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HJ 651-2013Technical specification of eco-environmental protection and reclamation for mining(On trial) (English PDF)

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Issued by

Ministry of Ecology and Environment

Level / Type

National · Mandatory

Issue date

January 1, 1970

Implementation date

January 1, 1970

Scope

HJ 651-2013 (Technical specification of eco-environmental protection and reclamation for mining(On trial)) is available as an English-translated PDF.

HJ 651-2013 — This standard specifies the exploration and mining of mineral resources during mining ecological environmental protection requirements, including dump, open-air Stope, tailings, mine roads, mining industrial sites, subsidence area, farm waste rock, mine ecological environment contaminated sites Guiding the technical requirements of conservation and restoration of governance.

This standard applies to coal, metal ores, non-metallic minerals, oil and gas mining, coal bed methane, gravel mining and other land mineral resources exploration, Ecological Environment Protection and Restoration after mining and mine closure process.

Ecological Environment Protection and Restoration of uranium, thorium and other radioactive mineral resources can be developed for implementation.

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Document preview — HJ 651-2013

National Standard of the People's Republic of China

Issued by: Ministry of Ecology and Environment

Contents

  • Foreword
  • 1. Scope .1
  • 2 Normative references .1
  • 3 Terms and definitions
  • 4 General requirements for mine ecological environment protection and recovery Governance
  • 5 Mine ecological protection
  • 6 4 prospector ecological restoration
  • 7 .4 dump ecological restoration
  • 8 Open Pit Ecological Restoration
  • 9 .5 tailings Ecological Restoration
  • 10 Mine ecological restoration 6 dedicated road
  • 11 Mine industrial site ecological restoration
  • 12 Mine air pollution control .6
  • 13 Mine Water Pollution Control
  • 14 7 Subsidence recovery and management
  • 15 Recovery and management of waste rock field
  • 16 7 Treatment of contaminated sites
  • 17 Assessment and Management .8
  • 18 Standards and the supervision of

Foreword

To implement the "People's Republic of China Environmental Protection Law", "People's Republic of China Environmental Impact Assessment Law" and "the State Council Opinions on Strengthening Key Environmental Protection Tasks "to regulate the development of mineral resources in the process of Ecological Environment Protection and Restoration Work to promote mine ecological environment protection, development of this standard.

This standard specifies the mineral resources exploration and mining process, dump, open pit, tailings, mine roads, Technical guidance mine industrial site, subsidence area, waste rock fields, mines and other contaminated sites and mine ecological environment protection and recovery Governance Surgery requirements.

This standard was proposed by the Ministry of Environmental Protection Natural Ecology Protection Department.

This standard is developed by the Ministry of Environmental Protection Science, Technology organization.

This standard is mainly drafted by. Environmental Protection Department of the Nanjing Institute of Environmental Sciences, Ministry of Environmental Protection Standards Institute, Sinosteel Maanshan Institute of Mining Research Co., Ltd. (the State Environmental Protection Mine Solid Waste Treatment and Disposal Engineering Technology Heart) and the Cold and Arid Regions Environmental and Engineering Research Institute.

This standard MEP July 23, 2013 for approval.

This standard since July 23, 2013 implementation.

The standard explanation by the Ministry of Environmental Protection.

Mine Ecological Environment Protection and Restoration Technical Specifications (Trial)

1 Scope

This standard specifies the exploration and mining of mineral resources during mining ecological environmental protection requirements, including dump, open-air Stope, tailings, mine roads, mining industrial sites, subsidence area, farm waste rock, mine ecological environment contaminated sites Guiding the technical requirements of conservation and restoration of governance.

This standard applies to coal, metal ores, non-metallic minerals, oil and gas mining, coal bed methane, gravel mining and other land mineral resources exploration, Ecological Environment Protection and Restoration after mining and mine closure process.

Ecological Environment Protection and Restoration of uranium, thorium and other radioactive mineral resources can be developed for implementation.

2 Normative references

The standard content of the following documents cited in the articles. For undated references, the effective version applies this standard.

GB 3095 Ambient Air Quality Standard GB 3838 Surface Water Quality Standards GB 5084 irrigation water quality standards GB 8978 Integrated Wastewater Discharge Standard GB 9078 industrial furnace air pollutant emission standards GB 11607 Fisheries water quality standards GB/T 14848 groundwater environmental quality standards GB 14500 radioactive waste management GB 16297 Air Pollutant Emission Standards GB 18484 Hazardous Waste Incineration Pollution Control Standard GB 18597 Hazardous Waste Storage Pollution Control Standard GB 18598 Hazardous Waste Landfill Pollution Control Standard GB 18599 general industrial solid waste storage and disposal site pollution control standards GB 20426 coal industry emission standards GB 21522 coalbed methane (CMM) emissions standards (provisional) GB 25465 aluminum industry emission standards GB 25466 Lead, zinc industrial pollutant discharge standards GB 25467 copper, nickel, cobalt, industrial pollutants emission standards GB 25468 magnesium, titanium industrial pollutant discharge standards GB 26451 rare earth industry emission standards GB 28661 iron ore mining industry emission standards GB 50433 technical specification of construction project HJ/T 294 standard clean production of iron ore mining industry HJ/T 358 standard clean production of nickel mineral processing industry HJ 446 Cleaner production standard coal mining industry HJ 607 mineral oil waste recycling pollution control technical specifications HJ 652 mine ecological environment protection and recovery management program (plan) preparation (for Trial Implementation) AQ 2006 tailings safety technology UDC-TD reclamation technical standards (Trial)

3 Terms and Definitions

The following terms and definitions apply to this standard.

3.1 Mine Ecological Environment Protection

It means to take the necessary preventive and protective measures to avoid or mitigate the exploration and mining of mineral resources caused ecological damage and environmental Pollution.

3.2 Ecological environment in mining recovery

It refers to the exploration and mining of mineral resources in the process of all kinds of ecological destruction and environmental pollution take artificial measures to promote and rely on students Ecosystem self-regulation and self-organization, gradual recovery and reconstruction of its ecological functions.

3.3 EXPLORATION

It refers to the activities of exploration of mineral resources in the exploration license specified range.

3.4 Surface Mining

Chang Lu finger from surface mining sites mined useful minerals or mineral deposits on the cover (including rocks, soil, etc.) peeled After revealing seam mining process, also known as open pit mining.

3.5 Underground mining

It refers to the use mine shaft, inclined shaft tunnel in the form of peace from the underground deposit useful minerals recovery process.

3.6 Filling Mining

With the advance of mining face refers to the underground mined-out area into the filling material, control the surrounding rock collapse and ground displacement and deformation.

3.7 Topsoil

Refers to the soil profile closest to the surface of a level (A layer), the general thickness of 20 ~ 30cm, black soil and chernozem of A Layer thickness up to 50 ~ 100cm.

3.8 Dump

Refers to the place mine stripping and excavation for Dumping was concentrated emissions, including the inner and outer dump dump, also known as waste rock, row Rock field.

3.9 Open Pit

It refers to surface mining activities in the formation of "empty field" or "empty", also known as open-air goaf.

3.10 Tailings

Taniguchi defined by damming or enclosure constructed for storage after sorting discharge tailings beneficiation field locations.

3.11 Mine Subsidence

Refers to mining caused the original stress state of equilibrium above the Mined rock is destroyed, the occurrence of falling, broken, bent Music and other movement and deformation, eventually involving the surface, forming a subsidence basin subsidence and fissures terrain.

3.12 Mine industrial site

It refers to the building ground for the mine production systems and auxiliary production systems and services, structures and related facilities of the venue.

3.13 Waste rock field

It refers to concentrated emissions and carbon-bearing rock disposal sites and other rock ore mining coal and other solid wastes generated in the process.

3.14 Mine contaminated sites

It refers to the result of accumulation, storage, processing, disposal or other means (such as migration) carrying harmful substances to human health or life State environmental harm or risk having potential mining region of space.

4 General requirements for mine ecological environment protection and recovery Governance

4.1 prohibited legally designated nature reserves, scenic spots, forest parks, drinking water source protection areas, cultural relics Prohibited location, geological heritage protection areas, basic farmland protection areas and other important ecological protected areas and other laws and regulations Mining area. Prohibited the landscape important break in the road, both sides of the fairway and important ecological sensitive targets visible range Bad significant open pit mining.

4.2 Mineral resources development activities should be consistent with national and regional planning of the main functional areas, ecological function zoning, environmental protection regulations Planning requirements, to take effective preventive and protective measures to avoid or mitigate the development of mineral resources activities caused ecological damage and environmental Pollution.

4.3 adhere to the "prevention first, combining prevention with control, process control" principle, the mine ecological environment protection and recovery through governance Exploitation of mineral resources of the entire process. According to the priority tasks of mine ecological environment protection and recovery management reasonably determine the mine ecological Protection and partition recovery and management, optimize production and living space pattern mining. The introduction of new technologies, new methods, new technology to improve mine Mountain ecological protection and restoration governance.

4.4 All mining enterprises should control requirements of this standard, implementing mine ecological environment protection and recovery management program.

Various types of site restoration 4.5 after treatment should achieve. security and stability, to humans and animals and plants does not pose a threat; on the surrounding environment is not Pollution; harmony with the surrounding natural environment and landscape; restore the basic functions of land, according to local conditions to achieve sustainable utilization of land Use; the overall regional ecological functions are protected and restored.

5 Mine ecological protection

5.1 Construction of mineral resource base in the key (important) people's governments at all levels of the ecological functions of the area determined by the national and local, shall enter Line ecological impact and economic loss assessment, according to the results of the assessment and the relevant provisions of the Controlled exploitation, reduce the ecological space Occupancy, does not affect the regional leading ecological functions. In the water shortage, environmental capacity is small, fragile ecosystems, earthquakes and ground Mass disaster prone areas, to strictly control the exploitation of mineral resources.

5.2 before mining should investigate the status of biodiversity in the region that could affect the mining areas and a variety of mining activities, for National or local flora and fauna or protected ecosystems, or to be taken in situ conservation and other measures to protect the ex situ conservation of biological diversity Mine Sex.

5.3 Alpine region open pit mining, setting dump and tailings, should be stripped of turf layer concentrated conservation, restoration satisfy conditions Promptly after transplantation, restore vegetation; strictly control the construction site and construction of a temporary road area and scope, reduction of surface vegetation damage.

5.4 desert sand and mineral resources development should avoid the area prone to erosion and ecological degradation zone, reducing mining, dumping and transport and other activities on soil crust, vegetation and sandy gravel screen area damage and disturbance; dump, yard and tailings and other venues should be taken around Block and cover other anti-erosion measures.

5.5 Mineral Resources Development erosion sensitive areas should be scientifically set up the open pit, waste dump, tailings and yard and take flood prevention, Conservation Measures drainage, slope protection, engineering Landang, to reduce the destruction of natural vegetation.

5.6 In the basic farmland protection areas as mining, mine subsidence area governance programs should be combined to determine the priority backfill mining area, to prevent Secondary treatment table; the need to protect water exploration blocks, should take effective measures to avoid damage to groundwater.

5.7 mining solid wastes generated should be stacked in a special place, and to take measures to prevent secondary pollution; prohibits the river, lake Water Park, reservoirs and flood discharge channels geotechnical, oily garbage, mud, cinder, coal and other solid wastes.

5.8 assess the impact of mining activities on surface water and groundwater, to avoid the destruction basin water balance and water environment pollution; and mining areas it should be kept a safe distance between the river environment, to prevent the mining of river creatures, riparian vegetation, river water environment function and anti Hong'an Full devastating effects.

Private road alignment should be around 5.9 Mining avoid environmentally sensitive areas and environmentally sensitive points, to prevent an adverse environmental protection goals ring.

All types of construction site before 5.10 Dump, stope, tailings, mine dedicated roads, depending on the soil type of topsoil should be Peeling. Mine stripping of soil tillage, layer, and respond to heart and backfill soil alone peeling, stripping topsoil thickness love Under the condition of not less than 30cm; for mine uncultivated soil collection, a separate deal with topsoil stripping, if the thickness of topsoil Less than 20cm, at least 20cm thick soil layer of soil below the soil close to the heart and then the table together constitute a separate stripping Off; alpine region stripped topsoil should be retained divot peel thickness of not less than 20cm. Topsoil stripping can not be shop Regulation has to cover the site, select the appropriate venues storage, enclosure and take other measures to prevent soil erosion.

6 Prospecting Ecological Restoration

After 6.1 prospecting activities should be based on similar principles of landscape, soil prospecting caused damage to vegetation and surface landscape Recovery.

6.2 pairs of hydrogeological conditions, land farming and road safety implications or in the rivers, lakes, coastal berm or important buildings Was near the well drilling or pit backfill should be closed, and restore its original ecological functions.

7 Dump ecological restoration

7.1 Geotechnical requirements for Dumping

7.1.1 arrange the order of the abandoned rock will facilitate revegetation of geotechnical emissions on top.

7.1.2 release was prior to mining should be abandoned row of radioactive and hazardous material identification, sediment containing radioactive components of the abandoned should meet Co GB 14500 requirements, the identification of hazardous waste shall be in accordance with GB 18597, GB 18598 and other standards Disposal, other types of discarded release material discharge requirements shall comply with the relevant requirements of GB 18599.

7.2 Dump Water Conservation and stability requirements

7.2.1 Dump substrate slope greater than 1. 5, the foundation should be whittled stepped. There Inner Dump existing ground water point range, Dumping should be built before the hydrophobic culvert in the ditch, culvert hydrophobic.

7.2.2 dump should be set to complete the drainage system, located in the valley of the dump flood control and drainage facilities to be provided to avoid obstruction Flood, to prevent blockage of farmland, increasing soil erosion and induced geological disasters.

7.2.3 has rich water dump or a large number of loose material discharged steep site, and there may be other landslides, the collapse of the dump should be taken to protect the toe or stopped ballast works.

7.3 Dump vegetation restoration

7.3.1 Total Dump height greater than 10m should be open-slope cutting, each step height does not exceed 5-8m, step width should More than 2m, stairs slope gradient of less than 35°, and create favorable conditions for forest vegetation restoration surface.

7.3.2 full utilization project collected before topsoil covering the dump surface, cover soil thickness according to the type of vegetation restoration and field Definitely use. Restore agricultural vegetation, soil thickness should be more than 50cm; restore the ecological grass shrub or landscape use the land, according to the soil conditions appropriate source casing.

7.3.3 arid and sandstorm area dump vegetation restoration does not have the conditions, material should be covered with gravel to prevent wind erosion.

7.3.4 dump vegetation restoration should Linze Lin advised grass, the grass, grass and shrub priority, after the resumption of vegetation coverage should not be lower than the local Similar land vegetation cover, vegetation type is similar to the original type, harmony with the surrounding natural landscape. There may not use foreign Harmful plant species were dump vegetation restoration. Alien species have been used to cause harm vegetation restoration should take manual eradication, Biological control, chemical control and other measures to clean up.

7.4 Dump recovery recycling

Dump should be adapted to local conditions into agriculture, forestry, animal husbandry, construction and other types of land ecological restoration after specific recovery Project implementation with reference to UDC-TD and other relevant standards.

8 Open Pit ecological restoration

Site remediation and soil covering 8.1 Site remediation and soil covering the open stope method is determined according to the field gradient. Horizontally and 15° gentle slope may be less Filling materials, farming pine floor, digging high and low pad method; 15° above steep slopes can fill digging, masonry plant raw basin (groove) Filling, mixing spray, plastic casing ladder, placed bags of plants, stone wall cage filling methods.

8.2 Open Pit vegetation restoration

8.2.1 Slope should remain stable after treatment. Non-arid areas open pit slope should be restored vegetation. Slope design and restoration measures Requirements shall comply with the requirements of GB 50433.

8.2.2 transport links located on both sides of the surrounding urban residential areas, scenic spots and other visual range Quarry Pits and bare rock, it should be taken to hanging seeding, planting vines and other engineering and biological measures for recovery, dang mouth with the surrounding landscape and restored Coordination.

8.3 Open Pit recovery and utilization

Within the open pit as a dump, Conservation and site stability, vegetation restoration required by the implementation of 7.2-7.3. dew Days when stope omission Inner Dump, according to the following requirements.

8.3.1 Overburden mining-containing hazardous or radioactive substances, in accordance with the requirements of 7.1.2 implementation.

8.3.2 Open Pit plains should be flat, after backfilling ecological restoration, and in harmony with the surrounding landscape surface located Mountain open pit slope and platform can be maintained.

8.3.3 Open Pit backfill ground level should be done before the full use of the collected works of topsoil and open stope is covered in weathered Surface (casing requires execution by 7.3.2), with wind and sand and soil conservation measures.

When open pit land recycling 8.3.4 recovered in slope, soil depth, stability, soil environment safety and other aspects of the whole land shall meet the relevant requirements.

9 Tailings Ecological Restoration

9.1 Tailings stability requirements

Drainage tailings, enclosure, seepage, stability and other measures with reference to AQ 2006 execution.

9.2 Tailings casing and restoration

9.2.1 Tailings after the close of the library should be depending on weather conditions, toxic tailings pollutants, restore vegetation and their locations within the tailings dam and dam Complex manner, the situation of different thickness of soil source casing, according to local conditions vegetation restoration and utilization. Restore vegetation casing Thickness of not less than 10cm.

9.2.2 arid sand areas, do not have the conditions for vegetation restoration of tailings, gravel and other materials should be covered.

9.2.3 After restoring tailings used for agricultural production, to deal with tailings cover soil (including tailings plant root elongation zone) Pollutant detection and safety of agricultural products were evaluated to determine the agricultural use patterns based on the assessment results.

9.3 Ecological Restoration tailings recycling

Tailings recycling or recovery were approved when the library closed tailings re-enabled by the environmental impact assessment should be developed Recovery planning and implementation of the tailings management program. Tailings recycling end of ecological restoration in accordance with the requirements of this standard.

10 Mining dedicated road ecological restoration

10.1 Mining dedicated road land area should be strictly controlled and scope. Excavation and embankment projects taken spoil shall be based on the track Road construction progress in a planned way...

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This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 9 pages — is available in the English PDF.

Referenced standards

Normative references

GB 9078

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