Proceedings: 9th Tall Timbers Fire Ecology Conference 1969 Lightning Effects on The Forest Complex ALAN R. TAYLOR, RESEARCH FORESTER USDA Forest Service Intermountain Forest and Range Experiment Station Ogden, Utah Stationed at N orthern Forest Fire Laboratory Missoula, Montana is an ever-present part of our natural environment. Brooks (1925) stated that the earth experiences 44,000 thunderstorms per day and that some 1,800 storms are in progress at any given moment. The U.S. Department of Commerce (1966) estimates that these storms produce, collectively, 100 cloud-to-ground lightning discharges each second-or more than 8 million discharges striking the globe each day. If these discharges were evenly distributed over the earth, some half million of them would strike in the world's 8,000 million acres of forested lands every day. These estimates support Viemeister's (1961)· claim that lightning strikes thousands of trees around the world every day. American forestry literature lends further support. From an early survey that included all U.S. National Forests of his day, Plummer (I912) reported that more than 76,000 trees were damaged by lightning in a 4-year period. Wads\vorth (1943) noted that lightning accounted for one-third of the timber mortality in a 15 -year study in the ponderosa pine (Pinus ponderos,1 Laws.) forests of LIGHTNIKG 127 Proceedings: 9th Tall Timbers Fire Ecology Conference 1969 ALA~ R. TAYLOR northern Arizona. Ffolliott and Barger (1967), also working in northern Arizona, found that lightning had damaged fully 10 percent of the 634 sawtimber trees they examined. In western Montana, Taylor (1964a) tallied some 1,000 lightning-struck live Douglas-fir (Pseudotsuga 111enziesii var. glauca (Beissn.) Franco) trees on 10,000 acres of forest land, and Johnson (1966a) reported that lightning directly accounted for 4 percent of the mortality of 406 old-growth ponderosa pines examined in western .i\10ntana. In Pennsylvania, Nelson (1958) found lightning the greatest single cause of mortality (25 percent) of 1,300 mature eastern hemlock (Tsuga canadensis Carr.) trees. Similarly, Trousdell (1955) found lightning one of the greatest single causes of death of loblolly pine (Pinus taeda L.) seed trees in Georgia, and Reynolds (1940) claimed that lightning was directly or indirectly responsible for fully 70 percent of the total volume loss in pine forests in southern Arkansas. Finally, Vogi (1968) reports that more than 30 percent of the Jeffrey pines (Pinus jeffreyi Grev. and Balf.) growing at elevations between 7,000 and 8,000 feet on Mt. Pinos in southern California showed effects of lightning discharges. DIRECT EFFECTS This brief review confirms that lightning strikes frequently in forested areas of this country. Now let's consider some of the consequences. FOREST WILDFIRES Wildfire is probably the most important immediate consequence of lightning in North American forests (Fig. 1). Annually, lightning causes some 10,000 to 15,000 forest fires in the United States. These fires damage commercial timber, watersheds, wildlife, forage, and outdoor recreation values. The total economic loss is difficult to estimate, but lightning fire suppression costs alone may amount to $50 million per year (Barrows, 1966). The problem is most acute in the Western States, where 70 percent of all forest fires are caused by lightning. There a single thunderstorm can start tens of fires in minutes over miles of virtually inac128 FIG. 1. Lightning discharge produced by a small but hard-hitting thunderstorm, typical of those occurring in the northern Rocky l\lountains. Left-hand channel ignited crown foliage of grand fir tree on ridgetop, Sept. 6, 1966. USDA Forest Sen'ice photo. cessible terrain. In August 1961, lightning started nearly 600 fires in one 3-day period on the National Forests in J\lontana, Idaho, Oregon, and \ Vashington (U.S. Dep. Agr., Forest Service, 1962). This characteristic consequence of lightning-many fires in a short timetaxes fire suppression agencies beyond all reasonable limits of manpmver and equipment, and suppression costs soar. 129 ALAN R. TAYLOR The fire-setting discharge :-Most lightning discharges that strike forested lands do not start fires. Why? Certainly, many discharges strike noncombustibles on the forest floor. But many others apparently travel through highly combustible forest fuels yet cause no fire. This suggests that fire-setting discharges may somehow differ from those that do not cause fire. The hypothesis that lightning fires are caused by a special type of electrical discharge is not new. Working with laboratory sparks, McEachron and Hagenguth (1942) hypothesized that explosive effects of lightning discharges result from very short-duration return strokes such as those depicted by the sharp "spikes" in the oscillograph record of the discharge (Fig. 2). The traces here show changes caused by the lightning discharge in the atmospheric electric field. McEachron and Hagenguth reasoned that ignition is most r- --+j 100 milliseconds RI R2 R3 FAST FIELD CHANGE SLOW FIELD CHANGE FIG. 2. This oscillograph record shows fast and slow electric field change traces of a discharge that started a forest fire in western Montana on August 11, 1968. Note the long-continuing current phase following the R3 stroke. 130 LIGHTNING EFFECTS ON THE FOREST likely to occur when a discharge contains, in addition to one or more fast return strokes, a long-continuing current phase in which current flows continuously in the lightning channel for a relatively long duration. This is shown following the third return stroke in Figure 2 (R3), where the upper trace decays slowly to the smooth baseline after some 100 milliseconds of continuous current flow. McEachron and Hagenguth's views apparently were accepted by other workers (Berger, 1947; i\1alan, 1963; Loeb, 1966), but until 1967 only one published work (Norinder et al., 1958) documented characteristics of two lightning discharges and compared their ignition effects. We recently documented the characteristics of 10 lightning discharges that started forest fires in western Montana (see Fuquay et ai., 1967 for data on seven of them). Nine of the 10 strikes exhibited the characteristic long-continuing current phase proposed by McEachron and Hagenguth. One of these nine discharges, recorded in Figure 2, started the forest fire photographed just minutes after ignition and shown in Figure 3. These 10 events, obtained from six storms during the period 196568, support the hypothesis that most lightning fires are caused by discharges having a long-continuing current phase. Mechanisms of lightning-caused ignition :-Lightning discharges develop high temperatures in their ionized paths between cloud and ground. Peak color temperatures of the channel in air range from about 21,000° to 31,000oK. (Zkivlyuk and Nlandel'shtam, 1961; Prueitt, 1963; Uman, 1964 and 1966). i\1uch less is known about the . peak temperatures developed in and near the ground terminal of the lightning discharge, but the literature records evidence of energy sufficient to melt and vaporize several metals (Bellaschi, 1935), to fuse sand particles (Schonland, 1950), and to ignite forest fuels (Barrows, 1951 a). Until now, little has been published about the forest fuel ignition mechanisms of lightning. The subject has only peripheral interest for most workers in lightning research, and to date no definitive publication has appeared. Writers of general texts on lightning have given only perfunctory attention to the problem, usually indicating that Joule heating is the primary mechanism involved. Thus, the 131 ALAN R. TAYLOR FIG. 3. This incipient forest fire was started by the discharge depicted in Figure 2. This photograph was taken minutes after the discharge was recorded at ground station 17 miles away. USDA Forest Service photo. state of knowledge about ignition mechanisms of forest fuels by lightning is summarized in this generalization: The passage of a lightning discharge current through high-resistance forest fuels may result in ignition if the current flow is sustained long enough to heat the fuels to their ignition points. Other mechanisms may also result in ignition by lightning. Research just now beginning at the Northern Forest Fire Laboratory will examine the yarious processes of heat transfer for forest fuel ignition by lightning. Forest fuels :-Considerina the liahtnina-fire phenomenon in terms b b b of its several components-the discharge, the fuels, the antecedent and attendant meteorological environment, the topographical environment, and the fire itself-none is more complex and less understood than the fuels-particularly their role in ignition. We know little beyond the fact that forest fuels are susceptible 132 LlGHTXIXG EFFECTS ON THE FOREST to ignition by lightning. Intuitively \\"e feel that, given a "suitable discharge" to a natural fine fuel particle or bed, some form of pyrolysis or ignition will probably occur and, given some range of combined fuel and meteorological conditions, the ignition will either spread to surrounding fuels or become extinguished. Which fuels are most frequently first ignited by lightning? Plummer (1912), probably the first to survey and publish a comprehensive report on the lightning fire problem, concluded (p. 30): " . . . the majority of forest fires caused by lightning striking trees is due to the presence of dry duff, humus, or litter at the base of the tree." Plummer's statement has been repeated from other areas including the pine-forest belts of Russia (Gribanov, 1955). Likewise Nlorris (1934) tabulating 5,000 Forest Service lightning fire reports from 22 forests in Washington and Oregon, found that needles and duff were the fuels first ignited in 42 percent of the fires. However, he ranked live trees as the most frequent first-ignited fuel on two forests and snags as the most frequent on three others. He reported that shrubs were less important than live trees and snags, and that rotten wood and logs or stumps were seldom the ignition material for lightning fires. This statement contrasts with that of Fobes (1944), who claimed that lightning-caused fires in Alaine usually started in the punky wood of stumps and tree stubs. Barrows' (1951 a) comprehensive treatise on fires in the northern Rocky i\lountains classified 11,835 fires by timber type, according to material first ignited (table 27, p. 86). Importance of these fuel types was indicated by their frequency as first-ignited fuel, as follows: Snags Duff on ground \Vood on ground G reen tree tops 34 percent 30 " 12 " " 10 Grass, moss on tree, slash, brush, and v,eeds followed in descending order of frequency. Comparing all ground fuels to aerial fuels (snags, green tree top, and moss on tree), Barrows' table shows that aerial fuels \vere first ignited in 48 percent of all fires. A recent 4-year Canadian survey of 3,615 lightning-caused fires (Kourtz, 1967) shows that duff, grass, and moss were the first fuels 133 ALAN R. TAYLOR FIG. 4. Latent lightning-caused fire smoldered in decayed heartwood of this live Douglas-fir for 6 days before the tree collapsed and spread fire to ground fuels. USDA Forest Service photo. ignited in more than 60 percent of these fires. An earlier report on the same study (Kiil and Fraser, 1962) noted that survey data from 1960 showed aerial fuels were ignited first in about 40 percent of 620 fires examined. Komarek (I 968), reporting on lightning fires in National Forests in California during 1966, stated that duff and snags ranked first and second, respectively, as fuels first ignited. This review emphasizes that most forest fuels are susceptible to ignition by lightning. However, empirical observations on small lightning fires in the northern Rocky lVIountains lead me to suggest that lightning typically ignites initially only the finer particles of any fuel "struck" by it. The situation appears roughly analogous to the setting of a fire in a fireplace: It too must be started with fine kindling. Some examples of this include the ignition of granular particles of decayed wood in the hearts of trees (Fig. 4); lichens and needles in tree crowns (Fig. 5); oleoresin deposits in tree bole in134 LIGHTNING EFFECTS ON THE FOREST FIG. 5. Left. Lightning discharge on August 3, 1968, in western Montana damaged the western larch, center, and ignited crown fuels in grand fir, right. Fire consumed upper two-thirds of crown. USDA Forest Service photo. FIG. 6. Right. Lightning discharge caused momentary ignition of volatile oleoresin deposits on old interior ring-shake defect (dark areas above hardhat) in this Douglasfir. USDA Forest Service photo. teriors (Fig. 6); and wood slivers resulting from old wounds when a new lightning furrow is partially superimposed upon an old lightning scar (Taylor, 1969) (Fig. 7). The damaged face of a lightningstruck subalpine fir (Abies lasiocarpa (Hook.) Nutt.) trunk is shown in Figure 8. In this tree the discharge created its own kindling, raising and charring hundreds of wood fibers on the surface, but no "forest fire" resulted. This phenomenon, apparently not heretofore reported in the literature, has been observed frequently by the author on both fired and unfired lightning-damaged conifers in the West. Other examples of lightning creating kindling material include the splintering of bare snags, poles, and live tree boles. The latent (holdover) lightning fire:-One of the most common 135 ALAN R. TAYLOR FIG. 7. Left. New lightning damage superimposed on 6-year-old lightning scar on western larch fired by a discharge in western Montana. Lighter portion of furrow in upper part of photo is new damage. Ignition occurred on another superimposed section just out of picture to the right. USDA Forest Service photo. FIG. 8. Right. Discharge split this subalpine fir, raising and charring the tips of wood fibers on damaged surfaces. No "forest fire" resulted. USDA Forest Service photo. but least understood lightning fire phenomena is the so-called "holdover" or latent lightning fire. Such a fire goes undetected for several hours or days (occasionally weeks and months), apparently smoldering in or surrounded by fuels too wet or otherwise unable to support flaming combustion. When fuel and weather conditions are right, the fire spreads, produces smoke and flames, and may be detected (Fig. 4). 136 LIGHT~ING EFFECTS ON THE FOREST How often latent lightning fires occur depends upon one's arbitrary selection of elapsed time between origin and discovery of the fire. F or example, one might classify as latent fires all those not discovered within 12 (or 48, or 72) hours after estimated time of origin. The tabulation below shows the percentages of lightning fires not discovered within those specified time periods, as reported by several wnters. Area NF* R-1, E zone NF, R-l, \Y zone NF, R-5 NF, R-6 NF, R-1 (all) Canada Lightning Fires Lndiscovered 'Yithin Hours: 12 24 72 45 36 42 41 61 20 21 33 22 23 40 6 9 10 10 II Basis, No. Fires Years of Record Source 2,020 14,348 4,363 5,300 14,489 3,615 1931-45 1931-45 19II-20 1940-44 1950-65 1960-63 Barrows (1951b) Barrows (1951b) Show and Kotok (1923) Morris (1948) Losensky** Kourtz (1967) * National Forests of the Forest Service region indicated, e.g., R-l. ** Unpublished data tabulated in 1967 by B. J. Losensky; on file at the Northern Forest Fire Laboratory, Missoula, Montana. These data suggest that some 40 percent of all lightning-caused fires in the far Western United States are undiscovered 12 hours after estimated origin; that about 25 percent are still undiscovered 24 hours after origin; and that 10 percent remain undiscovered 72 hours after origin. Apparently the situation in Canada is similar, although the percentages differ in two of the elapsed time classes. Thus, a considerable percentage of fires must be classed as latent fires even if 72 hours is the selected time-lapsed boundary. Little is known about the fuel and weather conditions attending this type of fire. Most writers suggest that precipitation accompanying lightning keeps fires dormant in duff (i\1orris, 1948; Bennett, 1958) or snags (Show and Kotok, 1923) until these fuels dry out sufficiently to support flaming combustion. This seems true enough, but the generalization must be examined critically and many obser137 ALAN R. TAYLOR FIG. 9. Left. Lightning struck this Douglas-fir and extensively damaged the back side of the trunk (not sho\,,;n) and remond outermost bark scales from about half the circumference of the trunk (white patches, entire length shown). Charred bark on lower bole resulted from earlier ground fire not associated with lightning damage. USDA Forest Service photo. FIG. 10. Right. Douglas-fir shows three spiral lightning furrows (upper left, middle, and lower sections of bole) caused by single lightning event. Here lightning removed bark only, exposing outer wood. USDA Forest Service photo. vations must yet be made if we expect to understand and predict the occurrence of this phenomenon. So much for the major facets of lightning-caused wildfire. I turn now to some non fire lightning effects. As we shall see, these more subtle and less-known lightning effects collectively take a significant toll of forest resources. 138 LIGHTNING EFFECTS OX THE FOREST TREE INJURY AND MORTALITY Individual trees:-Trees frequently become the ground terminals of lightning discharges. Though lightning does not always strike the tallest trees in a forest, it often does (Taylor, 1964a; Kourtz, 1967); and these trees are often the most commercially valuable ones in the stand (Wadsworth, 1943; Johnson, 1966b). Even though most trees struck by lightning probably are not killed outright (Taylor, 1964a), they often suffer loss of increment (Georgievskij, 1963) and volume (Wadsworth, 1943) through structural damage and become susceptible to attack by insects and diseases (Lindh, 1949; Kourtz, 1967). Some trees survive several discharges over the years (Plummer, 1912 ; Taylor, 1969)~ but others die soon after they are hit; sometimes they show no outward signs of injury (Stone, 1914; Stevens, 1916; Hawley, 1937). On still other trees, lightning removes only the outer bark flakes· in its path along the trunk (Dodge, 1936). This superficial flaking is sometimes observed on severely damaged trees (Fig. 9). In conifers the most common damage is a shallow, uniform furrow 2 to 10 inches wide that spirals along the trunk exposing only the outermost layers of sapwood in its path (Vanderlinden, 1907; l\1urray, 1958; Taylor, 1965). Some discharges cause as many as three such furrows at once (Fig. 10). But greater damage is fairly common; and when wood is removed from the bole, it is usually ejected as two parallel slabs or slivers of nearly equal dimensions. Figure 11 shows the locations and distances of two slabs, A and A', ejected from a Douglas-fir tree, and Figure 12 indicates their respective original positions on the bole. Sometimes lightning virtually destroys a tree (Stevens, 1921; McEachron, 1940; Vie meister, 1961) (Fig. 13). Damage to the tree bole is the most obvious, but all parts of the tree are vulnerable. Sometimes lateral roots are severed at the base of a lightning-struck tree (Fig. 14). Branchlets and needles are often damaged by flying bark and wood debris (Fig. 15). Clusters of conifer needles several feet from a damaged bole surface may be damaged by finely divided particles of outer bark ejected from the bole by the electrical discharge (Fig. 16). On some trees several hundred clusters of needles are damaged this \vay. 139 FIG. 11. Pair of 8-foot-long wood slabs marked A and A' was removed from tree (right, background) by discharge to the locations shown. Parallel-slab phenomenon is typical in western conifers where wood is removed by lightning. USDA Forest Service photo. FIG. 12. The pair of slabs in Figure 10 is shown here leaning against parent tree. Symbols indicate identifying limb stubs that show respective original positions of slabs on tree. USDA Forest Service photo. 140 FIG. 13. "Lightning is not averse to striking more than once in the same spot-but frequently once is sufficient." (McEachron 1940). Douglas-fir tree was severed cross sectionally and split longitudinally; one 12-foot chunk was hurled 60 feet, and short-duration ignition occurred on the portion left standing. USDA Forest Service photo. FIG. 14. Soil excavation at base of lightning-struck ponderosa pine shows severed lateral roots (see entire tree at arrow in Figure 17). USDA Forest Service photo. 141 FIG. 15. In this cluster of 153 ponderosa pine needles, growing 4 feet from lightning-damaged bole surface, 136 needles were damaged, showing a total of 613 impact sites from fiying bark particles. Sixty of these impact sites contained embedded particles of outer bark. USDA Forest Service photo. FIG. 16. This particle of outer bark is embedded in a needle from damaged cluster shown in Figure 15. USDA Forest Sen-ice photo. 142 LIGHTNIXG EFFECTS ON THE FOREST Tree groups :-The preceding discussion was directed primarily toward the familiar situation wherein a single tree is struck by lightning. But in many parts of the world, lightning injures and kills groups of trees in a stand as well as individuals. In a typical group kill, external damage is usually visible on only one or two trees in or near the center of the group (LaRue, 1922; Murray, 1958). Other trees around the damaged stems die or show decline, often in a circular pattern (Hauberg, 1960; Anderson, 1964). Tree group mortality caused by lightning has seldom been reported in the United States (but see Stevens, 1918 ; Jackson, 1940; Komarek, 1964); but the literature abounds with such reports from other parts of the world including Sumatra (LaRue, 1922), Honduras (Reinking, 1930), England (Peace, 1940; Shipley, 1946), New Zealand (New Zealand Forest Service, 1954), Scotland (i\1urray, 1958), Borneo (Anderson, 1964; Brunig, 1964), and Australia (Minko, 1966) . Review of the literature on group mortality cited above indicates that those groups apparently were damaged by lightning alone. Curiously, another virtually independent body of literature on forest entomology (discussed in the next section) attributes group killing of trees entirely to bark beetles initially attacking a single lightningdamaged tree in the stand. INDIRECT EFFECTS ATTACKS BY INSECTS Entomologists have long knmvn that lightning-damaged conifers apparently attract several genera of bark beetles (Coleoptera: Scolytidae) (Hopkins, 1909; St. George, 1930; Doane et a/., 1936; Hetrick, 1942; Miller and Keen, 1960; Dixon and Osgood, 1961; Johnson, 1966b; Anderson and Anderson, 1968). The apparent relationship is not well understood, and little is known about frequency of its occurrence. Most entomologists consider this problem minor in comparison with others vying for their attention. The theory that attacks by bark beetles OIl single lightningdamaged trees may lead to mass attacks on surrounding trees has been long accepted (Hopkins, 1909; Reynolds, 1940; Thatcher, 1960; 143 ALAN R. TAYLOR McMullen and Atkins, 1962) . Hodges, l studying physiological changes in southern pines following lightning damage, noted that 26 group infestations by the southern pine beetle (Dendroctonus frontalis Zimm.) in one township in Louisiana each contained at least one lightning-damaged tree. Schmitz and Taylor (1969) recently documented a case of group mortality involving lightning damage and attack by the pine engraver beetle (Ips pini Say) in a stand of 96 young ponderosa pine in western Montana (Fig. 17). Lightning blasted a 66-foot spiral strip of bark from the bole of the struck tree and severed numerous lateral roots. Seventy-three trees within 80 feet of the struck tree were attacked by beetles, and 84 percent of these attacks were successful. On the basis of their observations of root damage to the struck tree and in view of the two bodies of literature on group mortality noted, Schmitz and Taylor suggest the possibility, as did Komarek ( 1964), that lightning may cause unobserved physiological damage to trees surrounding an obviously struck tree, making them susceptible to beetle attack. Understandably, entomologists' research efforts are directed chiefly toward major insect epidemics and measures for controlling them. However, on the basis of the U.S. Department of Commerce estimates of lightning occurrence cited earlier, it appears possible that some 182 million lightning discharges strike on forested lands over the world each year. Hence, the role of lightning in insect ecology may be \vorth further consideration. DAMAGE FROM DISEASES Occasional association of lightning InJury with tree diseases has been \vell documented (Boyce, 1920; Sharples, 1933; Furtado, 1935; Hawley, 1937; Peace, 1962; Komarek, 1964; Hinds and Hawksworth, 1966; Kourtz, 1967). Sharples showed that the so-called bud rot in Malayan coconut palm (Cocos nucifera) is caused by lightning injury and has killed many palms. He also supported Weir's claim (I929) that the so-called dieback of rubber trees (Hevea brasiliensis) 1 Personal communication (October 21, 1966) from Dr. John D. Hodges, Plant Physiologist, Southern Forest Experiment Station. 144 LIGHTNING EFFECTS ON THE FOREST FIG. 17. Aerial view of group kill in western Montana. Ultimately, 73 of 96 ponderosa pine saplings and poles within 80-foot radius of the mature, lightningstruck pine (arrow) were attacked by pine engraver bark beetles. USDA Forest Service photo. was due primarily to lightning and noted that lightning-caused root damage could make a tree particularly vulnerable to root diseases. V ogl (1968) suggests the possibility that cro"Wll rot of the California fan palm (Washingtonia filifera) is preceded by lightning injury to the terminal buds. Apparently no such claims have been made concerning crown or root diseases of conifers in the United States. When its protective bark is removed, a tree usually becomes susceptible to infection. Hence, the large number of lightning discharges into forested areas might be expected to open up potential courts of disease in many thousands of trees throughout the world each year. Most of the reports cited above suggest that lightning injuries to trees are so infrequent as to cause little concern to pathologists or 145 ALA~ R. TAYLOR resource managers. I suggest that, although many other forest disease problems may be more urgent, lightning damage is a more significant precursor of tree diseases than has been generally realized and that the problem deserves further attention. DISCUSSION This paper has dealt with the lightning effects and influences that cause primary concern in protection of the forest complex-forest fire, mortality, injury, and damage from insects and diseases. Although it was written within the framework of protection-oriented research, it should not be construed to indicate that either the author or his organization considers lightning fire and other lightning effects are always and irrevocably harmful. Indeed as Vogi points out, some effects of lightning are beneficial: the culling of overmature and insect- and disease-ridden trees; the needed thinning and other beneficial treatments of forest stands; and, apparently, even the perpetuation of certain tree species. Regarding the little known long-range ecological effects of lightning, Komarek (1964, p. 170) states: It is a truism in ecological thought that any environmental force acting upon living matter, plants or animals, by a process of natural selection, will cause those genes to be selected out of the germ plasm or "gene banks" that will best allow that living matter to succeed in a struggle for existence. Not only has lightning developed fire adaptations, or as most geneticists would prefer, selected out those "preadaptations" for the most successful existence \vith conditions created by fires; but also that plants at least have developed similarly in regard to lightning itself. This is to say, that the reaction to the lightning stroke and attendant . conditions are different in different vegetations. Plants, animals, and possibly life itself, have evolved through a long process of natural selection in an environment where lightning and fires so initiated have been an important factor, more important than many ecologists may realize. Recognizing these useful aspects of lightning effects, the aim of forest protection research is not ultimately the exclusion of all lightning and its effects, but a greater understanding of both and the 146 LIGHTNING EFFECTS ON THE FOREST ability to predict and exercise some control over them for the continuing benefit of mankind. BIBLIOGRAPHY Anderson, J. A. R. 1964. Observations on climatic damage in peat swamp forest in Sarawak. Commonwealth Forest. Rev. 43 (2): 145-158. Anderson, Neil H., and David B. Anderson. 1968. ips bark beetle attacks and brood de\'e!opment on a lightning-struck pine in relation to its physiological decline. The Florida Entomol. 51 (1) : 23-30. BarrO\vs, J. S. 1951 a. Forest fires in the northern Rocky Mountains. V .S.D .A. 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Mem. 3 (24): 147-164, illus. Brunig, E. G. 1964. A study of damage attributed to lightning in two areas of Sborea albida forest in Sarawak. Commonwealth Forest. Rev. 43 (2) : 134-144. Dixon, John c., and E. A. Osgood. 1961. Southern pine beetle: a review of present knowledge. V.SD.A. Forest Serv., Southeastern Forest Exp. Sta. Pap. 128, 34 pp., illus. Doalle, R. \V., E. C. Van Dyke, W. J. Chamberlin, and H. E. Burke. 1936. Forest insects. 463 pp. New York: McGraw-Hill Book Co. Dodge, A. W. 1936. Lightning damage to trees. Pp. 43-55, in: Twelfth Nat. Shade Tree Conf. Proc. Ffolliott, Peter F., and Roland L. Barger. 1967. Occurrence of stem features affecting quality in cutover southv.:estern ponderosa pine. V.SD.A. Forest Serv. Res. Pap. R.\I-28, 11 pp., illus. Fobes, C. B. 1944. Lightning fires in the forests of Maine. ]. Forest. 42:291-293. Fuquay, Donald :\1., Robert G. Baughman, Alan R. Taylor, and Robert G. Hawe. 1967. Characteristics of seven lightning discharges that caused forest fires. ]. Geophys. Res. 72 (24) :6371-73, illus. Furtado, C. X. 1935. Lightning injuries to trees. J. i\'1alayan Branch Roy. Asiatic Soc. XIII, Part II, pp. 157-162. Georgie\'skij, "K. P. 1963. [Damage to trees by lightning.] Lesn. Hoz. 16(10) :47-50. Gribanm', L. "K. 1955. Grozovye Yavleniya i Leshye pozhary. [Thunderstorms and forest fires.] Botan. Zh. 11 0) :429-432, illus. V.SD.A. Forest Servo trans!' Hauberg, P. A. 1960. Lynnedslag i skov. [Lightning damage to forests.] Dansk Sko\'forenings Tidsskr. 45 (6) :236-246. Hawley, Ralph C. 1937. Forest protection. 262 pp. New York: John Wiley and Sons, Inc. 147 ALAN R. TAYLOR Hetrick, L. A. 1942. Some observations of Ips bark beetle attack on pine trees. J. Econ. Entomol. 35 (2) : 181-183. Hinds, Thomas E., and Frank G. Hawksworth. 1966. Indicators and associated decay of Engelmann spruce in Colorado. V.S.D.A. Forest Servo Res. Pap. RM-25, 15 pp., illus. Hopkins, A. 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