Mosquito larval consumption of toxic arborescent leaf-litter, and its biocontrol potential
. Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf‐litter for mosquito contro...
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| Published in | Medical and veterinary entomology Vol. 17; no. 2; pp. 151 - 157 |
|---|---|
| Main Authors | , , , , |
| Format | Journal Article |
| Language | English |
| Published |
Oxford, UK
Blackwell Science Ltd
01.06.2003
Wiley |
| Subjects | |
| Online Access | Get full text |
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| Abstract | . Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf‐litter for mosquito control, feeding rates of third‐instar mosquito larvae were assessed for examples of three genera: Anopheles stephensi Liston, Aedes aegypti (L) and Culex pipiens L. (Diptera: Culicidae).
When immersed in a suspension of non‐toxic leaf‐litter particles (∼0.4 mm), pre‐starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1–2 h ingestion time, filling the intestine up to six to seven abdominal segments for Ae. aegypti, but maxima of five abdominal segments for Cx. pipiens and An. stephensi.
Using three methods to quantify consumption of three materials by third‐instar larvae of Ae. aegypti, the average amount of leaf‐litter (non‐toxic 0.4 mm particles) ingested during 3 h was determined as ∼20 µg/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine (∼100 µm particles extracted from leaf‐litter) during 3 h was ∼80 µg/larva for Ae. aegypti, but only ∼30 µg/larva for Cx. pipiens and 15 µg/larva for An. stephensi, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by Ae. aegypti was intermediate: ∼40 µg/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by Ae.aegypti larvae (humine four‐fold, cellulose two‐fold more than leaf‐litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf‐litter ingested.
Bioassays of toxic leaf‐litter (decomposed 10 months) with 4‐h exposure period (ingestion time) ranked the order of sensitivity: Ae. aegypti (LC50 < 0.03 g/L) > An. stephensi (LC50 = 0.35 g/L) > Cx. pipiens (LC20 > 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf‐litter (0.4 mm particles), as little as 15–30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf‐litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. |
|---|---|
| AbstractList | Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder
Alnus glutinosa
(L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf‐litter for mosquito control, feeding rates of third‐instar mosquito larvae were assessed for examples of three genera:
Anopheles stephensi
Liston,
Aedes aegypti
(L) and
Culex pipiens
L. (Diptera: Culicidae).
When immersed in a suspension of non‐toxic leaf‐litter particles (∼0.4 mm), pre‐starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1–2 h ingestion time, filling the intestine up to six to seven abdominal segments for
Ae. aegypti
, but maxima of five abdominal segments for
Cx. pipiens
and
An. stephensi
.
Using three methods to quantify consumption of three materials by third‐instar larvae of
Ae. aegypti
, the average amount of leaf‐litter (non‐toxic 0.4 mm particles) ingested during 3 h was determined as ∼20 µg/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine (∼100 µm particles extracted from leaf‐litter) during 3 h was ∼80 µg/larva for
Ae. aegypti
, but only ∼30 µg/larva for
Cx. pipiens
and 15 µg/larva for
An. stephensi
, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by
Ae. aegypti
was intermediate: ∼40 µg/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by
Ae.aegypti
larvae (humine four‐fold, cellulose two‐fold more than leaf‐litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf‐litter ingested.
Bioassays of toxic leaf‐litter (decomposed 10 months) with 4‐h exposure period (ingestion time) ranked the order of sensitivity:
Ae. aegypti
(LC
50
< 0.03 g/L) >
An. stephensi
(LC
50
= 0.35 g/L) >
Cx. pipiens
(LC
20
> 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf‐litter (0.4 mm particles), as little as 15–30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf‐litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. Previously we described the mosquito larvicidal properties of decomposed leaf-litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf-litter for mosquito control, feeding rates of third-instar mosquito larvae were assessed for examples of three genera: Anopheles stephensi Liston, Aedes aegypti (L) and Culex pipiens L. (Diptera: Culicidae). When immersed in a suspension of non-toxic leaf-litter particles (approximately 0.4 mm), pre-starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1-2 h ingestion time, filling the intestine up to six to seven abdominal segments for Ae. aegypti, but maxima of five abdominal segments for Cx. pipiens and An. stephensi. Using three methods to quantify consumption of three materials by third-instar larvae of Ae. aegypti, the average amount of leaf-litter (non-toxic 0.4 mm particles) ingested during 3 h was determined as approximately 20 microg/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine (approximately 100 microm particles extracted from leaf-litter) during 3 h was approximately 80 microg/larva for Ae. aegypti, but only approximately 30 microg/larva for Cx. pipiens and 15 microg/larva for An. stephensi, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by Ae. aegypti was intermediate: approximately 40 microg/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by Ae. aegypti larvae (humine four-fold, cellulose two-fold more than leaf-litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf-litter ingested. Bioassays of toxic leaf-litter (decomposed 10 months) with 4-h exposure period (ingestion time) ranked the order of sensitivity: Ae. aegypti (LC50 < 0.03 g/L) > An. stephensi (LC50 = 0.35 g/L) > Cx. pipiens (LC20 > 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf-litter (0.4 mm particles), as little as 15-30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf-litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. . Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf‐litter for mosquito control, feeding rates of third‐instar mosquito larvae were assessed for examples of three genera: Anopheles stephensi Liston, Aedes aegypti (L) and Culex pipiens L. (Diptera: Culicidae). When immersed in a suspension of non‐toxic leaf‐litter particles (∼0.4 mm), pre‐starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1–2 h ingestion time, filling the intestine up to six to seven abdominal segments for Ae. aegypti, but maxima of five abdominal segments for Cx. pipiens and An. stephensi. Using three methods to quantify consumption of three materials by third‐instar larvae of Ae. aegypti, the average amount of leaf‐litter (non‐toxic 0.4 mm particles) ingested during 3 h was determined as ∼20 µg/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine (∼100 µm particles extracted from leaf‐litter) during 3 h was ∼80 µg/larva for Ae. aegypti, but only ∼30 µg/larva for Cx. pipiens and 15 µg/larva for An. stephensi, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by Ae. aegypti was intermediate: ∼40 µg/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by Ae.aegypti larvae (humine four‐fold, cellulose two‐fold more than leaf‐litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf‐litter ingested. Bioassays of toxic leaf‐litter (decomposed 10 months) with 4‐h exposure period (ingestion time) ranked the order of sensitivity: Ae. aegypti (LC50 < 0.03 g/L) > An. stephensi (LC50 = 0.35 g/L) > Cx. pipiens (LC20 > 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf‐litter (0.4 mm particles), as little as 15–30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf‐litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. Previously we described the mosquito larvicidal properties of decomposed leaf-litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf-litter for mosquito control, feeding rates of third-instar mosquito larvae were assessed for examples of three genera: Anopheles stephensi Liston, Aedes aegypti (L) and Culex pipiens L. (Diptera: Culicidae). When immersed in a suspension of non-toxic leaf-litter particles (∼0.4 mm), pre-starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1–2 h ingestion time, filling the intestine up to six to seven abdominal segments for Ae. aegypti, but maxima of five abdominal segments for Cx. pipiens and An. stephensi. Using three methods to quantify consumption of three materials by third-instar larvae of Ae. aegypti, the average amount of leaf-litter (non-toxic 0.4 mm particles) ingested during 3 h was determined as ∼20 µg/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine (∼100 µm particles extracted from leaf-litter) during 3 h was ∼80 µg/larva for Ae. aegypti, but only ∼30 µg/larva for Cx. pipiens and 15 µg/larva for An. stephensi, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by Ae. aegypti was intermediate: ∼40 µg/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by Ae.aegypti larvae (humine four-fold, cellulose two-fold more than leaf-litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf-litter ingested. Bioassays of toxic leaf-litter (decomposed 10 months) with 4-h exposure period (ingestion time) ranked the order of sensitivity: Ae. aegypti (LC50 < 0.03 g/L) > An. stephensi (LC50 = 0.35 g/L) > Cx. pipiens (LC20 > 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf-litter (0.4 mm particles), as little as 15–30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf-litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. Previously we described the mosquito larvicidal properties of decomposed leaf-litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn., due to toxic polyphenols and other secondary compounds. To further examine the biocontrol potential of toxic leaf-litter for mosquito control, feeding rates of third-instar mosquito larvae were assessed for examples of three genera: Anopheles stephensi Liston, Aedes aegypti (L) and Culex pipiens L. (Diptera: Culicidae). When immersed in a suspension of non-toxic leaf-litter particles ( similar to 0.4 mm), pre-starved larvae of all three species ingested sufficient material in 30 min to fill the anterior gut lumen (thorax plus two to three abdominal segments). Gut filling peaked after 1-2 h ingestion time, filling the intestine up to six to seven abdominal segments for Ae. aegypti, but maxima of five abdominal segments for Cx. pipiens and An. stephensi. Using three methods to quantify consumption of three materials by third-instar larvae of Ae. aegypti, the average amount of leaf-litter (non-toxic 0.4 mm particles) ingested during 3 h was determined as similar to 20 mu g/larva (by dry weight and by lignin spectrophotometric assay). Consumption of humine ( similar to 100 mu m particles extracted from leaf-litter) during 3 h was similar to 80 mu g/larva for Ae. aegypti, but only similar to 30 mu g/larva for Cx. pipiens and 15 mu g/larva for An. stephensi, with good concordance of determinations by dry weight and by radiometric assay. Cellulose consumption by Ae. aegypti was intermediate: similar to 40 mu g/larva determined by radiometric assay. Apparent differences between the amounts of these materials ingested by Ae.aegypti larvae (humine four-fold, cellulose two-fold more than leaf-litter) may be attributed to contrasts in palatability (perhaps related to particle size or form), rather than technical discrepancies, because there was good concordance between results of both methods used to determine the amounts of humine and leaf-litter ingested. Bioassays of toxic leaf-litter (decomposed 10 months) with 4-h exposure period (ingestion time) ranked the order of sensitivity: Ae. aegypti (LC sub(50) < 0.03 g/L) > An. stephensi (LC sub(50) = 0.35 g/L) > Cx. pipiens (LC sub(20) > 0.4 g/L). When immersed in the high concentration of 0.5 g/L toxic leaf-litter (0.4 mm particles), as little as 15-30 min ingestion time (exposure period) was sufficient to kill the majority of larvae of all three species, as soon as the gut lumen was filled for only the first few abdominal segments. Possibilities for mosquito larval control with toxic leaf-litter products and the need for standardized ingestion bioassays of larvicidal particles are discussed. |
| Author | Rey, D. Ravanel, P. Tilquin, M. David, J. P. Meyran, J. C. |
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| CitedBy_id | crossref_primary_10_1371_journal_pone_0003432 crossref_primary_10_1017_S0007485311000861 crossref_primary_10_1371_journal_pntd_0005034 crossref_primary_10_1016_j_biochi_2006_04_007 crossref_primary_10_1603_ME11073 crossref_primary_10_3390_insects12070657 |
| Cites_doi | 10.1023/A:1005456124756 10.1023/A:1019920310315 10.1139/z97-091 10.1146/annurev.en.37.010192.002025 10.1006/jipa.1998.4810 10.1002/1520-6327(200008)44:4<143::AID-ARCH1>3.0.CO;2-A 10.1046/j.1570-7458.2001.00793.x 10.1007/978-1-4684-6429-0_2 10.1016/S0764-4469(00)00136-0 10.2307/2401636 10.1002/(SICI)1096-9063(199901)55:1<47::AID-PS859>3.0.CO;2-# 10.1023/A:1020953804114 10.1163/9789004476547_012 10.1023/A:1015257700992 10.1023/A:1005632403561 10.1093/jmedent/26.3.210 10.1006/jipa.1995.1096 10.1021/es00005a016 10.1007/978-1-4757-5897-9 10.1002/etc.5620210109 10.1046/j.1570-7458.1998.00370.x 10.1021/jf0205155 10.1006/mpev.2001.0950 10.1006/jipa.1999.4886 10.1016/S0367-326X(99)00145-8 10.7202/706071ar 10.1093/jee/18.2.265a 10.1016/0147-6513(92)90010-Z 10.1006/eesa.2000.1952 10.2307/1938943 10.1127/archiv-hydrobiol/147/1999/25 10.1016/S0021-9673(99)01007-9 |
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| Keywords | Aedes aegypti • Anopheles stephensi • Culex pipiens • bioassays • biological control • cellulose • consumption rate • detritus • humine • larval feeding rate • ingestion capacity • larval control • larval habitat • larvicides • leaf-litter • lignin • mosquito control • mosquito larvae • polyphenols • France |
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| Snippet | . Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn.,... Previously we described the mosquito larvicidal properties of decomposed leaf-litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn.,... Previously we described the mosquito larvicidal properties of decomposed leaf‐litter from deciduous trees, especially the alder Alnus glutinosa (L) Gaertn.,... |
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| SubjectTerms | Aedes - drug effects Aedes - physiology Aedes aegypti Alnus glutinosa Animals Anopheles - drug effects Anopheles - physiology Anopheles stephensi bioassays Biodiversity Biodiversity and Ecology biological control cellulose consumption rate Culex - drug effects Culex - physiology Culex pipiens Culicidae decomposed leaf litter detritus Diet dose response Ecology, environment Environmental Sciences Feeding Behavior food intake France Global Changes humin humine ingestion ingestion capacity insect pests insecticidal properties Intestines - physiology larvae larval control larval feeding rate larval habitat larvicides leaf-litter Lethal Dose 50 Life Sciences lignin mortality Mosquito Control mosquito larvae Pest Control, Biological Plant Leaves - toxicity plant litter polyphenols toxic substances toxicity |
| Title | Mosquito larval consumption of toxic arborescent leaf-litter, and its biocontrol potential |
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