River Watershed fecal coliform, dissolved oxygen, pH, arsenic, and mercury total maximum daily load study. Olympia, WA: Washington State Dept. of Ecology, 2004.

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14

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, OR: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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15

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, OR: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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16

Fisher, Lawrence H. Effect of water-column pH on sediment-phosphorus release rates in Upper Klamath Lake, Oregon, 2001. Portland, Or: U.S. Dept. of the Interior, U.S. Geological Survey, 2004.

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17

Day, Norman. The effects of low environmental pH and reversed seasonal temperatures on swimming performance in the brown trout Salmo trutta. Birmingham: University of Birmingham, 1999.

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18

Joy, Joe. Walla Walla River Basin pH and dissolved oxygen total maximum daily load: Water quality improvement report. [Olympia, Wash.]: Washington State Dept. of Ecology, 2007.

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19

Joy, Joe. Walla Walla River Basin pH and dissolved oxygen total maximum daily load: Water quality improvement report. [Olympia, Wash.]: Washington State Dept. of Ecology, 2007.

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20

Lawrence, Sally. Stillaguamish River Watershed fecal coliform, dissolved oxygen, pH, arsenic, and mercury total maximum daily load (water cleanup plan): Submittal report. Olympia, WA: Washington State Dept. of Ecology, 2005.

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21

Whiley, Anthony J. Colville National Forest temperature, bacteria, pH and dissolved oxygen total maximum daily load (water cleanup plan): Submittal report. Olympia, WA: Washington State Dept. of Ecology, 2005.

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22

Whiley, Anthony J. Colville National Forest temperature, bacteria, pH and dissolved oxygen total maximum daily load (water cleanup plan): Submittal report. Olympia, WA: Washington State Dept. of Ecology, 2005.

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23

Joy, Joe. Data summary: Stillaguamish River Watershed fecal coliform, dissolved oxygen, pH, mercury, and arsenic total maximum daily load study. Olympia, WA: Washington State Dept. of Ecology, 2004.

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24

Dan, Binkley, ed. Acidic deposition and forest soils: Context and case studies of the southeastern U.S. New York: Springer-Verlag, 1989.

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25

Hempleman, Christine. Henderson Inlet Watershed fecal coliform bacteria, dissolved oxygen, temperature, and pH total maximum daily load: Water quality improvement report implementation strategy, vol. II. Olympia, WA: Washington State Dept. of Ecology, 2006.

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26

Rupert, Michael. Relations among rainstorm runoff, streamflow, pH, and metal concentrations, Summitville Mine area, upper Alamosa River basin, southwest Colorado, 1995-97. Denver, Colo: U.S. Dept. of the Interior, U.S. Geological Survey, 2001.

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27

Baldwin, Karin. Walla Walla Watershed PCBs, chlorinated pesticides, fecal coliform, temperature, pH, & dissolved oxygen total maximum daily load: Water quality implementation plan. Olympia, Wash.]: Washington State Dept. of Ecology, 2008.

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28

Mechanisms by which bacterial cells respond to pH. [S.l.]: John Wiley & Sons, 1999.

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29

Nguy*ên, Thanh Bình. Đ*inh hư*ơng quy ho*ach phát tri*ên và các d*ư án kêu g*oi vi*ên tr*ơ và đ*âu tư nư*ơc ngoài vào xây d*ưng cơ s*ơ h*a t*âng và b*ao v*ê môi sinh thành ph*ô Hà N*ôi =: Planning orientation and investment projects for development of infrastructure systems and environment enhancement of Hanoi City. Hà N*ôi: Giao thông v*ân t*ai, 1994.

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30

NEBEL. ABC News/Ph Video Library, Volume II. 5th ed. Prentice-Hall, 1998.

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31

A, Lorenz R., Weber C. F, U.S. Nuclear Regulatory Commission. Division of Safety Issue Resolution., and Oak Ridge National Laboratory, eds. Iodine evolution and pH control. Washington, DC: Division of Safety Issue Resolution, Office of Nuclear Regulatory Research, U.S. Nuclear Regulatory Commission, 1992.

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32

Beed, Martin, Richard Sherman, and Ravi Mahajan. Metabolic, endocrine, and environmental injury. Oxford University Press, 2013. http://dx.doi.org/10.1093/med/9780199696277.003.0006.

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Metabolic acidosisHypernatraemiaHyponatraemiaHyperkalaemiaHypokalaemiaHypercalcaemiaHypocalcaemiaHyperphosphataemiaHypophosphataemiaHypermagnesaemiaHypomagnesaemiaDiabetic ketoacidosisHyperosmolar hyperglycaemic stateHypoglycaemiaAddison’s diseaseThyroid stormPhaeochromocytoma and carcinoid syndromeMalignant hyperpyrexia and neurolept malignant syndromeHyperthermia and heat injuryHypothermiaMetabolic acidosis is defined as pH <7.36 associated with low bicarbonate (<23 mmol/L). PaCO...
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33

C, Beahm E., U.S. Nuclear Regulatory Commission. Division of Reactor Program Management., and Oak Ridge National Laboratory, eds. Iodine volatility and pH control in the AP-600 reactor. Washington, DC: Division of Reactor Project Management, Office of Nuclear Reactor Regulation, U.S. Nuclear Regulatory Commission, 1998.

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34

Gerritsen, Robert J. Effects of acid precipitation on stream pH, Sawmill Creek, Mississauga. 1988, 1988.

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35

Meinrath, Günther, and Petra Schneider. Quality Assurance for Chemistry and Environmental Science: Metrology from pH Measurement to Nuclear Waste Disposal. Springer, 2007.

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36

Meinrath, Günther, and Petra Schneider. Quality Assurance for Chemistry and Environmental Science: Metrology from PH Measurement to Nuclear Waste Disposal. Springer London, Limited, 2007.

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37

Meinrath, Günther, and Petra Schneider. Quality Assurance for Chemistry and Environmental Science: Metrology from pH Measurement to Nuclear Waste Disposal. Springer, 2014.

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38

Allen, H. Lee, Philip Schoeneberger, Drew McAvoy, Dan Binkley, and Charles T. Driscoll. Acidic Deposition and Forest Soils: Context and Case Studies of the Southeastern United States. Springer London, Limited, 2012.

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39

Hazelton, Pam, and Brian Murphy. Interpreting Soil Test Results. CSIRO Publishing, 2016. http://dx.doi.org/10.1071/9781486303977.

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Interpreting Soil Test Results is a practical reference enabling soil scientists, environmental scientists, environmental engineers, land holders and others involved in land management to better understand a range of soil test methods and interpret the results of these tests. It also contains a comprehensive description of the soil properties relevant to many environmental and natural land resource issues and investigations. This new edition has an additional chapter on soil organic carbon store estimation and an extension of the chapter on soil contamination. It also includes sampling guidelines for landscape design and a section on trace elements. The book updates and expands sections covering acid sulfate soil, procedures for sampling soils, levels of nutrients present in farm products, soil sodicity, salinity and rainfall erosivity. It includes updated interpretations for phosphorus in soils, soil pH and the cation exchange capacity of soils. Interpreting Soil Test Results is ideal reading for students of soil science and environmental science and environmental engineering; professional soil scientists, environmental scientists, engineers and consultants; and local government agencies and as a reference by solicitors and barristers for land and environment cases.
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40

D, Boehnke. Environment Chem Lab Exprimts&ph Molec Pkg. Addison Wesley Longman, 2002.

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41

Gardew, Gail, Gail Cardew, and Derek Chadwick. Bacterial Responses to PH. Wiley & Sons, Incorporated, John, 2008.

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42

Schweitzer, George K., and Lester L. Pesterfield. The Aqueous Chemistry of the Elements. Oxford University Press, 2010. http://dx.doi.org/10.1093/oso/9780195393354.001.0001.

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Most fields of science, applied science, engineering, and technology deal with solutions in water. This volume is a comprehensive treatment of the aqueous solution chemistry of all the elements. The information on each element is centered around an E-pH diagram which is a novel aid to understanding. The contents are especially pertinent to agriculture, analytical chemistry, biochemistry, biology, biomedical science and engineering, chemical engineering, geochemistry, inorganic chemistry, environmental science and engineering, food science, materials science, mining engineering, metallurgy, nuclear science and engineering, nutrition, plant science, safety, and toxicology.
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43

Brönmark, Christer, and Lars-Anders Hansson. The Biology of Lakes and Ponds. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780198713593.001.0001.

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The Biology of Lakes and Ponds focuses on the interactions between the abiotic frame, such as turbulence, temperature, pH and nutrients, and the organisms, including interactions with and among organisms at the individual, population and community level. The book fills this niche between traditional limnology and evolutionary ecology by focusing on physiological, morphological and behavioural adaptations among organisms to abiotic and biotic factors and how interactions between biotic processes and abiotic constraints determine the structure and dynamics of lake and pond systems. In addition, the book describes and analyses the causes and consequences of human activities on freshwater organisms and ecosystems and covers longstanding environmental threats, such as eutrophication and acidification, as well as novel threats, such as biodiversity loss, use of everyday chemicals and global climate change. However, also signs of improvement and the possibilities to restore degraded ecosystems are discussed and provide hope for future generations.
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44

Dalbeth, Nicola. Epidemiology. Oxford University Press, 2016. http://dx.doi.org/10.1093/med/9780198748311.003.0003.

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The aetiopathogenesis of gout is initiated by urate overproduction and uric acid under-excretion, leading to hyperuricaemia. Foods such as seafood, red meat, beer, and sugar-sweetened beverages contribute to overproduction. Under-excretion is mediated by renal and gut uric acid transporters such as SLC2A9, ABCG2, and URAT1. In hyperurcaemia, there is formation of monosodium urate (MSU) crystals in joints, with acute gouty arthritis mediated by the innate immune system occurring in response to these crystals. Factors such as urate concentration, proteins present in synovial fluid, temperature, and pH control crystal nucleation and growth. Activation of the inflammasome by MSU crystals and production of interleukin-1ß‎ is central to acute gouty arthritis. Advanced gout occurs when there is persistent gouty arthritis and tophus with the tophus being an organized immune tissue response to MSU crystals that involves both innate and adaptive immune cells. Progression through the gout checkpoints (hyperuricaemia, MSU crystal formation, and immune response) is governed by inherited genetic variants, lifetime environmental exposures, and their interaction.
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45

Kirchman, David L. The physical-chemical environment of microbes. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198789406.003.0003.

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Many physical-chemical properties affecting microbes are familiar to ecologists examining large organisms in our visible world. This chapter starts by reviewing the basics of these properties, such as the importance of water for microbes in soils and temperature in all environments. Another important property, pH, has direct effects on organisms and indirect effects via how hydrogen ions determine the chemical form of key molecules and compounds in nature. Oxygen content is also critical, as it is essential to the survival of all but a few eukaryotes. Light is used as an energy source by phototrophs, but it can have deleterious effects on microbes. In addition to these familiar factors, the small size of microbes sets limits on their physical world. Microbes are said to live in a “low Reynolds number environment”. When the Reynolds number is smaller than about one, viscous forces dominate over inertial forces. For a macroscopic organism like us, moving in a low Reynolds number environment would seem like swimming in molasses. Microbes in both aquatic and terrestrial habitats live in a low Reynolds number world, one of many similarities between the two environments at the microbial scale. Most notably, even soil microbes live in an aqueous world, albeit a thin film of water on soil particles. But the soil environment is much more heterogeneous than water, with profound consequences for biogeochemical processes and interactions among microbes. The chapter ends with a discussion of how the physical-chemical environment of microbes in biofilms is quite different from that of free-living organisms.
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46

Kreider, Kenneth G. Assessment of uncertainties in measurement of pH in hostile environments characteristic of nuclear repositories. Supt. of Docs., U.S. G.P.O. [distributor], 1991.

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47

Rengel, Zdenko. Handbook of Plant Growth pH as the Master Variable (Books in Soils, Plant and the Environment). CRC, 2002.

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48

Rayment, George E., and David J. Lyons. Soil Chemical Methods - Australasia. CSIRO Publishing, 2010. http://dx.doi.org/10.1071/9780643101364.

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Soil Chemical Methods – Australasia describes over 200 laboratory and field chemical tests relevant to Australasia and beyond. The information and methodology provided across 20 chapters is comprehensive, systematic, uniquely coded, up-to-date and designed to promote chemical measurement quality. There is guidance on the choice and application of analytical methods from soil sampling through to the reporting of results. In many cases, optional analytical ‘finishes’ are provided, such as flow-injection analysis, electro-chemistry, multiple flame technologies, and alternatives to chemical testing offered by near-range and mid-range infrared diffuse reflectance spectroscopy. The book supersedes and updates the soil chemical testing section of the 1992 Australian Laboratory Handbook of Soil and Water Chemical Methods of Rayment and Higginson, while retaining method codes and other strengths of that Handbook. Chapters cover soil sampling, sample preparation and moisture content; electrical conductivity and redox potential; soil pH; chloride; carbon; nitrogen; phosphorus; sulphur; gypsum; micronutrients; extractable iron, aluminium and silicon; saturation extracts; ion-exchange properties; lime requirements; total miscellaneous elements; miscellaneous extractable elements; alkaline earth carbonates and acid sulfate soils. In addition, there are informative Appendices, including information on the accuracy and precision of selected methods. This book targets practising analysts, laboratory managers, students, academics, researchers, consultants and advisors involved in the analysis, use and management of soils for fertility assessments, land use surveys, environmental studies and for natural resource management.
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49

Pereira, Égina Glauce Santos. A argumentação nas Audiências Públicas do Supremo Tribunal Federal a questão de valores: Relação entre doxa e endoxa. Brazil Publishing, 2020. http://dx.doi.org/10.31012/978-65-5861-103-5.

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The present time enables a broad production on rhetoric, once we coexist with growing pluralist issues as well as a higher demand for more elaborated argumentative constructions to support standpoints. Among Legal Studies it is not that different, especially because of the methodological changes which involve applying and understanding the norm, which cooperates to build a broader argumentative environment, becoming necessary to insert value as an element of application, besides the fact and the norm. Along the thesis, we intend to focus, first, on the role of doxa concerning the legislation which is produced on the pronouncements of the individuals involved in the PH, built by authority discourses which are based in a doxa related to the STF itself. A second role would be to allow an interconnection among legal, political and social discourses. In the discursive production at the PH, at the STF, endoxas (medical discourse, biomedical, biological, religious, besides the legal discourse, which used to be the only one) are used to reach society (representative of doxa), aimed at reaching society in general through a wide dissemination of the utterances by the media. This explains why the decisions made by the STF need to be based and legitimated by society. For those decisions to be legitimate, they have to include the participation or the understanding of society, democracy requirement.
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50

Kirchman, David L. Community structure of microbes in natural environments. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198789406.003.0004.

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Community structure refers to the taxonomic types of microbes and their relative abundance in an environment. This chapter focuses on bacteria with a few words about fungi; protists and viruses are discussed in Chapters 9 and 10. Traditional methods for identifying microbes rely on biochemical testing of phenotype observable in the laboratory. Even for cultivated microbes and larger organisms, the traditional, phenotype approach has been replaced by comparing sequences of specific genes, those for 16S rRNA (archaea and bacteria) or 18S rRNA (microbial eukaryotes). Cultivation-independent approaches based on 16S rRNA gene sequencing have revealed that natural microbial communities have a few abundant types and many rare ones. These organisms differ substantially from those that can be grown in the laboratory using cultivation-dependent approaches. The abundant types of microbes found in soils, freshwater lakes, and oceans all differ. Once thought to be confined to extreme habitats, Archaea are now known to occur everywhere, but are particularly abundant in the deep ocean, where they make up as much as 50% of the total microbial abundance. Dispersal of bacteria and other small microbes is thought to be easy, leading to the Bass Becking hypothesis that “everything is everywhere, but the environment selects.” Among several factors known to affect community structure, salinity and temperature are very important, as is pH especially in soils. In addition to bottom-up factors, both top-down factors, grazing and viral lysis, also shape community structure. According to the Kill the Winner hypothesis, viruses select for fast-growing types, allowing slower growing defensive specialists to survive. Cultivation-independent approaches indicate that fungi are more diverse than previously appreciated, but they are less diverse than bacteria, especially in aquatic habitats. The community structure of fungi is affected by many of the same factors shaping bacterial community structure, but the dispersal of fungi is more limited than that of bacteria. The chapter ends with a discussion about the relationship between community structure and biogeochemical processes. The value of community structure information varies with the process and the degree of metabolic redundancy among the community members for the process.
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