FIRST SCHEDULE
{{(*rr 5, 6, 7, 10, 33, 38)}}
AMBIENT AIR QUALITY TOLERANCE LIMITS
Table 1: Ambient Air Quality Tolerance Limits| | Pollutant | Time weighted Average | | | |
| | | | Industrial area | Residential, Rural and Other area | Controlled areas*** |
| 1. | Sulphur Dioxide(SO2); | Annual Average* | 80 ☐g/m3 | 60 ☐g/m3 | 15 ☐g/m3 |
| | | 24 hours** | 125 ☐g/m3 | 80 ☐g/m3 | 30 ☐g/m3 |
| | | Annual Average | | 0.019ppm/50☐g/m3 | |
| | | Month Average | | | |
| | | 24 Hours | | 0.048ppm/125☐g/m 3 | |
| | | One Hour | | | |
| | | Instant Peak | | 500 ☐g/m3 | |
| | | Instant Peak (10 min) | | 0.191 ppm | |
| 2. | Oxides of Nitrogen (NOx); | Annual Average* | 80 ☐g/m 3 | 60 ☐g/m 3 | 15 ☐g/m 3 |
| | | 24 hours** | 150 ☐g/m 3 | 80 ☐g/m 3 | 30 ☐g/m 3 |
| | | 8 hours | | | |
| | | Annual Average | | 0.2 ppm | |
| | | Month Average | | 0.5 ppm | |
| | | 24 Hours | | 0.4 ppm | |
| | | One Hour | | 0.8 ppm | |
| | | Instant Peak | | 1.4 ppm | |
| 3. | Nitrogen Dioxide | Animal Average | 150 ☐g/m 3 | 0.05 ppm | |
| | | Month Average | | 0.08 ppm | |
| | | 24 Hours | 100 ☐g/m | 0.1 ppm | |
| | | One Hour | | 0.2 ppm | |
| | | Instant Peak | | 0.5 ppm | |
| 4. | Suspended particulate matter (SPM) | Annual Average* | 360 ☐g/m 3 | 140 ☐g/m 3 | 70 ☐g/m 3 |
| | | 24 hours** | 500 ☐g/m 3 | 200 ☐g/m 3 | 100 ☐g/m 3 |
| | | | Industrial area | Residential, Rural and Other area | Controlled areas*** |
| | | mg/Kg | | | |
| | Pollutant | Time weighted Average | | | |
| | | Annual Average **** | | 100 ☐g/m 3 | |
| | | 24 hours *** | | 180 ☐g/m 3 | |
| 5. | Respirable particulate matter (<10☐m)(RPM) | Annual Average* | 70 ☐g/m 3 | 50 ☐g/m 3 | 50 ☐g/m 3 |
| | | 24 hours** | 150 ☐g/Nm 3 | 100 ☐g/Nm 3 | 75 ☐g/Nm 3 |
| 6. | PM2.5 | Annual Average | 35 ☐g/m 3 | | |
| | | 24 hours | 75 ☐g/m 3 | | |
| 7. | Lead (Pb) | Annual Average* | 1.0 ☐g/Nm 3 | 0.75 ☐g/Nm 3 | 0.50 ☐g/m 3 |
| | | 24 hours** | 1.5 ☐g/m 3 | 1.00 ☐g/m 3 | 0.75 ☐g/m 3 |
| | | Month Average | | 2.5 | |
| 8. | Carbonmonoxide (CO)/carbon dioxide(CO2) | 8 hours** | 5.0 mg/m 3 | 2.0 mg/m 3 | 1.0 mg/m 3 |
| | | 1 hour | 10.0 mg/m 3 | 4.0 mg/m 3 | 2.0 mg/m 3 |
| | | mg/Kg | | | |
| | | 24 hours** | | | |
| 9. | Hydrogen Sulphide | 24 hours** | 150☐g/m 3 | | |
| 10. | Non-methane hydrocarbons | | | | |
| | | instant Peak | 700ppb | | |
| 11. | Total VOC | 24 hours** | 600 ☐g/m 3 | | |
| 12. | Ozone | 1-Hour | 200 ☐g/m 3 | 0.12 ppm | |
| | | 8 hour (instant Peak) | 120 ☐g/m 3 | 1.25 ppm | |
| 13. | Odour | | | | |
Legendc)ppm – parts per milliond)ppb – parts per billione)Values at Standard Temperature and Pressure (STP)f)Conversion factors from ppm to mg/m 3 and mg/m 3 to ppm are stipulated under the Eleventh Scheduleg)*[Annual Arithmetic mean of minimum 104 measurements in a year taken twice a week 24 hourly at uniform interval.]h)[** 24 hourly/8 hourly values should be met 98% of the time in a year. However, 2% of the time, it may exceed but not on two consecutive days.]i)Whenever and wherever two consecutive values exceeds the limit specified above for the respective category, it would be considered adequate reason to institute regular/continuous monitoring and further investigations.j) ☐ the 24-hour limit may not be exceeded more than three times in one year;k) ** 24-hour limit may not be exceeded more than three times in one year micrograms/m 3l) *** Not to be exceeded more than once per year average concentrationm) *** In coversion of units from ppm to mg/m 3 and vice versa shall use guidelines set out under Part II of the Fifth Schedule.R20Table 2: Ambient Air Quality at Property Boundary for General Pollutants| | Pollutant | Time weighted Average | Property Boundary |
| 1 | Particulate matter (PM) | Annual Average* | 50 ☐ g/m3 |
| | | 24 hours** | 70 ☐ g/m3 |
| 2. | Oxides of Nitrogen (NOx); | Annual Average* | 80 ☐ g/m3 |
| | | 24 hours** | 150 ☐ g/m3 |
| 3. | Sulphur oxides (SOx); | Annual Average* | 50 ☐ g/m3 |
| | | 24 hours** | 125 ☐ g/m3 |
| 4. | Hydrogen Suphide | 24 hours** | 50 ☐ g/m3 |
| 5. | Ammonia | 24 hours** | 100 ☐ g/m3 |
Note.a)For residential premises in designated industrial areas, the above standards do not apply.b)For industries in designated residential areas, standards for residential areas shall apply.SECOND SCHEDULE
Priority Air Pollutants
Part I: General Source Pollutantsa)Particulate matter (Dust, black smoke, smog, aerosols);g)Volatile organic Compounds (VOC);h)Hydrogen Sulphide (H2S);i)Hydrogen Chloride (HCL);j)Lead and its compounds;m)Dioxins and furans (PCDD and PCDF).Part II - Mobile Source Pollutantsb)Volatile organic Compounds (VOC);Part III: Greenhouse gases (GHG)d)Hydrofluorocarbons (HFCs);e)Perfluorocarbons (PFCs); andf)Sulphur hexafluoride (SF6)THIRD SCHEDULE
EMISSION LIMITS FOR CONTROLLED AND NON-CONTROLLED FACILITIES
INSERT IMAGE Pg. 3201, 3202, 3203, 3204, 3205, 3206LegendSF: Suphur Fuel*1.5-3.0% only justified by project specific considerations i.e. add secondary treatment to meet levels of 1.5% Sulphur** dependent on water availability for injectionCI: Compression IgnitionSI: Spark IgnitionDF: Dual FuelDA: Degraded AreaNDA: Non-degraded AreaThe chimney or stack should have a minimum height of 10 metres above ground level and clear the highest of the building by not less than 3 metres for all roofs. The topography and height of adjacent buildings within 50 metres radius should be taken into account.Toxic Equivalent (TEQ) is the sum of the toxic equivalent factors (TEF) of a mixture congeners contained in a compound. The compound 2,3,7 8-tetrachlorodibenzo-pdioxin (TCDD) was assigned a TEF of 1 after being identified, by International Association of Radiology and Cancer (IARC) and World Health Organisation (WHO), as the most toxic of all compounds, and as carcinogenic to humans, based mainly on studies of cases involving accidental or occupational heavy exposure. Therefore the TEF is a weighting factor.g - gramμg- microgramkg – kilogram (1,000g)mg - milligramμg- microgramm3 – cubic metreppm – parts per millionFOURTH SCHEDULE
AIR POLLUTION MONITORING PARAMETERS FROM STATIONARY SOURCES
INSERT TABLE Pg. 3208, 3209,And any other parameter as may be prescribed by the Authority from time to timeLegenda)* - parameters to be monitoredb)Frequency – dependent on parameter and reported on a quarterly basisFIFTH SCHEDULE
General GuidelinesPart I - Exempted Equipment and Activitiesa)Air pollutant detector, air pollutant recorder, combustion controller or combustion shut-off.b)Air conditioning or comfort ventilating systems.c)Vacuum cleaning systems used exclusively for office applications or residential housekeeping.d)Ventilating or exhaust systems for print storage room cabinets.e)Exhaust systems for controlling steam and heat.f)Maintenance, repair, or replacement in kind of equipment for which a permit to operate has been issued.g)Equipment which emits only nitrogen, oxygen, carbon dioxide, and/or water vapour.h)Ventilating or exhaust systems used in eating establishments where food is prepared for the purpose of consumption.i)Equipment used to liquefy or separate oxygen, nitrogen or the rare gases from the air.k)Outdoor painting and sand blasting equipment.l)Lawnmowers, tractors, farm equipment and construction equipment.m)Fire schools or fire fighting training.n)Residential wood burning stoves and wood burning fireplaces.o)Buildings, cabinets, and facilities used for storage of chemicals in closed containers.p)Sewage treatment facilities.r)Inactive wastewater treatment systems.s)Non-contact water cooling towers (water that has not been in direct contact with process fluids).t)Laundry dryers, extractors, or tumblers used for fabrics cleaned with a water solution of bleach or detergents.u)Equipment used for hydraulic or hydrostatic testing.v)Blueprint copiers and photographic processes.w)Inorganic acid storage tanks equipped with an emission control device.x)Any fuel burning equipment used exclusively for providing domestic electrical power of a capacity not greater than 100 KVA.Part II — Guideline on Conversion factorsa)ppm to mg/m3 - airThe conversion between ppm and mg/m³ is dependent on both the molecular weight of the substance and the temperature at which the conversion is made. The assumption is that the pollutant behaves as an ideal gas and as such, 1 mole of the substance occupies 22.4 litres at standard temperature (273K) and pressure (101.3 kPa). This is consistent with normalised concentrations, and it is therefore not normally necessary to take account of the temperature or pressure difference in the conversion. However, when converting ppm to mg/m³ at actual discharge conditions, it is important to take account of the necessary factors.To convert from ppm to mg/m3, the following formula should be used:mg/m3 = ppm x (MW/22.4) x (273/T) x (P/101.3)Where MW is the molecular weight of the substance (in grams)T is the temperature at which the conversion is to be made (degrees Kelvin)P is the pressure at which the conversion is to be made (kPa)To convert from mg/m3 to ppm, the following formulae should be used:ppm = mg/m3 x (22.4/MW) x (T/273) x (101.3/P)Part IV — Emission Reduction Measures of Dark Smoke from Chimneys1)Avoid overloading burners with fuel oil.2)Use the correct fuel to air ratio by proper adjustment of the air and fuel supplies.3)Avoid flame impingement on any cold surface.4)Avoid carbon build-up in the boiler and furnace tubes and maintain the boiler and furnace settings in good condition.5)Clean the burner at regular intervals and remove the carbon deposits from the nozzle with soft article after soaking, the nozzle in Kerosene.6)Use the correct atomizing nozzle and atomizing pressure.7)Check for worn or distorted parts of the burner and replace the damaged parts.8)Allow sufficient time in lighting up the burners from cold and adopt the correct start-up procedures as recommended by the burner manufacturers.9)Keep the mesh at the inlet of the air blower clear at all timesPart V — emissions report format-The emissions report format shall include -(a)an estimate of the emissions for the relevant(b)all the data applicable to the emissions sources, in respect of the licensed facility.(c)Estimates of annual emissions shall be made based on the following methods, in order of preference –(1)continuous emission monitoring data;(2)calculation of SO2 emissions based on fuel use and sulphur content data including combustion processes in which exhaust gases do not come in contact with products;(3)most recent and representative stack monitoring measurements conducted in the previous five years and activity data for the year for which emissions are estimated;(4)emission factor or equivalent methods and activity data for the year;(5)emission factor or equivalent methods and plant capacity data;(6)mass balance (including fuel use data) based on the two previous years or the most recent representative year;(7)other approved methods supported by calculation and documentation, and the procedures set out by the AuthorityPart VI — Measures or operating procedures to control fugitive emissionsThe following measures or operating procedures may be used to control fugitive emissions —(a)from storage piles through use of enclosures, covers or stabilisation, minimising the slope of the upwind face of the pile, confining as much pile activity as possible to the downwind side of the pile and such other methods or techniques as are approved by the Authority.(b)by enclosing, covering, watering, or otherwise treating loaded haul trucks and railroad cars, or limiting size of loads, to minimise loss of material to wind and spillage.(c)by minimising the area of disturbed land or tailings.(d)by planting special wind break vegetation at critical points.(e)by prompt removal of coal, rock minerals, soil, and other dust-forming debris from paved roads and scraping and compaction of unpaved roads to stabilise the road surface as often as necessary to minimise re-entrainment of fugitive particulate matter from the road surface.(f)by minimising the period of time between initially disturbing the soil and revegetating or other surface stabilization.(g)by restricting the areas to be blasted at any one time.(h)by restricting the speed of vehicles in or around mining, tailing or quarrying operations.(i)by re-vegetating, mulching, or otherwise stabilising the surface of all areas adjoining roads that are a source of fugitive particulate emissions.(j)by substituting covered conveyor systems for haul trucks.(k)by using synthetic or re-vegetative covers.(l)by restricting vehicular travel to established paved roads.(m)by watering or chemical stabilisation of unpaved roads as often as necessary to minimise re-entrainment of fugitive particulate matter from the road surface, or paving of roads.Part VII — Opacity Measurement GuidelinesThe darkness of smoke is determined by comparing the shade of smoke to the shades on a Ringelmann Chart which consists of four squares with grids, which denoted shade 1 to shade 4. The darkness covered in each of these four squares represents twenty percent, fourty percent, sixty percent and eighty percent opacity respectively. Ringelmann shade O is completely white and shade 5 is totally black. Therefore, Ringelmann shade 1 corresponds to smoke of twenty percentopacity.The regulations stipulate that dark smoke emission from any chimney or relevant plant must not exceed:-i)8 minutes in any period of four hours; orii)3 minutes continuously at any one time.Part VIII - Guideline on sources of fugitive emission air pollutantsThe following are the sources of fugitive emissions:(a)construction activities;(b)storage and handling, including loading and unloading, of materials such as bauxite, alumina, gypsum, or Portland cement or the raw materials therefore;(c)mining and quarrying activities;(f)tailings piles and ponds;(g)demolition activities;(h)blasting activities; and(i)Sandblasting operations.Part IX — Occupational Air Quality GuidelinesThe owner or operator shall control the exposure to employees by:-1)limiting the amount of harmful substances used which may pollute the indoor environment;2)limiting the number of employees who will be exposed or may be exposed;3)limiting the period during which an employee will be exposed or may be exposed;4)introducing engineering control measures for the control of exposure, which may include the following:a.Process separation, automation or enclosure.b.Installation of local extraction ventilation systems to process and equipment.c.tools for the control of emission of an air borne hazardous substances.e.Substituting hazardous substances with less hazardous ones.5)Providing suitable respiratory protective breathing equipment.6)Where respiratory protective equipment is provided, the employer shall ensurea)that the relevant equipment is capable of controlling the exposure to below the Occupational Exposure Level for the relevant harmful substance;b)that the relevant equipment is correctly selected and properly used;c)that information, instructions, training and supervision which is necessary with regard to the use of the equipment is known to the employees; andd)that the equipment is kept in good condition and efficient working orderPart X — Guideline on NOxsa)Existing fuel burning equipment shall be presumed to meet the definition of Best Available Technology if the owner or operator proves to the satisfaction of the Authority that the emission levels in the Third Schedule can be met.b)If the owner or operator does not prove as described in paragraph (a) of this section, Best Available Technology shall be installed by the owner with the goal of achieving the presumptive emission limits as set forth in the Third Schedule.c)If actual achievable emission levels following installation of such combustion modification technology are greater than the presumptive emission limits in the Third Schedule these actual emission levels will become Best Available Technology for those sources.d)If the owner or operator does not comply with paragraphs a or b of this section, alternative NO control technology and emission X limitation proposals shall be required and approved by the Authority.e)Compliance with the emission levels as determined above is based upon twenty-four hour rolling averaging period, Continuous Emission Monitoring Systems approved by the Authority will be used.Part XI — contents of a compliance planA compliance plan shall include but not limited to: –(a)a description of the current compliance status of the facility with respect to all applicable requirements, including all sources that exceed emission standards or targets or are predicted to exceed ambient air quality monitoring locations at which ambient air quality standards or guideline concentrations are exceeded, and any other administrative or other requirements that have not been satisfied;(b)a statement of the methods used to determine the facility's compliance status, including a description of all monitoring, record keeping, reporting and test methods, and any other information necessary to verify compliance with or to enforce applicable requirements;(c)a statement that the facility will continue to comply with each applicable requirement in respect of which compliance is currently achieved at the facility; and(d)in respect of each applicable requirement for which compliance is not currently achieved at the facility –(i)a detailed statement of how the facility will achieve compliance;(ii)a proposed compliance schedule setting forth the remedial measures to be taken, including a sequence of actions with milestones leading to compliance;(iii)if the facility is subject to a control order, the proposed schedule of remedial measures shall incorporate the order and shall be at least as stringent as the order;(iv)a schedule for submission of progress reports to the Authority at least once in every six months or more frequently if so required by the licence; and(v)a schedule for the submission of compliance reports to the Authority, at least once in every six months or more frequently if so required by the licence, indicating what, if any, progress has been made in relation to the schedule and the milestones.Part XII - Guideline for Assessment of Air Quality(1)Such assessments, firstly, shall establish actual levels of the given pollutants based on representative measurements, surveys or assessments.(2)For areas where actual levels of a given pollutant are above the standard values stipulated for that pollutant, the preliminary assessment shall include the following:a)establish source contributions to ambient air concentrations of the pollutant of concern;b)characterize future trends in ambient air concentrations of the pollutant of concern given a “business as usual” scenario;c)identify emission reduction measures suited to reduce contributions from major sources and associated time frames for implementation;d)assess the environmental benefit of measures to reduce and maintain air quality within limit values;e)determine the technical feasibility of measures to reduce and maintain air quality within limit values;f)evaluate the economic viability of measures to reduce and maintain air quality within limit values;g)assess the social acceptability and policy applicability measures to reduce and maintain air quality within standard values;h)prioritize emission reduction measures on the basis of their environmental benefits, technical feasibility, economic viability, and social acceptability;i)determine the time required to reduce air pollutant concentrations to fall within the standard values taking into account the implementation of prioritized emission reduction measures.Part XIII — Guideline on Results of Emissions Sampling and AnalysisResults of emissions sampling and analysis shall be as follows-(1)Results of emissions sampling and analysis shall be expressed in metric units consistent with the emission standards or targets set out in these Regulations or in the conditions, if any, imposed in the relevant licence.(2)Measurements of emissions into the atmosphere from stacks, vents or other air pollutant sources, which are reported to the Authority whether voluntarily or as a requirement of these Regulations or of any condition of a licence, shall be reported to the Authority in the form of a test report that includes the following information –(a)the testing methods and results, certified as being true, accurate, and in compliance with these Regulations by the person responsible for conducting the emissions test;(b)the name and location of the facility, the name and location of the source tested, the purpose of the tests, the test participants and their titles, and the date of the performance test;(c)a summary of the results, setting out emission rates for each pollutant and a comparison with applicable emission standards or targets and with any emission limits in the licence;(d)a description of the facility tested and the type of process and control equipment utilised;(e)a description of the process sampled and associated emission control devices referenced to process, and locations at which sampling took place consistent with information provided in the relevant licence application or licence, as the case may be;(f)a schematic of each location sampled including duct diameter, direction of flow, dimensions to nearest upstream and downstream disturbances, including the number of duct diameters, location and configuration of the sampling ports, nipple length and port diameters, and the number and configuration of traverse points;(g)confirmation that sampling locations meet the criteria in the test methods set out in the Eleventh Schedule, or the reasons why those locations do not meet such criteria and a discussion of the effect on results;(h)a discussion of special traversing or measurement schemes (if any);(i)a process flow diagram, maximum design capacities, a fuel analysis and heat value for heat input rate determinations, process and control equipment operating conditions, stack height, exit diameter, volumetric flow rate, exit temperature, exit velocity and a discussion of variations from normal plant operations;(j)a description of the sampling methods used;(k)a brief discussion of the analytical procedures, with justifications for any variance from prescribed method procedures;(l)the number of sampling points, time per point and the total sampling time per run;(m)a cross-sectional diagram showing sampling points and a diagram of the sampling train;(n)a diagram showing stack dimensions, sampling location and the distance from the nearest flow disturbance upstream and downstream, respectively, of the sampling points;(o)results and calculations in units consistent with the applicable emission limits with one complete calculation using actual data for each type of test performed;(p)the tabulated data and results of the process weight rate or heat input rate in metric units, the referenced or derived conversion factors, the stack gas flow rate, the measured emissions given in units consistent with the applicable emission limits, the visible emissions observations or six consecutive minute average continuous opacity monitor readings, and the average value of emissions from any continuous gaseous emissions monitoring system in units consistent with applicable emission limits;(q)quality assurance procedures;(r)appendices with raw data and details of calculations, including –(i)raw production data signed by the source official;(ii)photocopies of all raw data;(iii)a chain of custody report; and(iv)copies of all calibration data;(s)for particulate matter tests, copies of visible emissions evaluations or opacity monitor readings, and, for gaseous pollutant tests, copies of any continuous gaseous emissions monitoring system readings during the tests.Part XIV: Minimum Stack Height RequirementsINSERT IMAGEHg = H + 1.5L; whereHg = Good Engineering Practice stack height measured from the ground level elevation at the base of the stackH = Height of nearby structure(s) above the base of the stackL= Lesser dimension, height(h) or width(w), of nearby structures‘Nearby Structures’ = Structures within/touching a radius of 5L but less than 800mPart XV – GUIDELINES ON AIR DISPERSION MODELLING ASSESSMENT
(a)as part of the baseline ambient air quality assessment report to be submitted once at the first renewal.(b)In order to determine the impacts of emissions from stationary sources at a certain location on will carry out an air dispersion assessment on the facility.(c)In determination of the fall out point of an existing facility the input data into the dispersion model shall its actual operating parameters.(d)Determination of the fall out point of a proposed facility, the input data into the dispersion model shall be its designed parameters.(e)The dispersion modeling report to be submitted to the Authority shall be in the dispersion modelling report format prescribed under Part…….. of the Fifth Schedule.(f)Dispersion modeling assessment referred to above shall be carried out using the dispersion models prescribed under part….. of the methods of test and analysis.SEVENTH SCHEDULE
ACCEPTABLE EMISSION CONTROL TECHNOLOGIES AND STRATEGIES
List of Acceptable Emission Control Technologies
| | Air Pollutants | Emission Control technologies and strategies | Remarks |
|---|
| 1. | Particulate Matter | Mechanical collectors (dust cyclones, multi cyclones) | |
| | | Electrostatic precipitator | |
| | | Filter bags (bag houses) | |
| | | Particulate scrubbers | |
| 2. | Nitrogen Oxides (Nox) * | Low NOx burners | |
| | | Selective catalytic reduction(SCR) | |
| | | Selective non-catalytic reduction(SNCR) | |
| | | NOx scrubbers | |
| | | Exhaust gas recirculation | |
| | | Catalytic converter | |
| 3. | Volatile Organic Compounds (VOC), hydrocarbons | Adsorption systems, such as activated carbon | |
| | | Flares | |
| | | Thermal oxidizers | |
| | | Catalytic oxidizers | |
| | | Biofilters | |
| | | Absorption (scrubbing) | |
| | | Cryogenic condensers | |
| 4. | Sulphur Oxides (SOx) | Wet scrubbers | |
| | | Dry scrubbers | |
| | | Flue gas desulphurization | |
| 5. | Carbon Oxides | Thermal oxidizers | |
| 6. | Hydrogen Sulphides | Absorption (scrubbing) | |
| 7. | Hydrogen Chloride | Dry Scrubbers, | |
| | | Adsorption systems, such as activated carbon | |
| 8. | Dioxins and Furans | Cyclone | |
| | | Electrostatic precipitator | |
| | | Filter bag | |
| | | Wet scrubber | |
| | | Quenching and subsequent wet scrubber | |
| | | Catalytic oxidation (selective catalytic reaction) | |
| | | Catalytic Filter bag | |
| | | Dry absorption in resins (carbon | |
| | Air Pollutants | Emission Control technologies and strategies | Remarks |
| | | particles dispersed in a polymer matrix) | |
| | | Entrained flow reactor with added activated carbon or coke/lime or limestone solutions and subsequent Filter bag Filter bag | |
| | | Fixed bed or circulating fluidized bed reactor, adsorption with activated carbon or open hearth coke | |
| 9. | Metals (Hg, Pb,) | Sorbent Injection Technology | |
| | | Electro-Catalytic Oxidation(ECO) | |
| | | K-Fuel | |
| 10. | Particulate matter, Sulphur oxides, nitrogen oxides | Cleaner fuels, Sustainable aviation fuels, raw materials substitution, processed change or modification | |
| 10. | Any other technology approved by the Authority from time to time |
* NotesBest Available Technology (BAT) for this category of equipment will consist of combustion modification technology including either:(a)low NO burner technology with low excess air(b)Air if technically feasible; or(c)flue gas re-circulation with low excess air.EIGHTH SCHEDULE
Emission monitoring report1.Name of Industry...................................2.Name of contact person.............................3.Position of contact person.........................4.Business registration No...........................5.Address............................................Telephone No. ……………………………….. Fax.......................Email:................................................6.Source of pollutants..................................................................................................................................................................................................................................................................................................7.Emission concentrations and Quantities (mg/l, kg/day)....................................................................................................................................................................................................................................................................................................................................................................................8.Emission Control Technology...................................................................................................................................................................................................................................................................................................................................................................................9.Status of Compliance to Emission Limits.......................................................................................................................................................................................................................................................................................................................................................................Signature…….………………………… dated…… day of………………..……… 20……Position…………………………………………10.Official use onlyRecommendations.......................................................................................................................................................................................................................................................................................................................................Dated this…………………. day of……………. 20…….Signature……………………………………(Seal)NINTH SCHEDULE
Emission LicencesForm I:Application Form for Emission Licence1.Name of Company.....................................................................2.AddressFax………………………………… E-mail:...............................................................Name of Contact Person..................................................................3.LocationLR No…………… Street………….… Area………….… Sub-County…………..…….Town……………… County…………………..4.Activity............................................................................5.Duration:From……….…. day/…………………...………..…………./month…………………./year7.Stack Emissions(a)Normal operational conditions(i)………………………………………………………………………………….………(ii)………………………………………………………….………………………………(iii)…………………………………………………….……………………………………(iv)……………………………………………………….…………………………………(b)Start-up, maintenance and shut-down conditions(i)………………………………………………………………………………….………(ii)………………………………………………………….………………………………(iii)…………………………………………………….……………………………………(iv)……………………………………………………….…………………………………8.Other relevant information on non-point sources or fugitive emissions any other operating requirements relating to atmospheric discharges………………………9.Ambient air quality reporting(i)on-site point source emission measurement10.Anticipated Date of compliance……. day…… month………. year.11.Road map to compliance with standards under Seventh Schedule(i)………………………………………………………………………………….………(ii)………………………………………………………….………………………………(iii)…………………………………………………….……………………………………(iv)……………………………………………………….…………………………………Signature of Applicant……………………………….. Date……………………………Position……….………………………………………FOR OFFICIAL USE13.Review Period ( To be filled out by the Authority)From............ day/.............. /month................... /yearFrom............ day/.............. /month................... /yearFrom............ day/.............. /month................... /yearFrom............ day/.............. /month................... /yearApproved/Not approved………………………………………..…………………………..................Dated this…………………. day……………………………. of 20…….Signature…………………….……………………(Seal)Form II Reporting on Emission Limit Exceedence1.Name of Company.............................................................................2.AddressTel……………… Fax……………… Email……………...Name of Contact Person....................................................................3.LocationLR No…………… Street……………… Area………..…… Division……………….….Town…………..……. District………………..…….. Province……………………………4.Source(s) that Caused the Excess Emissions.a)………………………………...…………………………………………………b)……………………………………………………...……………………………c)………………………………………………...…………………………………5.First observation of the excess emissions.a)The time………………. date…………….……..……….. of …………….. Year6.The cause and expected duration of the excess emissions.(a)Cause………………………………………………………………(b)Expected Duration of Exeedence (No.)………… hours (No.)…………… days (No.)…………… months7.Estimated rate of emissions for sources subject to numerical emission limitations…………………..(mg/m3) (expressed in the units of the applicable emission limitation) and the operating data and calculations used in determining the magnitude of the excess emissions8.The proposed corrective actions and schedule to correct the conditions causing the excess emissions.a)……………………………………………………….…………………………b)……………………………………………………………….…………………9.The test methods listed under the Fifth Schedule or any other approved by the Authority shall be used. The results of the tests shall be submitted to the Authority within 45 days after completing the test.Signature of Applicant………………………….……….. Date……………………………Position……….………….………………………………Form III Provisional Emission LicenceTHE ENVIRONMENTAL MANAGEMENT AND COORDINATION ACT
PROVISIONAL EMISSION LICENCE
Application Reference No.………………………………………………..Licence No.………………………………………......................................FOR OFFICIAL USEThis is to certify that the application for emission into the atmosphere received from………………………………. (name of applicant) of…………………………(address) to the National Environment Management Authority in accordance with Air Quality Regulations for………………………………………………………………… (facility) located at………………………………………………………………………………… (locality, district and province) has been evaluated and a licence is hereby issued for emission, subject to the attached conditions.Dated this………………………..……….. day of…………………………… 20……….Signature:………………………………(Official Stamp)Director GeneralThe National Environment Management AuthorityConditions of Licence1.This Licence is valid for a period of……………………………………. from the date hereof.2.Frequency of Monitoring (Daily/Weekly/Monthly/Quarterly)………………………3.…………………………………………………………………………………………4..…………………………………..……………………………………………………Form IV Application for Initial Emission Licence1.Name of Company................................................................2.AddressBox..........................................................................Tel………….………………. Fax……………… E-mail:....................................................Name of Contact Person..............................................................3.LocationLR No…………… Street…………… Area………………… Division………………….Town………………. District………………………….. Province…………………………4.Type of Industry...................................................................5.Name(s) of emitting Equipment.....................................................................................................................................................................................................................................................................................................................................................................................................6.Site Plan Layout, (attach sketch)(a)Distance of the equipment to the nearest building…………………………………...(b)Height of the above referred building…………………………………………………(c)Nearest sensitive area or facility……………………………………………….………(d)Immission (fall-out) point………………………………………………………………7.Operating Emission levels(i)………………………………………………………………………………(ii)………………………………………………………………………………(iii)………………………………………………………………………………(iv)………………………………………………………………………………8.Proposed Emission Control Mitigation Measures(v)………………………………………………………………………………(vi)………………………………………………………………………………(vii)………………………………………………………………………………(viii)…………………………………………………………………………..9.Additional information required………………………….……………………………………10.Start-up, and shut-down of the equipmenta)Methods.................................................................b)Expected Frequency of Occurence..............................................c)Duration of occurrence................................................................d)Projected emitted Pollutants(i)……………………………………………………………………..………(ii)……………………………………………………………………..………(iii)……………………………………………………………………..………(iv)……………………………………………………………………..………11. (a)Nature of emissions (gaseous, particulates)(i)…………………………………………….…………………………………………(ii)………………………………………………………………………………………(iii)………………………………………………………………………………………(iv)……………………………………………………………….………………………(b)Concentration of the emissions(i)…………………………………………….…………………………………………(ii)………………………………………………………………………………………(iii)………………………………………………………………………………………Signature of Applicant………………………..……….. Date……………………………Position……….………………………………………FOR OFFICIAL USEApproved/Not approved..........................................................Dated this…………………. day…………………………………………. of 20………..….Signature……………………………………(Seal)Form V Initial/Renewal Emission LicenceTHE ENVIRONMENTAL MANAGEMENT AND COORDINATION ACT
EMISSION LICENCEApplication Reference No.………………………………………………..Licence No. ……………………………………….......................................FOR OFFICIAL USEThis is to certify that the application for emission into the atmosphere received from………………………………. (name of applicant) of…………………………………….. (address) to the National Environment Management Authority in accordance with Air Quality Regulations for…………………………………………………………………………………… (facility) located at……………………………………………………………………… (locality, district and province) has been evaluated and a licence is hereby issued for emission, subject to the attached conditions.Dated this………………………..……….. day of………………...………… 20……….Signature:…………………………………(Official Stamp)Director GeneralThe National Environment Management AuthorityConditions of Licence1.This Licence is valid for a period of…………………………... from the date hereof.2.Frequency of Monitoring (Daily/Weekly/Monthly/Quarterly)……………………….3.…………………………………………………………….…………………………...4.…………………………………………………………………………………………5.………………………..………………………………………………………………..FORM VI Application for Renewal of Emission Licence1.Name of industry...............................................2.Name of contact person.................................................Name of contact person...................................................3.Position of contact person........................................................4.Business registration No....................................................................5.Previous Licence No..........................................................6.Address..........................................................................Telephone No.…………………… Fax………………. Email:...........................................7.Emission source(s)...................................................................................................................................................................................................................................................................................................................................................................................................8.Emission control measures (Environmental Management Plan)Signature of Applicant…………………………….…….. Date……………………………Position……….………………………………………Official useApproved/Not approved…………………………………………………….Dated this…………………. day…………………………..……. of 20…….Signature……………………………………(Seal)FORM VII: Notification of Transfer of Emission Licence1.0.Details of Current LicenceName of current emission licence holder.......................................PIN No.......................................................................Address......................................................................Telephone No.……………………………..…………Fax ..........................................Email:......................................................................Application No. of current emission licence.........................................Date of issue of the current emission licence........................................2.Details of the Transferee2.1.Name of facility.................................................................2.2.PIN No.................................................................2.5.Address..........................................................2.6.Telephone No.………………………………… Fax.............................................2.7.Email:..............................................................2.8.Name of contact person..........................................................3.0.Capacity of transferee to operate the facility (financial, technological, manpower)(Conditions)..............................................................................................................................................................................................................................................................................4.0.Reasons for transfer of licence..................................................................................................................................................................................................................................................................................................................5.0.Declaration by transferor and transfereeIt is hereby notified that……………………………… of …………………………. on this day of………………………………transferred emission licence No.…………………..to ………………. of………………………………who will assume his responsibility for all liability under this project.Name……………………………………….. Name………………………………………..Address…………………………………….. Address……………………………………..Signed……………………………………… Signed………………………………………Date………………………………………… Date…………………………………………6.0.For Official UseApproved/Not Approved…………………………………………………………………..………………………………………………………………………………………………Comments……………………………………………………………………………..……………………………………………………………………………………………………Officer…………………………………….Signature……………………….Date………...FORM VIII: Certificate of Transfer of Emission LicenceThis is to certify that the Emission Licence No.………………. issued on…………………… (date) to………………………….… (name of previous holder) of………………………………… (address) regarding……………… (type of facility) whose activities include…………located at……………… (town, district) has been transferred to………………………………………… (name of new holder)……………………………………………………… (nature of variation) with effect from …………………….(date of transfer) in accordance with the provisions of the Act.Dated this…………………. day of……………. 20…….………….Signature……………………………………(Seal)FORM IX: Application of Variation of Emission Licence1.Previous Applications(If any.............................................................................................................................................................................................................................................2.1.Name of Industry.................................................................2.2.Name of contact person.....................................................................2.3.Position of contact person.............................................................2.4.Business registration No.........................................................................2.5.Address...............................................................2.6.Telephone No. …………………………………Fax ....................................................2.7.Email:..........................................................................3.Details of Current Emission Licence3.1.Name of current holder........................................................3.2.No. of current emission licence .....................................................3.3.Date of issue of the current emission licence..................................................4.1.Current emission limits..............................................................................................................................4.2.Proposed variations..........................................................4.3.Reasons for variations.......................................................4.4.Describe the atmospheric effects.................................................................4.5.Describe the effects on ambient air quality.....................................................4.6.Describe the effects on the performance of the equipment...........................................4.7.Describe the measures proposed to reduce emission impacts.......................................5.0.Declaration by ApplicantI hereby certify that the particulars given above are correct and true to the best of my knowledge and belief. I understand the emission licence may be suspended, varied or cancelled if any information given above is false, misleading, wrong or incomplete.Name………………………………… position…………………… signature……………On behalf of…………………………….……….…………… (company name and seal)………………………..date…………………………..……….Official useApproved/Not approved.....................................................Dated this…………………. day…………………….of 20…….Signature……………………………………(Seal)FORM X: Certificate of Variation of Emission LicenceThis is to certify that the emission Licence No. …………………….………. issued on ……………………(date) to………………………..…………… (name of firm) of……………………………(address) regarding……………………… (type of facility) whose activities include………………………………………………………… located at…………………………… (town, district) has been varied to………………………………………………………………………………………………………………………………………………………………………………………………………………………………………………………… (nature of variation) with effect from ……………………. (date of variation) in accordance with the provisions of the Act.Dated this…………………. day ……………. of 20…….Signature……………………………………(Seal)Form XI: Register of Emission Licence| Type of Industry | Name of proponent | Location of facility | Emission licence No. | Date of Issue | Conditions attached to Licence | Licence Serial No. if | Status of Licence | Name of filing officer | Date and Signature of filing officer | Remarks |
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TENTH SCHEDULE
RECORD OF POLLUTION EXPOSURE RESULTS
Form I: Record of Pollution Exposure Results| | Record of Pollution Exposure Assessment |
| 1. | Name of facility…………………………………………….. |
| 2. | Contact Address…………………………………………….. |
| | Contact person…………………………………………….. |
| 3. | Location …………………………………………….. |
| 4. | Date…………………………………………….. |
| 5. | Time of the assessment……………………………. |
| 6. | Type of Work Place…………………………………………….. |
| 7. | Measuring methods(i)....................................................................................(ii)...................................................................................(iii)..................................................................................(iv).................................................................................. |
| 8. | Type of measurements (e.g. gases, dust, fumes….)(i)………………………………………………..(ii)………………………………………………..(iii)……………………………………………….. |
| 9. | Tabulated results of the measurements and compliance limits | | | |
| | Pollutant | Measured result | Exposure limit | Remarks |
| | (i) | | | |
| | (ii) | | | |
| | (iii) | | | |
| | (iv) | | | |
| 9. | Number of persons exposed……………………… | | | |
| 10. | Recommended remedial measures(i)………………………………………………..(ii)………………………………………………..(iii)……………………………………………….. |
| 11. | Name of the assessor……………………………..Signature of the Assessor…………………………Organization/Company/Firm….………………………………….. |
ELEVENTH SCHEDULE
METHODS OF TEST AND MEASUREMENT OF AIR POLLUTANTS
List of methods of test and measurement of air pollutants| Standard |
| 1 | KS ISO 10155 Stationary source emissions -- Automatedmonitoring of mass concentrations of particles -- Performance characteristics, test methods and specifications |
| 2 | KS ISO 10397 Stationary source emissions -- Determination of asbestos plant emissions -- Method by fibre count measurement |
| 3 | KS ISO 10780: Stationary source emissions -- Measurement of velocity and volume flow rate of gas streams in ducts |
| 4 | KS ISO 10849: Stationary source emissions -- Determination of the mass concentration of nitrogen oxides -- Performance characteristics of automated measuring systems |
| 5 | KS ISO 11338-1: Stationary source emissions -- Determination of gas and particle-phase polycyclic aromatic hydrocarbons -- Part 1: Sampling |
| 6 | KS ISO 11338-2: Stationary source emissions -- Determination of gas and particle phasepolycyclic aromatic hydrocarbons -- Part 2: Sample preparation, clean-up and determination |
| 7 | KS ISO 11564: Stationary source emissions -Determination of the mass concentration of nitrogen oxides - Naphthylethylenediamine photometric method |
| 8 | KS ISO 11632: Stationary source emissions -Determination of mass concentration of sulfur dioxide - Ion chromatography method |
| 9 | KS ISO 12039: Stationary source emissions - Determination of carbon monoxide, carbon dioxide and oxygen - Performance characteristics and calibration of automated measuring systems |
| 10 | KS ISO 12141: Stationary source emissions - Determination of mass concentration of particulate matter (dust) at low concentrations - Manual gravimetric method |
| 11 | KS ISO 14164: Stationary source emissions - Determination of the volume flow rate of gas streams in ducts - Automated method |
| 12 | KS ISO 15713: Stationary source emissions - Sampling and determination of gaseous fluoride content |
| 13 | KS ISO 7708: Air quality - Particle size fraction definitions for health-related sampling |
| 14 | KS ISO 11041: Workplace air - Determination of particulate arsenic and arsenic compounds and arsenic trioxide vapour - Method by hydride generation and atomic absorption spectrometry |
| 15 | KS ISO 11174: Workplace air - Determination of particulate cadmium and cadmium compounds - Flame and electrothermal atomic absorption spectrometric method Standard |
| 16 | KS ISO 15202-1: Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 1: Sampling |
| 17 | KS ISO 15202-2: Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 2: Sample preparation |
| 18 | KS ISO 15202-3: Workplace air - Determination of metals and metalloids in airborne particulate matter by inductively coupled plasma atomic emission spectrometry - Part 3: Analysis |
| 19 | KS ISO 15767: Workplace atmospheres - Controlling and characterizing errors in weighing collected aerosols |
| 20 | KS ISO 16107: Workplace atmospheres - Protocol for evaluating the performance of diffusive samplers |
| 21 | KS ISO 16200-1: Workplace air quality -- Sampling and analysis of volatile organic compounds by solvent desorption/gas chromatography -- Part 1: Pumped sampling method |
| 22 | KS ISO 16200-2: Workplace air quality -- Sampling and analysis of volatile organic compounds by solvent desorption/gas chromatography -- Part 2: Diffusive sampling method |
| 23 | KS ISO 16702: Workplace air quality -- Determination of total isocyanate groups in air using 2-(1-methoxyphenyl) piperazine and liquid chromatography |
| 24 | KS ISO 16740: Workplace air -- Determination of hexavalent chromium in airborne particulate matter -- Method by ion chromatography and spectrophotometric measurement using diphenyl carbazide |
| 25 | KS ISO 17733: Workplace air -- Determination of mercury and inorganic mercury compounds -- Method by cold-vapour atomic absorption spectrometry or atomic fluorescence spectrometry |
| 26 | KS ISO 17734-1: Determination of organonitrogen compounds in air using liquid chromatography and mass spectrometry -- Part 1: Isocyanates using dibutylaminederivatives |
| 27 | KS ISO 17734-2: Determination of organonitrogen compounds in air using liquid chromatography and mass spectrometry -- Part 2: Amines and aminoisocyanates using dibutylamine and ethyl chloroformate derivatives |
| 28 | KS ISO 20552: Workplace air -- Determination of mercury vapour -- Method using gold-amalgam collection and analysis by atomic absorption spectrometry or atomic fluorescence spectrometry |
| 29 | KS ISO 4224 : Ambient air -- Determination of carbon monoxide -- Non-dispersive infrared spectrometric method |
| 30 | KS ISO 6767: Ambient air -- Determination of the mass concentration of sulfur dioxide -- Tetrachloromercurate (TCM)/pararosaniline method |
| 31 | KS ISO 7996: Ambient air -- Determination of the mass concentration of nitrogen oxides -- Chemiluminescence method Standard |
| 32 | KS ISO 8186: Ambient air -- Determination of the mass concentration of carbon monoxide -- Gas chromatographic method |
| 33 | KS ISO 10312: Ambient air -- Determination of asbestos fibres -- Direct transfer transmission electron microscopy method |
| 34 | KS ISO 10313: Ambient air -- Determination of the mass concentration of ozone -- Chemiluminescence method |
| 35 | KS ISO 10473: Ambient air -- Measurement of the mass of particulate matter on a filter medium -- Beta-ray absorption method |
| 36 | KS ISO 10498: Ambient air -- Determination of sulfur dioxide -- Ultraviolet fluorescence method |
| 37 | KS ISO 12884: Ambient air -- Determination of total (gas and particle-phase) polycyclic aromatic hydrocarbons -- Collection on sorbent-backed filters with gas chromatographic/mass spectrometric analyses |
| 38 | KS ISO 13794: Ambient air -- Determination of asbestos fibres -- Indirect-transfer transmission electron microscopy method |
| 39 | KS ISO 13964: Air quality -- Determination of ozone in ambient air -- Ultraviolet photometric method. |
| 40 | KS ISO 14965: Air quality -- Determination of total non-methane organic compounds -- Cryogenic pre-concentration and direct flame ionization detection method |
| 41 | KS ISO 14966: Ambient air -- Determination of numerical concentration of inorganic fibrous particles -- Scanning electron microscopy method |
| 42 | KS ISO 16362: Ambient air -- Determination of particle-phase polycyclic aromatic hydrocarbons by high performance liquid chromatography |
| 43 | KS ISO 7168-1: Air quality -- Exchange of data -- Part 1: General data format |
| 44 | KS ISO 7168-2: Air quality -- Exchange of data -- Part 2: Condensed data format |
| 45 | KS ISO 9169: Air quality -- Definition and determination of performance characteristics of an automatic measuring system |
| 46 | KS ISO 11222: Air quality -- Determination of the uncertainty of the time average of air quality measurements |
| 47 | KS ISO 13752: Air quality -- Assessment of uncertainty of a measurement method under field conditions using a second method as reference |
| 48 | KS ISO 14956: Air quality -- Evaluation of the suitability of a measurement procedure by comparison with a required measurement uncertainty |
| 49 | KS ISO 20988: Air quality -- Guidelines for estimating measurement uncertainty |
| 50 | KS ISO 16622: Meteorology -- Sonic anemometers/thermometers -- Acceptance test methods for mean wind measurements |
| 51 | KS ISO 17713-1: Meteorology -- Wind measurements -- Part 1: Wind tunnel test methods for rotating anemometer performance Standard |
| 52 | KS ISO 17714: Meteorology -- Air temperature measurements -- Test methods for comparing the performance of thermometer shields/screens and defining important characteristics |
| 53 | KS ISO 16000-1: Indoor air -- Part 1: General aspects of sampling strategy |
| 54 | KS ISO 16000-2:Indoor air -- Part 2: Sampling strategy for formaldehyde |
| 55 | KS ISO 16000-3: Indoor air -- Part 3: Determination of formaldehyde and other carbonyl compounds -- Active sampling method |
| 56 | KS ISO 16000-4: Indoor air -- Part 4: Determination of formaldehyde -- Diffusive sampling method |
| 57 | KS ISO 16000-5: Indoor air -- Part 5: Sampling strategy for volatile organic compounds (VOCs) |
| 58 | KS ISO 16000-6: Indoor air -- Part 6: Determination of volatile organic compounds in indoor and test chamber air by active sampling on Tenax TA sorbent, thermal desorption and gas chromatography using MS/FID |
| 59 | KS ISO 16000-8: Indoor air -- Part 8: Determination of local mean ages of air in buildings for characterizing ventilation conditions |
| 60 | KS ISO 16000-9: Indoor air -- Part 9: Determination of the emission of volatile organic compounds from building products and furnishing -- Emission test chamber method |
| 61 | KS ISO 16000 -10: Indoor air -- Part 10: Determination of theemission of volatile organic compounds from building products and furnishing --Emission test cell method |
| 62 | KS ISO 16000-11: Indoor air -- Part 11: Determination of theemission of volatile organic compounds from building products and furnishing --Sampling, storage of samples and preparation of test specimens |
| 63 | KS ISO 16017-1: Indoor, ambient and workplace air – Sampling and analysis of volatile organic compounds by sorbent tube/thermal desorption/capillary gaschromatography -- Part 1: Pumped sampling |
| 64 | KS ISO 16017-2: Indoor, ambient and workplace air -- Sampling and analysis of volatile organic compounds by sorbent tube/thermal desorption/capillary gaschromatography -- Part 2: Diffusive sampling |
| 65 | KS ISO 4219: Air quality - Determination of gaseous sulphur compounds in ambient air - Sampling equipment |
| 66 | KS ISO 4220: Ambient air - Determination of a gaseous acid air pollution index -Titrimetric method with indicator or potentiometric end-point detection. |
| 67 | KS ISO 4221: Air quality - Determination of a mass concentration of sulphur dioxide in ambient air - Thorin spectrophotometric method |
| 68 | KS ISO 4225: Air quality - General aspects - Vocabulary |
| 69 | KS ISO 4226: Air quality - General aspects - Units of measurement Standard |
| 70 | KS ISO 6768: Ambient air - Determination of the mass concentration of nitrogen dioxide - modified Griess - Saltzman method |
| 71 | KS ISO 7934: Stationary source emissions - Determination of the massconcentration of sulphur dioxide - Hydrogen peroxide / barium perchlorate – Thorinmethod |
| 72 | KS ISO 8518: Workplace air - Determination of particulate lead and leadcompounds - Flame or electrothermal atomic absorption spectrometric method |
| 73 | KS ISO 8672: Air quality - Determination of the number concentration of airborneinorganic fibres by phase contrast optical microscopy - Membrane filter method |
| 74 | KS ISO 8756: Air quality - Handling of temperature, pressure and humidity data |
| 75 | KS ISO 8760: Workplace air - Determination of mass concentration of carbonmonoxide - Method using detector tubes for short -term sampling with direct indication |
| 76 | KS ISO 8761: Workplace air - Determination of m ass concentration of nitrogendioxide - Method using detector tubes for short -term sampling with direct indication |
| 77 | KS ISO 8762: Workplace air - Determination of vinyl chloride - Charcoal tube / gaschromatographic method |
| 78 | KS ISO 9096: Stationary source emissions - Determination of the concentration and mass flow rate of particulate material in gas-carrying ducts – Manual gravimetric method |
| 79 | KS ISO 9359: Air quality - Stratified sampling method for assessment of ambient airquality |
| 80 | KS ISO 9486: Workplace air - Determination of vaporous chlorinated hydrocarbons- Charcoal tube / solvent desorption / gas chromatographic method |
| 81 | KS ISO 9487: Workplace air - Determination of vaporous aromatic hydrocarbons -Charcoal tube / solvent desorption / gas chromatographic method |
| 82 | KS ISO 9835: Ambient air - Determination of a black smoke index |
| 83 | KS ISO 9855: Ambient air - Determination of the particulate lead content ofaerosols collected on filters - Atomic absorption spectrometric method |
| 84 | KS ISO 10396: Stationary source emissions - Sampling for the automated determination of gas concentrations |
| 85 | KS 2060: Motor gasolines - Specification |
| 86 | KS 1515: Code of practice for inspection of road vehicles |
| 87 | KS 03-1289: Specification for illuminating kerosene |
| 88 | KS 1309-1: Specification for diesel fuels - Part 1: Automotive gas oil. |
| 89 | KS 03-1309-2: Specification for diesel fuels - Part 2: Industrial diesel oil (IDO). |
| 90 | KS 03-1310: Specification for fuel oils |
| 91 | KS 03-91: Specification for liquefied petroleum gases (LPG). |
TWELFTH SCHEDULE
ACCEPTALBLE MOBILE EMISSION CONTROL TECHNOLOGIES
Mobile SourcesThe aim of these guidelines is without sacrificing performance, improve engine performance through understanding pollutant formation mechanism, ensure precise control of engine parameters, such as air/fuel ratio, spark timing, airflow, optimize on exhaust gas treatment.List of mobile emission control technologies| | Pollutant | Control measures |
| | NOX Exhaust | Exhaust Gas Recirculation (EGR) Valves |
| | HC, CO Exhaust | Three Way Catalyst (TWC), 2nd Air Pumps |
| | Evaporative Emissions | Canisters |
| | Crankcase e/m s Positive | Crankcase Valve PCV valves |
| | On Board Display (Obd-2) | Precise a/f control |
| | | Dual Oxygen Sensors |
| | | Individual cylinder a/f control |
| | | Adaptive fuel control |
| | | Electronic throttle control |
| | | Improved induction |
| | | Heat optimized exhaust system |
| | | Leak-free exhaust system |
| | Particulate matter | Diesel Oxidation Catalyst (DOC) |
| | | Diesel particulate filter (DPF) |
| | | Flow Through Filter (FTF) |
| | | Retrofit, Repower, or Replace |
And any other technology that may be approved by the Authority from time to timeList of evaporative emission control technologies| | Cause | Measure |
| 1 | Diffusion | Precise purge control and optimization of canister structure |
| 2 | Leakage | Modification of designs for locking parts and fuel filler cap |
| 3 | Permeation | Material changes for hoses in fuel line |
| 4 | Evaporation while fueling | Improve sealing by putting elastic cap around the nozzle of fueling gun |
| 5 | Fuel Temperature | Reduce the fuel amount returning to fuel tank Limit the fuel tank temperature |
THIRTEENTH SCHEDULE
FEES
The fees chargeable under these Regulations shall be as specified hereafter.(a)Application for:(i)Emission Licence for listed emitting facility - KShs.5,000/=(ii)Emission Licence for other emitting facility than (i) above - KShs.5,000/=(iii)Variation of emission licence: KShs.3,000/=(iv)Transfer of emission licence - KShs.3,000/=(b)Annual Licence fee for Emission into the atmosphere(i)Facility listed in 14th schedule under category I - KShs.50,000/=(ii)Facility listed in 14th schedule under category II - KShs.30,000/=(iii)Polluting facility not in 14th Schedule other than (i) and (ii) above - KShs.20,000/=(c)Variation of emission Licence is 10% of the Annual Licence fee(a)Application fees for mobile source testing centres; - 50,000/-(b)Annual operational license for mobile source testing centres – 100,000/-(c)Mobile Source Operator or owner Emission testing fee to be charged by the Designated Testing Centres for each mobile source as follows| | Mobile source | Kshs |
| i. | Motorcycles and tricycles | 1,000/- |
| ii. | Motor vehicles less than 3.5 tonne in tare weight | 5,000/- |
| iii. | Motor Vehicles exceeding 3.5 tonne but less than 7 tonne in tare weight | 10,000/- |
| iv. | Motor vehicles exceeding 7 tonne in tare weight | 20,000/- |
| v. | Locomotives | 30,000/- |
| vi. | Marine and Freshwater Vesselsa) Motorized boatsb) Ships and ferries | |
| vii. | Aircrafts | 50,000/- |
Pollution taxa)A deviation of 10% from the emission limits shall attract an additional 100% of total cost of the emission testing fee.b)Any incremental deviation for every 10% or part thereof shall attract an additional kshs. 20,000FOURTEENTH SCHEDULE
LIST OF CONTROLLED FACILITIES
Part IFertilizer manufacturing plants(d)Hot mix asphalt batching plants(g)Manufacture of soda ash(h)Mineral processing and production plants;(i)Paint manufacturing plants(j)Pesticide formulation and manufacturing plants(k)Petroleum refineries and depots;(l)Pharmaceutical industries(m)Phosphate rock processing plants;(n)Portland cement plants (clinker plants included);(o)Sulphur recovery plants;(p)Sulphuric, or nitric acid plants;(s)Any other chemical processing industry(u)Hydrocarbon recycling plant(v)Copper smelting (primary and secondary)(w)Gold mine ores processing plant(x)Upstream petroleum facilitiesEdible oil processing plantsTanneriesSugar processing plantsCoal plantsQuarry operationsAny other facility that the Authority may prescribePart IIii.Secondary aluminium production plants;iii.Plastic recycling plants;vi.Midstream petroleum facilitiesviii.Any other facility that the Authority may prescribePart IIIStockpiling or storage of materialsMajor construction sitesOutdoor spraying/paintingAny other facility that the Authority may prescribePART I - VehiclesCars,Trucks, MotorcyclesTricyclesPART II - marine vesselsPART III – locomotivesPART IV - AircraftsFIFTEENTH SCHEDULE
Code of Conduct for Designated and Licensed air quality measurement Laboratories
| No. | Item | Subject Matter |
| 1 | Citation | This may be cited as the code of conduct for air quality measurement laboratories |
| 2 | Application | This code of conduct shall apply to all designated and licensed air quality measurement laboratories |
| 3 | Fundamental Principles | Designated and licensed air quality measurement Laboratories shall:a) Uphold and advance integrity in the conduct of their workb) Be professional and honest in their service to clientsc) Shall avoid conflicts of interest.d) Subject their emission measurement staff to at least two refresher courses annually within their scope of designation |
| 4 | Obligations to Clients | Designated and licensed Laboratories shall;a. Act in professional manner to clientb. Not solicit or accept financial or other valuable consideration, directly or indirectly, from clients or other parties in connection with work for employers or clients for which they are responsible.c. Not disclose facts, data or information obtained in a professional capacity without the prior consent of the client.d. Not falsify or misrepresent datae. Interpret issues to the client and offer advice in an objective and truthful manner |
| 5 | Obligations to the Authority | The designated and licensed Laboratory shall ensure that;i. Only competent personnel identified in the designation process are involved in the testing and approval of the analysis reportii. Any change in the competent personnel is duly approved by the Authorityiii. Only equipment evaluated for the laboratory is used for the relevant measurementsiv. Where subcontracting is undertaken of the equipment the analysis results will be countersigned by the subcontracted laboratoryv. Emissions measurements are conducted for only parameters relevant for the sectorvi. All equipment used in testing for the particular parameters are validly calibratedvii. Emissions tests are done in line with methods set in this Regulationsviii. Emission measurement results are not falsified |
| 6 | Consequences of non-compliance | Any designated laboratory which contravenes this code of conduct risks having its designation withdrawn by the Director-General. |