Разделы презентаций


Saint-Petersburg State University University of Stavanger “ Joint

Содержание

Lesson 9 The Ecological Monitoring of Soils Condition

Слайды и текст этой презентации

Слайд 1Saint-Petersburg State University

University of Stavanger

“Joint Norwegian-Russian Master of Science program in

Geoecological monitoring and rational use of natural resources in the Northern oil and gas production regions”
Saint-Petersburg State University        University of Stavanger “Joint Norwegian-Russian Master of

Слайд 2Lesson 9
The Ecological Monitoring of Soils Condition

Lesson 9 The Ecological Monitoring of Soils Condition

Слайд 3Migration and accumulation of chemical substances in the landscape are

largely determined by the properties of depositing landscape components -

soil cover and vegetation.
Migration and accumulation of chemical substances in the landscape are largely determined by the properties of depositing

Слайд 4Soil is the only component of the landscape, which arises

from the interaction of all other landscape components:
the rocks,

air, natural waters, vegetation, microorganisms and animals.

Soil is the only component of the landscape, which arises from the interaction of all other landscape

Слайд 5All the pollutants into the air or water, are deposited

on the surface of the soil and are absorbed by

plants.
All the pollutants into the air or water, are deposited on the surface of the soil and

Слайд 6As the main landscape component, soil can be considered as

an integral indicator of pollution of natural-territorial complexes, giving an

idea of the quality life-supporting components - air and water
As the main landscape component, soil can be considered as an integral indicator of pollution of natural-territorial

Слайд 7On the other hand, contaminated soils themselves are sources of

secondary pollution of air, surface and groundwater.

On the other hand, contaminated soils themselves are sources of secondary pollution of air, surface and groundwater.

Слайд 8The quality of soils/substrates and their toxicity is determined by

the chemical composition of the soil and the content of

pollutants
The quality of soils/substrates and their toxicity is determined by the chemical composition of the soil and

Слайд 9Physical-chemical parameters of soils are included in the list of

the general characteristics of the sanitarian parameter of land.

Soil texture,
Acid-alkaline conditions,
Organic matter content
and other properties of soil

which determine the mobility of chemical elements and the intensity of their involvement in the biological cycle.

Physical-chemical parameters of soils are included in the list of the general characteristics of the sanitarian parameter

Слайд 10
Particle size classifications used by different countries, diameters in

μm

Particle size classifications used by different countries, diameters in μm

Слайд 11Russian classification of mechanical components of soil
(Н. А. Качинский,

1958)

Russian classification of mechanical components of soil (Н. А. Качинский, 1958)

Слайд 12Classification of soils according to texture (Н. А. Качинский, 1958)

Classification of soils according to texture (Н. А. Качинский, 1958)

Слайд 13In the United States, twelve soil texture classifications are defined

by the United States Department of Agriculture USDA:
Clay
Silt
Sand


Loam
Silty clay
Sandy clay
Clay loam
Silt loam
Sandy Loam
Loamy sand
Silty clay loam
Sandy clay loam
Determining the soil textures is often aided with the use of a soil texture triangle.
In the United States, twelve soil texture classifications are defined by the United States Department of Agriculture

Слайд 14The soil pH is a measure of the acidity or

alkalinity in soils. pH is defined as the negative logarithm

(base 10) of the activity of hydronium ions (H+ or, more precisely, H3O+aq) in a solution.


In water, it normally ranges from -1 to 14, with 7 being neutral. A pH below 7 is is acidic and above 7 is alkaline.
The pH value in soils - 2,5 to 12,5.

The soil pH is a measure of the acidity or alkalinity in soils.   pH is

Слайд 15Acidity in soils comes from H+ and Al3+ ions in the

soil solution and sorbed to soil surfaces.

While pH is

the measure of H+ in solution, Al3+ is important in acid soils because between pH 4 and 6, Al3+ reacts with water (H2O) forming AlOH2+, and Al(OH)2+, releasing extra H+ ions. Every Al3+ ion can create[ 3 H+ ions.

Many other processes contribute to the formation of acid soils including rainfall, fertilizer use, plant root activity and the weathering of primary and secondary soil minerals. Acid soils can also be caused by pollutants such as acid rain and mine spoilings.

Acidity in soils comes from H+ and Al3+ ions in the soil solution and sorbed to soil surfaces.

Слайд 16The neutral soil reaction corresponds to a pH of 6.1-7.4.


If the pH is higher than 7.4, then the reaction

of the soil is alkaline, lower - acidic.
In this case, acidic soils are classified as follows:
very strongly acidic - pH is within <4.0,
strong acid - pH 4.1-4.5,
medium acid - pH 4.6-5.0,
slightly acid - pH 5.1- 6.0,
weakly alkaline soils have pH 7.5-8.5,
strongly alkaline soils 8.6-10.0,
sharply alkaline pH> 10.0

The neutral soil reaction corresponds to a pH of 6.1-7.4. If the pH is higher than 7.4,

Слайд 17The United States Department of Agriculture Natural Resources Conservation Service,

formerly Soil Conservation Service classifies soil pH ranges as follows

The United States Department of  Agriculture Natural Resources Conservation Service, formerly Soil Conservation Service classifies soil

Слайд 18Map of soil acidity (T. Hengl)

Map of soil acidity (T. Hengl)

Слайд 19 Soil organic matter
It can be divided into

three general pools:
living biomass of microorganisms,
fresh and partially

decomposed residues,
and humus: the well-decomposed organic material.
Soil organic matterIt can be divided into three general pools: living biomass of microorganisms,

Слайд 20humus (coined 1790–1800; from the Latin humus: earth, ground) refers

to the fraction of soil organic matter that is amorphous

and without the cellular cake structure characteristic of plants, micro-organisms or animals.
Humus significantly influences the bulk density of soil and contributes to moisture and nutrient retention. Soil formation begins with the weathering of humus.

humus (coined 1790–1800; from the Latin humus: earth, ground) refers to the fraction of soil organic matter

Слайд 21Humus has a characteristic black or dark brown color and

is organic due to an accumulation of organic carbon. The

three major horizons are: (A) surface horizon, (B) illuvial horizon (subsoil) and (C) substratum. Some soils have an organic horizon (O) on the surface. Hard bedrock, which is not soil, uses the letter R.
Humus has a characteristic black or dark brown color and is organic due to an accumulation of

Слайд 22Biogenic elements (N, P, K, Ca ctr.),

Macroelements (Si, Na,

Mg ctr.),

Microelements, trace elements (Cu, Zn, Pb, Cd, Ni,

Cr, Hg, As, Sb, Co, Mn, Ba Sr, Mo, V ctr.).
Biogenic elements (N, P, K, Ca ctr.), Macroelements (Si, Na, Mg ctr.), Microelements, trace elements (Cu, Zn,

Слайд 23The six most common elements associated with organic molecules—carbon, nitrogen,

hydrogen, oxygen, phosphorus, and sulfur—take a variety of chemical forms

and may exist for long periods in the atmosphere, on land, in water, or beneath Earth’s surface.
The six most common elements associated with organic molecules—carbon, nitrogen, hydrogen, oxygen, phosphorus, and sulfur—take a variety

Слайд 24 Thus, contamination results in:
Changing the physical and chemical characteristics

of soils: - change in texture, - change

in the total saturation of the base (pH shift, etc.) - accumulation of toxic substances.


Water migration of pollutants and pollution of natural waters.
The absorption of pollutants by living organisms and their involvement in the biological cycle.

Thus, contamination results in: Changing the physical and chemical characteristics of soils:   - change

Слайд 25The methods of soils investigation
Main soil horizons

The methods of soils investigationMain soil horizons

Слайд 26 Soil profiles are studied at monitoring stations.

Description of soil profile includes description of soil horizons

(color, soil texture, moisture, structure, density, composition, neoplasm, inclusions, carbonate reaction with HCl, the transition of the horizon and other features )
Soil profiles are studied at monitoring stations.  Description of soil profile includes description of

Слайд 27The chemical composition of soils is the specific indicator of

anthropogenic environmental pollution of terrestrial ecosystems

The chemical composition of soils is the specific indicator of anthropogenic environmental pollution of terrestrial ecosystems

Слайд 28Taking, storage and transportation of soil samples are carried out

in accordance with applicable standards (ГОСТ 17.1.5.02-80; ГОСТ 17.1.5.05-85; ГОСТ

17.4.3.01-83; ГОСТ 17.4.4.02-84)

Taking, storage and transportation of soil samples are carried out in accordance with applicable standards (ГОСТ 17.1.5.02-80;

Слайд 29ГОСТ 17.4.4.02-84
EQUIPMENT, MATERIALS, REAGENTS
Shovels by ГОСТ 19596—74. Knives for soil

by ГОСТ 23707—79. Knives from polyethylene or polystyrene. Soil drills.
A

refrigerator that maintains the temperature from 4 to 6 ° C. Refrigerators-bags.Laboratory balance for general use by ГОСТ 24104—80 with a maximum load of 200 and 1000 g. Enameled cuvettes. Glass crystallizers. Soil sieve with a mesh of 0.25; 0.5; 1; 3 mm by ГОСТ 3584—73.
Laboratory glass spirits by ГОСТ 10090—74.
Porcelain mortars and pestles by ГОСТ 9147—80.
Mortars and pistils of jasper, agate or fused corundum.
Vials or cans of glass wide-necked with ground glass stoppers with a capacity of 300, 500, 800, 1000 cm3.
Banks or boxes of food polyethylene or polystyrene. Metal spatulas by ГОСТ 19126—79.
Plastic spatulas by ГОСТ 19126—79.
Scoops.
Wrapping paper by ГОСТ 8273—75.
Medical glue.
Tracing paper by ГОСТ 892—70.
Cloth bags.
Packages and film polyethylene.
Parchment by ГОСТ 2995—73.
Tampons cotton-gauze sterile.
Cardboard Boxes.
Acid, hydrochloric acid by ГОСТ 3118—77, pure for analysis, a solution with a mass fraction of 3 and 10%.
Sodium hydroxide by ГОСТ -1328—77.
Rectified ethyl alcohol by ГОСТ 18300—72.
Technical formalin by ГОСТ 1625—75, The highest grade, a solution with a mass fraction of 3%.
Sodium chloride by ГОСТ 4233—77, Isotonic solution with a mass fraction of 0.85%.
ГОСТ 17.4.4.02-84EQUIPMENT, MATERIALS, REAGENTSShovels by ГОСТ 19596—74. Knives for soil by ГОСТ 23707—79. Knives from polyethylene or

Слайд 30The sample is taken from each genetic horizon –
the

material is taken from one place of the horizon, or

one layer of the soil profile, typical of this horizon, or layer.
The sample is taken from each genetic horizon – the material is taken from one place of

Слайд 31Sample from two horizons: Peaty & humic horizon О /А0А1

(Ат) and mineral one В (Вg)

Sample from two horizons: Peaty & humic horizon О /А0А1 (Ат) and mineral one В (Вg)

Слайд 32A sample from each of the two layers О/Ат and

T of organogenic soils

A sample from each of the two layers О/Ат and T of organogenic soils

Слайд 33Sampling of soil is carried out by the envelope or

by diagonal methods in such a way that each sample

represents a part of the soil, typical of the genetic horizons or layers of this soil type.


Number of point samples is determined according to
ГОСТ 17.4.3.01-83

Sampling of soil is carried out by the envelope or by diagonal methods in such a way

Слайд 34Weight of a point sample is not less than 1

kg (0.5 kg). The possibility of secondary contamination of samples is

excluded by stripping of soil profile wall before sampling by a polyethylene or plastic knife.
Weight of a point sample is not less than 1 kg (0.5 kg).   The possibility

Слайд 35
Soil samples for physical-chemical analysis are dried to air-dry state

according to ГОСТ 5180-75 (without direct sunlight!)

Air-dried samples stored

in cloth bags, in cardboard boxes or in glass containers.
Soil samples for physical-chemical analysis are dried to air-dry state according to ГОСТ 5180-75 (without direct sunlight!)

Слайд 36Soil samples taking for analysis of hydrocarbons, are placed in

plastic bags, tightly closed and in this form are transmitted

to the laboratory
Soil samples taking for analysis of hydrocarbons, are placed in plastic bags, tightly closed and in this

Слайд 37The list of contaminants measured in samples of soils

According to Evaluation of the background (initial) state of the

environment of licensed area of oil&gas fields, Yamalo-Nenets Autonomous District
The list of contaminants measured in samples of soils   According to Evaluation of the background

Слайд 38Resolution of the Government YaNAO from 14.02.2013 N 56-P (as

amended on 11.26.2013) "On the territorial system of surveillance of

the environment within the boundaries of the licensed areas subsoil for the purpose of oil and gas fields in the Yamal-Nenets Autonomous Okrug"

pH values ,
concentration of NO3 ̃, PO4 ̃̃̃, SO4 ̄̃, Cl¯
HC ,
benzo(a)pyrene,  
 anionic surfactant synthetic
Total Fe, Pb, Zn, Mn, Ni, Cr VI, Cd
phenols

Resolution of the Government YaNAO from 14.02.2013 N 56-P (as amended on 11.26.2013)

Слайд 39The list of laboratory analyses of soils
* - Cu, Zn,

Ni, Co, Pb, Cd, V, Mn, Ba, Cr, Hg

The list of laboratory analyses of soils* - Cu, Zn, Ni, Co, Pb, Cd, V, Mn, Ba,

Слайд 40The regional geochemical background of soil
The rule of calculation of

the regional geochemical background

х + ,
where х – average arithmetic,  – standard deviation

Anomaly concentration х + 2
High anomaly concentration х + 3
The regional geochemical background of soilThe rule of calculation of the regional geochemical background

Слайд 41Content of chemical elements in soils of Zapadno-Jarojachinskoe petroleum field,

mg/kg

Content of chemical elements in soils of Zapadno-Jarojachinskoe petroleum field, mg/kg

Слайд 42Distribution of HC in soils of Zapadno-Jarojachinskoe petroleum field, mg/kg

Distribution of HC in soils of Zapadno-Jarojachinskoe petroleum field, mg/kg

Слайд 43

Percent Distribution of PAH
in soils of Zapadno-Jarojachinskoe

petroleum field

Percent Distribution of PAH in soils of Zapadno-Jarojachinskoe petroleum field

Слайд 44Total Coefficient of Soil Pollution

where: Сi опр – value is determined by the content

of i-toxicant in the soil ;
Сi рф – value of regionally-background content in the soil of i-toxicant .
Total Coefficient of Soil Pollution		     	 where: Сi опр – value is determined

Слайд 45The indexes of total pollution of landscape components are calculated.

The estimation of environmental pollution degree is made.

The indexes of total pollution of landscape components are calculated. The estimation of environmental pollution degree is

Слайд 46Distribution of Soil Pollution
Index
allowable degree of pollution,

weak level of pollution, the average degree

of pollution
Distribution of Soil Pollution Indexallowable degree of pollution,   weak level of pollution,

Слайд 47Method of the main component of the factorial analysis
It is

revealed 5 factors defining 85 % of all correlation communications.

Hg68 Zn62 Cu53 HC40
V64 Cr59

It is interpreted as anthropogenous factor, caused by pollution as a result of investigation and development oil-gas deposits of a tundra zone.
Method of the main component of the factorial analysisIt is revealed 5 factors defining 85 % of

Слайд 48Parity of natural and anthropogenic factors in the formation of

the chemical compound of oil-gas deposits soils of Urengoj-tundra

Parity of natural and anthropogenic factors in the formation of the chemical compound of oil-gas deposits soils

Обратная связь

Если не удалось найти и скачать доклад-презентацию, Вы можете заказать его на нашем сайте. Мы постараемся найти нужный Вам материал и отправим по электронной почте. Не стесняйтесь обращаться к нам, если у вас возникли вопросы или пожелания:

Email: Нажмите что бы посмотреть 

Что такое TheSlide.ru?

Это сайт презентации, докладов, проектов в PowerPoint. Здесь удобно  хранить и делиться своими презентациями с другими пользователями.


Для правообладателей

Яндекс.Метрика