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Pesticide soil contamination mainly affects earthworm male reproductive parameters Eduardo Bustos-Obregn, Roger Iziga Goicochea Biology of Reproduction Unit. Program of Morphology, ICBM Faculty of Medicine, University of Chile, Santiago, Chile Asian J Androl 2002 Sep; 4: 195-199
|
Pc
concentration |
Survival
(%) at different exposure days |
||
5
days |
15
days |
30
days |
|
0 |
95.0 |
97.5 |
76.3 |
444 |
97.5 |
90.0 |
32.5 |
739 |
90.0 |
91.3 |
13.8 |
1478 |
91.3 |
7.5 |
0 |
Table 2 shows the total number of sperms per worm and in Table 3, values are corrected for body weight. It can be seen that in Table 2 there is no much changes in the sperm number after Pc. When corrected for body weight, low and mid doses show significantly higher figures at 15 or 30 days.
Table 2. Total number of E. foetida spermatozoa exposed to three concentrations of Pc at 5, 15 and 30 days after exposure, mean SD, n = number of worms. cP<0.01, compared with controls ( Dunnet test).
Pc
concentration |
No.
of sperm (107) at different exposure days |
||
5
days |
15
days |
30
days |
|
0 |
8.782.93
(n=10) |
5.902.61
(n=8) |
4.830.91
(n=6) |
444 |
8.423.61
(n=10) |
9.582.58
(n=8) |
7.654.42
(n=6) |
739 |
7.782.95
(n=10) |
6.682.51
(n=8) |
1.294.45c
(n=5) |
1478 |
8.634.47
(n=10) |
8.072.23
(n=4) |
|
Table 3. Total number of E. foetida spermatozoa per mg of body weight exposed to three concentrations of Pc at 5, 15 and 30 days after exposure, mean SD, n = number of worms. bP < 0.05, cP < 0.01, compared with controls (Dunnet test).
Pc
concentration |
No.
of sperm per mg of body (104) at different exposure days |
||
5
days |
15
days |
30
days |
|
0 |
11.263.56
(n=10) |
7.572.64(n=8) |
7.760.79(n=6) |
444 |
14.016.81
(n=10) |
16.595.47(n=8) |
15.294.87c(n=6) |
739 |
12.714.57
(n=10) |
13.156.46(n=8) |
15.025.92c(n=5) |
1478 |
14.926.59
(n=10) |
12.932.31b(n=4) |
|
In agreement with these results, the seminal receptacle diameter, their lumina and luminal area are larger in worms treated with mid- and high Pc doses. There seems to be no change in the hatchability of capsules obtained from treated worms, since the number of worms was not different from controls.
Table 4 shows the histometric data obtained for the seminal receptacles. Table 5 shows the number of cocoons and of worms born from them after 5 weeks of rearing.
Table 4. Seminal receptacle diameter (SR), luminal diameter (L-SR) and luminal area in E. foetida exposed to three concentrations of Pc. mean SD, cP<0.01, compared with controls ( Dunnet test).
Pc
concentration |
SR
diameter ( mm) |
L-SR
diameter ( mm) |
L-SR
area (104 mm2) |
0 |
188.5417.55 |
142.5919.59 |
1.590.42 |
444 |
190.5035.28 |
146.3036.77 |
1.781.03 |
739 |
270.8036.34c |
238.9036.77c |
4.561.35c |
1478 |
287.9738.91c |
236.5748.71c |
4.521.79c |
Table 5. Total number of capsules and worms born in E. foetida exposed to three concentrations of Pc. bP<0.05, compared with controls (Dunnet test).
Pc
concentration |
Capsules
(N1) |
Worms
born( N2) |
N2/N1 |
0 |
220 |
315 |
1.4b |
444 |
77 |
126 |
1.6b |
739
|
84 |
110 |
1.3b |
1478 |
54 |
86 |
1.6b |
Data on body weight of the worms (controls taken as 100 %) are given in Figure 1 for the 3 doses of Pc used at the different time intervals analyzed. A marked weight loss is seen by 15 days. Figure 2 and 3 show the percentage of germ cells with damaged DNA at 5 or 15 days of exposure to the 3 doses of Pc, as revealed by the comet assay. The damage observed by 5 days with the three Pc doses is evident only with the highest dose.
Figure
1. Changes of body weight in E. foetida exposed to three concentrations
of Pc at 5, 15 and 30 days after exposure. compared with controls, control
= 100 %.
Figure 2. Percentage of nuclei
of male germ cells in E. foetida with damaged DNA at 5 days after
exposure (comet assay), cP<0.01, compared with control
(chi-square test).
Figure 3. Percentage of nuclei
of male germ cells in E. foetida with damaged DNA at 15 days after
exposure (comet assay), cP<0.01, compared with control
(chi-square test).
Concerning gross anatomical changes in all worms only coiling was observed with the two higher doses of Pc by 5 and 15 days after exposure and also at 30 days with the lowest dose. Locomotion and feeding of control worms was normal under routine inspection and much less active at all periods for the Pc treated animals. Edema was seldom seen, unrelated to the Pc dose at 15 or 30 days. Constriction or evisceration that has been reported for other chemicals in the literature [1] was not observed.
4 Discussion
Mortality has been the most frequently used parameter to evaluate the chemical toxicity in earthworms [11, 12, 14]. It is postulated, however, that survival is less sensitive from an ecotoxicological point of view [21]. The lethal effect of a chemical is not a necessary consequence in intoxication and sub lethal effects may be produced. Therefore, growth and reproduction, addressed in the present work, have been recommended as useful sub lethal criteria [22,23].
Weight loss in our observations is a valuable indicator of physiological stress, related to the degree of intoxication and time of exposure [1, 24]. A similar trendhas been reported for organochlorine pesticides intoxication [1, 11, 25] and for the effects of fungicides and herbicides in Lumbricus terrestris and Eisenia foetida [26-28].
Coiling, another symptom seen in 100 % of the Pc treated worms, is the consequence of alteration in muscular function elicited by organophosphoric pesticides, which may explain the difficulties for locomotion of the intoxicated worms and their relative inability to feed themselves. These facts are related with weight loss. Reproduction is also interfered, since worms find their partner less easily and copulation is abnormal in terms of mating posture. There is probably also an alteration in the neuromuscular system involved in sperm transfer. Ejection of sperm seems also to be hindered and therefore a large number of spermatozoa is found in intoxicated worms in spite of a clear effect on sperm production under Pc treatment.
Numerous reproductive parameters have been studied in earthworms exposed to various xenobiotics, cocoon production, hatching, viability of the worms produced [11, 14, 15, 29, 30] and sexual maturation [13]. All these are very important issues, but require a very long time of observation. Sperm count seems to be a very sensitive marker [1,16], though in our observations this parameter was probably interfered by the weight loss suffered by the treated worms.
Although the number of capsules produced by Pc treated worms was clearly decreased, the viability of worms hatched from them was not noticeably affected. This may imply that the quality of the ova is not damaged by Pc. Also the sexual characteristics of the worms were not affected.
Genotoxic evaluation, such as that performed using the comet assay, may prove to be a sensitive and useful tool for detecting effect of different chemical pollutants in a variety of organisms, from plants to mammals [20]. It clearly shows that Pc is genotoxic for male germ cells of E. foetida in our experimental conditions, which may be related to increased apoptotic rates of these cells, as has been demonstrated in mice [31].
In conclusion, reproductive parameters of earthworms exposed to agropesticides seem to be useful bioindicators of soil pollution and promising tools to predict genotoxic damage of the germ cell elements.
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Correspondence
to: Dr. Eduardo Bustos-Obregn, P.O. Box 70061, Santiago 7, Chile.
Tel: +56-2-678 6450 Fax: +56-2-7373158
E-mail: ebustos@machi.med.uchile.cl
Received 2002-02-17 Accepted 2002-06-28