277
Toxicology Letters, 18 (1983) 277-284 Elsevier
CHANGES IN HEMOLYMPH GLUCOSE, HEPATOPANCREAS GLYCOGEN, TOTAL CARBOHYDRATES, PHOSPHORYLASE AND AMINO TRANSFERASES OF SUMITHION-STRESSED FRESHWATER RICE-FIELD CRAB (OZIOTELPHUSA SENEX SENEX) (Crustacean;
pesticide; glucogenesis)
A. BHAGYALAKSHMI,
P. SREENIVASULA
REDDY*
and R. RAMAMURTHI
Department of Zoology, Sri Venkateswara University, Tirupati - 517502 (A.P.) (India) (Received
March
(Revision
received
(Accepted
18th, 1983) April
May l&h,
19th, 1983)
1983)
SUMMARY Adult crabs were exposed to 3 concentrations Hemolymph
glucose
demonstrating the controls
Significant
and elevations
when compared influences
of sumithion
in each group
with a control
group
over a 20-day period.
over the course of the experiment.
The group
the most acute and sustained hyperglycemia (2 ppm sumithion) was then analyzed, for changes in hepatopancreas glycogen, total carbohydrates, phosphorylase
aminotransferases. bohydrates
levels were monitored
(P
of phosphorylase
with controls.
of hyperglycemic
These changes hormone,
depressions
in hepatopancreas
and transaminases are discussed
which is released
were observed
glycogen
and
total
in sumithion-stressed
with respect to gluconeogenesis into hemolymph
of stressed
as also and carcrabs
and possible
crab.
INTRODUCTION
Due to indiscriminate and widespread use of pesticides in agricultural and public health operations, many non-target species, some of them important members of food chain, are adversely affected. The tragic incidence of ‘Handigodu syndrome’ of Karnataka has been suggested to be long-term consumption of pesticide-exposed crabs and fish by the local population [l]. In view of this, an elaborate programme to evaluate the impact of pesticides on the physiology and biochemistry of some selected ‘non-target’ animals of the rice-field ecosystem has been undertaken. * To
whom
Abbreviations:
0378-4274/83/$
correspondence AAT,
should
aspartate
be addressed.
aminotransferase;
03.00 0 Elsevier
Science Publishers
AlAT,
B.V.
alanine
aminotransferase.
278
of
Previous studies by our group have shown sumithion (10 hg) to crabs induces
acetylcholinesterase [2]. This
report
activity discusses
that administration of a single dose a significant inhibition in the of nerve mass after 1, 3, 7, 14 and 24 h of intoxication
some
of the
biochemical
changes
in the
crab
after
sumithion intoxication. Crabs were exposed to 3 concentrations of sumithion over 20 days and the group demonstrating the most acute and sustained hyperglycemia was analyzed as also the controls for changes in hepatopancreas glycogen, total carbohydrates, phosphorylase and aminotransferases. MATERIALS
AND
METHODS
Animals Healthy freshwater rice-field crabs (Oziotelphusa senex senex) were collected from local rice fields. 300 crabs with a body weight of 30 -t 2 g (mean * SD) were placed in glass aquaria and allowed to acclimatize for 2 weeks. Ambient temperature was maintained at 26 + 2°C and relative humidity 85 rt 5% under a 12:12 (06.00 to 18.00; 18.00 to 06.00 h) light-dark regimen. The crabs were fed an ad lib. diet of frog muscle daily. The medium in which they were placed was changed after each 24 h.
Pesticide Technical grade (96% w/v) sumithion (fenitrothion; 0,0-dimethyl-O-(3 methyl-4-nitrophenyl) phosphorothioate) obtained from Rallis India Ltd (Bangalore) was used. Sumithion was first dissolved in ethanol and diluted with tap water so that the final concentration was 0.5, 1 and 2 ppm containing 0.001% ethanol. The control crabs were kept in tap water containing the same ethanol concentration (0.001%) as in tap water containing sumithion.
Experimental
design
Following the acclimatization of sumithion. A fourth group group at various time intervals
period, the crabs were exposed to 0.5, 1 and 2 ppm served as control. Crabs were sampled from each up to 20 days of exposure. As mortalities occurred
at the highest sumithion concentration, only crabs which were normal from all external appearances were sampled. To minimize circadian rhythm in the metabolic status of the crabs all sampling was done between 09.00 and 11 .OO h. Crabs were taken individually and hemolymph was taken from the arthrodial membrane using a syringe. The hepatopancreas was excised and frozen. Hemolymph glucose level was determined in all the crabs 1, 3, 5, 7, 15, and 20 days after exposure. Hepatopancreas glycogen, total carbohydrates, phosphorylase and aminotransferases were determined in each crab from the 2 ppm and the control group, 1, 3 and 5 days after exposure.
219
Hemolymph
glucose determination
A 1.O ml of the hemolymph was quickly deproteinized with barium hydroxide (1.5 ml) and zinc sulphate (1.5 ml). After thorough shaking, the precipitate mixture was centrifuged twice to obtain a clear supernatant which was drawn off and stored at 0°C. Glucose determinations were carried out by a calorimetric method [3]. Hepatopancreas
glycogen and TCHO determination
Tissue homogenates of 1% (w/v) were made in 10% trichloroacetic acid solution. Total carbohydrate level was estimated in trichloroacetic acid supernatant and glycogen in the ethanolic precipitate of trichloroacetic acid supernatants by the method of Carroll et al. [4]. A standard sample containing a known quantity of analar glucose solution was run with the experimental samples. The level of the contents was expressed as mg/g wet weight of tissue. Assay of phosphorylase
The activities of phosphorylase ‘a’ (active) and ‘ab’ (total) were estimated in the direction of glycogen synthesis by calorimetric determination of inorganic phosphate released from glucose l-phosphate. The assay has been described by Cori et al. [5]. Inorganic phosphate determinations were made by the method of Fiske and Subbarow [6].
-
1.0
PPm PPm
[)---o
2.0
PPm
I
I
I
I
I
3
5
7
15
Fig. 1. The mean hemolymph of sumithion
ppm sumithion
glucose
Y
levels (+ SD.) Significant
days 1, 3, 5 (P
and day 15 (P~0.01);
levels in hemolymph
I
20
S
for up to 20 days.
groups,
3, 5, 7 (PccO.001) Glucose
0.5
ad
1
DA
trations
CONTROL
-
of controls
for fresh-water differences
and day 7 (P
for 2.0 ppm sumithion throughout
crab exposed
from control
the experiment,
to different
1.0 ppm sumithion group,
days
concen-
levels are as follows: group,
0.5
days 1,
1, 3 and 5 (P
and on day 15 and 20, the 0.5 ppm
group and on day 20, the 1 .O ppm group were not significantly altered. determined in the 2.0 ppm group after day 5. N = 8 for all the groups.
Hemolymph
glucose
were not
280
Assay of aminotransferases The activity
of alanine
and aspartate
aminotransferases
was measured
by the
method of Reitman and Frankel [7]. The reaction mixture in a total volume ml contained: 100 pmol of phosphate buffer at pH 7.4; 20 pmol of L-aspartic (substrate
for AAT)
or 50 pmol of DL-alanine
(substrate
for AIAT);
of 1 acid
2 pmol of L-
ketoglutarate and 0.2 ml of tissue supernatant (5% w/v) prepared in ice-cold 0.25 M sucrose solution as enzyme source. The levels of oxaloacetate or pyruvate formed at the end of incubation (37°C) were measured on Bausch and Lomb calorimeter at 545 nm.
Protein determination In the enzyme source protein content was estimated al. [B] using bovine serum albumin as standard.
by the method
of Lowry et
Data analyses For statistical
analyses
of the data,
Student’s
t-test have been used throughout.
RESULTS
No mortalities occurred at either of the two lower sumithion concentrations or in the control group during the experiment. At the highest sumithion concentration (2 ppm) mortalities commenced after 24 h and continued until day 5. The crabs in this group were depleted by day 5 as a result of sampling and mortalities.
Hemolymph
glucose
The mean hemolymph
glucose levels for each group are shown in Fig. 1. Control
crabs showed a mean value of 8.83 + 0.09 mg of glucose/100 ml of hemolymph. Hemolymph glucose level was significantly (P< 0.001) higher than the control levels in all 3 experimental groups on day 1. The higher the sumithion concentration, the greater will be the hemolymph glucose level. The peak values were obtained at 3 days after exposure to 0.5 and 1 ppm of sumithion and at 5 days after exposure to 2 ppm. The glucose levels showed a gradual decrease from day 3 and the control value was approached at day 15 in crabs exposed to 0.5 ppm and at day 20 in crabs exposed
to 1 ppm.
Hepatopancreas
glycogen and total carbohydrates
Hepatopancreas glycogen and total carbohydrates for the control crabs and those in the highest sumithion concentration are shown in Fig. 2. In the sumithion-stressed crab, glycogen and total carbohydrate levels in hepatopancreas were significantly Glycogen and total carbohydrate levels of (P
281
Hepatopancreas phosphorylase Changes in hepatopancreas phosphorylase activity after sumithion intoxication are shown in Table I. Sumithion-exposure prompted significant elevation in the hepatopancreas phosphorylase activity. Both phosphorylase ‘a’ and ‘ab’ were augmented. The increase in phosphorylase ‘a’ is coupled with the increase in the ratio of phosphorylase a/ah. This indicates the interconversion of inactive phosphorylase to active phosphorylase and explains the decrease in glycogen content after sumithion-intoxication. Hepatopancreas aminotransferases The quantitative activities of AAT and AlAT in hepatopancreas of control and sumithion-exposed crabs after 1, 3 and 5 days are shown in Fig. 3. AAT and AlAT was significantly (P
The results of this study have shown that exposure to lower concentrations
2
-
CONTROL
-
2.0ppm
r
1.4
4
I
I
I
1
3
5
F
P
I
260
4-
I
I
I
1
3
5
DAYS
of
DAYS
glycogen
and total
carbohydrates
levels
(k SD.)
Fig. 2. The mean
hepatopancreas
sumithion-exposed sumithion-exposed
(2.0 ppm) freshwater crabs over 5 days. Glycogen and total carbohydrate levels in the crabs as compared with control crabs are significantly (PC 0.001) lower on days 1,
for control
and
3 and 5. N = 8 for all the groups. Fig. 3. The mean (+ S.D.) hepatopancreatic exposed
(2.0 ppm) freshwater
as compared
with the controls
aminotransferase
crabs over 5 days. Aminotransferase are significantly
(P
activity
levels for control
and sumithion-
levels in the sumithion-exposed
crabs
higher on days 1, 3 and 5. N = 8 in all groups.
282
sumithion
(0.5 and
hemolymph subsequently simply
1 ppm) cause a transitory
hyperglycemia.
The varied
levels of
glucose only occur during the first few days of sumithion exposure and approach control levels for the rest of the exposure time. This may
be due
to the accIimatization
of crabs
to the
toxicant.
At the
higher
sumithion concentration (2 ppm) (but still below LGo concentration), there is a more pronounced and sustained hyperglycemia. This is accompanied by a depletion of glycogen and total carbohydrate levels in hepatopancreas and a significantly higher Ievel of phosphorylase activity and the observed carbohydrate imbalances is, however, not unexpected. Elevation of phosphorylase activity in the h~patopancreas of the crab, whereby glycogenolysis results in hyperglycemia. Crabs stressed by pesticides such as sumithion exhibit gill damage and epithelial mucus accumulation which may lead to hypoxia (author’s unpublished data). There is evidence that this hypoxia in turn is a stimulus to increase circulating glucose levels as an anaerobic energy source. This elevation of hemolymph glucose levels during hypoxia has been attributed to an hyperglycemic agent [9]. Recent studies with crabs have demonstrated repetitive discharges of neurons and hyperglycemia in DDT-intoxicated crabs [lo]. Fingerman et al. [lo] suggested that the discharged material is hyperglycemic hormone. In view of previous findings, it is conceivable in the present case, that sumithion could cause discharge of hyperglycemic hormone from the neurosecretory cells that synthesize it, in a similar way. Earlier, Hohnke and Scheer [I 1] suggested that the primary role of the so-called ‘crustacean hyperglycemic hormone’ is not to elevate hemolymph sugar level, but to elevate intracellular glucose, through the degradation of glycogen by activating the enzyme phosphorylase. This glucose leak into hemolymph causes hyperglycemia [ 12, 131. Further, this suggestion is supported by the fact that in eyestaIk-ablated crabs, injec-
TABLE
I
VARIATIONS
IN HEPATOPANCREAS
SENEX SENEX AFTER Concentration
Enzyme
exposed
Control
2 ppm
EXPOSURE
PHOSPHORYLASE
ACTIVITY
OF OZIOTELPHUS~4
TO 2 ppm OF SUMITHION Autopsy
interval
(days)
_5
1
2
a
2.7 rt 0.1
2.7 + 0.1
2.7 + 0.1
ab
4.9 + 0.4
4.9 i
0.5
4.1 + 0.2
a % ab a
55 3.7 t 1.1*
4.0 t
0.9*
57 4.3 +- 1.0*
ab
1’ 40) 5.6 i 1.0**
(+ 48) 6.1 I 0.7*
(+ 57) 6.9 + 1.0*
a oio ab
55
(+ 15) 67
(+ 24) 66
c+ 45)
(+
(19)
(+
22)
62 0
Values are mean (pm01 of Pilmg protein/h) rt S.D. of eight individ~lals. VaIues in parentheses represent % change over control. Significantly different from control level at *p
283
tion of sumithion [I4] and BHC 1151did not increase the hemolymph glucose level and supports the hypothesis that the sinus gland in the eyestalks of this crab is the main release site for hyperglycemic hormone [ 161. Depletion of glycogen and total carbohydrates was significant (see Fig. 2) in the tissues of crab after exposure to sumithion [17]. Hence it is likely that, to meet the energy demands, the sumithion-exposed crabs depend on other sources for survival Since free amino acid content increases in the tissues of the sumithion-exposed crab [ 171this serves as a precursor for aminotransferases by converting the strategic compounds like cr-ketoglutarate, pyruvate, oxaloacetate, glutamate, alanine and aspartate for gluconeogenesis to meet the energy demands during the sumithion-imposed stress conditions, the same might be envisaged of the role of aminotransferases during sumithion intoxication of the crab. ACKNOWLEDGEMENTS
One of the authors (PSR) gratefully acknowledges financial support by the Council of Scientific and Industrial Research, New Delhi. We are also grateful to Rallis India Ltd. (Bangalore) for the supply of technical grade (96% w/v) sumithion. REFERENCES 1 Nationaf Institute of Nutrition, Annual report (Indian Council of Medical research publications), 1977, p. 184. 2 A. Bhagyalakshmi and R. Ramamurthi, Recovery of acetylcholinesterase activity from Fenitrothioninduced inhibition in the fresh water field crab (Oziotelphusu senex senex), Bull. Environ. Contam. Toxicol., 24 (1980) 866-869. 3 Technicon Corporation, Technicon Autoanalyzer Methodology, 1965, Bulletin N-26 I/II. 4 N.V. Carroll, R.W. Longiey and J.H. Roe, Glycogen determination in liver and muscle by use of anthrone reagent, J. Biol. Chem., 32 (1965) 583-593. 5 G.T. Cori, B. Illingworth and P.J. Keller, in S.P. Coiowick and N.O. Kaplan (Eds.), Methods in Enzymology, Vol. 1, Academic Press, New York, 1955, pp. 200-204. 6 C.H. Fiske and Y. Subbarow, The calorimetric determination of phosphorus, J. Biol. Chem., 66 (1925) 375. ‘7 S. Reitman and S. Frankel, A coiorimetric method for the determination of serum glutamic oxaloacetate and glutamic pyruvic transa~nases, Am. J. Clin. Pathol., 28 (1957) 56-63. 8 O.H. Lowry, N.J. Rosebrough, A.L. Farr and R.J. Randall, Protein measurement with Folin phenol reagent, J. Biol. Chem., 193 (1951) 265-275. 9 D. Porte and R.P. Robertson, Control of Insulin secretion by catecholamines, stress and the sympathetic nervous system, Fed. Proc. Fed. Am. Sot. Exp. Biol., 32 (1973) 1792-1796. 10 M. Fingerman, M.M. Hanumante, U.D. Deshpande and R. Nagabhushanam, Increase in the total reducing substances in the hemolymph of fresh water crab, ~~ryre~~~ff~u guerini, produced by a pesticide (DDT) and an indole-alkylamine (serotonin), Experientia, 37 (1981) 178-179. 1I L. Hohnke and B.T. Scheer, Carbohydrate metabolism in crustaceans. in M. Florkin and B.T. Scheer (Eds.), Vol. V, Academic Press, New York, 1970, pp. 147-164. 12 R. Keller and E.M. Andrew, The site of action of the crustacean hyperglycemic hormone, Gen. Comp. Endocrinol., 20 (1973) 572-578.
284
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