Ambient air - Biomonitoring with Higher Plants - Method of the standardized tobacco exposure

This European Standard applies to the determination of the impact of ground-level ozone on a bioindicator plant species (tobacco Nicotiana tabacum cultivars Bel-W3, Bel-B and Bel-C) in a given environment.
The present document specifies the procedure for setting-up and use of a system designed to expose these plants to ambient air. It also describes the procedure for leaf injury assessment.
Leaf injury caused by ozone appears in the form of necrosis or accelerated aging (senescence) on the leaves of the bioindicator. The macroscopically detectable leaf injury is used as the effect measure (see pictures in Annex A). The measure is the percentage of dead leaf area on the entire leaf surface.
The results of the standardised tobacco exposure indicate ozone-caused injury of the exposed bioindicators and thus enable a spatial and temporal distribution of the impact of ozone on plants to be determined.
This Standard applies to the outside atmosphere in all environments. This standard does not apply to the assessment of air quality inside buildings.
The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect.
The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect.

Außenluft - Biomonitoring mit Höheren Pflanzen - Verfahren der standardisierten Tabak-Exposition

Diese Europäische Norm gilt für die Bestimmung der Auswirkung von bodennahem Ozon auf eine als Bioindikator verwendete Pflanzenart (Sorten Bel-W3, Bel-B und Bel-C von Tabak Nicotiana tabacum) in einer bestimmten Umgebung.
Das vorliegende Dokument legt das Verfahren für das Einrichten und Anwenden eines Systems fest, das für die Exposition dieser Pflanzen gegenüber Außenluft vorgesehen ist. Es beschreibt außerdem das Verfahren der Beurteilung der Blattschädigung.
Eine durch Ozon hervorgerufene Blattschädigung tritt in Form von Nekrosen oder einer beschleunigten Alterung (Seneszenz) an den Blättern des Bioindikators auf. Die makroskopisch erkennbare Blatt-schädigung wird als Wirkungsmessgröße verwendet (siehe Bilder in Anhang A). Das Maß ist der prozentuale Anteil abgestorbener Blattfläche an der gesamten Blatt(ober)fläche.
Die Ergebnisse der standardisierten Tabak-Exposition zeigen ozonbedingte Schädigungen der exponierten Bioindikatoren an und ermöglichen somit eine Bestimmung der räumlichen und zeitlichen Verteilung der Auswirkung von Ozon auf Pflanzen.
Die Norm gilt für die Außenatmosphäre in allen Umgebungen. Die Norm gilt nicht für die Beurteilung der Luftqualität innerhalb von Gebäuden.
Das in der vorliegenden Europäischen Norm beschriebene Verfahren ersetzt nicht die Modellierung oder physikalisch-chemische Verfahren der direkten Messung von Luftschadstoffen, sondern ergänzt sie durch das Aufzeigen der biologischen Wirkung.

Air ambiant - Biosurveillance à l'aide de plantes supérieures - Méthode de l'exposition normalisée du tabac

La présente Norme européenne s’applique à la détermination de l’impact de l’ozone troposphérique sur une espèce de plante bioindicatrice (cultivars de tabac Nicotiana tabacum Bel-W3, Bel-B et Bel-C) dans un environnement donné.
Le présent document spécifie le mode opératoire de mise en place et de suivi d’un dispositif permettant l’exposition de ces végétaux à l’air ambiant. Il décrit également le mode opératoire d’évaluation des lésions foliaires.
Les lésions foliaires causées par l’ozone se traduisent par une nécrose ou un vieillissement accéléré (sénescence) des feuilles du bioindicateur. Les lésions foliaires visibles à l’oeil nu sont utilisées comme mesure de l’effet (voir les illustrations à l’Annexe A). La mesure est le pourcentage de surface foliaire nécrosée sur toute la surface de la feuille.
Les résultats de l’exposition normalisée du tabac indiquent les lésions causées par l’ozone des bioindicateurs exposés et permet ainsi de déterminer la distribution spatio-temporelle de l’impact de l’ozone sur les plantes.
La présente norme s’applique à l’atmosphère extérieure dans tous les environnements mais ne s’applique pas à l’évaluation de la qualité de l’air intérieur des bâtiments.
La méthode décrite dans la présente Norme européenne ne remplace pas la modélisation ou les méthodes physico-chimiques de mesurage direct des polluants atmosphériques, elle les complète en démontrant l’effet biologique.

Zunanji zrak - Biomonitoring z višjimi rastlinami - Metoda standardizirane izpostavljenosti tobaka

Ta evropski standard se uporablja za določanje učinka prizemnega ozona na bioindikatorje rastlinskih vrst (sorte tobaka Nicotiana tabacum Bel-W3, Bel-B2 in Bel-C) v določenem okolju. V tem dokumentu je opredeljen postopek za vzpostavitev in uporabo sistema, načrtovanega za izpostavljanje teh rastlin zunanjemu zraku. Opisuje tudi postopke ovrednotenja poškodb listov. Poškodbe listov, ki jih povzroči ozon, se pojavijo v obliki nekroze ali pospešenega staranja listov (biološko staranje) na listih bioindikatorja. Makroskopske poškodbe listov se uporabljajo kot bioindikator meritve učinka. Meritev je odstotek površine mrtvega lista glede na celotno površino lista. Rezultati standardizirane izpostavljenosti tobaka kažejo škodo, ki jo na izpostavljenih bioindikatorjih povzroča ozon, in s tem omogočajo prostorsko in časovno razporeditev vpliva ozona na rastline. Ta standard se uporablja za zunanjo atmosfero v vseh okoljih, vendar se ne uporablja za ocenjevanje kakovosti zraka v stavbah. Metoda, ki je opisana v tem evropskem standardu, ne nadomešča modeliranja ali fizikalno-kemijskih metod neposrednega merjenja onesnaževal zraka, ampak jih dopolnjuje s prikazom biološkega učinka.

General Information

Status
Published
Publication Date
16-Aug-2016
Withdrawal Date
27-Feb-2017
Technical Committee
CEN/TC 264 - Air quality
Current Stage
9093 - Decision to confirm - Review Enquiry
Start Date
15-Mar-2022
Completion Date
14-Apr-2025

Overview

EN 16789:2016 (CEN) - "Ambient air - Biomonitoring with Higher Plants - Method of the standardized tobacco exposure" specifies a standardized biomonitoring method to assess the biological impact of ground‑level ozone on plants using tobacco (Nicotiana tabacum cultivars Bel‑W3, Bel‑B, Bel‑C). The standard defines how to set up and use an exposure system that places these bioindicator plants in the ambient air, and how to assess and report ozone‑induced leaf injury. The effect measure is the percentage of dead leaf area (necrosis/senescence) of exposed leaves. EN 16789:2016 is intended for outdoor atmospheres and complements physico‑chemical ozone measurements and modelling by providing direct biological evidence of ozone impact.

Key topics and technical requirements

  • Test species and cultivars: use of Nicotiana tabacum cultivars Bel‑W3 (supersensitive), Bel‑C (intermediate) and Bel‑B (tolerant).
  • Exposure system: detailed requirements for the exposure device and exposure rack to ensure standardized contact between ambient air and test plants.
  • Plant cultivation: substrate, watering and growth conditions to prepare uniform test plants prior to exposure.
  • Exposure procedures: duration of exposure, selection of exposure locations (outdoor only), and environmental considerations (temperature, humidity, wind) that affect ozone uptake.
  • Visual injury assessment: leaf selection rules, identification of ozone‑specific necrosis vs. other injuries, and quantification method (percentage of necrotic area). Reference plates and photographs (Annex A) support consistent scoring.
  • Data handling & reporting: recommended documentation (Annex B), methods for missing values, statistical tests for spatial/temporal comparisons, graphical presentation and quality assurance/control procedures.

Practical applications

  • Mapping spatial and temporal distribution of ozone impact on vegetation.
  • Complementing ambient ozone monitoring networks and atmospheric modelling by providing biological effect data.
  • Supporting environmental impact assessments, agricultural risk appraisal, forestry health surveillance, and research on plant responses to ozone.
  • Informing policymakers, regulators and site‑specific permitting where biological effects are relevant.

Who should use this standard

  • Environmental agencies and air quality managers
  • Research laboratories and ecotoxicology groups studying ozone effects
  • Consultants doing biomonitoring, ecological risk assessments or compliance checks
  • Forestry and agricultural monitoring programs seeking biological indicators of air pollution

Related standards and context

EN 16789:2016 is a CEN standard intended to complement physico‑chemical monitoring and modelling used in EU air quality management (it supports the biological evidence needed under relevant EU air quality policy). Annexes provide photographic reference material and recommended documentation templates to ensure reproducible, comparable ozone biomonitoring data.

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EN 16789:2017 - BARVE

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Frequently Asked Questions

EN 16789:2016 is a standard published by the European Committee for Standardization (CEN). Its full title is "Ambient air - Biomonitoring with Higher Plants - Method of the standardized tobacco exposure". This standard covers: This European Standard applies to the determination of the impact of ground-level ozone on a bioindicator plant species (tobacco Nicotiana tabacum cultivars Bel-W3, Bel-B and Bel-C) in a given environment. The present document specifies the procedure for setting-up and use of a system designed to expose these plants to ambient air. It also describes the procedure for leaf injury assessment. Leaf injury caused by ozone appears in the form of necrosis or accelerated aging (senescence) on the leaves of the bioindicator. The macroscopically detectable leaf injury is used as the effect measure (see pictures in Annex A). The measure is the percentage of dead leaf area on the entire leaf surface. The results of the standardised tobacco exposure indicate ozone-caused injury of the exposed bioindicators and thus enable a spatial and temporal distribution of the impact of ozone on plants to be determined. This Standard applies to the outside atmosphere in all environments. This standard does not apply to the assessment of air quality inside buildings. The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect. The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect.

This European Standard applies to the determination of the impact of ground-level ozone on a bioindicator plant species (tobacco Nicotiana tabacum cultivars Bel-W3, Bel-B and Bel-C) in a given environment. The present document specifies the procedure for setting-up and use of a system designed to expose these plants to ambient air. It also describes the procedure for leaf injury assessment. Leaf injury caused by ozone appears in the form of necrosis or accelerated aging (senescence) on the leaves of the bioindicator. The macroscopically detectable leaf injury is used as the effect measure (see pictures in Annex A). The measure is the percentage of dead leaf area on the entire leaf surface. The results of the standardised tobacco exposure indicate ozone-caused injury of the exposed bioindicators and thus enable a spatial and temporal distribution of the impact of ozone on plants to be determined. This Standard applies to the outside atmosphere in all environments. This standard does not apply to the assessment of air quality inside buildings. The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect. The method described in this European Standard does not replace modelling or physico-chemical methods of direct measurement of air pollutants, it complements them by demonstrating the biological effect.

EN 16789:2016 is classified under the following ICS (International Classification for Standards) categories: 13.020.40 - Pollution, pollution control and conservation; 13.040.20 - Ambient atmospheres. The ICS classification helps identify the subject area and facilitates finding related standards.

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Standards Content (Sample)


2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.Zunanji zrak - Biomonitoring z višjimi rastlinami - Metoda standardizirane izpostavljenosti tobakaAußenluft - Biomonitoring mit Höheren Pflanzen - Verfahren der standardisierten Tabak-ExpositionAir ambiant - Biosurveillance à l'aide de Plantes Majeures - Méthode de l'exposition de tabac standardiséeAmbient air - Biomonitoring with Higher Plants - Method of the standardised tobacco exposure13.040.20Kakovost okoljskega zrakaAmbient atmospheresICS:Ta slovenski standard je istoveten z:EN 16789:2016SIST EN 16789:2017en,fr,de01-julij-2017SIST EN 16789:2017SLOVENSKI
STANDARD
EUROPEAN STANDARD NORME EUROPÉENNE EUROPÄISCHE NORM
EN 16789
August
t r s x ICS
s uä r t rä v râ
s uä r v rä t r English Version
Ambient air æ Biomonitoring with Higher Plants æ Method of the standardized tobacco exposure Air ambiant æ Biosurveillance à l 5aide de plantes supßrieures æ Mßthode de l 5exposition normalisße du tabac
Außenluft æ Biomonitoring mit Höheren Pflanzen æ Verfahren der standardisierten TabakæExposition This European Standard was approved by CEN on
s z June
t r s xä
egulations which stipulate the conditions for giving this European Standard the status of a national standard without any alterationä Upætoædate lists and bibliographical references concerning such national standards may be obtained on application to the CENæCENELEC Management Centre or to any CEN memberä
translation under the responsibility of a CEN member into its own language and notified to the CENæCENELEC Management Centre has the same status as the official versionsä
CEN members are the national standards bodies of Austriaá Belgiumá Bulgariaá Croatiaá Cyprusá Czech Republicá Denmarká Estoniaá Finlandá Former Yugoslav Republic of Macedoniaá Franceá Germanyá Greeceá Hungaryá Icelandá Irelandá Italyá Latviaá Lithuaniaá Luxembourgá Maltaá Netherlandsá Norwayá Polandá Portugalá Romaniaá Slovakiaá Sloveniaá Spainá Swedená Switzerlandá Turkey andUnited Kingdomä
EUROPEAN COMMITTEE FOR STANDARDIZATION COMITÉ EUROPÉEN DE NORMALISATION EUROPÄISCHES KOMITEE FÜR NORMUNG
CEN-CENELEC Management Centre:
Avenue Marnix 17,
B-1000 Brussels
t r s x CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Membersä Refä Noä EN
s x y z {ã t r s x ESIST EN 16789:2017

Reference plates and photographs for evaluating the percentage of necrosis on leaf surfaces . 24 Annex B (informative)
Documentation . 28 B.1 General . 28 B.2 Example of the information that shall be recorded at a given exposure location . 28 B.3 Example of the information that shall be recorded for a tobacco plant at a given assessment date . 30 Bibliography . 31 SIST EN 16789:2017

Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and the United Kingdom. SIST EN 16789:2017

« x r r mg/l. NOTE The NPK-content of commercial potting soils is frequently given as weight per litre of the product. As such, further fertilisation during cultivation and exposure of the bioindicator plants is not necessary. The substrate should have a pH between 5,5 and 6,5. Before putting the soil into the plant pots, it should be moistened if necessary. 4.1.3 Water For watering the plants drinking water quality (Council Directive 98/83/EC on the quality of water intended for human consumption [63]) is sufficient. If the values given there cannot be complied with, deionised water shall be used. 4.1.4 Exposure device The exposure of the bioindicators takes place in commercially available square plastic plant pots with the dimensions 13 cm × 13 cm (top rim) and a height of 13 cm (volume: ca. 1,25 l to 1,5 l; see Figure 1) or in round pots with comparable soil volume. Four holes are drilled into the base of the pots (if not already present in the purchased pots), through which two moistened glass fibre wicks (diameter: 5 mm to 6 mm, length: 50 cm to 70 cm) or other suitable suction wicks are inserted. The wicks serve as a continuous water supply during cultivation and exposure. At least 7 cm of the wicks should reach into the substrate. The length of loose ends should be chosen in such a way that both ends reach the bottom of the water storage container. As water storage container, a Euro standard stackable plastic container (60 cm × 40 cm × 12 cm) is used, into which an overflow is drilled approximately 2 cm below the upper edge. A white polystyrene block (60 cm × 40 cm × 11 cm) with at least two recesses (11,5 cm × 11,5 cm) into which the plant pots are put is placed onto this tub. In this way, mutual obstruction/shading of the growing plants is avoided. Suitable shaping of its lower edge prevents the block slipping off the tub (Figure 1). For the plants, wooden or bamboo sticks are used as support to prevent wind damage. SIST EN 16789:2017

Key 1: leaf with necrosis 2: polystyrene block 3: water reservoir 4: suction wick Figure 1 — Example of a device for the exposure of tobacco plants 4.1.5 Exposure rack The exposure rack consists of a solid frame construction (Figure 2). The tobacco plants are exposed at a height of 70 cm to 110 cm from ground level to the soil surface in the pots. During the exposure water is supplied by the wicks, which hang from the plant pots into the water reservoir. A filling quantity of 20 l enables two weeks of maintenance-free exposure. The exposure rack is covered with green shading fabric (shading rate 50 %) at the top and at three sides (east, south, west). It is open toward the north. The shaded plants react more sensitively to ground-level ozone than those under direct sunlight as the stomata of the leaves – being the dominating uptake path for ozone – remain open for longer periods of time. One can therefore expect a higher level of leaf injury in shaded plants. SIST EN 16789:2017

Key 1: metal frame construction, consisting of four frame elements (2 pieces 180 cm × 90 cm, 2 pieces 180 cm × 60 cm) 2: shading fabric at three sides (east, south, west) as well as at the top 3: stackable plastic containers (60 cm × 40 cm × 12 cm) as water storage containers 4: example of a polystyrene block (60 cm × 40 cm × 11 cm) with three complete pot-shaped recesses (11,5 cm × 11,5 cm) and recessed edge to prevent slipping 5: plastic pot (13 cm × 13 cm) with suction wicks Figure 2 — Exposure rack [SOURCE: [64]; modified] 4.2 Cultivation of plants The aim of the cultivation is a healthy, vigorous plant. The tobacco plants are cultivated in an environment which minimizes ambient ozone concentration (e.g. greenhouse, open-top chamber, phytotron, if possible supplied with charcoal-filtered air). Efforts should be made to ensure as constant temperature as possible during cultivation. At high temperatures the seedlings should be watered from top down using a sprinkler, in order to avoid overheating; at night the temperature should not drop below 10 °C. The aim is to produce plants at a comparable stage of development, and thus similar sensitivity, for all exposure periods. The tobacco is sown in trays with well-moistened standardized soil (see 4.1.2). The top layer consists of sieved soil, which is smoothed to a flat surface. The seeds are applied evenly and spread very thinly (1 seed/cm2 to 5 seeds/cm2). Since tobacco plants require light for germination, the seeds are not covered with soil. The seed trays are maintained at temperatures between 18 °C and 28 °C, in order to ensure a safe and rapid germination within five to 16 days. If higher temperatures occur, the trays should be kept in a shady place to avoid heat stress. During this time, the surface of the soil shall always be kept moist (e.g. under a transparent cover on the tray). Unused seeds can be stored in a refrigerator (4 °C to 6 °C) for future use (see 4.1.1). After the initial growth, the seedlings (see Figure 3a) should be transferred to a place with ample light. SIST EN 16789:2017

Figure 3a — Seedlings Figure 3b — Two leaf-stage The following cultivation procedure is recommended: Two to three weeks after sowing, the seedling reaches the two leaf-stage (two successive leaves after the two cotyledons; the latter do not count as leaves; see Figure 3b). At this stage, four small bunches of two to six seedlings each are taken from the sowing trays and transferred into the exposure pots (Figure 4). The pots should be kept in a shady place for five to seven days to allow proper root growth without heat and drought stress. Thereafter, a sunnier place is favourable for further growth.
Figure 4 — Tobacco seedlings, immediately after potting The plants are watered carefully the first time using a thin spout to avoid damage to the seedlings. The pots are put into a water storage container without the polystyrene block and set up in a protected, relatively shaded place. The bottom of each container is covered with some water, so that the soil in the pots always remains moist by the use of the suction wicks. In the next two to three days it is checked whether at least one plant from each of the four bunches has established (areas where no plant has established satisfactorily should be replanted). One week after the replanting at the latest, four seedlings out of the bunches are selected in such a way that in each pot remain four plants of different sizes (Figure 5). SIST EN 16789:2017

Figure 5 — Tobacco plants after selection to four plants/pot Five to six weeks after sowing, the plants will have reached a stage at which they begin to compete with each other. They are therefore thinned to one plant per pot (Figure 6). In doing so, either the largest, middle or smallest plant of each pot is left for exposure – depending on the general developmental stage (in order to get a set of plants as homogeneous in size and development as possible).
Figure 6 — Single tobacco plant Once the plants have reached the stage depicted in Figure 7, they are exposed at the monitoring location (soil should be well moistened beforehand). Before exposure at the latest, each plant shall be loosely tied to a wooden or bamboo stick (of at least 40 cm). SIST EN 16789:2017

Key left: leaf pattern of a tobacco plant; leaves 2 to 8 right: leaf pattern of a tobacco plant; leaves 1 to 8; leaves coloured grey = those used for visual injury assessment; a = ring added to mark the lower bound above which leaves are assessed Figure 7 — Tobacco plants at the exposure stage Leaf pattern of a plant ready for exposure (the leaf length refers to the blade only, not including the petiole): — The two cotyledons have already fallen off and are not counted. — Leaf 1 has reached a maximum size of approximately 2 cm–3 cm in diameter; it remains round. — Then follows a likewise round leaf of approximately 3 cm–5 cm maximum diameter (No. 2). — The next leaf (No. 3) is oval, bluntly pointed and reaches a maximum of hand size when fully grown. — The next leaf (No. 4) is the first leaf that features the typical tobacco leaf shape (pointed oval) and is substantially larger than leaf No. 3. Above this leaf a reference ring or a similar indicator is fitted at the beginning of the exposure. This indicator marks the lower bound above which visual injury assessment begins (see Clause 5). The exposure stage is considered to be reached when leaf 8, the fourth leaf above the reference ring, has a length of at least 10 cm, while leaf 9 is still shorter than 10 cm in total length. This stage is reached seven to 10 weeks after sowing depending on the local climatic conditions. A summary of the cultivation is given in Table 1. SIST EN 16789:2017

Exposure location 1 Exposure location 2 Exposure location 3 Leaf number 5 6 7 5 6 7 5 6 7 Plant 1 10 10 5 40 10 5 50 20 0 Plant 2 5 5 5 20 20 5 X 50 10 Plant 3 20 30 5 40 20 5 X X 30 Plant 4 10 10 5 50 20 10 40 50 20 Plant 5 20 10 10 X 30 10 60 40 20 6.2.3 Missing value completion Table 2 is expanded by adding a line below that contains the mean values for each location and leaf position that have not lost any reference leaves. In the example data set, this mean is based on five plants for Location 1, four plants for Location 2 and three plants for Location 3 (Table 3). If the data set contains no missing values, the data processing may proceed as shown in Table 5. SIST EN 16789:2017

Exposure location 1 Exposure location 2 Exposure location 3 Leaf number 5 6 7 5 6 7 5 6 7 Plant 1 10 10 5 40 10 5 50 20 0 Plant 2 5 5 5 20 20 5 X 50 10 Plant 3 20 30 5 40 20 5 X X 30 Plant 4 10 10 5 50 20 10 40 50 20 Plant 5 20 10 10 X 30 10 60 40 20 Means of plants without missing leaves 13,0 (65/5) 13,0 (6
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