Garbage from cleaning premises and territory. Instructions for handling waste of hazard class V "Waste (garbage) from cleaning the territories and premises of wholesale and retail trade in food products" FKKO waste from cleaning the territory and premises

The amount of waste from cleaning the area is determined by the formula:

M = S * m

Where: S – area of ​​hard coverings;

m – specific indicator of waste generation per 1 m2 – t/m2.

The calculation is presented in table 5.17.

Table 5.17.

S

m

M, t

Mm 3

Standard amount of waste: 0.38 t/year (0.6 m 3 /year)

Shelf life at the industrial site: 1 day

5.18. Unsorted ferrous metal scrap.

1. Scrap generated during vehicle repairs. The rate of scrap generation during repairs is calculated using the formula:

P P *

Q h.m. = ----- , t

10000

P P

/10000 - standard coefficient of scrap generation per 10,000 km t/km;

The calculation is presented in table 5.18.1.

Table 5.18.1.

Vehicle brand

P P ,km

Q f. , T

Niva, GAZ

Total:

2. Scrap generated when replacing vehicle components. The rate of scrap generation during repairs is calculated using the formula:

P P *

Q h.m. = ----- , t

N

P P - total vehicle mileage by brand, km;

/ N

N

The calculation is presented in table 5.18.2.

Table 5.18.2.

Vehicle brand

P P ,km

N

Q f. , T

Niva, GAZ

Total:

Standard amount of waste: 0.118t/year

Shelf life at the industrial site: 6 months

5.19. Unsorted aluminum scrap.

1. Waste generated during vehicle repairs is calculated using the formula:

P P *

Q color..m. = ----- , t

10000

P P - total vehicle mileage by brand, km;

/10000 - standard coefficient of scrap generation per 10,000 km, t/km;

The calculation is presented in table 5.19.1.

Table 5.19.1.

Vehicle brand

P P ,km

Q f. , T

Niva, GAZ

Total:

2. Scrap generated when replacing vehicle components. The rate of scrap generation during repairs is calculated using the formula:

P P *

Q h.m. = ----- , t

N

P P - total vehicle mileage by brand, km;

/ N - standard coefficient of scrap generation per N thousand kilometers;

N – the norm of vehicle mileage before the cap. repair, km.

The calculation is presented in table 5.19.2.

Table 5.19.2.

Vehicle brand

P P ,km

N

Q f. , T

Niva, GAZ

Total:

Standard amount of waste: 0.005 t/year

Shelf life at the industrial site: 6 months

A hazardous waste passport is prepared:

For waste that has dangerous properties(toxicity, fire hazard, explosion hazard, high reactivity, content of pathogens of infectious diseases);

For waste of I-IV class of hazard for the environment.

There are 4 units of such waste at the enterprise:

1. Mercury lamps, fluorescent mercury-containing tubes, used and defective;

2. Unsorted waste from household premises of organizations

3. Waste of paper and cardboard from office activities and office work

4. Waste (garbage) from cleaning the territory and premises of wholesale and retail trade in industrial goods

Initial information about waste, waste passports, subject to approval, are presented in the “Appendix...” to the project.

SECTION 5. LIST AND PHYSICAL-CHEMICAL CHARACTERISTICS OF WASTE
Table 1.10
Type of waste Production Technological process Hazard class for the natural environment Physico-chemical characteristics of waste

Name

FKKO code

Name

Name

State of aggregation

Solubility in water,

g/100 g

Composition of waste by components
Name

%

Waste fluorescent lamps

Premises

Room lighting

Insoluble

Glass Mercury Other metals Other

Premises

Cleaning

Insoluble

Food Residues Paper Mechanical impurities Textiles Glass Plastic Rubber Wood

Office work

Insoluble

Cellulose

Trading activities

Cleaning

Insoluble

Pulp Wood Textile

SECTION 6. JUSTIFICATION OF STANDARDS AND CALCULATION OF WASTE QUANTITY

1. Calculation of the formation of waste fluorescent mercury-containing lamps

The number of used fluorescent lamps is calculated using the formula:

N = n i * T i * t i / k i, (pcs/year)

The weight of the generated waste is determined by the formula:

M = N * m i, (tons/year)

n i – number of installed lamps of this type, pcs.;

Ti – number of working days per year;

ti – average operating time of one lamp per day, hour;

ki – operational service life of lamps, hour;

mi – weight of one lamp, tons

The calculation was carried out on the basis of the “Methodology for calculating waste generation volumes. Waste mercury-containing lamps" MRO-6-99 SPb.: 1999

Waste generation calculation

2. Calculation of unsorted waste generation from household premises of organizations

The mass of waste generated is calculated using the formula:

M = K people * N arr., (tons/year), where

K people - number of employees;

N arr - education standard, tons/year;

The calculation was carried out on the basis of regulatory data “Collection of specific indicators of production and consumption waste generation” M., 1999.

Waste generation calculation

3. Calculation of paper and cardboard waste generation from office activities and office work

The amount of waste is calculated using the formula:

M = m * N arr., (tons/year), where:

M – mass of generated waste, tons;

m – paper consumption at the enterprise, tons;

N arr – waste generation standard, %

The calculation of waste generation was carried out on the basis of regulatory data “Collection of specific indicators of production and consumption waste generation” M., 1999.

Waste generation calculation

Paper consumption at the enterprise m , tons/year

Waste generation standard

N arr. %

Mass of generating waste M, tons/year
1 2 3
0,144 8 0,0115
Total 0,0115

4. Calculation of waste generation from cleaning the territory and premises of wholesale and retail trade in industrial goods

The mass of waste generated is calculated using the formula:

M = S * N arr. * R, (tons/year), where

M is the mass of formed solids household waste, tons;

S - retail area, m2;

N arr - education standard, m 3;

p - density of generated waste tons/m3.

Calculation of the density of generated waste was carried out on the basis of the component composition of waste using the “Methodological recommendations for assessing the volume of production and consumption waste generation” GU NITsPURO, M.: 2003

The calculation of waste generation was carried out on the basis of regulatory data “Collection of specific indicators of production and consumption waste generation” M., 1999; " Guidelines to determine temporary standards for the accumulation of solid household waste" M.: 2005. SZO FSUE "Federal Center for Improvement and Waste Management of the Gosstroy of Russia"

Waste generation calculation

SECTION 7. OPERATIONAL WASTE FLOW SCHEME Table 1.11

Type of waste

Hazard class for fire safety equipment

Unit

Quantity (volume) of waste generation

in a year

Availability of waste at the beginning of the year

Received from other organizations

Name

FKKO code

Name

Quantity

Purpose of the appointment Territorial feature
Name Name
1 2 3 4 5 6 7 8 9 10 11 12

luminescent waste

3533010013011 1 T 168 0,00183
Unsorted waste from household premises of organizations 9120040001004 4 T 168 0,2
Waste of paper and cardboard from office activities and office work 5 T 168 0,0115
Waste (garbage) from cleaning the territory and premises of wholesale and retail trade in industrial goods 9120120001005 5 T 168 15,084
Used waste

Transferred to other organizations

Hosted at our own facilities

Quantity

Waste management operations

Quantity

Purpose of waste transfer

Territorial feature

Quantity

Operations by

placement

departure

Object type

Name

Name

Naimenov-

Name Name
13 14 15 16 17 18 19 20 21 22 23 24 25
0,00183 Temporary accumulation

IP Ivanyuk

Great Dane b/n 01.02.08

0,2 Accommodation There are no own waste disposal facilities
0,0115 Accommodation Solid waste landfill Salekhardremstroy dog. No. 183-08 s

There are no own waste disposal facilities

15,084 Accommodation Solid waste landfill Salekhardremstroy dog. No. 183-08 s

There are no own waste disposal facilities

SECTION 8. CHARACTERISTICS OF WASTE STORAGE AND ACCUMULATION PLACES

Waste (garbage) from cleaning the territory

Waste(garbage) are generated from cleaning the hard surfaces of the mine site areas.

Average composition waste (garbage) from cleaning areas next:

Paper, cardboard - 8.00%;

Wood - 11.00%;

Glass - 10.80%;

Stones, sand - 57.20%;

Plastic - 13.00%.

Paper, cardboard, wood

Wood (xylem), tissue, of perennial woody and shrub plants, consisting of cells with lignified membranes and having a vascular conducting system. Cell membranes are composed of several layers of very thin fibers called microfibrils, which are compactly arranged and directed in a spiral in each layer at a different angle to the cell axis. The microfibril consists of long, chain-like molecules of cellulose - a natural polymer of the composition (C 6 H 10 O 5) n, where n = 2,500 - 3,000. It is 40 - 50% in wood. The cell membrane also contains other organic (lignin - 20 - 30% and hemicellulose - 17 - 43%) and inorganic (0.17 - 0.27%) substances.

Average wood composition:

Cellulose - 40%;

Lignin - 30%;

Hemicellulose - 29.8%;

Inorganic - 0.2%.

All components that make up wood are of natural organic origin, consisting of compounds such as carbohydrates (fiber), that is, substances found in living nature, belong to the class of practically non-hazardous components with an average score (X i) equal to 4, and, therefore, a coefficient the degree of danger for the OPS (W i) equal to 10 6.

Glass

Glass- a solid amorphous material obtained by supercooling a melt of natural quartz (melt temperature is about 2,000C). The most important and common class is silicate glass, the main component of which is silicate (SiO 2).

The relative hazard parameter of glass for OPS (X i) is taken according to, X manganese = 3.33.

Stones, sand

Stones are represented mainly by natural minerals used for road surfaces, including: sand, gravel, limestone, crushed stone.

Sand consists of quartz grains (silicon dioxide SiO 2) of various sizes, with a slight admixture of feldspar (calcium aluminosilicate)

Gravel loose, coarsely clastic sedimentary rock, consisting of rounded fragments of rocks, sometimes minerals (for example, quartz) measuring 1-10 mm in diameter. There may be some sand present. By origin they distinguish between river, lake, glacial, etc.

Limestone- a widespread sedimentary rock consisting mainly of the mineral calcite in the form of remains of calcareous shells and skeletons various organisms or small crystalline grains.

Crushed stone- sharp-edged fragments of hard durable stone 5-150 mm in size, including natural crushed stone and crushed stone obtained by special crushing of hard rocks.

As mentioned above, the stones used for arranging the road surface are represented by inorganic natural minerals, that is, substances that occur naturally in nature and belong to the class of practically non-hazardous components with an average score (X i) equal to 4, and, therefore, a coefficient degree of danger for OPS (Wi) equal to 10 6.

Plastic

The entire volume of plastic is fully represented plastic bottles from drinks made from polyethylene terephthalate (PET). For the production of such bottles, special food-grade polyester is used, which does not contain, in particular, aldehydes.

Polyethylene terephthalate (polyethylene glycol terephthalate) - thermoplastic, density 1.38-1.40 g/cm 3, insoluble in water and organic solvents, at 40-150C soluble in phenols and their alkyl or chlorine derivatives, stable in dilute and concentrated acids, solutions weak alkalis (Na 2 CO 3, NaHCO 3, etc.). Polyethylene terephthalate is characterized by low hygroscopicity; it is obtained by polycondensation of terephthalic acid or its dimethyl ether with ethylene glycol.

The relative hazard parameter of waste components for the hazardous environment (X i) is calculated by dividing the sum of points for all parameters by the number of these parameters, taking into account physical and chemical characteristics each component.

The determination of primary hazard indicators of waste components (MPC v, MAC r.h., MAC s.s., LC 50, LD 50) is carried out taking into account.

X polyethylene terephthalate = (4+4+4+4) / 4 = 4,000.

The results of calculating the indicators of the degree of danger of waste components (waste (garbage) from cleaning the territory) for the natural environment are given below in tabular form.


CONCLUSION: the total indicator of the degree of hazard obtained by the calculation method K waste = 10,39 , which corresponds to 10 2 >K ex >10. Thus, waste (garbage) from street cleaning of areas belongs to hazard class IV.

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Approximate form

(name of company)

I APPROVED
(job title and organization name)
(last name, initials)
(signature)

" " G.

INSTRUCTIONS N...
on waste management of hazard class V
"Waste (garbage) from cleaning the territories and premises of wholesale and retail trade in food products"

G. (name)
(year)

CONTENT

1. GOAL 3
2. AREA OF APPLICATION 3
3. RELATED DOCUMENTS 3
4. TERMS AND DEFINITIONS 4
5. GENERAL INFORMATION ABOUT WASTE 5
6. HAZARDOUS PROPERTIES AND IMPACT OF WASTE COMPONENTS ON THE ENVIRONMENT AND HUMAN 6
7. WASTE GENERATION AND COLLECTION 6
8. CONDITIONS FOR TEMPORARY STORAGE AND WASTE ACCUMULATION 6
9. ACCOUNTING FOR WASTE GENERATION AND MOVEMENT 7
10. TRANSFER OF WASTE TO SPECIALIZED ENTERPRISES 7
11. TRANSPORTATION OF WASTE 8
12. MEASURES TO ELIMINATE EMERGENCY (EMERGENCY) SITUATIONS 8
13. DOCUMENT DATA 8
14. APPROVAL SHEET 9
15. MAILING SHEET 9
16. INFORMATION AND ISSUE SHEET 9

1. GOAL

1. GOAL

This instruction establishes the procedure and safety requirements for handling waste of hazard class V "Waste (garbage) from cleaning the territories and premises of wholesale and retail trade of food products" on .

2. AREA OF APPLICATION

The instructions are applied by the enterprise itself LLC "Name of the enterprise" and its divisions (branches).

3. RELATED DOCUMENTS

1. Federal Law of January 10, 2002 N 7-FZ “On Environmental Protection” ;

2. Federal Law of June 24, 1998 N 89-FZ “On Production and Consumption Waste” ;

3. Federal Law of March 30, 1999 N 52-FZ "On the sanitary and epidemiological welfare of the population" ;

4. Federal Law of December 21, 1994 N 68-FZ "On the protection of the population and territories from natural and man-made emergencies" ;

5. Federal Law of May 4, 2011 N 99-FZ “On licensing of certain types of activities” ;

6. Decree of the Government of the Russian Federation of October 23, 1993 N 1090 “On Traffic Rules”(With "Basic provisions for the admission of vehicles to operation and the responsibilities of officials to ensure road safety");

7. Order of Rosprirodnadzor dated May 22, 2017 N 242 “On approval of the federal classification catalog of waste” ;

8. Order of the Ministry of Natural Resources of Russia dated December 4, 2014 N 536 "On approval of the Criteria for classifying waste into hazard classes I-V according to the degree of negative impact on the environment" ;

9. Order of the Ministry of Natural Resources of Russia dated September 1, 2011 N 721 "On approval of the Accounting Procedure in the field of waste management" ;

10. SanPiN 2.1.7.1322-03 "Hygienic requirements for the disposal and disposal of production and consumption waste"(approved Resolution of the Chief State Sanitary Doctor of the Russian Federation dated April 30, 2003 N 80);

11. Sanitary rules for the maintenance of populated areas dated 08/05/1988.;

12. Rules for handling municipal solid waste, approved Decree of the Government of the Russian Federation of November 12, 2016 N 1156.

4. TERMS AND DEFINITIONS

Environmental safety is the state of protecting the natural environment and vital human interests from possible negative impact economic and other activities, emergency situations of natural and man-made nature, their consequences.
Security requirements environment(environmental requirements) - mandatory conditions, restrictions or a combination of them imposed on economic and other activities, established by laws, other regulatory legal acts, environmental regulations, state standards and other regulatory documents in the field of environmental protection.
Specialized organizations are legal entities and individual entrepreneurs that collect, use, neutralize, transport and dispose of waste and have licenses to carry out such activities in accordance with existing legislation.
Negative impact on the environment is the impact of economic and other activities, the consequences of which lead to negative changes in the quality of the environment.
Production and consumption waste (hereinafter - waste) - substances or objects that are generated in the process of production, performance of work, provision of services or in the process of consumption, which are disposed of, are intended for disposal or are subject to disposal in accordance with Federal Law of June 24, 1998 N 89-FZ “On Production and Consumption Waste”.
Municipal solid waste (MSW) - waste generated in residential premises during consumption individuals, as well as goods that have lost their consumer properties during their use by individuals in residential premises to satisfy personal and household needs. MSW also includes waste generated in the process of activities legal entities, individual entrepreneurs and waste similar in composition generated in residential premises during consumption by individuals.
Type of waste - a collection of waste that have common characteristics in accordance with the waste classification system;
Waste hazard class is a characteristic of the environmental hazard of waste, which is established by the degree of its negative impact with the direct or possible impact of hazardous waste on the environment in accordance with the criteria established by the federal executive body that carries out state regulation in the field of environmental protection.
Waste passport is a document certifying that waste belongs to the waste of the corresponding type and hazard class, containing information about its composition.
Waste management is the activity of collecting, accumulating, transporting, processing, recycling, neutralizing, and disposing of waste.
Waste disposal - storage and disposal of waste.
Waste storage - storage of waste in specialized facilities for a period of more than eleven months for the purpose of disposal, neutralization, and burial.
Waste disposal is the isolation of waste that is not subject to further disposal in special storage facilities in order to prevent the release of harmful substances into the environment.
Waste storage facilities are specially equipped structures that are equipped in accordance with the requirements of legislation in the field of environmental protection and legislation in the field of ensuring the sanitary and epidemiological well-being of the population and are intended for long-term storage of waste for the purpose of their subsequent disposal, neutralization, and burial.
Waste disposal facilities are specially equipped structures designed for waste disposal (landfill, sludge storage facility, including a sludge pit, tailings storage facility, rock dump, etc.) and including waste storage facilities and waste disposal facilities.
Waste disposal limit is the maximum permissible amount of waste of a particular type that is allowed to be disposed of in a certain way for a specified period of time in waste disposal facilities, taking into account the environmental situation in the given territory.
The waste generation standard is the established amount of waste of a specific type during the production of a unit of product.
Waste accumulation - temporary storage of waste (for a period of no more than eleven months) in places (sites) equipped in accordance with the requirements of legislation in the field of environmental protection and legislation in the field of ensuring the sanitary and epidemiological well-being of the population, for the purpose of their further disposal, neutralization, placement, transportation.
Waste transportation - moving waste using Vehicle outside the boundaries of a land plot owned by a legal entity or individual entrepreneur or provided to them with other rights.
Waste neutralization - reducing the mass of waste, changing its composition, physical and chemical properties (including combustion and (or) disinfection in specialized installations) in order to reduce the negative impact of waste on human health and the environment.
Fire hazard - the possibility of a fire occurring and/or developing.
Container - waste container designed for storing solid municipal waste, with the exception of bulky waste.
Container site - a place for accumulation of solid municipal waste, equipped in accordance with legal requirements Russian Federation in the field of environmental protection and legislation of the Russian Federation in the field of ensuring the sanitary and epidemiological well-being of the population and intended for the placement of containers and bunkers.