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    Calcium chloride and calcium bromide aqueous solutions of

    technical and analytical grade in Lemna bioassay

    Marija Vujevic a, Zeljka Vidakovic-Cifrek a,*, Mirta Tkalec a, Mihovil Tomic b,Ivan Regula a

    a Department of Botany and Botanical Garden, Faculty of Science, University of Zagreb, Rooseveltov trg 6, HR-10000 Zagreb, Croatiab CROSCO Co. (Integrated Drilling and Well Services, INA-Group), Ulica grada Vukovara 18, HR-10000 Zagreb, Croatia

    Received 1 October 1999; accepted 25 February 2000

    Abstract

    Saturated water solutions of calcium chloride, calcium bromide and their 1:1 mixture are commonly used as ``high

    density brines'' for pressure control in oil wells. To compare the eect of these chemicals of technical grade with the

    eect of the chemicals of analytical grade the Lemna test was used. The multiplication rate, fresh weight, dry to fresh

    weight ratio, area covered by plants and chlorophyll content were measured as toxicity parameters. The concentrations

    of tested chemicals were 0.025, 0.05, 0.075 and 0.1 mol dm3. Generally, the chemicals of both technical and analytical

    grade in concentrations of 0.025 mol dm3 stimulated the Lemna minor growth, while tested chemicals in concentrations

    of 0.05 mol dm3 did not aect the growth signicantly. The exceptions were results obtained by measuring fresh

    weight. Most of tested chemicals in concentrations of 0.075 mol dm3 and all chemicals in concentrations of 0.1 mol

    dm3 reduced the growth. No major dierences between eects of tested chemicals of technical and analytical grade on

    plant growth were observed, except that tested chemicals of analytical grade in concentrations of 0.1 mol dm 3 in-

    creased dry to fresh weight ratio much stronger than chemicals of technical grade. All tested chemicals in all con-

    centrations increased chlorophyll content. After treatment with chemicals of analytical grade much higher increase of

    chlorophyll a concentration in comparison to increase of chlorophyll b was noticed, while chemicals of technical grade

    caused more prominent increase of chlorophyll b. 2000 Elsevier Science Ltd. All rights reserved.

    Keywords: Lemna minor L.; Lemna test; High density brines; Calcium chloride; Calcium bromide

    1. Introduction

    Duckweed Lemna minor L. is a small oating fresh-

    water monocotyledon belonging to family Lemnaceae. It

    has been used as convenient bioassay organism in phy-

    totoxicity evaluation due to its small size, rapid growth,

    vegetative reproduction, ease of culture and sensitivity

    to numerous pollutants (Wang, 1986; Lewis, 1995). Till

    now Lemna bioassay has been used in detection of

    phytotoxicity of heavy metals (Smith and Kwan, 1989;Huebert and Shay, 1991; Huebert et al., 1993; Sajwan

    and Ornes, 1994), phenols (Cowgill et al., 1991), herbi-

    cides (Krsnik-Rasol and Rendic, 1977; Lockhart et al.,

    1989; Peterson et al., 1994; Fairchild et al., 1997), surf-

    actants (Dirilgen and Ince, 1995) and some chemical

    mixtures (Clement and Bouvet, 1993; Kanekar et al.,

    1993).

    Saturated calcium chloride and calcium bromide

    aqueous solutions of technical grade and their 1:1 mix-

    ture are commercially known as oil industry ``high

    density brines'' and have regularly been used in explo-

    ration and production of crude oil and natural gas

    (Schmidt et al., 1983). During the special operations,

    Chemosphere 41 (2000) 15351542

    * Corresponding author. Tel.: +385-1-48-26-262; fax: +385-

    1-48-26-262.E-mail address: [email protected] (Z. Vidakovic-Cifrek).

    0045-6535/00/$ - see front matter 2000 Elsevier Science Ltd. All rights reserved.

    PII: S 0 0 4 5 - 6 5 3 5 ( 0 0 ) 0 0 0 7 0 - 9

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    covered by plants and (5) chlorophyll a and chlorophyll

    b content and their ratio. All procedures were described

    by Tkalec et al. (1998).

    Results obtained by evaluation of growth parame-

    ters were represented as mean values of eight replicates.

    The control was represented as 100% and the resultsobtained with treated plants were represented as per-

    centage of control. Chemicals that aected Lemna mi-

    nor growth signicantly dierent (P ` 0X05) from each

    other and control were marked with dierent letters

    according to Duncans New Multiple Range Test

    (Duncan, 1955).

    Experiment for determination of chlorophyll a and

    chlorophyll b contents was repeated three times. Results

    were calculated as mean values and represented as per-

    centage of control.

    3. Results

    3.1. The inuence of tested chemicals on frond number

    Tested chemicals (CaCl2, CaBr2 and their 1:1 mix-

    ture) of both technical and analytical grade, added into

    the modied Hoaglands nutrient solution in concen-

    trations of 0.025 mol dm3 signicantly stimulated

    (P ` 0X05) the multiplication of plants (Fig. 1). On the

    contrary, all tested chemicals present in concentrations

    of 0.05 mol dm3 and CaBr2 and 1:1 mixture in con-

    centrations of 0.075 mol dm3 did not signicantly

    change the frond number in comparison with the con-

    trol. All tested solutions in concentrations of 0.1 mol

    dm3 and CaCl2 in 0.075 mol dm3 caused a signicantdecrease (P ` 0X05) of frond number.

    3.2. The inuence of tested chemicals on fresh weight

    CaCl2, CaBr2 and their 1:1 mixture of both technical

    and analytical grade in concentrations of 0.025 mol

    dm3 did not change the relative growth of fresh weight

    in comparison to control plants, except CaBr2 of ana-

    lytical grade that stimulated the growth (P ` 0X05).

    CaCl2 and CaBr2 of analytical grade in concentrations

    of 0.05 mol dm3 and CaBr2 of technical grade in con-

    centration 0.075 mol dm3

    also had no signicant eecton fresh weight (Fig. 2). Other solutions in 0.05 and

    0.075 mol dm3 and all solutions in 0.1 mol dm3

    inhibited the growth of fresh weight (P ` 0X05).

    3.3. The inuence of tested chemicals on dry to fresh

    weight ratio

    Tested chemicals of both technical and analytical

    grade present in concentrations of 0.025 and 0.05 mol

    Fig. 1. Relative growth of Lemna minor frond number after two week exposure to tested chemicals of analytical (left) and technical

    grade (right). Dierent letters on the top of the column indicate signicant dierences between treatments at P ` 0X05 by Duncans

    New Multiple Range Test.

    M. Vujevic et al. / Chemosphere 41 (2000) 15351542 1537

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    dm3 did not inuence dry to fresh weight ratio signi-

    cantly (P ` 0X05). Tested chemicals in higher concen-

    trations (0.075 and 0.1 mol dm3) increased observed

    ratio (Fig. 3). The exceptions were CaCl2 of analytical

    grade and CaBr2 of technical grade in concentrations of

    0.075 mol dm3 and CaCl2 and CaBr2 of technical grade

    in concentrations of 0.1 mol dm3. The most signicant

    increase was obtained by 0.1 mol dm3 tested solutions

    of analytical grade (P ` 0X05).

    3.4. The inuence of tested chemicals on the relative area

    covered by plants

    Tested chemicals of both technical and analytical

    grade in concentrations of 0.025 mol dm3 did not sig-

    nicantly increase the relative area covered by plants in

    comparison to control plants except 1:1 mixture

    (P ` 0X05). The relative area covered by duckweed

    treated with tested solutions in 0.05 and 0.075 mol dm3

    was similar to the relative area covered by control plants

    (Fig. 4). CaCl2, CaBr2 and their 1:1 mixture of both

    technical and analytical grade added into the modied

    Hoaglands nutrient solution in concentrations of 0.1

    mol dm3 decreased the relative area covered by plants

    (P ` 0X05).

    3.5. The inuence of tested chemicals on photosynthetic

    pigments content

    The chlorophyll a and chlorophyll b content in-

    creased correspondingly with the increase of tested

    chemicals concentration of both technical and analyti-

    cal grade (Figs. 5 and 6). In duckweed treated with

    tested chemicals of analytical grade the increase of

    chlorophyll a content was more prominent than the in-

    crease of chlorophyll b content. The consequence was

    increased chlorophyll a to chlorophyll b ratio (Fig. 5).

    On the contrary, in duckweed grown on nutrient solu-

    tion supplemented with tested chemicals of technical

    grade, the chlorophyll b content increased to a greater

    extent than chlorophyll a content, so the ratio was

    slightly decreased in comparison to control (Fig. 6).

    4. Discussion

    Tested chemicals in concentrations of 0.025 mol

    dm3 stimulated the Lemna minor growth similarly to

    results of Tkalec et al. (1998) obtained with 0.5% (v/v)

    dilution of high density brines (0.5% v/v CaCl2 solution

    contains 0.0218 mol dm3 CaCl2, while 0.5% v/v CaBr2

    Fig. 2. Relative growth of Lemna minor fresh weight after two week exposure to tested chemicals of analytical (left) and technical

    grade (right). Dierent letters on the top of the column indicate signicant dierences between treatments at P ` 0X05 by Duncans

    New Multiple Range Test.

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    solution contains 0.0266 mol dm3 CaBr2). This stimu-

    lative eect of tested salts in lower concentrations could

    be explained either by establishing better growth con-

    ditions by additional amounts of nutrients brought in

    with the sample (Wundram et al., 1997) or by positive

    eect of increased turgor (Oertli, 1975, cited by von Sury

    and Fluckiger, 1983). We also noticed that the inhibition

    caused by chemicals in concentrations of 0.1 mol dm3

    corresponded to results of Tkalec et al. (1998) obtained

    with high density brines in 2.0% (v/v) dilution (2.0% v/v

    CaCl2 solution contains 0.0867 mol dm3 CaCl2, while

    2.0% v/v CaBr2 solution contains 0.1066 mol dm3

    CaBr2). Since the present results as well as results of

    Tkalec et al. (1998) showed no signicant dierences

    between eects of CaCl2, CaBr2 and their 1:1 mixture in

    concentrations of 0.1 mol dm3, the inhibition could be

    due to the osmotic eect.

    Chemical analysis (Table 1) showed that there were

    not signicant amounts of heavy metals in high density

    brines solutions. But, it could be possible that other

    impurities (of inorganic or organic nature) were present

    in the samples. The eect of high density brines solutions

    on duckweed growth showed no major dierences in

    comparison to the eect of chemicals of analytical grade.

    There were few exceptions according to the Duncans

    New Multiple Range Test. Some solutions of analytical

    grade caused stronger stimulation of growth than solu-

    tions of technical grade (P ` 0X05): for example, inu-

    ence of mixture in concentrations of 0.025 and 0.075 mol

    dm3 on frond number (Fig. 1) and inuence of 0.025

    mol dm3 CaBr2 on fresh weight (Fig. 2). CaBr2 and 1:1

    mixture of analytical grade in concentrations of 0.1 mol

    dm3 inhibited the increase of frond number stronger

    than the same substances of technical grade (Fig. 1). The

    most obvious dierence between chemicals of technical

    and analytical grade was noticed in dry to fresh weight

    ratio, which was signicantly higher (P ` 0X05) aftertreatment with all three samples of analytical grade in

    concentrations of 0.1 mol dm3. The reason for such a

    result could be the starch accumulation in chloroplasts

    of treated plants due to disturbed sugar metabolism

    (Hillman, 1961; Severi, 1991). In our recent investiga-

    tions (data not shown) we conrmed the starch accu-

    mulation in chloroplasts of treated plants by microscopy

    and centrifugation of isolated chloroplasts in sucrose

    gradient.

    A few signicantly dierent results obtained after

    treatment with chemicals of analytical and technical

    grade could be explained by possible interactions of

    impurities with constituents of nutrient solution or with

    Fig. 3. Dry to fresh weight ratio in Lemna minor plants grown on modied Hoaglands nutrient solution supplemented with tested

    chemicals of analytical (left) and technical grade (right). Dierent letters on the top of the column indicate signicant dierences

    between treatments at P ` 0X05 by Duncans New Multiple Range Test.

    M. Vujevic et al. / Chemosphere 41 (2000) 15351542 1539

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    Fig. 5. Chlorophyll a and chlorophyll b content and their ratio in Lemna minor grown on modied Hoaglands nutrient solution

    supplemented with tested chemicals of analytical grade. Values are the average of three dierent experiments represented as percentage

    of control.

    Fig. 4. Relative area covered by Lemna minor plants grown on modied Hoaglands nutrient solution supplemented with tested

    chemicals of analytical grade (left) and technical grade (right). Dierent letters on the top of the column indicate signicant dierences

    between treatments at P ` 0X05 by Duncans New Multiple Range Test.

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    ions of tested solutions. Interactions between the con-

    stituents of the nutrient solution are well known (Wang,

    1992). As a consequence of such interactions, certainsubstances could be more available to plants than others

    and vice versa.

    Chemicals of both analytical and technical grade in-

    creased chlorophyll a and chlorophyll b content, but

    some dierences between chemicals of analytical and

    technical grade were noticed. Chemicals of analytical

    grade caused much greater increase of chlorophyll a

    content in comparison to increase of chlorophyll b

    content, so the chlorophyll a to chlorophyll b ratio was

    also increased (Fig. 5). On the other hand, chemicals of

    technical grade caused greater increase of chlorophyll b

    content in comparison to increase of chlorophyll acontent, so the ratio was slightly decreased (Fig. 6). It is

    possible that the presence of impurities in chemicals of

    technical grade promoted the formation of chlorophyll b

    from the chlorophyll a, possibly by oxidising methyl

    group on pyrol ring no. 2 into aldehyde group (Gil et al.,

    1995).

    Only minor growth dierences caused by chemicals

    of analytical and technical grade support the hypothesis

    that eect noticed after treatment with chemicals of

    technical grade used as high density brines was due to

    the major constituents of these solutions (Ca2, Cl and

    Br ions) and was not the consequence of impurities

    commonly present in chemicals of technical grade.

    However, chemicals of analytical and technical grade

    had dierent eect on chlorophyll pigments content in

    duckweed plants.

    References

    Arnon, D.I., 1949. Copper enzymes in isolated chloroplasts:

    Polyphenoloxidase in Beta vulgaris. Plant Physiol. 24, 115.

    ASTM D 511-93, 1995. Standard test methods for calcium and

    magnesium in water, Test method B, Atomic Absorption

    spectrophotometric. Annal Book of ASTM standards,

    Section 11, Water and Environmental Technology, Vol

    11.01 Water (1), American Society for Testing and Mate-

    rials, Philadelphia, PA.

    ASTM D 512-89, 1995. Standard test methods for chloride ionin water, Test method B, Silver nitrate titration. Annal

    Book of ASTM standards, Section 11, Water and Environ-

    mental Technology, Vol 11.01 Water (1), American Society

    for Testing and Materials, Philadelphia, PA.

    Clement, B., Bouvet, Y., 1993. Assessment of landll leachate

    toxicity using the duckweed Lemna minor. In: Proceedings

    of the Second European Conference of Ecotoxicology.

    Amsterdam. Sci. Total Environ. (Suppl.), 11791190.

    Cowgill, U.M., Milazzo, D.P., Landenberger, B.D., 1991. The

    sensitivity of Lemna gibba G-3 and four clones of Lemna

    minor to eight common chemicals using a 7-day test.

    Research J. WPCF 63 (7), 991998.

    Dirilgen, N., Ince, N., 1995. Inhibition eect of the anionic

    surfactant SDS on duckweed, Lemna minor with consider-

    Fig. 6. Chlorophyll a and chlorophyll b content and their ratio in Lemna minor grown on modied Hoaglands nutrient solution

    supplemented with tested chemicals of technical grade. Values are the average of three dierent experiments represented as percentage

    of control.

    M. Vujevic et al. / Chemosphere 41 (2000) 15351542 1541

  • 7/30/2019 PHYTO 11

    8/8

    ation of growth and accumulation. Chemosphere 31 (9),

    41854196.

    Duncan, D.B., 1955. Multiple range and multiple F tests.

    Biometrics 11, 142.

    Ensley, H.E., Barber, J.T., Polito, M.A., Oliver, A.I., 1994.

    Toxicity and metabolism of 2,4-dichlorophenol by the

    aquatic angiosperm Lemna gibba. Environ. Toxicol. Chem.

    13 (2), 325331.

    Fairchild, J.F., Ruessler, D.S., Haverland, P.S., Carlson, A.R.,

    1997. Comparative sensitivity of Selenastrum capricornatum

    and Lemna minor to sixteen herbicides. Arch. Environ.

    Contam. Toxicol. 32, 353357.

    Gil, J., Moral, R., Gomez, I., Navarro-Pedreno, J., Mataix, J.,

    1995. Eect of cadmium on physiological and nutritional

    aspects of tomato plant. 1 Chlorophyll (a and b) and

    carotenoids. Fresenius Environ. Bull. 4, 430435.

    Hillman, W.S., 1961. The Lemnaceae or duckweeds. Bot. Rev.

    27, 221287.

    Huebert, D.B., Dyck, B.S., Shay, J.M., 1993. The eect of

    EDTA on assessment of Cu toxicity in the submergedmacrophyte, Lemna trisulca L. Aquatic Toxicol. 24, 183

    194.

    Huebert, D.B., Shay, J.M., 1991. The eect of cadmium and its

    interaction with external calcium in the submerged aquatic

    macrophyte Lemna trisulca L. Aquatic Toxicol. 20, 5772.

    Kanekar, P., Kumbhojkar, M.S., Ghate, V., Sarnaik, S., 1993.

    Wola arrhiza (L.) Wimmer and Spirodela polyrrhiza (L.)

    Schleiden as test plant systems for toxicity assay of

    microbially treated dyestu waste water. J. Environ. Biol.

    14 (2), 129135.

    Krajncic, B., Devide, Z., 1980. Report on photoperiodic

    responses in Lemnaceae from Slovenia. Berichte des Geo-

    bot. Inst. 47, 7586.

    Krsnik-Rasol, M., Rendic, L., 1977. The eect of some triazinederivatives on the growth and development of duckweeds.

    Acta Bot. Croat. 36, 7582 (in Croatian).

    Lewis, M.A., 1995. Use of freshwater plants for phytotoxicity

    testing: a review. Environ. Pollut. 87, 319336.

    Lockhart, W.L., Billeck, B.N., Baron, C.L., 1989. Bioassays

    with a oating aquatic plant (Lemna minor) for eects of

    sprayed and dissolved glyphosate. Hydrobiologia 188/189,

    353359.

    Mazuran, N., Hrsak, V., Tomic, M., Papes, D., 1999. Eects of

    CaCl2 and CaBr2 on the fecundity of Planorbarius corneus

    L. Chemosphere 38 (10), 23452355.

    Peterson, H.G., Boutin, C., Martin, P.A., Freemark, K.E.,

    Ruecker, N.J., Moody, M.J., 1994. Aquatic phyto-toxicityof 23 pesticides applied at expected environmental concen-

    trations. Aquatic Toxicol. 28, 275292.

    Pirson, A., Seidel, F., 1950. Zell-und stowechselphysiologiche

    Untersuchungen an der Wurzel von Lemna minor unter

    besonderer Berucksichtigung von Kalium- und Calcium-

    mangel. Planta 38, 431473.

    Sajwan, K.S., Ornes, W.H., 1994. Phytoavailability and bioac-

    cumulation of cadmium in duckweed plants (Spirodela

    polyrrhiza L. Schleid.). J. Environ. Sci. Health A 29 (5),

    10351044.

    Schmidt, D.D., Hudson, T.E., Harris, T.M., 1983. Introduction

    on brine completion and workover uids. Part 1 Chemical

    and physical properties of clear completion brines. Petrol.

    Eng. Int. August, 8096.

    Severi, A., 1991. Eects of aluminium on some morphophys-

    iological aspects on Lemna minor L. Atti. Soc. Nat. e Mat.

    di Modena 122, 95108.

    Smith, S., Kwan, M.K.H., 1989. Use of aquatic macrophytes as

    bioassay method to assess relative toxicity, uptake kinetics

    and accumulated forms of trace metals. Hydrobiologia 188/

    189, 345351.

    Tkalec, M., Vidakovic-Cifrek, Z, Regula, I., 1998. The eect of

    oil industry ``high density brines'' on duckweed Lemna

    minor. Chemosphere 37 (13), 27032715.

    Vidakovic-Cifrek, Z., Tkalec, M., Horvatic, J., Regula, I., 1999.

    Eect of oil industry high density brines in miniaturized

    algal growth bioassay and Lemna test. Phyton cAnn. Rei

    Bot. 39 (3), 193197. (Special issue Second Slovenian

    Symposium on Plant Physiology. Gozd Martuljek, Slove-

    nia).von Sury, R., Fluckiger, W., 1983. The eect of dierent

    mixtures of NaCl and CaCl2 on the silver r (Abies alba

    Miller). Eur. J. For. Path. 13, 2430.

    Wang, W., 1986. Toxicity tests of aquatic pollutants by using

    common duckweed. Environ. Pollut. B 11, 114.

    Wang, W., 1992. Use of plants for the assessment of environ-

    mental contaminants. Rev. Environ. Contam. Toxicol. 126,

    87127.

    Wundram, M., Selmar, D., Bahadir, M., 1997. Representative

    evaluation of phytotoxicity reliability and peculiarities.

    Angew. Bot. 71, 139143.

    Marija Vujevic received her B.Sc. degree in 1998 from the

    University of Zagreb, Croatia. She is M.Sc. student at theFaculty of Science, University of Zagreb. The subject of hercurrent research is in vitro propagation of rare and endangeredCroatian plant species.

    Zeljka Vidakovic-Cifrek received her B.Sc. (1990), M.Sc. (1993)and Ph.D. (1999) degree from the University of Zagreb,Croatia. She is research assistant at the Department of Botany,Faculty of Science, University of Zagreb. Her research interestsfocus on inuence of various environmental factors on physi-ological processes in plants.

    Mirta Tkalec received her B.Sc. degree in 1996 from the Uni-versity of Zagreb, Croatia. She is currently M.Sc. student at theFaculty of Science, University of Zagreb. The main topic of herresearch is evaluation of stress factors by Lemna test.

    Mihovil Tomic received his B.Sc. degree from the University ofSarajevo, Bosnia and Herzegovina and M.Sc. degree from theUniversity of Zagreb, Croatia. He works in INA-Oil industryon analytical aspects in exploration and production of gas andoil as well as on pollution problems in oil industry.

    Ivan Regula is full professor of Plant Physiology at the De-partment of Botany and Botanical Garden, Faculty of Science,University of Zagreb, Croatia. His scientic interests includestructure and function of indolic compounds in plants as well asinuence of xenobiotics on plant metabolism.

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