Salt injury to landscape plants

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A2970 Salt injury to landscape plants K. A. D E L A H A U T A N D E. R. H A S S E L K U S Injury due to salt is most common on landscape plants growing near highways, streets, sidewalks, and driveways that are regularly salted during the winter for ice control. Most of the salt used for deicing is sodium chloride ordinary rock salt or table salt. On highways the major problem to plants is caused by salt spray kicked up by fast-moving traffic on wet, salted roads. The salt spray is deposited on nearby plants causing dehydration of the tissue. In the city, where traffic speeds are slower, the major problem is salt runoff washing into the soil or saltladen snow plowed or shoveled onto parkways. Salt in the soil may be absorbed by the roots and cause direct toxic effects or may simply prevent roots from taking up water. The symptoms become evident as growth begins in the spring and may take several years to fully develop. Salt applications made after March 1, when plants are beginning to break dormancy, cause the most damage because plants are actively growing and taking up soil water. Symptoms and effects Salt spray Symptoms of salt injury often appear suddenly in early spring once the weather begins to warm. The symptoms may develop progressively over several years and often multiple symptoms occur simultaneously. On deciduous plants, salt spray can kill buds and twigs. New shoots grow from the base of the branch producing dense clusters of twigs known as witches brooms. Often when flowering plants repeatedly fail to bloom, the cause may be attributed to bud injury by salt spray. When vegetative buds die, plants may become misshapen as the absence of branches on the side of the plant that receives salt spray becomes apparent. Landscape plants may also show slowed growth or thinning of the crown as twigs and sometimes large branches begin to die. Excess soil salt caused this leaf burn. Symptoms on deciduous plants typically appear during hot, dry weather when soil moisture is limited. The discolored trees next to the highway have been injured by salt spray. On evergreens, symptoms are most evident in early spring.

S A L T I N J U R Y T O L A N D S C A P E P L A N T S In conifers, salt spray causes browning or yellowing of the needles and twig dieback. These symptoms become evident in late February or early March. Initially, only the tips of the needles show discoloration. As spray damage worsens, the discoloration moves from the tip of the needle inward, eventually discoloring it completely. Once new growth begins to develop, affected trees appear to recover. However, close examination will reveal that the damaged needles remain discolored; only the new growth is green. Salt spray causes dehydration of plant tissue, impairing the tissue s ability to survive over winter. For example, buds that normally tolerate cold temperatures may be killed by those same cold temperatures when subjected to salt spray. Salt in the soil Salt that enters the soil harms plants differently than salt spray. Salt disrupts the balance of nutrients and water between the soil and the plant, causing plant decline. Salt causes soil particles to absorb moisture in the same way a salt shaker attracts moisture under humid conditions. Because the soil particles hold water more tightly, less water is available for uptake by the plant. Damage caused when salt enters the soil is slower acting and plants may not show symptoms for several years. Symptoms on deciduous plants grown in soil with high salt concentrations include browning along the edges of leaves. Leaf burn usually appears in late summer or during periods of hot, dry weather when soil moisture becomes limiting. Long-term symptoms of excess salt in the soil may be more subtle. Plants may be stunted, showing a general lack of vigor. Affected plants may produce fewer, smaller leaves that are often chlorotic. In addition, you may see premature fall coloration and leaf drop. All of these changes decrease the plant s capacity to convert light into sugar, causing a further decline in plant health. Another symptom of plant decline caused by high salt levels is reduction in the size of the flowers and fruit produced. High salt concentrations restrict the uptake of potassium and magnesium by the plant, causing general plant decline. Roots growing in salty soils absorb toxic levels of the sodium and chloride ions that make up common deicing salt. These ions accumulate in needles, buds, and twigs causing dehydration and an imbalance of nutrients. Too much salt in the soil can alter the physical structure of the soil. Excess sodium prevents soil from forming clumps. Poor clumping makes soil vulnerable to compaction, reducing soil permeability and aeration and increasing the likelihood of soil erosion and surface runoff. Diagnosis When making a diagnosis of salt injury, keep in mind that similar symptoms may result from several other causes. Construction injury, winter desiccation, air pollution, nutrient imbalances, improper planting, and root, vascular or canker diseases, all produce symptoms similar to those of salt injury. Fortunately there are certain patterns associated with salt injury that distinguish it from other causes. Salt spray injury The severity of damage increases with the volume and speed of traffic and the amount of salt used. The side of the plant facing the road is more severely damaged. Damage is more severe on plants growing downwind from the road. Most damage occurs within 30 50 feet of the road and decreases with distance from the road. Branches that were covered with snow show no signs of damage. Branches growing above the spray drift zone are not injured. On dense plants where salt spray can penetrate only a short distance in, damage appears only on the outer portions. Sheltered plants show no signs of injury. Soil salt injury Damage increases with the amount of salt used. Most damage occurs within 30 50 feet of the road and decreases with distance from the road. Plants growing in poorly drained soils or in areas where highway runoff collects are injured more severely. Plants that are only marginally hardy for the area are injured more severely than other marginally hardy plants grown away from the road. If you suspect salt injury, a soil test or tissue test should be done to confirm the diagnosis. Submit soil samples very early in the spring before rain washes salts down into the soil and out of the sampling area. Tissue samples should be collected in midsummer and submitted for chloride analysis. Be careful to avoid contaminating the sample. Use clean plastic gloves when handling the sample or prune the leaves directly

into a clean plastic bag. Contact your county Extension office for specific instructions on soil testing and tissue testing. Preventing injury The best method for preventing salt injury to plants is to reduce the amount of salt used. Limit applications to high risk locations such as high-speed roads, intersections, hills, steps, and walkways. Avoid applying pure salt; instead, mix salt with an abrasive material such as sand, ash, or cinders. Salt mixtures are particularly appropriate on low-volume roads and when temperatures are so cold that salt is ineffective. Or, consider using one of the products listed in table 1 as an alternative to rock salt. When applying a deicer, wait until after you ve finished shoveling and plowing. If possible, wait until after the threat of more snow has passed before spreading salt. This will help reduce the movement of salt from the pavement into the landscape. However, early applications of small amounts of salt can be very effective at preventing ice from freezing to the pavement. Do not use fertilizers to deice. The large amount needed to effectively melt ice can damage adjacent plants. Anti-desiccants or anti-transpirants are not effective in reducing salt injury and, in some cases, may actually increase damage. Cultural control New plantings Planning before planting is the best way to prevent salt injury to landscape plants. When planting in areas subjected to salt spray or runoff, consider these suggestions to minimize damage. Select plants with high salt tolerance. See tables 2 and 3 for common woody landscape plants grouped by relative salt tolerance. Plant on berms to prevent salty runoff water from moving into root zones. Place plants with low salt tolerance at least 60 feet from highways and 30 feet from city streets. Existing plantings For existing plantings, the following suggestions will help reduce damage caused by salty spray and runoff water. In late fall, place barriers (such as snow fences, burlap, or plywood) around plants to reduce exposure to salt spray. Avoid shoveling piles of saltladen snow over the root zones of sensitive plants. Flush high-saline areas with water in early spring to move salt out of the plant s root zone. Alter drainage patterns to direct salty runoff water away from plants. Table 1. Alternative products for ice control Product Advantages Disadvantages Calcium chloride Effective to 59 F Costs up to 10 times more than No visible residue when dry rock salt Will not damage soil structure Injures plants Dissolves easily and acts quickly Highly corrosive Magnesium chloride Effective to 25 F Costs twice as much as rock salt Fast acting at low temperatures May cause chloride toxicity Less corrosive than calcium chloride Absorbs moisture readily; must be and sodium chloride stored in dry area Calcium magnesium Biodegradable; not harmful to the Expensive costs 30 times more than acetate (pelleted deicer made environment rock salt from dolomitic limestone and Less corrosive than sodium chloride Less effective than salt in colder acetic acid) Can increase soil permeability temperatures Abrasive materials Inexpensive Will not melt ice (sand, ash, or cinders) Not harmful to trees and shrubs Requires reapplication to maintain Works at very low temperatures effective traction where salt is ineffective Bulky; must be removed from gutters each spring

Table 2. Salt spray tolerance of common woody landscape plants High tolerance Moderate tolerance Low tolerance Ash, white (Fraxinus americana) Aspen, bigtooth (Populus grandidentata) quaking (P. tremuloides) Cottonwood, eastern (Populus deltoides) Currant, alpine (Ribes alpinum) Euonymus, winged (Euonymus alata) Honeylocust (Gleditsia triacanthos) Horsechestnut (Aesculus hippocastanum) Juniper, Chinese (Juniperus chinensis) Larch, European (Larix decidua) Lilac, Japanese (Syringa reticulata) Locust, black (Robinia pseudoacacia) Maple, Norway (Acer platanoides) silver (A. saccharinum) Mockorange (Philadelphus spp.) Mountain ash (Sorbus spp.) Mulberry (Morus spp.) Pine, Austrian (Pinus nigra) Jack (P. banksiana) mugo (P. mugo) Poplar, black (Populus nigra) silver-leaved (P. alba) Redcedar, eastern (Juniperus virginiana) Rose, rugosa (Rosa rugosa) Russian-olive (Elaeagnus angustifolia) Snowberry (Symphoricarpus albus) Spruce, Colorado (Picea pungens) Sumac, fragrant (Rhus aromatica) smooth (R. glabra) staghorn (R. typhina) Virginia creeper (Parthenocissus quinquefolia) Walnut, black (Juglans nigra) Alder, speckled (Alnus rugosa) white (A. incana) Ash, green (Fraxinus pennsylvanica) Barberry, Korean (Berberis koreana) Birch, grey (Betula populifolia) paper (B. papyrifera) sweet (B. lenta) yellow (B. alleghaniensis) Boxelder (Acer negundo) Catalpa (Catalpa speciosa) Douglasfir (Pseudotsuga menziesii) Elm, American (Ulmus americana) Siberian (U. pumila) Forsythia (Forsythia X intermedia) Honeysuckle (Lonicera tatarica) Juniper, creeping (Juniperus horizontalis) Lilac, common (Syringa vulgaris) Linden, American (Tilia americana) Maple, amur (Acer ginnala) red (A. rubrum) sugar (A. saccharum) Oak, bur (Quercus macrocarpa) English (Q. robur) Pear, ornamental (Pyrus spp.) Pine, ponderosa (Pinus ponderosa) Privet (Ligustrum vulgare) Serviceberry (Amelanchier spp.) Viburnum, American cranberrybush (Viburnum trilobum) arrowwood (V. dentatum) European cranberrybush (V. opulus) nannyberry (V. lentago) Willow, black (Salix nigra) white (S. alba) Arborvitae (Thuja occidentalis) Barberry (Berberis thunbergii) Beech, American (Fagus grandifolia) Boxwood (Buxus sempervirens) Cherry, black (Prunus serotina) sand (P. besseyi) Chokecherry (Prunus virginiana) Coralberry, indiancurrant (Symphoricarpus orbiculatus) Crabapple (Malus spp.) Dogwood (Cornus spp.) Elder, American (Sambucus canadensis) European red (S. racemosa) Euonymus, European (Euonymus europaea) Filbert (Corylus spp.) Fir, balsam (Abies balsamea) Ginkgo (Ginkgo biloba) Hackberry, common (Celtis occidentalis) Hawthorn (Crateagus spp.) Hemlock, eastern (Tsuga canadensis) Hickory, shagbark (Carya ovata) Hornbeam, American (Carpinus caroliniana) Linden, littleleaf (Tilia cordata) Oak, pin (Quercus palustris) red (Q. rubra) white (Q. alba) Pine, red (Pinus resinosa) Scots (P. sylvestris) white (P. strobus) Quince, flowering (Chaenomeles speciosa) Redbud, eastern (Cercis canadensis) Redwood, dawn (Metasequoia glyptostroboides) Rhododendron (Rhododendron) Spirea, Vanhoutte (Spiraea X vanhouttei) Spruce, Norway (Picea abies ) white (P. glauca) Tuliptree (Liriodendron tulipifera) Viburnum, wayfaringtree (Viburnum lantana) Weigela (Weigela spp.) Yews (Taxus spp.)

Table 3. Soil salt tolerance of common woody landscape plants High tolerance Moderate tolerance Low tolerance Ash, white (Fraxinus americana) Cherry, black (Prunus serotina) Chokecherry (Prunus virginiana) Currant, alpine (Ribes alpinum) Honeylocust (Gleditsia triacanthos) Horsechestnut (Aesculus hippocastanum) Juniper, Chinese (Juniperus chinensis) Locust, black (Robinia pseudoacacia) Oak, bur (Quercus macrocarpa) pin (Q. palustris) red (Q. rubra) white (Q. alba) Pine, Austrian (Pinus nigra) mugo (P. mugo) Redcedar, eastern (Juniperus virginiana) Rose, rugosa (Rosa rugosa) Russian-olive (Elaeagnus angustifolia) Arborvitae (Thuja occidentalis) Aspen, bigtooth (Populus grandidentata) quaking (P. tremuloides) Birch, grey (Betula populifolia) paper (B. papyrifera) sweet (B. lenta) yellow (B. alleghaniensis) Boxelder (Acer negundo) Cherry, sand (Pinus besseyi) Cottonwood, eastern (Populus deltoides) Crabapple (Malus spp.) Fir, balsam (Abies balsamea) Honeysuckle (Lonicera tatarica) Juniper, creeping (Juniperus horizontalis) Lilac, common (Syringa vulgaris) Japanese (S. reticulata) Maple, amur (Acer ginnala) Norway (A. platanoides) silver (A. saccharinum) Pine, ponderosa (Pinus ponderosa) Scots (P. sylvestris) Poplar, black (Populus nigra) silver-leaved (P. alba) Privet (Ligustrum vulgare) Redbud, eastern (Cercis canadensis) Viburnum, European cranberrybush (Viburnum opulus) Alder, speckled (Alnus rugosa) white (A. incana) Barberry (Berberis thunbergii) Beech, American (Fagus grandifolia) Boxwood (Buxus sempervirens) Douglasfir (Pseudotsuga menziesii) Elm, American (Ulmus americana) Siberian (U. pumila) Euonymus, European (Euonymus europaea) winged (E. alata) Filbert (Corylus spp.) Hemlock, eastern (Tsuga canadensis) Hornbeam, American (Carpinus caroliniana) Larch, European (Larix decidua) Linden, American (Tilia americana) littleleaf (T. cordata) Maple, red (Acer rubrum) sugar (A. saccharum) Pine, red (Pinus resinosa) white (P. strobus) Spirea, Vanhoutte (Spiraea X vanhouttei) Spruce, Colorado (Picea pungens) Norway (P. abies) white (P. glauca) Tuliptree (Liriodendron tulipifera) Viburnum, American cranberrybush (Viburnum trilobum) arrowwood (V. dentatum) nannyberry (V. lentago) wayfaringtree (V. lantana) Walnut, black (Juglans nigra)

Copyright 1999 by the Board of Regents of the University of Wisconsin System doing business as the division of Cooperative Extension of the University of Wisconsin-Extension. Send inquiries about copyright permission to: Manager, Cooperative Extension Publishing, 432 N. Lake St., Rm. 103, Madison, WI 53706. Authors: K.A. Delahaut is an outreach specialist in horticulture and E.R. Hasselkus is professor emeritus of horticulture, College of Agricultural and Life Sciences, University of Wisconsin-Madison and University of Wisconsin-Extension, Cooperative Extension. Produced by Cooperative Extension Publishing, University of Wisconsin-Extension. University of Wisconsin-Extension, Cooperative Extension, in cooperation with the U.S. Department of Agriculture and Wisconsin counties, publishes this information to further the purpose of the May 8 and June 30, 1914 Acts of Congress; and provides equal opportunities and affirmative action in employment and programming. If you need this material in an alternative format, contact the Office of Equal Opportunity and Diversity Programs or call Cooperative Extension Publishing at 608-262-2655. This publication is available from your Wisconsin county Extension office or from Cooperative Extension Publishing. You can print or order online at cecommerce.uwex.edu/, call 877-WIS-PUBS (947-7827), or send a fax to 414-902-2679. A2970 Salt Injury to Landscape Plants SR-09-99