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Zmiana w ekosystemie drobnoustrojów pod wpływem pochodnych kwasów fenoxyoctowych w czarnoziemie

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R O C Z N IK I G L E B O Z N A W C Z E T. X X V I , Z . 2, W A R S Z A W A 1975

M. KECSKÉS, E. B AL Â ZS, K. SCHMIDT

THE CHANGE OF THE MICROBIAL ECOSYSTEM IN A CHERNOZEM AFFECTED BY PHENOXYACETICACID DERIVATIVES

Research Institute of Soil Science and Agricultural Chemistry of the Fungarian Academy of Sciences, Budapest, Research Institute for Plant Protection, Budapest

2,4-D is one of the oldest, most studied [3] and very common her­ bicide, from which more than 300 000 tons/year are produced throughout the world at the present time. It has been produced and applied in large quantities in Hungarian agricultural practice since 1954. The study of the interaction of phenoxyacetic derivatives and soil microorganisms is important not only for this reason but also as a comparison with other phenoxy derivatives as well as for the chlorine decreasing tendency in agricultural practice (protection of the environment). Some of our results are presented in this paper.

M ATERIAL AN D METHOD

Herbicides :

I — 2,4-D = dichloro-phenoxyaceticacid, II — 2,4,5-T = trichloro-phenoxyaceticacid, III — 2,4,5-TE = trichloro^phenoxy ethanol,

IV — Dikonirt D = 2,4,D-Na salt — carier material,

V — Trifenoxin 80 = 2,4,5,-T-iso-amylaesther — carrier material. The chemically pure, (I, II, III) and commercial Herbicides (IV, V) were tested on 75 strains of Rhizobium, Bacillus and Pseudomonas species and one strain of Agrobacterium tumefaciens in liquid culture and with agar gel diffusion technique on YM A [4] and nutrient agar media [3]. 2,4-D and Dikonirt were added to the samples of chernozem with forest residues [5] (originating from the Research Station of the Institute of Soil Science and Agricultural Chemistry of the Hungarian

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186 M. Kecskés, E. Balazs, K. Schmidt

Academy of Sciences at Martonvâsâr) in the amount of 0.1, 1.0, 5.0 and 10% and incubated at optimal temperature (26-29°C) and moisture (50% of the maximal water capacity) for 58 days. The change of m icro­ bial number was recorded on YMA, according to Fehér [1].

The 2,4-D Dikonirt residues of different soils were measured by the spectrophotometer and gas chromatograph [6].

R E SU LTS A N D D ISC U SS IO N

We did not find 2,4-D residues in 113 soil samples taken from 26 agri­ cultural and 10 experimental plots of 10 sites from 6 regions in Hungary representing different soil types [2] in spite of the fact that Dikonirt had been applied in these plots for 1-13 years.

When 2,4-D and 2,4-D-Na (Dikonirt) were added in model expe­ riments to the chernozem with forest residues, they were decomposed by the microorganisms in different ratios for 62 days (Figs 1 and 2). The chemically pure 2,4-D was decomposed more readily (58, 26, 78, 94%) than Dikonirt (51, 20. 43, 22%) having the carrier material, used in agricultural practice.

01%

1%

Fig. 1. R esidues in soil sam ples trea t­ ed w ith d iffere n t doses I

I H 2/HHia m 2,Ш а m 2,Ш а 5% 10% Altogether

Fig. 2. R esidues in soil sam ples trea t­ ed w ith d iffe ren t doses II

The growth of bacteria (Fig. 3) presumably the specialized bacterial flora, was generally stimulated by the 0.1 and 1.0% of 2,4-D and 0.1 Dikonirt treatments. Though this stimulative effect of 0.1 and 1.0% doses was much higher from the 8th day until the 25th day of incu­ bation, in the case of 2,4-D than with 0.1% Dikonirt, the effect of the latter on the number of bacteria increased gradually until the 43rd day of incubation. Although we intended to study only the change of bac­ terial number, we recorded the changes of ray fungi and microscopic fungi too. The number of ray fungi was slightly depressed by the 0.1% and markedly by treatments with both preparations.

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The change of the microbial.., 187 The 0.1 and 1.0% treatments of the investigated herbicides stimulated the multiplication of microscopic fungi after 2 and 4 weeks but especially after 43 days. Higher doses (5.0 and 10.0%) had a marked reducing effect.

Fig. 3. The change of number of bacteria in chernozem with forest residues affected, by 2,4-D and 2,4-D-Na

We found Bacillus strains in the treated soil samples described above during 62 days and these strains of Bacillus pasteurii, Bacillus subtilis var. niger and Bacillus cereus var. mycoides isolated by us (Fig. 4) were relatively more sensitive to Dikonirt D than to chemically pure 2,4-D which is supported by the data obtained with 26 tested strains of Rhizo­ bium species (Fig. 6).

The comparative sensitivity tests of 41 Rhizobium strains to Dikonirt and Trifenoxin (Fig. 5) revealed a relatively higher toxicity of Trife­ noxin than that of Dikonirt.

As it is apparent from Fig. 5 the chemically pure compounds (2,4,5- TE, 2,4,5-T, 2,4-D) proved to be less toxic to the different strains of species belonging to Pseudomonas, Bacillus and Rhizobium genera. The investigated strain of Agrobacterium tumefaciens behaved similarly.

According to the test o f 104 herbicides on 26 Rhizobium strains (Fig. 7) Dikonirt could be listed as a moderately inhibitory herbicide as well as Trifenoxin, though the latter was relatively more toxic to rhizobia both in the rate of inhibition and percentage of inhibited strains.

We did not find 2,4-D residues in many samples of different Hun­ garian soil types to which Dikonirt was applied earlier. Since it is

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188 M. K ecskés, Е. Balazs, K. S ch m idt

known to move down quickly and to be readily decomposed under aerobic conditions we suggest on the basis of our experience with other pesticides e.g. gamma BHC [3] a more intensive survey of the pesticide contamination of soils with the introduction of the biologically m icro- biologically and chemically controlled ’’Pesticide cadastrial” .

Rhizobium

species strainsMo. of Oikonirt Trifenoxin

Leguminosarum 8 m m E U S Phoseoli 5 ШШ Trifolii 8 m m ш ш т * Lupini 2 1Japonicum 8 И Я в — i Meliloti 10 я в

Bacillus Strain 2 ,4 -0 2,4-D-Na,

Pasteurii Bi Й Й Н ш ат й Bz Ш

=S=3

Вб Subtilis var. niger 03 и B7 I Bn Ж ШШ Cereus vor. mycoides X7i я м и *72т т A ltogether : 41

Inhibition in ram Inhibition in m m

Fig. 4. 2,4-D and 2,4-D-Na sensitivity Fig. 5. Sensitivity of rhizobia to Di-

of bacilli konirt and Trifenoxin

Bacteria strainsNo. o f 2,4,5-TE 2,4,5-Т 2,4-D Dikonirt Trifenoxin

Pseudomonas 9 m

ш

Ш

им

m

Bacillus 17 ——. ■ .. ..73,

Rhizobium 3 и И ~ ~г 3

Agrobacterium 1

m

Ьти

Inhibition in m m

Fig. 6. Phenoxyaceticacid sensitivity of bacterial strains

In this system a combination of the above mentioned methods is recommended to detect the persistence of pesticides not only when the danger is great or the damage already inevitable, but also for prognostic and preventive purposes.

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The change o f the m icrobial.. 189 Inhibition Herbicides Inhibitory zone TTlTfl Inhibited ,strains

%

Slight Kloben Ц 1 65,0 Gesatop 50 Щ n o Moderate Dihonirt 28,0 92,0 Trifenoxin 36,1 100,0 Strong A ret it 80,0 100,0 Basomid 88,1 100,0

Fig. 7. Herbicides sensitivity of 26 Rhizobium strains

a survey of pesticides in the soil and the tests with micro- and macro- organisms showing the soil contamination degree with pesticides are an absolute necessity.

CONCLUSIONS

1. The chemically pure 2,4-D was decomposed much more than the commercial herbicide preparation Dikonirt D in the different treatments during 62 days, in a chernozem with forest residues soil.

2. The smaller doses of 2,4-D and occasionally Dikonirt stimulated the multiplication of the specialized bacterial flora with higher doses reducing the number of bacteria, (ray fungi) and microscopic fungi.

3. The decreasing toxicity order of phenoxyaceticacids and deriva­ tives tested on bacilli isolated from chernozem with forest residues soil treated with 2,4-D and Dikonirt D and different strains of species of Rhizobium, Bacillus and Pseudomonas genera was as follows: the che- micaly pure 2,4-D Dikonirt, Dikonirt Trifenoxin; the chemically pure 2,4,5-TE, 2,4,5-T, 2,4-D Dikonirt and Trifenoxin commercial preparations.

4. Though 2,4-D residues were not found in 113 samples of different soil types, microbiological and plant tests as well as chemical analyses of other soil pesticides in the soil call for a more increased control of the pesticide content in soils, with the introduction of "Pesticide ca- dastrial” system based on quick biological microbiological and chemical tests.

REFERENCES

[1] B a l e n e g g e r R.: Talajvizsgâlati modszerkönyv, Mezögazdasagi, Kiadó, Bu­ dapest 1953.

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190 M. K ecskés, Е. Balazs, K. S ch m idt

between phenoxy derivatives, and soil microorganisms as well as 2,4-D residues in different, Hungarian soil types. Paper awarded a prize in a com­ petition of the Hungarian Academy Sei. Budapest 1973.

[31 K e c s k é s M. , B a l a z s E.: Proc. of the 2nd Congr. of Yugoslav Micro­ biologists, Opatija (in print) 1973.

[41 K e c s k é s M. , V i n c e n t J. M.: Agrokém. és Talajtan 18, 1969, 57. [5} S z ü c s L.: Agrokém. és Talajtan 12, 1963, 299.

[61 T o t h A., R o n a n é K o v â c s Z., B a l â z s E.: Publ. Univ. Horticult. Bu­ dapest. 35, 1971, 311.

M. K E C SK É S, Е. B A L A Z S , K . SCH M ID T

ZM IA N A W EKOSYSTEMIE DROBNOUSTROJÓW

POD W PŁYW EM POCHODNYCH K W A SÓ W FE N O XYOCTOWYCH W CZARNOZIEMIE

Instytut Gleboznawstwa i Ogrodnictwa AN W RL i Instytut Ochrony Roślin, Budapeszt, Węgry

S t r e s z c z e n i e

Badano rozkład kwasów fenoxyoctowych i ich pochodnych w glebie oraz ich toksyczność w stosunku do drobnoustrojów glebowych. 2,4-D był rozkładany w glebie (w 113 próbkach różnych gleb) szybciej niż Dikonirt. 2,4-D w małych dawkach zwiększał, a w dużych dawkach zmniejszał ilość mikroorganizmów. Zbadano toksyczność herbicydów rodzaju Bacillus, Pseudomonas i Rhizobium.

Zasugerowano wprowadzenie do praktyki rolniczej lepiej sprawdzonego pod względem biologicznym i chemicznym katastralnego systemu stosowania pesty­ cydów. М. К Е Ч К Е Ш , E. Б А Л Я З, К . Ш М ИДТ ИЗМЕНЕНИЯ В ЭКОСИСТЕМЕ МИКРООРГАНИЗМОВ . ПОД ВЛИЯНИЕМ ПРОИЗВОДНЫХ <ï>EHOKCHYKCYCHbIX КИСЛОТ В ЧЕРНОЗЕМЕ Институт почвоведения и садоводства Венгерской Академии Наук.. Институт защиты растений, Будапешт. ВНР Р е з ю м е Исследовали разложение феноксиуксусных кислот и их производных в почве, а также их токсичность по отношению к почвенным микроорганиз­ мам. 2,4-D разлагался в почве (в 113 образцах разных почв) быстрее, чем диконирт. 2,4-D в низких дозах повышал а в высоких дозах сокращал число микроорганизмов. Исследовали токсичность гербицидов на видах Bacillus, Pseu­ domonas и Rhizobium. Выдвинуто предложение внедрения в сельскохозяйственное производство лучше испытанной в биологическом и химическом отношении кадастральной системы применения пестицидов.

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