Cabinet of Ministers Regulations No. 485 in Riga on 21 June 2011 (pr. No 39 33) certain types of hazardous waste management order Issued under the waste management Act, article 17, eighth and article 36 a i. General provisions 1 the questions determines: 1.1. procedures for the managed polihlorēto biphenyls and terphenyls polihlorēto containing wastes, waste oil, waste batteries and accumulators and waste caused by waste from the titanium dioxide industry;
1.2. the waste batteries and accumulators collection, treatment and recycling sliding;
1.3. batteries and accumulators waste collection and processing volumes and deadlines, as well as a procedure for the provision of the report on the implementation of the activities.
II. Polihlorēto biphenyls and terphenyls-polihlorēto waste management 2. Polihlorēto biphenyls and terphenyls polihlorēto containing wastes are those wastes containing polychlorinated biphenyls and polychlorinated terphenyls, monomethyl, methane, monomethyl-or any mixture containing more than 0.005% for some of these substances (by weight).
3. polihlorēto Polihlorēto biphenyls and terphenyls waste containing the operator or possessor kept separate from flammable objects, chemicals and chemical products, to prevent the emergence of fire hazards.
 4. polihlorēto Polihlorēto biphenyls and terphenyls-containing waste is prohibited to burn the ships.
5. do not clean equipment (e.g. transformers, capacitors, containers) that contains or has contained polihlorēto of polihlorēto biphenyls and terphenyls, may be disposed of only in landfills for hazardous waste, which have received the permission of polluting activities of category A according to the laws and regulations on pollution, if not purified equipment disposal does not cause more pollution than combustion.
III. Oil product waste management 6. Oil product waste is waste oil and other petroleum products containing wastes.
7. waste oil means any mineral or synthetic origin of lubricating oil or industrial oils (such as applied to internal combustion engine and gearbox oils, mineral lubricating oils, oils for turbines and hydraulic oils), which have become unfit for the originally intended purpose of use.
8. Oil waste disposal service or the possessor shall ensure oil waste separately from other types of waste, where this is technically possible and match the permissions received A or B category contaminating activities or waste management licence conditions.
9. Oil waste disposal service or the possessor shall ensure that the following requirements have been met, if the steps above are technically feasible, economically justified and satisfy the permission received in category (A) or (B) for pollutants or waste management licence conditions: 9.1 is mixed waste oil products that have different properties;
9.2. are not mixed waste oil with other kinds of waste or substances, if such mixing impedes their future recovery or disposal;
9.3. are made of petroleum products waste recycling;
9.4. performing a recovery of petroleum products;
9.5. are made of petroleum products waste storage or disposal of waste management regulatory laws.
10. Oil waste disposal service or the possessor as you receive the permit of category A or B operation carried out polluting oil waste treatment in such a way as not to endanger the environment, human life and health, and respect the laws and regulations on waste management in specific priority requirements.
11. waste oil regeneration process must not negatively affect human health and the environment. The recovery process resulting in oil products must not contain hazardous waste. The content of polychlorinated biphenyls and polychlorinated terphenyls in regenerated oil products concentration must not exceed 50 parts per million.
12. polihlorēto Polihlorēto biphenyls and terphenyls containing oil waste is allowed to recover, if after the recovery process is possible to separate polihlorēto biphenyls and polychlorinated biphenyls or the polihlorēto biphenyls and polychlorinated terphenyls contents after the recovery is less than 50 parts per million.
13. it is prohibited to: 13.1. waste oil enter the Inland watercourses, water bodies, groundwater, and drainage systems;
13.2. bury by oil residues resulting from the processing of waste in places that are not dedicated;
13.3. to process oil this way, causing air pollution which exceeds the emission limits laid down in the permit (A) or (B) pollutant categories, or permit the operation of air pollutant emissions from stationary sources of air pollution;
13.4. to mix oil with the polychlorinated biphenyl or other hazardous waste.
IV. Batteries and accumulators waste management 14. This provision in paragraph 23 that person supports the collection of waste batteries and accumulators, separate from other municipal and hazardous waste to promote the separately collected waste batteries and accumulators for recycling and prevent batteries and accumulators waste disposal in municipal waste.
15. This provision 23. the persons referred to in paragraph 1 shall ensure that: 15.1 portable batteries and accumulators and batteries and accumulators used in the collection of the available collection points located in the vicinity of the end users, having regard to population density;
15.2. all identifiable batteries and accumulators collected under the waste management Act, article 33, or according to the legislation on waste electrical and electronic equipment management, are handled and processed pursuant to the laws and requirements of health, safety and waste management.
16. together with the equipment for batteries and accumulators collected waste electrical and electronic equipment processing equipment operators removed or separated from the collected waste electrical and electronic equipment and passes that rule 19. above the battery or the battery processing equipment operator. The meaning of these provisions the device's electrical and electronic equipment according to the legislation on waste management, which is fully or partly powered by batteries or accumulators or you can run the battery or battery.
17. All types of batteries and battery manufacturers to ensure all collected batteries and battery storage, processing and processing under this provision 19, 20, 21, 26, 27, 29, 30 and 31 of the said requirements.
18. Batteries and accumulators waste treatment are all activities carried out by the waste batteries and accumulators after they have been in the battery or the battery processing equipment (hereinafter referred to as processing equipment) operator of waste batteries and accumulators for sorting, preparation for recycling or preparation for disposal.
19. Batteries and accumulators waste storage (including temporary storage) of the site or the processing equipment operator shall be: 19.1. water and pollutants-pretinfiltrācij cover or a suitable container;
19.2. the durable shelter against precipitation;
19.3. the collection of surface run-off and oil receivers, if applicable at the place of storage is intended to store waste batteries and accumulators from which possible oil retention.
20. in addition to paragraph 19 of these regulations to the requirements of processing equipment operator shall be provided: 20.1. weights of waste batteries and accumulators weight;
20.2. water and contaminants-pretinfiltrācij cover with surface drainage collection facilities and, where appropriate, with oil receivers, as well as precipitation hardened covers sites that are stored and processed waste batteries and accumulators;
20.3. suitable sites for the storage of components separated;
20.4. sewage discharge and purification systems.
21. Treatment facility operator shall ensure that all liquids including acid, separation of waste batteries and accumulators.
22. National Environment Service regional environmental administration at least once a year check the processing equipment is complying with environmental protection laws and regulatory requirements and licence conditions.
23. Waste batteries and accumulators collection and recycling performance these rules 26 and 27 the time limits referred to in paragraph provides: 23.1. producers of batteries and accumulators;
23.2. the waste management law in the second paragraph of article 33 of the said waste batteries and accumulators the operator.

24. in paragraph 23 of these rules that person determines the waste batteries and accumulators collection as a percentage of the amount obtained by dividing the relevant calendar year the collected portable batteries and accumulators waste weight with the manufacturer in the calendar year concerned and the two previous calendar years on the market of batteries and accumulators average weight (annex 1), including batteries and accumulators inserted devices. Calendar year concerned in the market of portable batteries and accumulators weight calculated from the end-users in Latvia during the year, sales of portable batteries and accumulators minus the weight of portable batteries and accumulators that weight has left the territory of Latvia before sales end user. Each of the batteries or battery on the market lists only one time.
25. The provisions referred to in paragraph 24 of these rules for the calculations referred to in paragraph 23 people use the producers of batteries and accumulators in the registry data or on the basis of producers of batteries and accumulators reģistrāsavākt data and other data sources, statistical based assessment. The amount of the collection in accordance with the provisions of paragraph 24 shall be calculated each calendar year.
26. in paragraph 23 of these rules that person shall provide such portable waste batteries and accumulators collection rate: 26.1 to 26 September 2012 – 25%;
26.2. until 2016 September 26-45%.
27. This provision a person referred to in paragraph 23 of each year, provides processing equipment delivered to the waste batteries and accumulators, recycling the following: processing at least 65 27.1.% of lead-acid batteries and accumulators, the average weight, ensuring maximum technically possible lead to the degree of processing, if it not entailing disproportionate costs;
27.2. processing at least 75% of nickel-cadmium batteries and accumulators in the medium weight, ensuring maximum technically possible recycling of cadmium, if it not entailing disproportionate costs;
27.3. recycles at least 50% of the other types of waste batteries and accumulators, the average weight.
28. the processing amount is determined by the percentage of the waste batteries and accumulators, the average weight of delivered waste treatment facility the previous year.
29. the waste batteries and accumulators can be handled and processed in other countries, if the cross-border transport of waste shall be carried out according to the European Parliament and of the Council of 14 June 2006, Regulation No 1013/2006 on shipments of waste.
30. Outside the European Union exported waste batteries and accumulators including the mass collection and processing, if the exporter can prove that the waste recycling has taken place in the country of the importer in accordance with the requirements of these regulations is equivalent and other waste batteries and accumulators regulations governing the management of requirements.
31. producers of batteries and accumulators or batteries and accumulators waste managers (if the manufacturer has entered into with them the contract) every year to 20 April for the previous calendar year shall be submitted to the manufacturer of the batteries and accumulators register: 31.1. report on the Latvian market of batteries and accumulators placed sales (also for battery users directly to the sales volumes of batteries and accumulators and other individuals sold quantities of batteries and accumulators for resale to the third battery and battery users) and for Latvia in batteries and accumulators collected in accordance with this volume Rule 26 (annex 2);
31.2. the report on Latvia collected batteries and battery recycling (annex 2).
32. the manufacturer of the batteries and accumulators to provide users information about batteries: 32.1. used in batteries and accumulators the possible harmful effects of the substance on the environment and human health;
32.2. the collection of batteries and battery separately from the household waste and opportunities to participate in waste batteries and accumulators collection of distributed, thus contributing to the further processing of the waste and recycling;
32.3. users of batteries and accumulators available for waste batteries and accumulators collection and recycling possibilities;
32.4. batteries and accumulators the user the importance of batteries and battery recycling.
33. a distributor of batteries and accumulators inform users of batteries and accumulators on the possibility of transfer of waste batteries and accumulators in the respective markets.
V. titanium dioxide industrial waste management 34. Titanium dioxide industrial waste is any waste from the titanium dioxide manufacturing process resulting residue from which their holder discards or intends or is required to discard.
35. it is prohibited to enter the Baltic Sea surface or ground water, and the sea all the way to bury waste from the titanium dioxide industrial waste, including: 21.8. solid waste;
35.2. pamatatsārm, which originates from the filtration phase following hydrolysis of the titanilsulfāt solution plant using the sulphate process: including: 35.2.1. with those related to pamatatsārm acid waste containing more than 0.5% free sulphuric acid and various heavy metals;
35.2.2. pamatatsārm, diluted 0.5% to content or less free sulphuric acid;
35.3. hlorīdproces titanium dioxide-based industrial waste containing more than 0.5% free hydrochloric acid and heavy metals, as well as such waste, which has been diluted until it contains 0.5% or less free hydrochloric acid;
35.4. filtration salts, sludges and liquid waste arising from this provision and 35.2 35.3. processing of waste referred to in point (concentration or neutralization) and containing various heavy metals, but not including neutralized and filtered or decanted waste containing only traces of heavy metals and which, before any dilution, has a pH value above 5.5.36. Forbidden to manage waste from the titanium dioxide industrial waste if it is possible for immediate or accumulating impacts on the aquatic environment and fish resources.
37. for the waste management licence or permit (A) or (B) the polluting activities of category, the titanium dioxide industrial waste authorities in addition to the regulations on the procedure of piesakām A, B, and C categories of activities and pollutants in question permits A and B category contaminating activities, submit national environment service regional environmental administration information about: 37.1. titanium dioxide industrial waste accumulation and biopārveidošan of biological materials or sediments;
37.2. titanium dioxide industrial waste vulnerability to physical, chemical or biochemical change and possible interactions of the environment with other organic and inorganic materials;
37.3. the possibility of harm to natural resources or to adversely affect the natural resources;
37.4. precautionary measures to prevent environmental pollution by waste from the titanium dioxide industrial waste (human activities directly or indirectly to the environment entered the waste from the titanium dioxide industry, which may pose a threat to human health, negatively affect the environment (for example, ecosystems, landscapes, specially protected natural areas) or interfere with the use of its resources according to purpose);
37.5. the location where sampling (sampling points), the object from which samples are to be taken, the distance of the site from the nearest pollutant disposal point and the depth or height at which the samples are to be taken.
38. Titanium dioxide industrial waste disposal facility operators to perform once a month and their waste environmental influence (such as water, soil, Earth, air, in which waste from the titanium dioxide industry wastes are emitted) monitoring and not less frequently than quarterly, announces results of national environment service regional environmental administration and local authorities, in the territory of which the equipment is located. Titanium dioxide industrial waste disposal facility, the operator shall provide a sampling of the same location and depth under identical conditions.
39. Titanium dioxide industrial waste includes waste monitoring, composition and toxicity test to determine compliance with the applicable requirements set out in the permit.
40. Titanium dioxide industrial waste affected environmental monitoring includes the following checks: 24.9. Visual inspection: 40.1.1. topography and tipping site management;
40.1.2. impact on Earth;
40.1.3. disposal sites overall ecological situation;
40.1.4. General changes;
40.2. the chemical test: 40.2.1. acidity;
40.2.2. the iron content (solution and particle);
40.2.3. calcium content;
40.2.4. toxic metal content, if any (in the solution and in the form of particulate matter);
40.2.5. sulphur dioxide and dust in the background.
41. the requirements above ground or buried in located in the titanium dioxide atkritumuparaug sampling, the parameters to be measured, the minimum and the number of times the sampling and monitoring methods of analysis specified in annex 3 to these regulations.

42. at the national environment service regional environmental management request in addition to the provisions referred to in annex 3 parameters having not filtered underground water samples, vanadium, manganese, nickel, zinc (mg/litre) detection using atomic absorption spectrophotometry method, or the quantity of chromium (milligrams/litre) detection using molecular absorption spectrophotometry method.
43. Titanium dioxide industrial waste disposal facility, the operator shall provide the titanium dioxide industrial waste monitoring and comparability between the results by choosing: suitable 43.1. titanium dioxide industrial waste monitoring and analysis methods;
43.2. sampling containers and containers;
43.3. the sample taken conservation methods;
43.4. transport of samples taken, storage conditions and preparation for analysis.
44. Titanium dioxide industrial waste disposal equipment operator sampling and sample analysis results to the log or other information media, which is available in the environmental State inspectors and the local authorised persons within the territory of which the titanium dioxide industrial waste disposal facility.
VI. final question 45. Be declared unenforceable in the Cabinet of 22 September 2008. Regulation No 789 "certain types of hazardous waste management procedures" (Latvian journal, 2008, 152. no; 2010, 16. no).
Informative reference to European Union directives, the regulations include provisions resulting from: 1) of the Council of 16 September 1996, Directive 96/59/EC on the disposal of polychlorinated biphenyls and polychlorinated terphenyls (PCB/PCT);
2) of the European Parliament and of the Council of 6 September 2006 on the directive 2006/66/EC on batteries and accumulators and waste batteries and accumulators repealing Directive 91/157/EEC;
3) Council on 20 February 1978 directives 78/176/EEC on waste from the titanium dioxide industry;
4) Council of 3 December 1982 of Directive 82/883/EEC on procedures for the surveillance and monitoring of environments concerned by waste from the titanium dioxide industry;
5) Council of 24 January 1983 by Directive 83/29/EEC, amending Directive 78/176/EEC on waste from the titanium dioxide industry;
6) the European Parliament and of the Council of 19 November 2008, Directive 2008/98/EC on waste and repealing certain directives;
7) the European Parliament and of the Council of 24 November 2010, the EU directive 2010/75/on industrial emissions (integrated pollution prevention and control).
Prime Minister v. dombrovsky environmental protection and regional development Minister r. vējonis annex 1 Cabinet 21 June 2011 regulations No 485 portable batteries and accumulators collection, calculation of the amount of no PO box
The collection of data for the calculation of annual reporting of producers of batteries and accumulators to the registry 1. X + 1 sales year 1 (S1) 2 X + 2 outlets in year 2 (S2)-3 X + 3-sales year 3 (S3) year 3 (C3) collected collection rate (ratio CR3) = 3 x C3/(S1 + S2 + S3) + 4 X 4 sales in year 4 (S4) in the collected volume 4 (C4) collection rate (CR4) = 3 x C4/(S2 + S3 + S4) (target value 25%)
 
5. X + 5 Outlet 5 (S5) in the collected volume 5 (C5) collection rate (CR5) = 3 x C5/(S3 + S4 + S5) CR4 + 6 X 6 outlets 6 (S6) in the collected volume 6 (C6) collection rate (CR6) = 3 x C6/(S4 + S5 + S6) CR5 7. X + 7 sales in year 7 (S7) in the collected volume 7 (C7) collection rate (CR7) = 3 x C7/(S5 + S6 + S7) CR6 + 8 X 8 sales in year 8 (S8) collected in 8 volumes (C8) collection rate ( CR8) = 3 x C8/(S6 S7 S8 + +) (45%) of the target value
CR7 9. X + 9 sales in year 9 (S9) in the collected volume 9 (C9) collection rate (CR9) = 3 x C9/(+ S8 + S9 S7) 10 X + 10 Outlets CR8 10 (S10) 10th annual amount collected (C10) collection rate (CR10) = 3 x C10/(S8 + S9 + S10) CR9 11. X + 11, etc.
etc.
etc.
CR10 etc.
 
 
 
 
Note the. X-2008.
Environmental protection and regional development Minister r. vējonis annex 2 Cabinet 21 June 2011 regulations No 831 report of Latvia on the market of batteries and accumulators, sales of Latvia collected batteries and accumulators waste volumes and for all types of batteries and battery recycling period from ____ ___ ____ year. ___ _____ to ____ ___ of ___. ___ ____ 1. Details on batteries or battery manufacturer: 1.1 1.2. company registration number, registered office 1.3 1.4. registration number of producers of batteries and accumulators in the register and the registration date 2. information on the Latvian market of batteries and accumulators placed volumes: no PO box
 Type of batteries and accumulators placed on the market of Latvia, batteries and battery total weight (tonnes) 2.1 portable batteries or accumulators 2.2. in vehicles or other pašgājējtehnik used in batteries or batteries 2.3. Industrial batteries or accumulators 3. information about all types of batteries and battery recycling: no PO box
 Type of batteries and accumulators collected batteries and accumulators waste volume (tonnes) in Latvia, the recycled waste batteries and accumulators total weight (tonnes) in the other Member State of the European Union revised the waste batteries and accumulators total weight (tons) outside the European Union, the recycled waste batteries and accumulators, the total weight (tonnes) 3.1 portable batteries or accumulators 3.2. Vehicles or other pašgājējtehnik used in batteries and accumulators 3.3 industrial batteries or accumulators certify the message contains the information is complete and true.
The manufacturer or pārstāvis1 producer: name, surname, personal code number title or term and date of issue's signature2 Z.v. 2 Date2 ____ ____ ____ ____ ___ notes.
1 signed by the person whose right to represent the company is registered in the commercial register. If the right of representation has not been registered, then, when a message is submitted in person, accompanied by an authorisation document certifying the right to represent the person concerned.
2 do not fill out, if the electronic document is drawn up according to the law on electronic document design.
Environmental protection and regional development Minister r. vējonis annex 3 Cabinet 21 June 2011 regulations No 485 requirements above ground or buried in located in the titanium dioxide waste sampling inspection and sampling requirements parameter minimum sampling and analysis (annual) analysis method 1. Unfiltered surface water around the landfill site, which might be affected, and outside, especially in the where the water flows out of the landfill.
Samples are taken at the same time, the depth of 50 cm to a pH of 1 Elektrometrij.
The measurement shall be made at the time of sampling (mg/l) 1 SO4 Gravimetry.
Complexometric titration. Molecular absorption spectrophotometry 2. Unfiltered groundwater around the landfill site, which might be affected, and beyond, especially where water flows out of the landfill.
Samples are taken at the same time Ie (mg/l) 1 atomic absorption spectrophotometry Fe (mg/l) 1 atomic absorption spectrophotometry.
Molecular absorption spectrophotometry Ca (mg/l) 1 atomic absorption spectrophotometry. Complexometric titration of Cu, Pb (mg/l) 1 atomic absorption spectrophotometry. Complexometric titration of Cl (mg/l) 1 Titrimetrij (Mora) environmental protection and regional development Minister r. vējonis