ČSN EN ISO 14050 - Environmentální management – Slovník
| Stáhnout normu: | ČSN EN ISO 14050 (Zobrazit podrobnosti) Zákazníci, kteří mají na svém počítači sjednanou od České agentury pro standardizaci (ČAS) službu ČSN on-line pro elektronický přístup do plných textů norem v pdf (verzi pro firmy nebo pro jednotlivce), mohou zde přímo otevírat citované ČSN. |
| Datum vydání/vložení: | 2021-03-01 |
| Třidící znak: | 010950 |
| Obor: | Systémy environmentálního managementu |
| ICS: |
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| Stav: | Platná |
- 3.1.1 organization
- 3.1.2 interested party stakeholder
- 3.1.3 top management
- 3.1.4 management system
- 3.1.5 policy
- 3.1.6 objective
- 3.1.7 risk
- 3.1.8 hazard
- 3.1.9 process
- 3.1.10 competence
- 3.1.11 documented information
- 3.1.12 performance
- 3.1.13 continual improvement
- 3.1.14 effectiveness
- 3.1.15 requirement
- 3.1.16 conformity
- 3.1.17 nonconformity
- 3.1.18 corrective action
- 3.1.19 audit
- 3.1.20 measurement
- 3.1.21 monitoring
- 3.2.1 environmental management
- 3.2.2 environment
- 3.2.3 ecosystem
- 3.2.4 ecosystem service
- 3.2.5 natural resource
- 3.2.6 environmental baseline
- 3.2.7 target group
- 3.2.8 third party
- 3.2.9 sustainable development
- 3.2.10 prevention of pollution
- 3.2.11 area of concern
- 3.2.12 environmental topic area
- 3.2.13 methodology
- 3.2.14 transparency
- 3.2.15 benchmark
- 3.2.16 equity share
- 3.2.17 local authority
- 3.2.18 site
- 3.2.19 facility
- 3.2.20 environmental aspect
- 3.2.21 environmental impact pathway
- 3.2.22 environmental impact
- 3.2.23 environmental impact factor
- 3.2.24 indicator
- 3.2.25 key performance indicator KPI
- 3.2.26 combined indicator
- 3.2.27 environmental performance
- 3.2.28 environmental performance evaluation EPE
- 3.2.29 environmental performance indicator EPI
- 3.2.30 management performance indicator MPI
- 3.2.31 operational performance indicator OPI
- 3.2.32 environmental condition indicator
- 3.2.33 environmental condition
- 3.2.34 sphere of influence
- 3.2.35 trade-off
- 3.3.1 environmental management system EMS
- 3.3.2 environmental policy
- 3.3.3 environmental objective
- 3.3.4 compliance obligation
- 3.3.5 maturity level
- 3.3.6 procedure
- 3.4.1 verification conformity assessment
- 3.4.2 verification statement
- 3.4.3 verification team
- 3.4.4 verification body
- 3.4.5 verifier
- 3.4.6 verification plan
- 3.4.7 verification report
- 3.4.8 environmental claim verification
- 3.4.9 technology
- 3.4.10 environmental technology
- 3.4.11 environmental technology verification
- 3.4.12 environmental added value
- 3.4.13 intrusive investigation
- 3.4.14 professional scepticism
- 3.4.15 completeness check
- 3.4.16 consistency check
- 3.4.17 sensitivity check
- 3.4.18 test body
- 3.4.19 test plan
- 3.4.20 test report
- 3.4.21 validation
- 3.4.22 validation statement
- 3.4.23 validation team
- 3.4.24 validation body
- 3.4.25 validator
- 3.4.26 complaint
- 3.4.27 validation criteria
- 3.4.28 level of assurance
- 3.4.29 conflict of interest
- 3.4.30 accreditation
- 3.4.31 accreditation body
- 3.4.32 objective evidence
- 3.4.33 audit client
- 3.4.34 auditee
- 3.4.35 audit team
- 3.4.36 technical expert
- 3.4.37 auditor
- 3.4.38 combined audit
- 3.4.39 joint audit
- 3.4.40 internal audit
- 3.4.41 audit programme
- 3.4.42 audit scope
- 3.4.43 audit plan
- 3.4.44 audit criteria
- 3.4.45 audit evidence
- 3.4.46 audit findings
- 3.4.47 audit conclusion
- 3.4.48 certification
- 3.4.49 environmental information validation
- 3.4.50 environmental information verification
- 3.4.51 environmental information statement environmental information claim
- 3.5.1 product system
- 3.5.2 process energy
- 3.5.3 product flow
- 3.5.4 energy use
- 3.5.5 product system value
- 3.5.6 product system value indicator
- 3.5.7 product standard
- 3.5.8 fitness for purpose
- 3.5.9 product environmental criteria
- 3.5.10 product environmental aspect
- 3.5.11 performance tracking of an organization
- 3.5.12 product
- 3.5.13 co-product
- 3.5.14 intermediate product
- 3.5.15 final product
- 3.5.16 service life
- 3.5.17 consumer
- 3.5.18 raw material
- 3.5.19 release
- 3.5.20 design and development
- 3.5.21 product function characteristic
- 3.5.22 ecodesign
- 3.5.23 recyclable
- 3.5.24 upgradability
- 3.5.25 double counting
- 3.5.26 packaging
- 3.5.27 supply chain
- 3.5.28 value chain
- 3.6.1 life cycle
- 3.6.2 life cycle assessment LCA
- 3.6.3 life cycle inventory analysis
- 3.6.4 life cycle inventory analysis result
- 3.6.5 life cycle impact assessment LCIA
- 3.6.6 life cycle interpretation
- 3.6.7 functional unit
- 3.6.8 system boundary
- 3.6.9 unit process
- 3.6.10 ancillary input
- 3.6.11 feedstock energy
- 3.6.12 elementary flow
- 3.6.13 energy flow
- 3.6.14 intermediate flow
- 3.6.15 reference flow
- 3.6.16 allocation
- 3.6.17 environmental mechanism
- 3.6.18 impact category
- 3.6.19 impact category indicator
- 3.6.20 weighting factor
- 3.6.21 cut-off criteria
- 3.6.22 category endpoint
- 3.6.23 characterization factor
- 3.6.24 uncertainty analysis
- 3.6.25 sensitivity analysis
- 3.6.26 organizational life cycle assessment OLCA
- 3.6.27 critical review
- 3.6.28 critical review statement
- 3.6.29 critical review report
- 3.6.30 commissioner of the critical review
- 3.6.31 independent external expert
- 3.6.32 independent internal expert
- 3.6.33 life cycle thinking life cycle perspective LCT
- 3.6.34 primary data
- 3.6.35 secondary data
- 3.6.36 basic data
- 3.6.37 physical object
- 3.6.38 site-specific data
- 3.6.39 quantitative data
- 3.6.40 quantitative information
- 3.6.41 data generator
- 3.6.42 data documentation format
- 3.6.43 data documentor
- 3.6.44 data commissioner
- 3.6.45 data field
- 3.6.46 data quality
- 3.6.47 information module
- 3.6.48 eco-efficiency
- 3.6.49 eco-efficiency indicator
- 3.6.50 eco-efficiency profile
- 3.6.51 comparative eco-efficiency assertion
- 3.7.1 environmental label
- 3.7.2 ecolabelling body
- 3.7.3 environmental claim
- 3.7.4 self-declared environmental claim
- 3.7.5 qualified environmental claim
- 3.7.6 explanatory statement
- 3.7.7 comparative assertion
- 3.7.8 Type I environmental labelling programme
- 3.7.9 Type III environmental declaration
- 3.7.10 Type III environmental declaration programme
- 3.7.11 declared unit
- 3.7.12 product category rules PCR
- 3.7.13 product category rules review PCR review
- 3.7.14 product category rules committee PCR committee
- 3.7.15 core rules
- 3.7.16 programme operator
- 3.7.17 footprint
- 3.7.18 footprint communication
- 3.7.19 environmental communication
- 3.7.20 environmental communication policy
- 3.7.21 environmental communication objective
- 3.7.22 environmental communication target
- 3.7.23 environmental communication strategy
- 3.8.1 climate
- 3.8.2 climate scenario
- 3.8.3 climate change
- 3.8.4 climate action
- 3.8.5 adaptation to climate change climate change adaptation
- 3.8.6 climate change mitigation
- 3.8.7 adaptive capacity
- 3.8.8 environmental integrity
- 3.8.9 eligibility criteria
- 3.8.10 climate change impact
- 3.8.11 climate sensitivity
- 3.8.12 climate change risk climate risk
- 3.8.13 vulnerability
- 3.8.14 vulnerability assessment
- 3.8.15 climate change exposure
- 3.8.16 land
- 3.8.17 arable land
- 3.8.18 land use LU
- 3.8.19 direct land use change dLUC
- 3.8.20 indirect land use change iLUC
- 3.8.21 agroecosystem
- 3.8.22 biodiversity biological diversity
- 3.8.23 biogenic
- 3.8.24 biogenic carbon
- 3.8.25 biomass
- 3.8.26 transformation
- 3.9.1 greenhouse gas GHG
- 3.9.2 global warming potential GWP
- 3.9.3 carbon dioxide equivalent CO2e CO2 equivalent
- 3.9.4 greenhouse gas source GHG source
- 3.9.5 greenhouse gas sink GHG sink
- 3.9.6 greenhouse gas reservoir GHG reservoir
- 3.9.7 sector
- 3.9.8 greenhouse gas emission GHG emission
- 3.9.9 direct greenhouse gas emission direct GHG emission
- 3.9.10 indirect greenhouse gas emission indirect GHG emission
- 3.9.11 energy indirect greenhouse gas emission energy indirect GHG emission
- 3.9.12 other indirect greenhouse gas emission other indirect GHG emission
- 3.9.13 downstream greenhouse gas emission downstream GHG emission
- 3.9.14 upstream greenhouse gas emission upstream GHG emission
- 3.9.15 out of stream greenhouse gas emission out of stream GHG emission
- 3.9.16 avoided greenhouse gas emission avoided GHG emission
- 3.9.17 greenhouse gas emission reduction GHG emission reduction
- 3.9.18 baseline scenario greenhouse gas baseline scenario GHG baseline scenario
- 3.9.19 base year
- 3.9.20 greenhouse gas emission factor GHG emission factor
- 3.9.21 directed action
- 3.9.22 greenhouse gas removal GHG removal
- 3.9.23 greenhouse gas removal enhancement GHG removal enhancement
- 3.9.24 greenhouse gas removal factor GHG removal factor
- 3.9.25 direct greenhouse gas removal direct GHG removal
- 3.9.26 greenhouse gas project GHG project
- 3.9.27 greenhouse gas project proponent GHG project proponent
- 3.9.28 greenhouse gas programme GHG programme
- 3.9.29 greenhouse gas inventory GHG inventory
- 3.9.30 greenhouse gas information system GHG information system
- 3.9.31 greenhouse gas activity data GHG activity data
- 3.9.32 greenhouse gas report GHG report
- 3.9.33 greenhouse gas statement GHG statement
- 3.9.34 greenhouse gas consultancy services GHG consultancy services
- 3.9.35 verification
- 3.9.36 validation
- 3.9.37 intended user
- 3.9.38 materiality
- 3.9.39 responsible party
- 3.10.1 water footprint
- 3.10.2 water footprint inventory
- 3.10.3 direct water footprint inventory
- 3.10.4 indirect water footprint inventory
- 3.10.5 water footprint inventory analysis
- 3.10.6 water footprint assessment
- 3.10.7 water footprint impact assessment
- 3.10.8 water footprint profile
- 3.10.9 water body
- 3.10.10 water quality
- 3.10.11 water availability
- 3.10.12 water scarcity
- 3.10.13 water use
- 3.10.14 water withdrawal
- 3.10.15 freshwater
- 3.10.16 brackish water
- 3.10.17 seawater
- 3.10.18 surface water
- 3.10.19 groundwater
- 3.10.20 fossil water
- 3.10.21 water degradation
- 3.10.22 water table
- 3.10.23 drainage basin
- 3.10.24 elementary water flow
- 3.11.1 carbon footprint of a product CFP
- 3.11.2 partial carbon footprint of a product partial CFP
- 3.11.3 carbon footprint of a product – product category rules CFP–PCR
- 3.11.4 carbon footprint of a product study CFP study
- 3.11.5 carbon offsetting
- 3.12.1 management accounting
- 3.12.2 environmental benefit
- 3.12.3 co-benefit
- 3.12.4 discounting
- 3.12.5 financial control
- 3.12.6 monetary valuation
- 3.12.7 monetary value
- 3.12.8 reference unit of monetary value
- 3.12.9 total economic value
- 3.12.10 use value
- 3.12.11 non-use value
- 3.12.12 externality external effect
- 3.12.13 internalization
- 3.12.14 willingness to pay WTP
- 3.12.15 willingness to accept compensation WTA
- 3.12.16 environmental dependency
- 3.12.17 environmental dependency pathway
- 3.12.18 environmental cost
- 3.12.19 value transfer
- 3.12.20 revealed preference
- 3.12.21 stated preference
- 3.12.22 external environmental cost
- 3.12.23 external environmental benefit
- 3.12.24 affected human population
- 3.12.25 equity weighting
- 3.12.26 reference situation baseline
- 3.12.27 good
- 3.12.28 marginal utility
- 3.12.29 cost
- 3.12.30 material flow
- 3.12.31 material flow cost accounting
- 3.12.32 material distribution percentage
- 3.12.33 material balance
- 3.12.34 cost allocation
- 3.12.35 cost assignment
- 3.12.36 system cost
- 3.12.37 energy cost
- 3.12.38 energy loss
- 3.12.39 material cost
- 3.12.40 waste management cost
- 3.12.41 environment-related internal cost
- 3.12.42 environment-related internal benefit
- 3.12.43 environmental dependency cost
- 3.12.44 environmental damage cost
- 3.12.45 quantity centre
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Nahlásit chybu
3.10.16 brackish water
water containing dissolved solids at a concentration less than that of seawater (3.10.17), but in amounts that exceed the normally acceptable standards for municipal, domestic and irrigation uses
3.10.16 brakická voda
voda obsahující rozpuštěné pevné látky v koncentraci nižší, než je koncentrace mořské vody (3.10.17), ale v množstvích, která překračují běžně přijatelné standardy pro použití v obcích, v domácnostech a pro zavlažování