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Environmental meauserments waste water discharges quality of the soil

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Title: Environmental meauserments waste water discharges quality of the soil


1
Environmental meauserments - waste water
discharges- quality of the soil
Melina Dajic Valjevac, dipl.ing.hem
Vrnjacka Banja, October 2007
2
Environmental meauserments - requirements -
  • To determine quality for the purpose of
    diferent usage agriculture, water suply,
    irigation etc
  • State of the environement before, during
  • and after civil enginering works,
    construction of industry etc.
  • To investigate impacts.
  • To sutisfy regulative - polluter pays
    principle
  • Monitoring
  • Research

3
Meauserment of waste water discharges
  • Define source diffuse or point
  • Distribution of pollution spatial
  • boundaries of the investigation, number
  • of wastewater discharges etc.
  • Pollution load c x v

Concentration of polution surfactants, oil and
grease, phenols, cyanides, PAH, PCB
Water and air volume Soil mass
4
Meauserments of waste water discharges - quantity
-
  • velocities (flow) meter for open flows,
  • Pito tubes
  • Volumetric methods
  • Automatic meauserments

5
Meauserments of waste water discharges- quantity
-
6
Meauserments of waste water discharges - quality
-
  • Physical and chemical
  • Microbiological

7
Meauserments of waste water discharges - quality
-
  • Sampling
  • Taking representative sample
  • Some parameters of quality require special
    bottles (glass, PVC, desinfected for microbiology
    etc.)
  • Analisis at site temperature, pH, conductivity,
    disolved oxygen, turbidity
  • Analisis in the laboratory

8
Analisis of physical and chemical parameters in
water
  • Temperature, Turbidity, color, odor, taste
  • pH value, Conductivity, total solids, suspended
    solids, total dissolved solids, volatile matter,
  • Hardness total, carbonate
  • Heavy metals Ca, Mg, Fe,
  • Free CO2, Chlorides, Ammonia, Nitrate, nitrite,
    phosphorus (total and orthophosphate), sulphate,
    consumption of KMnO4 , COD,
  • Indicators of pollution heavy metals (Pb, Cu,
    Cd, Cr, Hg, Zn, As, Ni), surfactants, oil and
    grease, phenols, fluorides, cyanides, pesticides,
    PAH, PCB, TOC.

9
Methodes for analisis of physical and chemical
parameters in water
  • Instrumental pH-meter, turbidymeter,
    Conductometer, oxymeter, spectrophotometer (UV,
    Atomic absobtion), chromatography (gas, liquid),
    TOC, TON etc.
  • Volumetric (titration) acid-base,
    sedimentation, oxidation - reduction
  • Gravimetric difference in mass

10
Meauserments of waste water discharges - quality
-
  • Physical and chemical
  • Microbiological

11
Analisis of microbiological parameters
  • Total aerobioc mesofilic bacteria in 1 ml
  • Total coliforms in 100 ml
  • Fecal coliformes in 100 ml
  • Fecal Streptococci in 100 ml
  • Proteus in 100 ml
  • Sulphitereducing Clostridia in 100 ml
  • Pseudomonas aeruginosa in 100

12
Determination of the pollution load in waste
water expresed as population equivalent (PE)
  • Population equivalent (in waste-water monitoring
    and treatment) refers to the amount of
    oxygendemanding substances whose oxygen
    consumption during biodegradation equals the
    average oxygen demand of the waste water produced
    by one person. For practical calculations, it is
    assumed that one unit equals 54 grams of BOD per
    24 hours.
  • population equivalent (p.e.) is a measure of
    pollution representing the average organic
    biodegradable load per person per day it is
    defined in Directive 91/271/EEC as the organic
    biodegradable load having a five-day biochemical
    oxygen demand (BOD5) of 60g of oxygen per day.

13
Determination of the pollution load in waste
water expresed as population equivalent (PE)
  • Site works 48 h
  • Meauserment of flow every 15 minutes
  • Sampling every 15 minutes to prepare 2 h
    composite samples
  • Meauserment of temperature every 2 h

14
Determination of the pollution load in waste
water expresed as population equivalent (PE)
  • Laboratory analysis
  • On 2h composite samples
  • Total suspended solids (filtration)
  • Chemical consumption of oxygen (dychromatometric
    method)
  • biochemical oxygen demand (BOD5)
  • Total nitrogen (N-Kjeldahl)
  • Total phosphorus (spectrophotometric)
  • On 24h composite samples
  • Toxicity
  • Specific parameters depend on industry heavy
    metals, oil and grease, surfactants

15
Toxicity
  • Results of the specific parameter analisis are
    not in the acount for the PE, but their impact is
    partialy covered by analyze of toxicity.
  • Test Daphnia magna is standard methode for the
    determination of toxicity for waste water
  • Daphnia magna are small organisms very sensitve
    on the presence of different pollution. Daphnia
    magna grows in the laboratory on certain
    temparature, food and by often cleaning.
  • Generaly test consist of exposure of the certain
    number organisms Daphnia magna in the diferent
    waste water dilutions.
  • Result of the analyse is the dilution of the
    waste water in which 50 exposed organisms die.
    So, the lower result means the higher toksistiy.

16
Calculation of the pollution load in waste water
expresed as population equivalent (PE)
  • PE EsmEom EN EP Etok Rt
  • Esm Tsm/55 - PE by suspended matter
  • EomTom /40 x K - PE by organic matter
  • EN TN /12 - PE by nitrogen
  • EP TP/2 - PE by phosphorus
  • Tsm, Tom TN i TP - pollution load (q x c)
    by suspended
  • and organic matter, total nitrogen and
    phosphorus.
  • K1/1,7 n ? (HPK/BPK5)
  • Etok 1000 / 48hLC50 q - PE by toxicity
  • RT q Tmax 104 / 1,56 TD - PE by
    temperature

17
PE for the thermal power plant in Tuzla
  • Relevant data
  • Two discharge outlets waste water from the slag
    disposal site and from the main colector
  • High pH value - high toxicity
  • High concentrations of the suspended matter

18
PE for the thermal power plant in Tuzla
  • - flow -

19
PE for the thermal power plant in Tuzla
20
PE for the thermal power plant in Tuzla
  • Population equivalent is calculated for each
    discharge outlet separetly, and the final result
    is sum of PEs.
  • PE PE1 PE2 245151 29417 27456
  • Total PE is additionaly corected if the industry
    is not worked by 100 capacity during
    meauserments.
  • Capacity was 63
  • PE 274568 / 0,63 435 822 PE

21
Poluter pays
  • 2,00 KM (around 1 ) for 1 PE
  • industries are clasify in the four group that pay
    for their waste water polution in a different
    ways
  • Big industries according to the determination
    of PE
  • Smaler industries - by comparison with the
    similar bigger industries
  • More smaler industries acording to the indexes
    taking from the rule
  • More smaler industries and population according
    to the quantity of waste water

22
Analysis of the surface water
  • Monitoring
  • To asses impacts on quality

23
Regulation regarding monitoring of surface water
  • The state of Bosnia and Herzegovina is regulated
    by the Dayton Agreement and comprises three
    separate administrative units (two entities and
    one district) Republic of Srpska (RS),
    Federation of Bosnia and Herzegovina (FBIH,
    divided into 10 cantons) and Brcko District.
  • Water stream categorization published in Official
    gazette SR BiH, no 42/67, and enforced as a
    federal act based on the Water Law, article 242,
    paragraph 4, published in Official Gazette
    Federation of BiH, no 18/98
  • The Act on classification of waters and sea of
    Yugoslavia falling within borders of SR BiH
    (Official gazette SR BiH, no 42/67.), that is
    accepted as a federal act on the whole territory
    of Federation BiH
  • Four categories and classes of water

MAC prescribed in FBIH
24
Regulation regarding monitoring of surface water
  • The Act on classification of waters and
    categorization of water streem, u published in
    Official gazette RS, no 42/01, harmonised
    according to EC
  • Water is clasified in five clases

MAC prescribed in FBIH
25
Interpretation of the comparison to the MAC
  • If analysis determine result that is over MAC in
    only one parameter then water is out of
    prescribed class.

26
  • Analyze of soil quality

27
Soil definition
  • Soil is generally defined as the top layer of the
    Earths crust. It is formed by mineral particles,
    organic matter, water, air and living organisms.
  • Food and other agriculture production, essential
    for human survival, and forestry are totally
    dependent on soil. Almost all vegetation
    including grassland, arable crops and trees, need
    soil for the supply of water and nutrients and to
    fix their roots.
  • Soil stores and partly transforms minerals,
    organic matter, water and energy, and diverse
    chemical substances. It functions as a natural
    filter for groundwater, the main source for
    drinking water, and it releases CO2, methane and
    other gases in the atmosphere.
  • Science that deal with quality of soil is
    pedology

28
Negative impacts on land
  • Due to the impact of surface exploitation of
    various resources (coal, iron ore, aluminium,
    clay), so called technogene deserts were
    formed. At this point they cover around 15.000
    20.000 ha.
  • Negative impacts on land, caused by various
    factors, can be grouped into for basic groups
    such as infection, contamination, degradation and
    destruction

29
Negative impact on soil
  • Diffuse soil contamination
  • from combustion of lead-containing petrol in car
    motors, from dust and air emissions from
    metal-processing industries or from use of
    various fuels (coal, fuel oil) for the heating of
    houses.
  • Surplus soil from construction work in central
    urban areas and industrial areas is also often
    contaminated
  • typically seen in old urban areas, areas built on
    landfills from central urban areas, along major
    roads and near metal-processing plants.

30
Contamination of soil
  • Acidifying contaminants (Deposition of airborne
    pollutants releases into soils acidifying
    contaminants (e.g. SO2, NOx) gradually decrease
    the buffering capacity of soils resulting with
  • releasing of aluminium and other toxic metals
    into aquatic systems.
  • favouring the leaching out of nutrients with
    subsequent loss of soil fertility and possible
    eutrophication problems in water and excess of
    nitrates in drinking water.
  • damaging beneficial soil micro-organisms, slowing
    down biological activity.
  • heavy metals (e.g. cadmium, copper) in
    fertilizers and animal feed. Possible uptake of
    cadmium in the food chain.
  • several organic compounds (e.g. dioxins, PCBs,
    PAHs).

31
Contamination of soil
  • Pesticides are toxic compounds deliberately
    released into the environment to fight plant
    pests and diseases. They can accumulate in the
    soil, leach to the groundwater and evaporate into
    the air from which further deposition onto soil
    can take place. They also may affect soil
    biodiversity and enter the food chain.
  • While the use of pesticides is regulated, and
    they should be only applied following Good
    Farming Practice, pesticides have been found to
    leach through the soil into groundwater and to be
    eroded with soil into surface water. Accumulation
    in soil occurs, in particular of those compounds
    now prohibited in the EU.

32
Monitoring of soil
  • Monitoring is a tool for early detection of
    environmental effects on soil and soil processes.
    Monitoring programme can help to reduce or
    mitigate environmental damage. Monitoring can
    also assist in the development of strategies for
    soil protection and environmental management.

33
  • The basic general parameters essential for
    the effective characterization of all sites at
    which soils are to be directly monitored are
  • A sampling design that allows for long-term,
    robust assessment
  • Soil profile description such as soil structure,
    evidence of compaction, status of the soil
    surface, depth the impermeable layers, stoniness
    etc.
  • Soil classification
  • Identification of soil parent material
  • Site characteristics, such as slope, historical
    and current land use and land management recorded
    according to an agreed system

34
  • An agreement is required on sampling depth
  • Soil bulk density
  • Pore size distribution, and stone content and
    stone size
  • Particle size distribution (sand, silt, clay)
  • Soil pH (water, an electrolyte)
  • Soil cation exchange capacity
  • Soil water holding capacity and the water
    retention curve
  • Hydraulic conductivity
  • Depth to groundwater
  • Mineralogy.

35
  • There is a strong case for linking the elements
    of interest to those likely to increase from
    atmospheric deposition, from additions of sewage
    sludge, or from other wastes, and these relate
    strongly to various existing EU directives
  • Arsenic (As), Cadmium (Cd), Chromium (Cr), Copper
    (Cu), Mercury (Hg),
  • Nickel (Ni), Lead (Pb), Zinc (Zn), Uranium
    (U), Phosphorus (P) and nitrogen (N),
  • Organic compounds of potential interest cover a
    very wide spectrum. The organic compounds of
    greatest concern may be the following, but their
    monitoring in the soil is restricted to specific
    sites
  • Halogenated compounds (e. g. HCH, DDT/DDE),
  • Poly-aromatic hydrocarbons,
  • Polychlorinated-biphenyls,
  • Di-benzofurans and di-benzodioxins.

36
Metods for determination of dengerous matters in
solil
  • Concentrationof heavy metals
  • Exstraction in aqua regia total concentration
  • Exstraction in different reagents bioavillable
    concentrations
  • Detection on AAS
  • Polyaromatichydrocarbones exstraction by
    diferent extraction solutions and detection on
    gas or luiqid chromatography or spectrophotometry
  • Sumpor, nitrate and phosphate spectrophotometry
    and gravimetric

37
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