Author: Marc C. Hoshovsky, Global Invasive Species Team, The Nature Conservancy
- Arundo donax is a perennial grass that can reach up to 20 ft. (6.1 m) in height. Although it can be much shorter when damaged or stressed. The stem resembles a corn stalk.
- Leaves are long, flat and grow up to 1.5 ft. (0.5 m) long. They can be green or have variegated green and white stripes the length of the blade.
- Flowering occurs in late summer to early fall, when plants are most easily recognized because of the large, dense flower plumes that develop at the tops of the culms. The plums can grow up to 3 ft. (0.9 m) in length.
- No fruits or seeds typically outside of its native range. The plant spreads through rhizomes and stem nodes that come in contact with the soil.
- Ecological Threat
- Arundo donax invades wetlands such as ditches, stream banks and lake shores. Arundo donax competes for water, nutrients and radiation, suppresses and excludes native vegetation which degrades wildlife habitat, increases fire risks and interferes with flood control. Arundo donax is native to India and was introduced into the United States in the early 1800s for ornamental purposes.
Frequently called a bamboo by many landowners, although from an unrelated part of the grass family.
Arundo donax is a tall, erect, perennial cane- or reed-like grass, 2 to 8 meters high. It is one of the largest of the herbaceous grasses. The fleshy, almost bulbous, creeping root stocks form compact masses from which arise tough, fibrous roots that penetrate deeply into the soil. The culms reach a diameter of 1 to 4 cm and commonly branch during the second year of growth. These culms are hollow, with walls 2 to 7 mm thick and divided by partitions at the nodes. The nodes vary in length from 12 to 30 cm. The leaves are conspicuously two-ranked, 5 to 8 cm broad at the base and tapering to a fine point. The bases of the leaves are cordate and more or less hairy-tufted, persisting long after the blades have fallen. There can be variability in leaf and cane dimensions within a stand, possibly in response to water availability.
The flowers are borne in large (3 to 6 dm long) plume-like terminal panicles between March and September. The spikelets are several-flowered, approximately 12 mm long with florets becoming successively smaller. The rachilla is glabrous and disarticulates above the glumes and between the florets. The more or less unequal glumes are membranaceous, narrow and 3-nerved. They are also slender, pointed and as long as the spikelet. Lemmas are thin, 3-nerved and pilose. These are narrowed upward with the nerves ending in slender teeth; the middle one becomes an awn.
It has little or no genetic diversity in California  and may be effectively one clone across much of the world.
Although Arundo donax has been widely cultivated for a long time, little information on its biology or ecology has been published. Its rapid growth rate and strong vegetative competitive ability enables it to quickly invade new areas and dominate local vegetation. Very little has been published regarding effective ways of controlling arundo and it is difficult at this point to suggest the best strategy for managing the species.
Arundo donax is a native to the countries surrounding the Mediterranean Sea. From this area it has become widely dispersed, mostly through intentional introduction by man, into all of the subtropical and warm temperate areas of the world.
Arundo donax has been widely planted throughout the warmer areas of the U.S. as an ornamental. It is especially popular in the Southwest where it is used along ditches for erosion control. In California, giant reed has escaped cultivation and has become established in moist places, such as ditches, streams, and seeps in arid and cismontane regions. As early as 1820 it was so plentiful along the Los Angeles River that it was gathered for roofing materials. A. donax tolerates a wide variety of ecological conditions. It is reported to flourish in all types of soils, from heavy clays to loose sands and gravelly soils.
Plants grow best in well-drained soils where abundant moisture is available. It can spread from the water's edge up the banks and far beyond the zone previously occupied by riparian woody vegetation. Arundo donax was observed to grow well where water tables were close to, or at, the soil surface. Individual plants can tolerate excessive salinity.
Giant reed can be seriously retarded by lack of moisture during its first year, but drought causes no great damage to patches two- to three-years old. Individuals will survive extended periods of severe drought accompanied by low-pressure humidity or periods of excessive moisture. Arundo's ability to tolerate or even grow well under conditions of extreme drought is due to the development of coarse, drought-resistant rhizomes and deeply penetrating roots that can reach moisture at depth. A. donax can survive very low temperatures when dormant but is subject to serious damage by frosts after the start of spring growth.
Giant reed has played an important role in the culture of the western world through its influence on the development of music, which can be traced back 5000 years. The basis for the origin of the most primitive pipe organ, the Pan pipe or syrinx, was made from A. donax. Reeds for woodwind musical instruments are still made from the culms and no satisfactory substitutes have been developed.
Even before its musical qualities were appreciated, Egyptians used giant reed as early as 5000 B.C. to line underground grain storage. Mummies of the Fourth Century A.D. were wrapped in arundo leaves. Other uses for giant reed include: basket-work, garden fences and trellises, chicken pens, crude shelters, fishing rods, arrows, erosion control, livestock fodder, pulp and ornamental plants. Medicinally, the rhizome has been used as a sudorific, a diuretic, as an antilactant and in the treatment of dropsy.
Very little information is available in the literature regarding the biology of A. donax.
Perdue (1958) reports that arundo does not produce viable seeds in most areas where it is apparently well-adapted, although plants have been grown in scattered locations from seed collected in Asia. The importance of sexual reproduction to the species, as well as seed viability, dormancy, germination and seedling establishment, have yet to be studied and published.
Much of the cultivation of arundo throughout the world is initiated by planting rhizomes which root and sprout readily. Wild stands in the U.S. have been reported to yield 8.3 tons of oven-dry cane per acre , and the species is under consideration as a biofuel crop.
Giant reed grows rapidly. Growth rates up to 0.7 meters/week over a period of several months under favorable conditions is not unusual. Young culms develop the full diameter of mature canes; further growth involves thickening of the walls. The new growth is soft, very high in moisture and has little wind resistance.
Arundo can rapidly invade streambanks and roadside habitats from a few planted individuals. When established, it has a strong ability to outcompete and completely suppress native vegetation. Because it propagates vegetatively, it can form rather pure stands, often at the expense of other plants. In some areas it may so totally invade irrigation ditches as to reduce their water-carrying capacity. It also uses large volumes of water itself, possibly reducing downstream flow in drier riparian areas. It produces thickets that restrict access to riparian areas, and canes can be flammable in the dry season, and produce floating mats that can impede flow or damage bridges during floods.
A survey of 48 public agencies listed arundo as one of the top 53 weed species of concern. Arundo was nominated for Element Stewardship Abstract research by preserve managers from Santa Rosa Plateau and Creighton Ranch.
With proper management, areas infested with arundo may be restored to more desirable vegetation. Since arundo may be spread primarily by dispersal of rhizome fragments along watercourses, removal of the entire rootstock may be adequate to eradicate the plant. Research is needed to determine the importance of sexual reproduction in this species.
Weed control involves three fundamental objectives: prevention, eradication and control.
From a practical viewpoint, methods of weed management are commonly categorized under the following categories: physical, thermal, managerial, biological, and chemical. Physical methods include both manual and mechanical methods. Thermal methods include both broadcast burning or spot treatment with a flame thrower. Managerial methods include the encouragement of competitive displacement by native plants and prescribed grazing. Biological control is usually interpreted as the introduction of insects or pathogens which are highly selective for a particular weed species. Chemical control includes both broadcast and spot application.
The most desirable approach is that of an integrated pest management plan. This involves the optimum use of all control strategies to control weeds. This approach is generally accepted as the most effective, economical, and environmentally sound long- term pest control strategy. In cases where more than one control technique is used, the various techniques should be compatible with one another. Broadcast herbicide application, for example, may not work well with certain managerial techniques (i.e., plant competition).
The two types of physical control methods discussed below, manual and mechanical, produce slash debris that can be disposed of by several techniques. If cut before seeds are produced, debris may be piled and left for enhancement of wildlife habitat (i.e., cover for small mammals). Debris may be fed through a mechanical chipper and used as mulch during re-vegetation procedures. Care should be taken to prevent vegetative reproduction from cuttings. Burning the slash piles is also effective in disposing of slash.
Manual methods use hand labor to remove undesirable vegetation. These methods are highly selective and permit weeds to be removed without damage to surrounding native vegetation.
The Bradley Method is one sensible approach to manual control of weeds. This method consists of hand weeding selected small areas of infestation in a specific sequence, starting with the best stands of native vegetation (those with the least extent of weed infestation) and working towards those stands with the worst weed infestation. Initially, weeds that occur singly or in small groups should be eliminated from the extreme edges of the infestation. The next areas to work on are those with a ratio of at least two natives to every weed. As the native plant stabilizes in each cleared area, work deeper into the center of the most dense weed patches. This method has great promise on nature reserves with low budgets and with sensitive plant populations. More detailed information is contained in Fuller and Barbe (1985). Because of arundo's ability to readily recolonize an area, the best results for all control methods have come from systematic control, working from the top of a watershed down, and covering entire watersheds rather than piecemeal control.
Hand Pulling: This method may be used to destroy seedlings or plants up to two meters tall. Plants or seedlings are best pulled after a rain when the soil is loose. This facilitates removal of the rooting system, which may resprout if left in the ground. Plants should be pulled as soon as they are large enough to grasp but before they produce seeds.
Hand Digging: The removal of rootstocks by hand digging is a slow but sure way of destroying weeds which resprout from their roots. The work must be thorough to be effective. Every piece of root that breaks off and remains in the soil may produce a new plant. Such a technique is only suitable for small infestations or around trees and shrubs where other methods are not practical.
Mechanical methods use mechanized equipment to remove above ground vegetation. These methods are often non-selective in that all vegetation on a treated site is affected. Most mechanical equipment is not safe to operate on slopes over 30 percent. It is also of limited use where soils are highly susceptible to compaction or erosion or where excessive soil moisture is present. Site obstacles such as rocks, stumps or logs also reduce efficiency.
Chopping, Cutting or Mowing: Arundo donax may be trimmed back by tractor-mounted mowers on even ground or by scythes on rough or stony ground. Unwanted vegetation can be removed faster and more economically in these ways than by manual means and with less soil disturbance than with scarification. However, these methods are nonselective weed eradication techniques. They reduce biological control potential (other plants outcompeting arundo) and may open up new niches for undesirable vegetation. In addition, wildlife forage is eliminated. Another disadvantage of chopping, cutting or mowing is that perennial weeds usually require several cuttings before the underground parts exhaust their reserve food supply. If only a single cutting can be made, the best time is when the plants begin to flower. At this stage the reserve food supply in the roots has been nearly exhausted, and new seeds have not yet been produced. The long-term success of above-ground mechanical removal not in combination with other treatments is questionable.
Prescribed burning (Flame Thrower): A flame thrower or weed burner device can be used as a spot treatment to heat-girdle the stems at the base of arundo plants. This technique has advantages of being less costly than basal and stem herbicide treatments and is suitable for use during wet weather; it cannot be used during periods of wildfire hazard. Its effectiveness is comparable to manual cutting. The timing of the treatment may affect resprouting behavior.
Broadcast Burning: Large areas of weed infestation may be burned in order to remove the standing mature plants. This may be accomplished with or without a pre-spray of herbicides to kill and desiccate plants, Notably flammable plants usually do not require any pre-spray treatment. Used alone this method will not prevent resprouting from root crowns. Burning is best followed by 1) herbicide treatment of stumps, 2) subsequent burning to exhaust underground food reserves, and/or 3) revegetation with fast growing native species. Other considerations for the use of prescribed burning include the time and cost of coordinating a burn, and the soil disturbance resulting from firebreak construction.
Prescribed grazing: Giant reed is not very palatable to cattle, but during the drier seasons the animals do not hesitate to graze this species. The younger shoots are eaten first, followed by the upper parts of the older plants.
In many areas of California the use of Angora and Spanish goats is showing promise as an effective control for Arundo donax. In the Cleveland National Forest goats are herded for firebreak management of brush species on over 79,000 acres of land. Goats are less costly to utilize than mechanical and chemical control methods. They can negotiate slopes too steep to manage with machines and do not pose the environmental dangers inherent with herbicides.
A pioneer in the use of goats for weed control in urban settings is Richard Otterstad, owner of Otterstad's Brush Clearing Service (718 Adams St., Albany, CA 94706, (415) 524-4063). The primary weed control "tools" utilized by Otterstad's company are Angora goats and light-weight flexible fencing reinforced with electrified wire. Angora's are preferred over Spanish goats because their smaller size makes them easier to transport (Otterstad uses a pickup truck). Goats prefer woody vegetation over most grasses or forbs, in varying degrees. They will eat desirable woody vegetation if unprotected
Sheep are more selective than goats in their food choices but function well in grazing down a variety of plants. Sheep in feeding experiments may survive for extended periods on a strict diet of Arundo donax , thus sheep may be another practical alternative to mowing.
It is important to properly manage sheep grazing to prevent soil compaction problems which may occur when sheep are allowed to graze an overly damp area. Sheep are valuable not only for weed control but also for additional income from the sale of their wool and their contribution of fertilizer to the soil.
The term "biological control" is used here to refer to the use of insects or pathogens to control weeds. The introduction of exotic natural enemies to control plants is a complex process and must be thoroughly researched before implementation to prevent biological disasters. Such tools are not normally suitable for preserve managers to implement.
A. donax is the subject of an active biological control research program (as of 2006) of the USDA Agricultural Research Service in Texas. Much still needs to be learned about the effectiveness of insects and pathogens at controlling the species. The green bug (Schizaphiz graminum) has been observed to feed on arundo during the winter. In France Phothedes dulcis caterpillars may feed on it. Zyginidia guyumi uses A. donax as an important food source in Pakistan. A moth borer (Diatraea saccharalis) has been reported to attack it in Barbados.
Please notify the California Field Office of The Nature Conservancy of any field observations in which a native insect or pathogen is seen to have detrimental effects on arundo.
Detailed information on herbicides are available in such publications as Weed Science Society of America (1983) or USDA (1984), and will not be comprehensively covered here. The Weed Science Society publication gives specific information on nomenclature, chemical and physical properties of the pure chemical, use recommendations and precautions, physiological and biochemical behavior, behavior in or on soils and toxicological properties for several hundred chemicals. In applying herbicides it is recommended that a dye be used in the chemical mixture to mark the treated plants and thus minimize waste.
There are several herbicide options available, and translocating herbicides are generally considered the only effective tool for long-term control of large infestations. They are able to kill the rhizomes, and thus minimize the resprouting. As with all methods, returning to the site for up to ten years to spot treat resprouts from surviving rhizomes is the only way to prevent a rapid recolonization of the site. Southern California managers have had success with dye-marked broadcast spraying of a glyphosate solution (which produces a delayed effect but up to 95% kill within 3 months of application; Hong and Leu 1979). Glyphosate is also easy and effective for spot-retreatment and translocates to attack the rhizomes. Dowpon-C-grass-killer, based on sodium salts of dalapon and TCA, is applied as a full coverage foliar spray to control deep rooted perennial grasses. Arnold and Warren (1966) used it at a rate of 15 pounds per 100 gallons (plus 2 quarts of surfactant) in late spring and summer on A. donax. This rate gave good top growth kill in 2 to 4 weeks. A small amount of regrowth was evident in 6 months. Fall applications at the same rates resulted in no regrowth the following spring. Horng and Leu (1979) studied the effects of several herbicides on arundo in Taiwan. 2,2 DPA at 6-8 kg/ha gave 80% kill within 25 days. Following either glyphosate or 2,2 DPA application with doses of paraquat showed much faster and more complete control. Paraquat alone at 0.72 kg/ha effectively controlled arundo. Two applications of paraquat was just as effective as a single application. Asulam did not adequately control A. donax.
Detailed observations focused on the vegetational change of the affected area over time will help to determine what method of control would be most efficient.
No quantitative monitoring studies of arundo were discovered in the original preparation of the Element Stewardship Abstract. More may have been created since.
Much more information on seed biology, seedling establishment, growth patterns, and synecology needs to be gathered about arundo. Of great interest is the importance of sexual reproduction over vegetative propagation in the establishment of the plant in new locations. Does arundo produce viable seed in California?
Management research needs include questions such as, what are the most appropriate means of controlling arundo in riparian areas with minimal disturbance to the surrounding native vegetation?
- Global Invasive Species Database. 2011. Invasive Species Specialist Group (ISSG) of the IUCN Species Survival Commission
- University of Florida, IFAS Extension, Center for Aquatic and Invasive Plants
- Plant Conservation Alliance's Alien Plant Working Group
- Department of Conservation and Recreation
- California Invasive Plant Council
- USDA NRCS PLANTS
- USDA ARS GRIN
Management Resources and Programs
- ↑ Perdue, R. E. 1958. Arundo donax - source of musical reeds and industrial cellulose.Econ. Bot. 12(4):368-404. 1.00 1.01 1.02 1.03 1.04 1.05 1.06 1.07 1.08 1.09 1.10 1.11
- Ahmad, R., P-S Liow, D.F. Spencer, and M. Jasieniuk. 2008. Molecular evidence for a single genetic clone of invasive Arundo donax in the United States. Aquatic Botany 88:113-120.
- ↑ Robbins, W. W., M. K. Bellue, and W. S. Ball. 1951. Weeds of California. California Dept. Agric., Sacramento. 3.0 3.1 3.2
- ↑ Wells, M. J., K. Duggan, and L. Henderson. 1980. Woody plant invaders of the central Transvaal. Pp. 11-23 in Proc. 3rd National Weeds Conf. South Africa. 4.0 4.1
- Rezk, M. R. and T. Edany. 1979. Comparative responses of two reed species to water table levels. Egypt. J. Bot. 22(2):157-172.
- Iverson, M.E. 1994. The impact of Arundo donax on water resources. In: Jackson, N.E., P.Frandsen, S. Douthit (eds.), November 1993 Arundo donax workshop proceedings, pp 19-25. Ontario, CA
- Armer, A. 1964. Report by the statewide control committee of the California State Chamber of Commerce.
- ↑ Watson, H. K. 1977. Present weed control projections for the year 2001. Unpublished manuscript. Copy on file at The Nature Conservancy, California Field Office, 785 Market Street, 3rd Floor, San Francisco, CA 94103. 8.0 8.1
- ↑ Fuller, T. C. and G. D. Barbe. 1985. The Bradley method of eliminating exotic plants from natural reserves. Fremontia 13:(2): 24-26. 9.0 9.1
- Jones and Stokes Associates. 1984. Transmission right-of-way vegetation management program: analysis and recommendations. Prepared for Seattle City Light, Seattle,Washington. Copy on file at The Nature Conservancy, California Field Office, 785 Market Street, 3rd Floor, San Francisco, CA 94103.
- Wynd, F. L., G. P. Steinbauer, and N. R. Diaz. 1948. Arundo donax as a forage grass in sandy soils. Lloydia 11(3):181-184
- Daar, S. 1983. Using goats for brush control. The IPM Practioner 5(4):4-6.
- Andres, L. 1979. Untitled. Unpublished manuscipt. Copy on file at the Nature Conservancy, California Field Office, 785 Market Street, 3rd Floor, San Francisco, CA 94103.
- Fratteggiani-Bianchi, R. 1963. [Possibilities of using the leaves of the common cane (A.donax) in animal feeding]. Riv. Zootec., Milano 36(6):343-353.
- Zuniga, G.E., V. H. Argandona, H. M. Niemeyer, and L. J. Corcuera. 1983. Hyroxamic content in wild and cultivated Gramineae. Phytochemistry 22(12):2665-2668.
- Dufay, C. 1979. [Phothedes dulcis, new record for the French fauna (Lepidoptera:Noctuidae)]. Alexanor 11(2):82-84 (in French).
- Ahmed, M., A. Jabbar, and K. Samad. 1977. Ecology and behavior of Zyginidia guyumi(Typholocyloinae:Cicadellidae) in Pakistan. Pak. J. Zool. 9(1): 79-85.
- Tucker, R. W. E. 1940. An account of Dicatraea saccharalis with special refernce to its occurrence in Barbados. Trop. Agric., Trinidad 17:133-138.
- Weed Science Society of America. 1983. Herbicide handbook.
- United States Department of Agriculture. 1984. Pesticide background statements. Vol. I:Herbicides. Agric. Handbook No. 633, U.S. Government Printing Office, Washington,D.C.
- Arnold, W. J. and L. E. Warren. 1966. Dowpon C. Grass Killer - a new product for controlling perennial grasses such as Johnson grass and Bermuda grass. Down to Earth 21(4):14-16.
- Horng, L. C. and L. S. Leu. 1979. Control of five upland perennial weeds with herbicides.Pp. 165-167 in Proc. 7th Asian-Pacific Weed Sci. Soc. Conference.
- Veselack, M. S. and J. J. Nisbet. 1981. The distribution and uses of Arundo donax(abstract). Proc. Indiana Acad. Sci. 90:92.