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CIV 264 - Lecture Introduction to Environmental Engineering Kodwo Beedu Keelson Msc Env Eng

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  • CIV 264 - Lecture

    Introduction to Environmental Engineering

    Kodwo Beedu Keelson Msc Env Eng

  • MODULE CONTENTS

    Microbial Processes

    Reactor Hydraulics

    Water Quality Parameters

  • Microbial Processs

  • CONTENTS

    Role of microorganisms

    Biological conversions in treatment plants

  • Bacteria (most important in wastewater treatment)

    Algae

    Fungi

    Protozoa

    Types of Microorganisms

  • The removal of carbonaceous BOD, nitrogen, phosphorous

    and the stabilization of organic matter are accomplished

    biologically by using a variety of microorganisms, mainly

    bacteria

    The microorganisms convert the colloidal and dissolved

    carbonaceous organic matter into cells, more or less

    degraded organic compounds, various minerals and gases

    The cells in the suspended sludge can be removed from the

    treated liquid by gravity settling, because cells have a

    specific gravity greater than that of water.

    Role of Microorganisms

  • Energy and carbon are both required for the

    maintenance of the cell and for the synthesis of new

    cellular material

    Autotrophic organisms use inorganic carbon as carbon

    source it is called autotrophic.

    Heterotrophic organisms use organic carbon as carbon

    source

    Energy and Carbon Sources for Microorganisms

  • Biological growth

    Hydrolysis

    Decay

    Conversions in Biological Treatment Plants

  • Bacteria are only able to utilize very small and simply

    built molecules directly for growth

    Acetic acid, ethanol, methanol, propionic acid, glucose

    and ammonium, nitrate etc.

    Bigger molecules have to be hydrolyzed first

    Biological Growth

  • Conversion of large molecules into small, directlydegradable molecules

    The hydrolysis process is a slow process compared tothe biological growth process

    Therefore, the hydrolysis will often be the rate-limitingstep in biological wastewater processes

    Hydrolysis can be described as a first order process

    Hydrolysis

  • Slowly biodegradable material is released and then

    hydrolyzed to soluble substrate

    Soluble substrate is used by the viable biomass for

    growth, yielding new cell material

    Decay of biomass is described as a first order process

    with respect to the biomass concentration

    Decay

  • Reactors

  • MODULE CONTENTS

    Reaction Kinetics

    Reactor Vessels

  • Reaction Kinetics

  • Zero Order Reaction Kinetics

    Rate of reaction is independent of proportional to

    the concentration of reactant

    Occurs in reactions in which a catalyst comes into

    plays a part

    dC/dt = K

  • First Order Reaction Kinetics

    Rate of reaction is proportional to the concentration

    dC/dt = -Kc

    k is the first order reaction rate constant (1/T)

    c is the concentration (M/L3)

    Reactions in water and wastewater treatment plants

    are assumed to follow first order reaction kinetics

  • Second Order Reaction Kinetics

    Reactions involving two species A and B

    dCA/dt = -KCACB

    dCB/dt = -KCACB

    k is the second order reaction rate constant (L3/T.M)

  • Reaction Vessels

  • What is a reactor vessel?

    Any natural water body or artificial tank or enclosure

    that receives and discharges water

    Biogeochemical transformations occur in reactors

    such that the effluent has characteristics different

    from the influent

  • Fully mixed tank

    Plug-flow

    Types of Reactor

  • Influent concentration (Cin)

    Effluent concentration (C)

    Residence time (tR)

    Reaction rate constant (k)

    Volumetric loading rate (v)

    Reactor Variables

    Reactor volume (V)

    Flow rate (Q)

    Reactor liquid depth (D)

    Dispersion factor (d)

    Surface loading rate (s)

  • Characteristics of Fully-mixed Tanks

    Influent is mixed instantly and completely

    Uniform concentration in tank = Concentration in outflow

  • Treatment Efficiency in Fully-mixed Tanks

  • Characteristics of Plug-flow Tanks

    Long tank of small cross-section

    There is little or no longitudinal mixing of the influent

    Uniform concentration in tank is different from outflow

  • Treatment Efficiency in Plug-flow Tanks

  • Non-ideal Flow in Reactors

    Short circuiting - density currents, wind-driven currents

    can cause flow to go directly from inlet to outlet, by

    passing much of the tank volume

    Dead zones Short circuiting - density corners, stagnant

    zones, swirling eddies are parts of tank not contributing

    much to treatment, shortening effective detention time

  • Water Quality Parameters

  • MODULE CONTENTS

    Physical Water Quality Parameters

    Chemical Water Quality Parameters

    Biological Water Quality Parameters

  • The term water quality relates to all the constituentsof water including both dissolved substances andany other substances carried by the water.

    Water pollution may be defined as the presence inwater of impurities in such quantities and of suchnature as to impair the use of the water for a statedpurpose.

    The concentration of the pollutant is given by theexpression c = Mass/Volume. usually expressed inmg/L

    What is Water Quality?

  • All receiving waters can assimilate wastes to some extentdepending on the natural selfpurification capacity

    Water quality problems or issues arise when the pollutantloads exceed this capacity

    Water quality parameters makes it possible to assessextent of water pollution and hence water/wastewatertreatment methods

    3 types of water quality parameters physical, chemical,biological

    Significance of water quality parameters

  • Physical Water Quality Parameters

  • Physical parameters define those

    characteristics of water that respond to the

    senses of sight, touch, taste, or smell.

    Parameters that fall into this category include

    suspended solids, colour, taste, odour,

    temperature, turbidity

    Physical Water Quality Parameters

  • Categories of solids

    Type of Solid Size (m) Specific Gravity

    Gross > 6000 0.9 1.2

    Grit > 150 2.6

    Suspended 0.45 1.4 2.0

    Dissolved < 0.45 -

  • Gross sanitary solids also known as aesthetic, refractory orintractable solids include faecal matter, toilet paper, sanitarypads and condoms.

    The particular concern about gross solids these solids istheir aesthetic impact when they are discharged into waterbodies.

    Grit which is also called sewer sediment includes sand,gravel and any other solids that have higher specific gravitythan organic biodegradable solids.

    The problems associated with grit include partial or totalblockage of pipes which leads to a loss of hydraulic capacity.

    Gross solids and Grit

  • The total suspended solids (TSS) content is the organic andinorganic solid matter which is maintained in suspension, andretained when the sample is filtered (0.45 m pore size)

    The retained filter material that can be volatized and burnedoff when ignited at 500C is classified as volatile

    Volatile solids, VS, are presumed to be organic matter andfixed solids, FS, is the inert residue

    The ratio of VS to FS, typically, 70%, is used to characterizewastewater with respect to the amount of organic matterpresent

    Suspended and Dissolved solids

  • The total suspended solids (TSS) is used

    to measure the quality of wastewater

    Total suspended solids

  • Turbidity is a measure of the light-transmittingproperties of water

    Turbidity is used to indicate water quality withrespect to colloidal and residual suspendedmatter

    Turbid water is aesthetically displeasing

    Turbidity measurements are usually made onclean water

    Turbidity

  • Pure water is colourless, but water in nature is often

    coloured by foreign substances.

    Water whose colour is partly due to suspended matter is

    said to have apparent color.

    Colour contributed by dissolved solids that remain after

    removal of suspended matter is known as true colour

    True colour may be measured in potable water analysis

    Colour

  • The terms taste and odour are themselves definitive ofthis parameter.

    Substances that produce an odour in water will almostinvariably impart a taste.

    However, there are many mineral substances thatproduce a taste but no odour.

    Odours produced by organic substances may pose morethan a problem of simple aesthetics, since some of thosesubstances may be carcinogenic.

    The taste and odour parameter is associated with potablewater

    Taste and Odour

  • Temperature is not typically used to evaluate directlyeither potable water or wastewater.

    It is, however, one of the most important parameters innatural surface-water systems.

    The temperature of surface waters governs to a largeextent the biological species present and their rates ofactivity.

    Temperature also has a pronounced effect on solubilityof gases.

    Wastewater is typically warmer than the local watersupply because of warm wash water and industrialcontributions

    Temperature

  • Chemical Water Quality Parameters

  • The chemical parameters refer to those parameters

    associated with the solvent capabilities of water

    Parameters that fall into this category include total

    dissolved solids, alkalinity, hardness, organics and

    nutrients (nitrogen and phosphorus)

    Chemical Water Quality Parameters

  • This refers to the material remaining in water after

    filtration for suspended solids analysis (0.45 m pore

    size)

    Dissolved solids may be organic or inorganic in nature

    Dissolved solids may produce odour, taste and colour in

    water

    TDS is used in analysis of water and wastewater

    Total dissolved solids

  • Alkalinity is defined as the quantity of ions in water that

    will react to neutralise hydrogen ions

    Alkalinity is the measure of the ability of water to

    neutralise acids

    Main constituents of alkalinity include hydroxides (OH-),

    carbonates (CO32-), bicarbonates (HCO3

    -)

    Alkalinity is used in analysis of natural waters to

    determine buffering capacity

    Alkalinity

  • Hardness is defined as the concentration of multivalentmetallic cations in solution

    Hardness is classified as carbonate hardness andnoncarbonated hardness, depending upon the anionswith which it associates

    Carbonate hardness in the hardness that is equivalentto the alkalinity

    Noncarbonated hardness refers to any hardness inexcess of the carbonated hardness

    Analysis for hardness is made on natural waters and onwaters intended for potable supplies and certainindustrial uses

    Hardness

  • Organic compounds in water are unstable and arereadily oxidized either biologically or chemically

    End products include such as carbon dioxide, nitrates,sulphates and water

    Decomposition of organic matter in wastewater bymicro-organisms consumes dissolved oxygen (DO)

    An indirect indication of the amount of organic materialin wastewater can be derived from the BOD,COD, TOCtests

    Organics

  • Biochemical Oxygen Demand (BOD) - indicates the amount

    of oxygen required by aerobic micro-organisms to

    decompose the organic matter in a sample of water in a

    defined time period e.g. 5 days

    Chemical Oxygen Demand (COD) measures the oxygen

    equivalent of organic matter that can be oxidized by a string

    oxidizing agent e.g. potassium dichromate

    Total Organic Carbon (TOC) measures the total organic

    content of a compound

    Tests for Organics

  • Phosphorus is an aquatic plant nutrient

    Phosphorus can contribute to eutrophication and

    reduction of dissolved oxygen

    Phosphorus can be expressed as total, organic or

    inorganic (ortho- and poly-) phosphorus

    Most of the phosphorus occurring in wastewater is in

    the inorganic form

    Phosphorus

  • Nitrogen is also an aquatic plant nutrient that cancontribute to eutrophication and reduction of dissolvedoxygen

    Nitrogen exists in four main forms: organic nitrogen,ammonia nitrogen, nitrite and nitrate

    The term total nitrogen is used to refer to the sum of allthese forms in a sample of wastewater

    Organic and ammonia nitrogen make up most of thetotal nitrogen in wastewater

    Nitrogen

  • Biological Water Quality Parameters

  • This refers to those parameters associated with the absenceor presence of aquatic organisms in a given body of water

    Aquatic organisms range in size and complexity from thesmallest single-cell microorganism to the largest fish

    Based on their known tolerance for a given pollutant, certainorganisms can be used as indicators of the presence ofpollutants

    A body of water hosting large numbers of species with wellbalanced numbers of individuals (species-diversity) isconsidered to be a healthy system

    Pathogens present in aquatic environments are capable ofinfecting, or transmitting diseases to humans

    Biological Water Quality Parameters

  • Bacteria

    Viruses

    Protozoa

    Helminths (worms)

    Types of Pathogens

  • Bacteria are single-celled microorganisms,usually colorless

    Bacteria are the lowest form of life capable ofsynthesizing protoplasm from the surroundingenvironment

    Gastrointestinal disorders are commonsymptoms of most diseases transmitted bywater-borne pathogenic bacteria.

    Bacteria

  • Viruses are the smallest biological structures known tocontain all the genetic information necessary for their ownproduction.

    Viruses are only visible with aid of electronic microscopes

    Viruses are obligate parasites that require a host in whichto live

    Waterborne viral infections usually involve disorders ofthe nervous system rather than of the gastrointestinaltract

    Viruses

  • Protozoa are the lowest form of plant life

    Protozoa are unicellular organisms more complex intheir functional activity than bacteria or viruses

    Protozoa can be free-living or parasitic, pathogenic ornonpathogenic

    Protozoal infections are usually characterized bygastrointestinal disorders of a milder form than thoseassociated with bacterial infections

    Protozoa

  • Helminth is a term used to describe parasitic worms

    The life cycles of helminths, often involve two ormore animal hosts, one of which can be human

    Water contamination may result from human oranimal waste that contains helminths.

    Helminths pose hazards primarily to those personswho come into direct contact with untreated water

    Helminths

  • Analysis of water of all the known pathogens would bevery time-consuming and expensive proposition

    Tests for specific pathogens are usually made onlywhen there is a reason to suspect that those particularorganisms are present

    At other times, the purity of water is checked usingindicator organisms

    An indicator organism is one whose presence presumesthat contamination has occurred and suggests thenature and extent of contaminant(s).

    Pathogen Indicators

  • Faecal coliforms (FC) - is an indicator of watercontamination with faecal matter. The common leadindicator is the bacteria Escherichia coli or E. coli.

    Total coliforms (TC) this encompasses faecalcoliforms as well as common soil microorganisms, andis a broad indicator of possible water contamination.

    Helminth analysis investigates the presence for wormseggs in water.

    Microbiological indicator tests