The Application of Green Seismic Survey Technology in Forested Areas and Its Ecological and Economic Effectiveness: Methodology and Practice of Application
Abstract
:1. Introduction
- An enhanced algorithm for performing an environmental and economic assessment of the use of resource-saving technologies for oil and natural gas exploration in forested areas is proposed. This comes after a critical analysis of the current methodological approaches and criteria for judging the effectiveness of exploration for hydrocarbons.
- A conceptual description of the green seismic technology, used to conduct prospecting work on hydrocarbons in forested areas is presented.
- The realization of hydrocarbon exploration projects in environmentally sensitive locations was the subject of an issue analysis. The findings of this analysis were used to identify and categorize the technical, financial, and environmental issues that prevent these projects in forested areas from becoming more efficient.
- Technical and economic calculations were carried out to justify the feasibility of using green seismic technology in comparison with traditional methods of geological exploration for hydrocarbon raw materials in regions with forested areas.
2. Materials and Methods
3. Results and Discussion
- -
- minimizing the negative effects of technology on the environment by cutting down on the amount of forest destruction on seismic profiles and by not using heavy machinery, which lessens the strain on the soil cover;
- -
- enhancing productivity in the areas of industrial safety and labor protection by executing safe drilling, lowering the number of field crew mobilizations, and reducing injuries during seismic surveys;
- -
- enhancing the quality of primary geophysical data by means of seismic investigation in densely forested areas that were previously unreachable.
4. Conclusions
- -
- obtain environmental insurance, which provides coverage for the risks of harm to the environment, life, health, and property of third parties in the process of work;
- -
- carry out corporate examination of geological exploration projects to improve the quality of documentation in terms of making timely environmental decisions aimed at reducing environmental risks.
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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Item No. | Name of the Indicator, [Units of Measure] | Value of the Indicator | |
---|---|---|---|
1. Ecological and Economic Indicators for Carrying Out Work on the Site | |||
Traditional Areal Seismic Survey | Green Seismic Survey | ||
1.1 | Area of work along the contour of excitation points, [km2] | 304 | |
1.2 | Area of work along the contour of reception points, [km2] | 516 | |
1.3 | Length of seismic profiles (forest clearings), [km] | 2180 | |
1.4 | Length of crossline profiles, [km] | 350 | 255 |
1.5 | Length of inline profiles, [km] | 350 | 255 |
1.6 | Profile width, [m] | 4 | 1.5 |
1.7 | Rent of forest land, [RUB/ha] | 8813 | |
1.8 | Area of forest land, [ha] | 1761 | 1286 |
1.9 | Volume of cut wood, [m3] | 172,800 | 126,203 |
1.10 | Cost of wood, [RUB for 1 m3] | 109 | |
1.11 | Average forest density, [pcs/ha] | 2000 | |
1.12 | Degree of forest cover of the territory, [%] | 80 | |
1.13 | Area of land subject to reforestation work, [ha] | 1023 | 747 |
1.14 | Cost of reforestation work, [RUB/ha] | 470,000 | |
2. Characteristics of the Raw Hydrocarbon Potential of the Licensed Subsoil Area | |||
2.1 | Volume of predicted resources, [thousand tons] | 720 | |
2.2 | Number of prospect wells, [units] | 1 | |
2.3 | Prospect well depth, [m] | 2750 |
Item No. | Name of the Indicator, [Units of Measure] | Equation | Characteristics of Indicators |
---|---|---|---|
1. Ecological Efficiency Indicators | |||
1.1 | Volume of wood [m3] | V1 = V0 − Vrs (1), where V1 is the change in wood volumes; V0 is the volume of wood cut down when using traditional geological exploration technology; Vrs is the volume of wood cut down when using resource-saving technology. | The indicator characterizes the change in wood volumes that can be achieved because of the use of resource-saving technology for geological exploration in forested areas. |
1.2 | Area of forest land within the licensed area [ha] | R1 = R0 − Rrs (2), where R1 is the change in the area of leased forest lands; R0—area of leased forest land using traditional technology; Rrs is the area of leased forest land using resource-saving technology | The indicator characterizes the amount of change in leased forests that can be achieved because of the use of resource-saving technology during geological exploration. |
1.3 | Scope of reforestation work [ha] | F1 = F0 − Frs (3), where F1 is the change in area for reforestation; F0—volume of reforestation work using traditional technology; Frs—volume of reforestation work using resource-saving technology. | The indicator characterizes the magnitude of the change in the necessary reforestation work [33] after geological exploration using resource-saving technology. |
1.4 | Number of trees [trees] saved | N = D × S × (R0 − Rrs) (4), where N is the number of preserved trees in the study area; D—average forest density (density of forest plantations) (trees/Ha), determined depending on avg. distances between trees, height and completeness of the forest stand, etc.; S—degree of forest cover of the territory, (%) is determined by the ratio of the forested area of land to the total area of the licensed area. | The indicator characterizes the number of trees saved from felling due to a decrease in forest lands during geological exploration using resource-saving technology. |
2. Economic efficiency indicators | |||
2.1 | Savings from deforestation [RUB] | EV = (R0 − Rrs) × C (5), where C is the cost of cutting down 1 hectare of forest. | The indicator characterizes the amount of money that a company will save when cutting down forests and carrying out geological exploration work. |
2.2 | Savings on forest land rental [RUB] | ER = (R0 − Rrs) × P (6), where P is the price for renting forest land depending on the region of work and is determined in accordance with [34]. | The indicator characterizes the amount of money that the company will save when renting land for geological exploration. |
2.3 | Savings on wood fees monetary units [RUB] | Ew = (V0 − Vrs) × W (7), where W is the cost of wood (RUB per 1 m3) and depends on the type of forest plantation and the distance of its removal, determined in accordance with [34]. | The indicator characterizes the amount of money that the company will save when determining the payment for felled trees to ensure geological exploration. |
2.4 | Savings on reforestation work [RUB] | EF = (F0 − Frs) × R (8), where R is the cost of reforestation work (RUB per 1 hectare) and is determined in accordance with the contract depending on the conditions of the area, its geographical location and type of work. | The indicator characterizes the amount of money that the company will save when assessing the implementation of reforestation work. |
2.5 | Integral economic effect [RUB] | E = EV + ER + Ew + EF (9) | This indicator shows how much money is saved by using resource-saving technology for geological investigation while still maintaining the natural environment. |
Item | Appraisal | Value | ∆ | Savings [Thousand RUB] |
---|---|---|---|---|
Deforestation [ha] | Post facto | 1761 | 475 | 47,500 |
Greenfield | 1286 | |||
Volume of wood [m3] | Post facto | 172,800 | 46,597 | 5079 |
Greenfield | 126,203 | |||
Area of forest land within LA [ha] | Post facto | 1761 | 475 | 4174 |
Greenfield | 1286 | |||
Scope of reforestation work [ha] | Post facto | 1023 | 276 | 131,362 |
Greenfield | 747 | |||
Total savings | 188,115 |
Item No. | Name of the Indicator | Traditional Technology | Resource-Saving Technology | Variation | |
---|---|---|---|---|---|
+/− | % | ||||
1 | Net Present Value [million RUB] | 320.5 | 327.2 | 6.7 | 1.02 |
2 | Internal rate of return [%] | 18.7 | 18.9 | 0.2 | 1.01 |
3 | Net Present Value of Returns | 1.46 | 1.50 | 0.04 | 2.74 |
4 | Payback period [years] | 4.4 | 4.1 | −0.3 | −6.8 |
5 | Expenditure on oil and gas exploration [million RUB] | 592 | 403.9 | −188.1 | −31.8 |
Sphere of Display | Risks | |
---|---|---|
Traditional Technology | Resource Saving Technology | |
1. Geological risks | 1.1 Reduced success rate of exploratory drilling | |
1.2 Unconfirmability of the value of hydrocarbon potential reserves | ||
1.3 Geological features of the license area (complex geological structures, obstacles to drilling) | ||
1.4 Erroneous interpretation of geological data obtained during research | ||
2. Ecological risks | 2.1 Negative impact on the natural environment (deforestation) | |
2.2 Forest fires [38] | ||
2.3 Increased load on the soil due to the operation of heavy equipment | - | |
2.4 Increased CO2 emissions | - | |
2.5 Impact on surface and groundwater | - | |
3. Production risks | 3.1 Injury to personnel during topographic and geodetic work, incl. felling | |
3.2 Personnel health (working in low temperatures) | ||
4. Technological risks | 4.1 Unreliability of technology during geological exploration due to equipment failure | |
4.2 Technical risks associated with the operation of transport and technical equipment in impassable taiga, under difficult weather conditions | ||
5. Economic risks | 5.1 Reducing the volume of seismic exploration while reducing the cost of hydrocarbons on the market | |
5 2 Delays in work completion, equipment downtime | ||
5.3 High volumes of investment in equipment production |
Probability of a Risk Event (y) | The Degree of Influence of the Risk Event on the Project (x) | ||
---|---|---|---|
Weak (0–0.4) | Medium (0.4–0.8) | Strong (>0.8) | |
High (>0.8) | Medium | High | Critical |
Medium (0.4–0.8) | Medium | High | High |
Low (0–0.4) | Low | Medium | Medium |
Risks | Traditional Technology | Resource-Saving Technology | ||||
---|---|---|---|---|---|---|
Potential Damage Consequences from the Risk (x) | Probability of Risk Occurrence (y) | Potential Damage Consequences from the Risk (x) | Probability of Risk Occurrence (y) | |||
Ecology | E1 | Negative impact on the natural environment (deforestation) | 0.75 | 0.97 | 0.73 | 0.25 |
E2 | Forest fires | 0.42 | 0.75 | 0.40 | 0.75 | |
E3 | Increased load on the soil due to the operation of heavy equipment | 0.71 | 0.73 | - | - | |
E4 | Increased CO2 emissions | 0.42 | 0.51 | - | - | |
E5 | Impact on surface and groundwater | 0.63 | 0.67 | - | - | |
Production | P6 | Injury to personnel during topographic and geodetic work, incl. felling | 0.96 | 0.79 | 0.93 | 0.20 |
P7 | Personnel health (working in low temperatures) | 0.63 | 0.57 | 0.60 | 0.57 | |
Technology | T8 | Unreliability of technology during geological exploration due to equipment failure | 0.88 | 0.10 | 0.80 | 0.31 |
T9 | Technical risks associated with the operation of transport and technical equipment in impassable taiga, under difficult weather conditions | 0.63 | 0.78 | 0.53 | 0.24 |
Ecology | ||||
---|---|---|---|---|
x1 | x2 | x3 | x4 | |
Region/ Indicator | Environmental Rating (Qualitative Indicator) | Ratio of the Area of Reforestation and Afforestation to the Area of Cut Down and Dead Forest Plantations [%] | Emissions of Pollutants into the Atmospheric Air from Stationary Sources [Thousands of Tons] | Expenses for Environmental Protection [Million RUB] |
KHMAO-Yugra | 50.00 | 73.00 | 1,142.00 | 29,896.00 |
Maximum value for Russia | 76.00 | 1,657.80 | 2,540.00 | 55,661.00 |
Minimum value for Russia | 43.00 | 23.60 | 2.00 | 63.00 |
Factor | Value of xi | Normalized Value of xi |
---|---|---|
x1 | 50.00 | 0.212 |
x2 | 73.00 | 0.970 |
x3 | 1142.00 | 0.449 |
x4 | 29,896.00 | 0.463 |
Range of Values, x(y) | Membership Function | |
---|---|---|
0 < = x(y) < = 0.167 | X1, Y1 (Very low) | 1 |
0.167 < x(y) < 0.333 | X1, Y1 | µ1 |
X2, Y2 (Low) | 1 − µ1 = µ2 | |
0.333 < = x(y) < 0.5 | X2, Y2 | µ2 |
X3, Y3 (Average) | 1 − µ2 = µ3 | |
0.5 < = x(y) < 0.667 | X3, Y3 | µ3 |
X4, Y4 (High) | 1 − µ3 = µ4 | |
0.667< x(y) < 0.833 | X4, Y4 | µ4 |
X5, Y5 (Very high) | 1 − µ4 = µ5 | |
0.833< x(y) <= 1 | X5, Y5 | 1 |
Factor | Subset Scale | Significance Level | ||||
---|---|---|---|---|---|---|
Very Low | Low | Average | High | Very High | ||
x1 | 0.72 | 0.28 | 0.1 | |||
x2 | 1 | 0.4 | ||||
x3 | 0.30 | 0.70 | 0.2 | |||
x4 | 0.22 | 0.78 | 0.3 | |||
classificator level | 5 | 4 | 3 | 2 | 1 |
Factor | Subset Scale (Weighted) | ||||
---|---|---|---|---|---|
Very Low | Low | Average | High | Very High | |
x1 | 0.07 | 0.03 | - | - | - |
x2 | - | - | - | - | 0.40 |
x3 | - | 0.06 | 0.14 | - | - |
x4 | - | 0.07 | 0.23 | - | - |
Sum | 0.07 | 0.15 | 0.37 | - | 0.40 |
nodal points | 0.165 | 0.332 | 0.499 | 0.666 | 0.833 |
y | 0.012 | 0.051 | 0.186 | - | 0.333 |
y integral | 0.583 |
Set of y Values | Level of Risk | Description |
---|---|---|
0.000–0.333 | Very low level |
|
0.167–0.500 | Low level |
|
0.333–0.667 | Medium level |
|
0.500–0.833 | High level |
|
0.667–1.000 | Very high level |
|
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Kalinina, O.; Metkin, D.; Bichevaya, O. The Application of Green Seismic Survey Technology in Forested Areas and Its Ecological and Economic Effectiveness: Methodology and Practice of Application. Sustainability 2024, 16, 1476. https://doi.org/10.3390/su16041476
Kalinina O, Metkin D, Bichevaya O. The Application of Green Seismic Survey Technology in Forested Areas and Its Ecological and Economic Effectiveness: Methodology and Practice of Application. Sustainability. 2024; 16(4):1476. https://doi.org/10.3390/su16041476
Chicago/Turabian StyleKalinina, Olga, Dmitry Metkin, and Olga Bichevaya. 2024. "The Application of Green Seismic Survey Technology in Forested Areas and Its Ecological and Economic Effectiveness: Methodology and Practice of Application" Sustainability 16, no. 4: 1476. https://doi.org/10.3390/su16041476
APA StyleKalinina, O., Metkin, D., & Bichevaya, O. (2024). The Application of Green Seismic Survey Technology in Forested Areas and Its Ecological and Economic Effectiveness: Methodology and Practice of Application. Sustainability, 16(4), 1476. https://doi.org/10.3390/su16041476