, - A reprint from WILDLIFE AND REFORESTATION IN THE PACIFIC NORTHWEST Hugh C. Black , Th I'S fil Abou e Wa s cr e t Thi. 'iV1i s File ated ss ca · , ns I·d by s c e a nn ntI· .(:lle h oWe · " ing d bY . ver, t h e Pri t he s SOtn nted oftw e tnls PUbl are h take icati s tna ave on bee n y rern a i n. o r C rect ed , . :I \ SYMPOSIUM PROCEEDINGS 1969 COPIES OF THESE PROCEEDINGS are available for $3.00 each from School of Forestry Oregon State University Corvallis, Oregon 97331 SCHOOL OF FORESTRY OREGON ST ATE UNIVERSITY PROTECTION OF CONIFEROUS SEEDS FROM RODENTS M. A. Radwan Pacifi c Northwest Forest and Range Expt. Sta. Olympia, Washington ABSTRACT Methods for protecting coniferous seed from rodents are reviewed. These include mechanical devices, poison baits, toxicants and repellents, and biological control. The review suggests the need for strengthening research on the protection of seeds, because today, available methods for the control of rodents arc inadequate. INTRODUCTION Regeneration of conifers from seed is often delayed or entirely prevented by various biota that destroy the disseminated seed before germination. The destructive agents include seed-cating rodents, birds, insects and other invertebrates, and fungi (2, 6, 14, 17). Although the depredation by these agents varies by area, seed species, and year, seed-eating rodents, especially deer mice (PeromysclIs sp.), shrews (Sorex sp.), ground squirrels (Citelllls sp.), and chipmunks (ElIlumias sp.) are generally recognized to cause the greatest losses of seed in the Pacific Northwest. Although we have measures to protect seed primarily from rodents,valuable seed is still lost to them and to other destructive agents. If, however, the actual causes of the loss of seed and effective chemicals to protect seed from each of these agents can be more accurately determined, surely a mixture of chemicals can be formulated to protect seed from all the destructive agents. Until then, a thorough knowledge of available methods of protection will help to guide our present and future efforts. DISCUSSION Mechanical Methods Seed in seed spots has been protected, with variable success, by many mechanical devices. These include mulches (26), paper pieces (7), and beer cans· (I I ). Wire screens, made of hardware cloth, or window screens provide the most practical protection, mechanically (12, 16). Some screens are partially closed at the top and do not require removal after the seed germinates (21). Screens, securely anchored with stakes, can withstand some trampling and frost heaving. Although they offer positive protection from rodents and birds, screens do not protect the seed from insects or fungi. Poison Baits A formulation of oats or wheat, with thallous sulfate or sodium fluoroacetate (1080) and a coloring material, has been devised to control seed-eating rodents (8. 18). Now, most poison baits for rodents on forestlands in the Pacific Northwest contain Compound 1080. It is applied to grain (usually soft. white wheat) at 2 ounces for each 100 pounds for hand distribution of from 2 to 4 pounds of grain for each acre, and at 10 ounces for each 100 pounds for aerial application of Y2 pound for each acre. The basis for these formulations and rates of application is not clear, although the original basis for th concentration of the formulation centered on the development of a bait that contained enough poison on one grain to kill a mouse. Recent tleld trials by the U. S. Bureau of Sport Fisheries and Wildlife have shown that reduction in the 52 concentrations of the formulation does not impair the e ffectiveness of the bait (W. E. Dodge, personal communication). More infonnation is needed to accurately determine levels of rodent populations that require baiting before the seeding of conifers and whether baiting is really · necessary when seeds are treated with endrin . \ Today, control of rodents is possible only for short periods of time with poison baits, because elimination of the initial rodent populations is incomplete and reinfestation from untreated areas is often rapid. Control may sometimes be effective if buffer strips are included in the baiting operation (8)-or by rebaiting (24). Also, poisons today are hazardous to nontarget species, antidotes are ineffective against primary and secondary poisoning of nontarget species, and warning symptoms are absent after ingestion. The University of California at Davis is now experimenting with Diphacin (Diphacinone) at concentrations of from 0.005 to 0.05 percent in oats. This chemical is a slow-acting anticoagulant and its antidote is vitamin K-I. It is considered much safer than the acute poisons, and preliminary experiments in California show it as effective as 1080. Compound 1080, directly applied at low concentrations to coniferous seed, has successfully protected untreated seeds because, after a sublethal dose of the bait, the rodents subsequently avoid the seed (25). Similar experiments with 1080 (15) and tetramine (3) failed, however. Consequently, the hypothesis of aversion to protect direct seeding or natural seedfall appears unpromising today. Addition of chemosterilants to poison baits to inhibit the reproductive ability of rodents that survive the toxicant has not been tried. This approach might be possible, if suitable chemosterilants were available. Direct Application of Toxicants and Repellents to the Seed For many years, chemicals have been applied directly to seed to protect it from rodents. Compounds tested in early trials included borax, carbolic acid, iodoform. naphthalene, quinine, tannic acid, zinc chloride,. zinc phosphide, and 1080 (22, 26). Recently, the U. S. Bureau of Sport Fisheries and Wildlife tried tetramine and endrin. Tetramine was obtained by the Bureau's Denver Wildlife Laboratory from the Bayer Company in Germany in the early 1950's. At first, the chemical was applied by soaking seed in an acetone solution for I hour. Later the treatment was changed to coating the seed with the chemical. The number of seedlings produced from treated seed shows that both treatments protected the seed somewhat (4, 9). The treatments, however, sometimes inhibited seed germination (5, 19) and did not protect seedlings, unaffected at germination, from rodents as originally claimed (19). Also, the Bayer Company discontinued , manufacture of the chemical, mainly because of its extreme toxicity. Tetramine, therefore, became unavailable for further seed treatment. Endrin to protect coniferous seed has been recommended by the U. S. Bureau of Sport Fisheries and Wildlife since 1956. A coating at 0.5 percent concentration (active ingredient from 50 percent wettable endrin powder), with an adhesive (Dow latex 512 R or Rhoplex AC 33) to hold the ingredient to the seedcoat and a coloring material (aluminum flake or monastral green pigment) is recommended. The treated seed is identifiable, and feeding by some birds may be discouraged with this treatment. Sometimes, 2 percent Arasan has been added to the formulation to protect the seed from disease, to repel birds, and to increase effectiveness of the treatment against rodents. Essentially, seed is treated by either of two ways. A mixture of the endrin (or endrin and Arasan) with the adhesive is applied to the seed. Or the seed is moistened with the adhesive and the active ingredient is applied. The seeds are then coated with aluminum flake or coloring pigment. Then, they may be returned to containers or left to dry overnight. The treatment with endrin protected the seed adequately from rodents and produced satisfactory regeneration of Douglas-fir in several field trials (I, 4, 13, 20). The treatment, however, especially when Arasan was added, sometimes inhibited germination (23). Also, it protected ponderosa pine seeds inadequately from chipmunks and ground squirrels. Some forest managers have recently indicated dissatisfaction with the recommended treatment of 0.5 percent on Douglas-fir seeds and have frequently increased t.l1e concentrations of endrin. For more than a decade, the endrin treatment of Douglas-fir seed has remained unchanged, except for the elimination of Arasan. This fungicide apparently failed to increase the effectiveness of the treatment as originally claimed (1). Improvement of the treatment can be done by carcful evaluation, both in cages and in the Held, to determine: (I) the best method for treatment of seed, (2) the minimum amount of endrin required for effective protection of seed, (3) the need for prebaiting when seed is treated with endrin, (4) the hazards to nontarget species, and (5) the possible benefits- of adding more effective bird repellent to the treatment. In the Animal Damage Project of the Pacific Northwest Station, we have attempted to iIT,lpregnate Douglas-fir seed with endrin. Our laboratory experiments showed that impregnation is possible, without impairment to the viability of seed, immediately following impregnation or after 4 months of storage. Our feeding tests with caged Peromyscus showed that impregnated seed was as effective as a coating treatment of I percent and significantly better than the recommended treatment of 0.5 percent. Impregnated seed had endrin in and on the seedcoat and in the edible portion of the seed. The total endrin present, however, was less than that possible with the treatment of 0.5 percent. Also, seedlings produced from impregnated seed were normal in appearance and growth. This method of treating seed appears promising. Because the edible portion of the seed is impregnated with the chemical, the chemical is protected from weathering and seeding equipment. Therefore, impregnated seeds may be effective against rodents for a longer time and. possibly. more effective against chipm unks and ground squirrels than coated seeds. But impregnated seeds may be more hazardous to some seed-eating birds and other nontarget species. Another approach to the protection of seed with chemicals has been tried. Laboratory studies at the University of California showed that deer mice detect seeds by sense of smell (10). Possibly, then, the odor of the seed could be masked with a chemical to make the seed undetectable by rodents. As our knowledge of factors that affect preferences of rodents and birds for seed increases, the application of naturally occurring compounds as repellents may be possible. Such compounds, I believe, will be safer and more effective than the chemicals now available. Biological Control Introduction of predators or disease to reduce rodent populations and thus protect seeds is among the possibilities for biological control. Today, however, such methods may lack sufficient promise for serious consideration. CONCLUSIONS AND RESEARCH NEEDS Methods now available for protection of coniferous seed from rodents are: (1) screens, (2) poison baits, and (3) endrin. Each method has limitations that can be eliminated only through research. Research is needed to: (I) reduce the cost of screens; (2) determine the minimum concentration of 1080 required for effective control of rodents, examine the value of prebaiting, and introduce safer rodenticides with attractants and chemosterilartts; (3) devise a more effective bird repellent for addition to the recommended endrin treatment; and (4) test, in the field, seed impregnated with endrin. Also, chemicals and other factors that affect detection of and preference for seed by animals should be investigated. Such investigations may lead to nonchemical methods of protection or, to chemicals that are safer and more effective than endrin. LITERATURE CITED I. DICK, JAMES, J. M. FINNIS, LEE O. HUNT, and NELSON B. KVERNO. "Treatment of Douglas-Fir Seed to Reduce Loss to Rodents." 1. Forest. 56:660-661. 1958. 2. DICK, JAMES, and NORMAN E. JOHNSON. "Carabid Beetles Damage Douglas-Fir Seed." J. Econ. Entomol. 51:542-544. 1958. 3. DICK, JAMES, and W. H. LAWRENCE. Protective Seeding with Tetramine-Coated Douglas-Fir Seed. Weyerhaeuser Timber Co. Forest. Res. Notes, 10 pp. 1957. 4. DIMOCK, EDWARD J. II. A Comparison of Two Rodent Repellents in Broadcast Seeding Douglas-Fir. U. S. D. A. Forest Servo Pacific Northwest Forest & Range Exp. Sta. Res. Pap. 20, 17 pp. 1957. 5. FINNIS, J. M. The Use of Tetramine in the Direct Seeding of Douglas-Fir in Coastal British Columbia. Brit. Columbia Forest Servo Res. Notes 31, 22 pp. 1955. 6. GASHWILER, JAY S. "Conifer Seed Survival in a Western Oregon Clearcut." Ecology 48:431-438. 1967. 7. HATTERSLEY, JOSEPH G. "A Method of Direct Seeding in S3 I Rodent Infested Areas of Summer Drought. " J. Forest. 51:579. 1953. 8. HOOVEN, EDWARD F. Some Experiments in Baiting Forest Lands for the Control of Small Seed Eating Mammals. Oreg. State Board Forest. Res. Jull. 8, 70 pp. 1953. 9. HOOVEN, EDWARD F. Field Test of Tetramine Treated Douglas-Fir Seed. Oreg. State Board Forest Res. Note 29, I I pp. 1956. 10. HOWARD, WALTER E.,and RONALD E. COLE. Olfaction in Seed Detection by Deer Mice. 1. Mammal. 48:147-150. 1967. I I. JUHREN, GUSTAF. Protecting Direct Seedings Rodent-Infested Areas. J. Forest. 48:443-444. 1950. in 12. KEYES, JOSEPH, and CLARENCE F. SMITH. "Pine Seed-Spot Protection with Screens in California." 1. Forest. 41:259-264. 1943. 13. KVERNO, NELSON B., and HARRY D. HARTWELL. (Comp.) Pacific Northwest 1955-56 and 1956-57 Experimental Seeding Studies. Progr. Rept.-November 1957. U. S. Fish & Wildlife Servo Bur. Sport Fisheries & Wildlife, 50 pp. 1957. 14. LAWRENCE, WILLIAM H., and J. H. REDISKE. Fate of Sown Douglas-Fir Seed. Forest Sci. 8:210-218. 1962. IS. MCKEEVER, STURGIS. Compound 1080 and Forest Regeneration. Characteristics of the Poison in Relation to Bait Shyness, Poison Shyness, Toxicity to Rodents, and Phytotoxicity to Conifer Seed. Calif. Dep. Conserv. Div. Forest. Resources Agency, 18 pp. (n. d.) 16. MILLER, CHARLES I. "An Economical Seed Spot Protector." J. Forest. 38:733-734. 1940. PURCHASED 54 BY 17. MOORE, A. W. Wild Animal Damage to Seed and Seedlings on Douglas-Fir Lands of Oregon and Washington. U. S. Dep. of Agr. Tech. Bull. 708,28 pp. 1940. 18. ORR-EWING, A. L. Rodent Control in Direct Seeding Through Use of Poisons. Brit. Columbia Forest Servo Res. Note 17,8 pp. 1950. 19. ROY,D. F. Seed Spot Tests with Tetramine-Treated Seed in Northem California. J. Forest. 55:442-445. 1957. 20. ROY, D. F. Seed Spotting with Endrin-Treated Douglas-Fir Seed in Northwestem Califomia. U. S. D. A. Forest Servo Pacific Southwest Forest & Range Exp. Sta. Tech. Pap. 61, 12 pp. 1961. 21. ROY, D. F., and G. H. SCHUBERT. K-S.creen Seed Spots. U. S. D. A. Forest Servo Calif. Forest & Range Exp. Sta. Forest Res. Note 88,2 pp. 1953. 22. SCHUBERT, G. H. A Trial of Three Chemicals as Rodent Repellents in Direct Seeding. U. S. D. A. Forest Servo Calif. Forest & Range Exp. Sta. Forest Res. Note 84, 2 pp. 1953. 23. SHEA, KEITH R. Field Survival of Thiram-Treated Douglas-Fir Seed. Weyerhaeuser Co. Forest. Res. Note 38,8 pp. 1961. 24. STEIN, WILLIAM I. More Natural Regeneration by Controlling Seed-Eating Rodents. U.S.D.A. Forest Servo Pacific Northwest Forest & Range Exp. Sta. Res. Note PNW-12,10 pp. 1964. 25. TEVIS, LLOYD JR. Behavior of a Population of Forest Mice When Subjected to Poison. J. Mammal. 37:358-370. 1956. 26. WILLIS, C. P. The Control of Rodents in Field Seeding. Soc. Amer. Forest. Proc. 9:365-379. 1914. THE FOREST SERVICE, U.S. DEPARTMENT OF AGRICULTURE, FOR OFFICIAL USE.