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mi.ttu.ee Possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat Ingo Valgma, Department of Mining, Tallinn University of Technology, Estonia M. Orru 1,2 , H. Milvek 1,2 , A. Anepaio 1 , S. Vendla 1 and I. Valgma 1 1 Tallinn University of Technology, Department of Mining, Estonia 2 Geological Survey of Estonia
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Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

Jan 21, 2015

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Page 1: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Possibilities for mitigating negative effects of noise and dust caused by extraction of

sand, gravel and peat

Ingo Valgma, Department of Mining, Tallinn University of Technology, Estonia

M. Orru1,2, H. Milvek1,2, A. Anepaio1, S. Vendla1

and I. Valgma1

1Tallinn University of Technology, Department of Mining, Estonia2Geological Survey of Estonia

Page 2: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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For

mining permit, an environmental impact assessment

(EIA)

is needed, including

assessment of noise and dust. •

Gravel

Sand•

Peat

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Peat, 700 kt/y

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Study area

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Peat dust

Peat production (milling and collection)Peat dust measurementsFine particle PM10 measurements were carried out following the Ambient Air Protection Act (RT I, 31.12.2010, 31)Fine particles

PM10 were

measured using the

Dust Trak II HC dust analyzer,

60 min

sycles

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Peat field, collectors

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Measuring dust

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Peat dust

Measurements of peat dust (fine particles less than 10 micrometer, PM10) diffusing in the ambient during an operating period of 30 minutes gave results between 0.002 and 0.448 mg/m³.

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Peat dust

Diffusion of dust is proportional to the distance from the source and the spreading distance itself is in exponential dependence. Therefore, critical quantities of dust spread only close to the source.

Based on the acquired knowledge, it is certain that the amount of peat dust will not cause a health hazard to the surrounding population.

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Page 11: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Peat production noise

Noise caused by the peat transport from peat production areas was measured during summer.

Production area had the average noise level of 40 dB.

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Page 12: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Peat field

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Page 13: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Noise measurements for pits

Noise levels were measured following the noise measurement method (RTL 2002, 38, 511) and each point was measured with TES 1254.

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Noise

Modelling with the CadnaA 4.1 software. •

Noise of the machinery

Impact of forest•

Transportation

noise

Size and location of spoils

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Noise model for pits

One excavator (80 dB), one mobile crusher (90 dB) and a dump truck (70 dB) were placed in every pit in the model.

Model shows

that the noise from the pit decreases

below 40 dB before reaching

inhabited areas•

The model indicates that pit noise will be marginal. The main sources of noise are the highway and other surrounding roads.

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Dust modelling for pits

Dust modelling was done with the CadnaA 4.1 software

fieldwork results, impact of forest, wind direction and speed, location of spoils

Excavator,

mobile crusher and truck•

Results show that already 300 meters away the dust level will be reduced below the upper limit of allowed levels

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Cumulative dust model

Dust from the Tatramäe II, Kruusa and Audevälja gravel pits spreads up to 300 meters away. As the Tatramäe II gravel pit is located 300 m away from the Kruusa and Audevälja pits, it is considered as separate dust source

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The Estonian Minister of Social Affairs sets the noise levels tolerable for life (4 March

2002, Regulation No. 42 "Standard Noise Levels for Residential and Recreational Areas, Residential and Public Buildings, and Noise Measurement Techniques").

This regulation permits noise level below 40 dB during the day and below 30 dB at night.

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Page 29: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Gravel pit noise + rally

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Cumlative noise leval

Measurements and modelling results indicate that when gravel pits are simultaneously operating, the noise level increases by 10 dB

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MITIGATING METHODS

Peat dust•

Preserving the surrounding forest (preferably to the width of at least 50 meters).

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Peat transportation machinery must ensure that the load is well enough closed to minimise the impact of dust to the environment.

Also, for the protection of employees’

health, peat mining machinery cabins have to be inaccessible

for

dust.

Pit roads should be moistened regularly and the maximum speed of transporting vehicles limited to 30km/h.

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Peat noise

The most important aspect in peat noise minimisation is the preservation of neighbouring forests, which ideally should be at least 50 meters wide.

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The results of this study show that the usual average noise level in peat fields is 58 dB.

If residential houses are at some distance from the production area and separated by a protective forest the noise level there will be low (35–40 dB).

The average content of fine peat dust (<10 μm, PM10) is usually 0.002–0.448 mg/m³

per

30 minutes during operation.35

Page 36: Valgma possibilities for mitigating negative effects of noise and dust caused by extraction of sand, gravel and peat(2)

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Measurements in sand and gravel pits show that the average content of fine dust (<10 μm, PM10) in ambient air is 0.011 mg/m³

per 60

minutes during operation. Permitted daily average limit is 0.5–2 mg/m3

for working

environment and 0.05 mg/m³

for living environment.

An important measure is preserving the surrounding forest (50 m).

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Thank You

[email protected]

mi.ttu.ee/mining

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