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APPENDIX I MC IV “Wide dispersive use” The term wide dispersive use should be used for a wide range of activities particularly when end users come into contact with the products. This means a large number of small point sources like households or line sources like traffic. Although the HEDSET allows for one entry of the MC only for all stages of the life-cycle, the approach of MCs is used in EUSES in many cases for several stages of the life-cycle. As can be seen from Table 1 interpretation is often different. Table 1 Interpretation of main category (MC) for relevant stages of the life-cycle 208 MC Life-cycle stage Interpretation Ia Production Non-isolated intermediates (Industrial category 3 or 9 & Use category 33) Ib Production Isolated intermediates stored on-site, or substances other than intermediates produced in a continuous production process Ib Formulation Dedicated equipment and (very) little cleaning operations Ic Production Isolated intermediates stored off-site, or substances other than intermediates produced in dedicated equipment Ic Formulation Dedicated equipment and frequent cleaning operations II Formulation Inclusion into or onto a matrix II Processing 1) Non-dispersive use (industrial point sources), or processing of intermediates in multi-purpose equipment III Production Multi-purpose equipment III Formulation Multi-purpose equipment III Processing 1) Non-dispersive use (industrial point sources), or processing of intermediates in multi-purpose equipment IV Processing 1) Wide dispersive use (many small point sources or diffuse releases; normally no emission reduction measures) 1) Processing refers to industrial / professional use 10. Remarks on the industrial categories This paragraph defines the scope of the Industry Categories (ICs) and presents some short remarks on the ICs in relation to the A- and B-tables. The definition is based on the examples specified in the HEDSET for substances classified in the appropriate ICs. One of the main problems using the A- and B-tables is the fact that it is often difficult to determine the correct tables to be used, i.e. to determine the correct IC-UC combination (industrial category-use category). The cause can be divided in two: 1. Correct categorisation is impossible because no suitable use category can be determined on account of the notification. Furthermore, problems may arise when the application of a substance takes place in a process that occurs in more than one industrial category. 2. The specification of the industrial category and/or use category by the notifier is wrong, and determination of the proper combination fails due to the fact that the detailed information of the notification may be cryptic.
APPENDIX I A table is presented for every IC in which for every possible stage of the life-cycle the MCs are marked (with ‘X’), which can be chosen or which are used automatically by the program on account of the choice made for the UC. If an MC can not be chosen or if no MC is needed a dot (.) has been placed in the table. Processing refers to industrial / professional use. IC 1. Agricultural industry Agricultural industry deals with the activities of growing crops (vegetables, grains, etc.) and raising cattle (for dairy products, meat and wool). It also comprises all allied activities such as pest control (application of pesticides, veterinary medicines), manuring, etc. There are no emission scenarios and use category documents for this IC. Emissions due to the application (stage of processing) of pesticides are beyond the scope of the TGD. Several UCs are distinguished in the release scenario of the A-tables, e.g. UC = 19 Fertilisers and UC = 41 Pharmaceuticals. Table for IC 1 of the MCs for the possible stages of the life-cycle which may be chosen on account of the UC chosen (for interpretation of the MC see Table 1): Stage Main category Ia Ib Ic II III IV Production . X X . X . Formulation . X X . X . Processing . . . . . . IC 2. Chemical industry: basic chemicals The HEDSET considers two different ICs for chemical industry, the industry where substances are produced through chemical reactions. The raw materials for chemical industry come from petrochemical industry (IC 9 “Mineral oil and fuel industry”), from plant or animal materials, or coal. IC 2 is dedicated to basic chemicals, where the definition for use of the release estimation tables is based on the examples given in the HEDSET: basic chemicals are substances used generally throughout all branches of chemical industry and usually in considerable amounts. Important basic chemicals are solvents (UC 48) and pH-regulating agents (UC 40) (acids, alkalis). There are no emission scenario and use category documents for this IC. In case a basic chemical is formulated A- and B-tables have been provided. Recovery is not considered as a feasible emission stage; emissions of chemicals such as catalysts are included in the emissions at the stage of processing. No distinction between UCs has been made in the emission tables so far; however, apart from UC = 48 “Solvents” most chemicals will have to be classified as UC = 40 “pH-regulating agents”, UC = 55/0 “Others”, and probably as UC = 43 “Process regulators”. Table for IC 2 of the MCs for the possible stages of the life-cycle which may be chosen on account of the UC chosen (for interpretation of the MC see Table 1): 209
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Institute for Health and Consumer P
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LEGAL NOTICE Neither the European C
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OVERVIEW This Technical Guidance Do
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CONTENTS 1 GENERAL INTRODUCTION ...
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4.2.3.4 Use of biodegradation scree
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1 GENERAL INTRODUCTION 1.1 BACKGROU
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GENERAL INTRODUCTION countries in t
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GENERAL INTRODUCTION PNEC is regard
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2 ENVIRONMENTAL EXPOSURE ASSESSMENT
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ENVIRONMENTAL EXPOSURE ASSESSMENT r
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2.2 MEASURED DATA ENVIRONMENTAL EXP
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ENVIRONMENTAL EXPOSURE ASSESSMENT w
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ENVIRONMENTAL EXPOSURE ASSESSMENT o
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ENVIRONMENTAL EXPOSURE ASSESSMENT T
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ENVIRONMENTAL EXPOSURE ASSESSMENT r
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Production ENVIRONMENTAL EXPOSURE A
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Back to processing Product at end o
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ENVIRONMENTAL EXPOSURE ASSESSMENT s
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Explanation of symbols ENVIRONMENTA
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ENVIRONMENTAL EXPOSURE ASSESSMENT s
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ENVIRONMENTAL EXPOSURE ASSESSMENT U
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ENVIRONMENTAL EXPOSURE ASSESSMENT a
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ENVIRONMENTAL EXPOSURE ASSESSMENT F
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2.3.5.1 Adsorption to aerosol parti
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ENVIRONMENTAL EXPOSURE ASSESSMENT I
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2.3.6.1 Hydrolysis ENVIRONMENTAL EX
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2.3.6.3 Photochemical reactions in
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constant of zero. However, if it ca
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ENVIRONMENTAL EXPOSURE ASSESSMENT A
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ENVIRONMENTAL EXPOSURE ASSESSMENT a
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Primary Settler Aeration Tank 2 5 3
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ENVIRONMENTAL EXPOSURE ASSESSMENT I
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ENVIRONMENTAL EXPOSURE ASSESSMENT d
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ENVIRONMENTAL EXPOSURE ASSESSMENT e
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Table 10 Overview of different expo
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ENVIRONMENTAL EXPOSURE ASSESSMENT -
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2.3.8.3 Calculation of PEClocal for
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ENVIRONMENTAL EXPOSURE ASSESSMENT W
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Guidance for calculating PEClocal i
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Concentration (% of initial) 160 14
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Calculation of PEClocalsoil For soi
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ENVIRONMENTAL EXPOSURE ASSESSMENT
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Output ENVIRONMENTAL EXPOSURE ASSES
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3 EFFECTS ASSESSMENT 3.1 INTRODUCTI
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3.2.1.1 Completeness of data New su
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EFFECTS ASSESSMENT • it is clearl
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EFFECTS ASSESSMENT 3.3 EFFECTS ASSE
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Table 16 Assessment factors to deri
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Input data EFFECTS ASSESSMENT The m
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Estimation of the PNEC The PNEC is
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EFFECTS ASSESSMENT biodegradability
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Table 17 Test systems for derivatio
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EFFECTS ASSESSMENT representative o
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In the partitioning method, it is a
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EFFECTS ASSESSMENT As mentioned in
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3.6.2.1 Calculation of PNEC using t
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3.7 EFFECTS ASSESSMENT FOR THE AIR
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EFFECTS ASSESSMENT procedure availa
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EFFECTS ASSESSMENT bioaccumulation
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EFFECTS ASSESSMENT For some chemica
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EFFECTS ASSESSMENT i.e. without enh
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Conversion factors for laboratory a
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EFFECTS ASSESSMENT • relative sen
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EFFECTS ASSESSMENT Earthworms are a
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MARINE RISK ASSESSMENT environment
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MARINE RISK ASSESSMENT of equal rel
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4.2.3.3 Marine biodegradation simul
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MARINE RISK ASSESSMENT In addition
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Explanation of symbols MARINE RISK
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MARINE RISK ASSESSMENT evaluate the
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MARINE RISK ASSESSMENT marine water
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MARINE RISK ASSESSMENT The addition
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MARINE RISK ASSESSMENT Statistical
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MARINE RISK ASSESSMENT sediment, fo
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Table 27 Assessment factors for der
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Page 167 and 168: MARINE RISK ASSESSMENT of different
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Page 173 and 174: MARINE RISK ASSESSMENT mechanisms s
Page 175 and 176: MARINE RISK ASSESSMENT The use of t
Page 177 and 178: 4.4.4.2 Assessment of measured BCF
Page 179 and 180: MARINE RISK ASSESSMENT required to
Page 181 and 182: Table 33 Overview of PEC/PNEC ratio
Page 183 and 184: RISK CHARACTERISATION If a refineme
Page 185 and 186: Classified dangerous to the Environ
Page 187 and 188: RISK CHARACTERISATION eaters. This
Page 189 and 190: 6 TESTING STRATEGIES 6.1 INTRODUCTI
Page 191 and 192: TESTING STRATEGIES Performance of a
Page 193 and 194: TESTING STRATEGIES Care must be tak
Page 195 and 196: Algal testing Algae toxicity test (
Page 197 and 198: TESTING STRATEGIES • long-term te
Page 199 and 200: Microbial assays TESTING STRATEGIES
Page 201 and 202: TESTING STRATEGIES A soil bioassay
Page 203 and 204: REFERENCES Brandes LJ, den Hollande
Page 205 and 206: REFERENCES IPCS (2000). Framework f
Page 207 and 208: REFERENCES OECD (1984f). Activated
Page 209 and 210: REFERENCES Pack S. (1993). A review
Page 211: REFERENCES US EPA (1996). Whole Sed
Page 214 and 215: APPENDIX I volume imported in the E
Page 218 and 219: APPENDIX I 210 Stage Main category
Page 220 and 221: APPENDIX I the number of days over
Page 222 and 223: APPENDIX I Stage Main category Ia I
Page 224 and 225: APPENDIX I manufacturing of motor c
Page 226 and 227: APPENDIX I 1. extension of the tabl
Page 228 and 229: APPENDIX I 220 A-tables Estimates f
Page 230 and 231: APPENDIX I PRIVATE USE Not applicab
Page 232 and 233: APPENDIX I IC = 3: CHEMICAL INDUSTR
Page 234 and 235: APPENDIX I IC = 5: PERSONAL /DOMEST
Page 236 and 237: APPENDIX I Table A4.1 continued Com
Page 238 and 239: APPENDIX I IC = 7: LEATHER PROCESSI
Page 240 and 241: APPENDIX I IC = 9: MINERAL OIL AND
Page 242 and 243: APPENDIX I WASTE TREATMENT Table A5
Page 244 and 245: APPENDIX I For the emission factors
Page 246 and 247: APPENDIX I INDUSTRIAL USE Table A3.
Page 248 and 249: APPENDIX I INDUSTRIAL USE Table A3.
Page 250 and 251: APPENDIX I PRIVATE USE Table A4.5 C
Page 252 and 253: APPENDIX I PRIVATE USE Table A3.16
Page 254 and 255: APPENDIX I 246 B-tables Estimates f
Page 256 and 257: APPENDIX I FORMULATION Table B2.2 f
Page 258 and 259: APPENDIX I IC = 3: CHEMICAL INDUSTR
Page 260 and 261: APPENDIX I IC = 5: PERSONAL/DOMESTI
Page 262 and 263: APPENDIX I IC = 7: LEATHER PROCESSI
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APPENDIX I IC = 11: POLYMERS INDUST
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APPENDIX I IC =13: TEXTILE PROCESSI
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APPENDIX I IC = 16: ENGINEERING IND
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APPENDIX I Appendix I-a: List of sy
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APPENDIX I No. Use Category No. Fun
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APPENDIX I Appendix I-b: List of sy
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APPENDIX I 290 Organic intermediate
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APPENDIX I Other IC/UC combinations
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APPENDIX II Appendix II Fate of che
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APPENDIX II b) Inherent biodegradab
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APPENDIX II log H % removal -4 -3 -
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APPENDIX III Appendix III Evaluatio
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APPENDIX III Field studies In gener
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APPENDIX IV together the mentioned
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290 Table 1 Selected soil test meth
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292 Table 1 continued Selected soil
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298 Table 1 Selected freshwater sed
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APPENDIX VII Appendix VII Toxicity
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APPENDIX VIII collection), and that
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APPENDIX VIII chemicals (see Sectio
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APPENDIX VIII Multimedia fate model
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APPENDIX VIII Monitoring data Metal
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APPENDIX VIII homeostatic regulatio
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APPENDIX IX based on the proportion
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APPENDIX IX Definition of “blocks
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APPENDIX IX these “blocks” will
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APPENDIX IX and PNECs for the “bl
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APPENDIX XI Appendix XI Environment
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APPENDIX XII Appendix XII Connectio
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APPENDIX XII +40% compared to 1992.
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APPENDIX XIII other substance is be
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APPENDIX XIV Taxonomic group No. of
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