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Page Background

The importance of the phenolic compounds for the plants is determined by

their participation in the oxy-reducing processes as oxidants and regulators in

phytosynthesis (Кретович, 1980). The different types of pollutions have direct

effect on the content of polyphenols in the medical plants (Иванчева и др.,

2000). The changes in their content is an adaptive reaction to extreme growing

condition and development of the plants ( К о н д р а т ю к и др., 1980; Ш к о л ь ­

н ик а , 1983).

MATERIALS AND METHODS

The samples for analysis from

Achillea crithmifolia

and

Tanacetum vulgare

were collected in 1998 in phase „blossoming" from different ecological sites

(Table 1). Voucher specimens are deposited at the Herbarium of the Institute

of Botany at Bulgarian Academy of Science in Sofia (SOM).

Table 1.

Origin of material investigated.

Species

District

Pollution

Achillea crithmifolia

W. et K.

Pirdop - Copper melting factory

Industrial

Achillea crithmifolia

W. et K.

Sofia - Tzarigradsko shosse

Transport

Achillea crithmifolia

W. et K.

Vitosha - Platoto

Background

Tanacetum vulgare

L.

Pirdop - Copper melting factory

Industrial

Tanacetum vidgare

L.

Sofia - Tzarigradsko shousse

Transport

Tanacetum vulgare

L.

Vitosha - Platoto

Background

Dried leaves and stems are rinsed with acetone to dissolve the exudate

materials that were concentrated by evaporation of the solvent. The qualitative

identification of flavonoids and tannins is performed by TLC chromatography,

sorbent: Polygram Si-gel/UV 254; system toluene/dioxan/acetic acid 90:25:4.

The individual compounds are identified by comparison with authentical

samples by TLC chromatography with Naturstoffreagentz. The quantitative

assessment of flavonoids and tannins is made according to the standard

methods.

RESULTS AND DISSCUSSION

The data from the analysis of the qualitative and quantitative presence of

flavonoid aglycones and tannins in the overground parts of

Achillea crithmifolia

and

Tanacetum vulgare

are shown on Table 2-5.

Table 2 shows that apigenin and 3,6,4'-trimethoxyquercetagetin are present

in high quantity in all samples. There is 3,4'-dimethoxy kaempferol in norm

in the samples with transport and background pollution and it is in high

quantity in industrial polluted district. 3,6,4'-trimethoxy-6-hydroxykaempferol

is presented in larger quantities in the transport polluted region, compared to

others. There are traces of 6,7-dimethoxy-6-hydroxyluteolin in all samples.

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