The High Cost of Urban Monocultures

Tree species diversity is a critical element of ecology sustainability, the most urgent of which is to minimize the impact of pests and disease outbreaks on urban canopy cover.

Anyone who has followed the introduction of Dutch Elm disease (DED) is already painfully aware of how devastating tree pest outbreaks can be. Where I live, in Minneapolis, MN, Dutch Elm disease dramatically impacted canopy cover in the 1970’s and 80’s. Prior to DED, Minneapolis was estimated to have between 200,000 and 600,000 Elms; there are now about 35,000 (that’s just 5 to 17 percent of the original population).The infestation left streets decimated. The cost of the outbreak wasn’t just the destruction of a nice, leafy view, either. Tree and stump removal, trimming, insect and disease control, inspection, and replanting as a result of DED amounted to $8 million in 1978 in Minneapolis alone, and more than $5 million dollars annually for the next nine years.

The single “benefit” of planting a monoculture – those “clean and simple” lines beloved by so many landscape architects that leave me cold – can never outweigh the costs.

Too Much of a Good Thing

Because they are very tough and can grow in difficult conditions, most U.S. cities spent the last 70 years planting American Elms and American Green Ash and unintentionally testing the notion that they are the optimal urban tree types. Two small insects, each less than .25” long – the Elm Bark Beetle and the Emerald Ash Borer – proved that toughness is not enough to save a monoculture. To date, we have lost over 90 percent of these very tough Elm and Ash city trees, and the canopy cover and ecosystem services of hundreds of communities have been left in shreds. If we plant only one type of tree in one place, hundreds of thousands of times, at some point in the not distant future they will be attacked by a pest or a disease that kills almost all of them. It doesn’t matter how tough the tree is.

A fact of modern development is that most trees planted in U.S. cities in the last 70 years that are not planted in parks, botanic gardens, arboreta, or private gardens have died prematurely. What other field of human endeavor in America has failed so spectacularly? Nuclear propulsion? No, nuclear power has powered U.S. Navy submarines and aircraft carriers for hundreds of millions of miles for the last 60 years (that’s over 5,000 reactor years) without a single incident. By this logic tree planting, which is widely agreed to be easy to do, has a much worse record of success than harnessing nuclear propulsion, which is widely agreed to be hard to do. I find this outrageous.

The High Cost of the Status Quo

As trees provide a wide range of ecological, social, and economic benefits, a sudden and large decrease in tree canopy cover has far reaching effects. One such effect is a dramatic reduction in stormwater volume and water quality benefits, which subsequently impact receiving water bodies. It is therefore not surprising that the 1970’s outbreak of Dutch Elm Disease in Minneapolis correlated with declining water quality in our Chain of Lakes. After canopy cover decreased across 15 square miles of Minneapolis over 20 years following the this outbreak, water quality also significantly declined in Minneapolis’ signature amenity. It took tens of millions of dollars to turn the water quality clock back to 1970, pre-DED.

Aside from the high direct costs, many indirect impacts result from water quality problems. For example, several studies found that real estate values go down as lake water quality decreases. Krysel et al (2003) studied the correlation between water clarity and lakeshore properties, using water clarity as a proxy for water quality. They found that water clarity positively affected prices paid for lakeshore properties located on Minnesota Lakes within the Mississippi Headwaters Board jurisdiction. Their results showed that if lakes experienced a one meter change in water clarity, the “expected property price changes for these lakes are in the magnitude of tens of thousands to millions of dollars.” The change in lakeshore property prices for a one meter change in water clarity varied from lake to lake. Other researchers also found correlations between water quality in Wisconsin (David 1968 in Krysel et al 2003), southeast Michigan (Brashares 1985 in Krysel et al 2003), and Maine (Boyle et al 1998 in Krysel et al 2003).

FX Elm_Sarah

If Minneapolis’ 1970’s urban forest had been more diverse, canopy cover would not have changed as dramatically due to DED. How would the costs that resulted from the water quality decline in Minneapolis’ Chain of Lakes and large scale elm removals compare with the costs of maintaining tree species diversity targets?

Today, we’re asking the same question about Emerald Ash Borer (EAB). How can we protect the Chain of Lakes, Minneapolis’ crown jewel, from future impacts of massive loss of tree canopy? Minneapolis currently has about 240,000 total ash trees: more than 30,000 are planted in streets, approximately 10,000 are planted on park properties, and an estimated 200,000 are planted on private property (Minneapolis Park and Recreation Board, 2014) In the words of the Minneapolis Park and Recreation Board, “Whether on public or private land, all ash trees are destined for infestation by EAB.” The number of ash trees that will be lost in Minneapolis due to EAB could therefore very likely be as great as the number of elms lost in the 1970’s and 1980’s.

Minneapolis is far from the only city prone to drastic negative environmental and economic impacts from tree pests and diseases. Rauch et al (2006) analyzed tree canopies in 12 cities in Eastern North America and found “an overabundance of Acer and Fraxinus,” both of which are susceptible to Asian longhorned beetle and EAB, respectively. They further report that “The most common genus of street tree was Acer. Maples were found in all cities where they comprised from 15% to 57% of the street trees. The next most common genera were Fraxinus and Quercus… In several of the cities surveyed, more than 50% of the street trees could be lost or require protection if these pest become widespread” (emphasis added). The ecological and financial impacts of these pests are enormous. Potential costs associated with removals of urban ash trees alone in the U.S., for example, are estimated at $20 billion to $60 billion, not including replacement costs (Cappaert et al 2005 in Rauch et al 2006). How far would $20 billion to $60 billion dollars go to increase diversity to reduce such catastrophic tree pest outbreaks? How about an order of magnitude less: $2 to $6 billion?

Where do we go from here?

Urban foresters recommend setting tree diversity targets to minimize the drastic effects of tree pest and disease outbreaks. For example, the “5-10-20” rule recommends a species, genus, family ratio of no more than 5 percent of one species, no more than 10 percent of one genus, and no more than 20 percent of one family for an urban forest. However, not many species can thrive in the limited soil volume provided in a typical urban growing condition, so the level of diversity of healthy urban trees that can realistically be achieved in urban conditions is extremely limited.

The most significant problem urban trees face is the inadequate volume of soil useable for root growth. Research has shown that trees need approximately two cubic feet of soil volume for every one square foot of canopy area (e.g. Lindsey and Bassuk 1991). Most urban trees, confined to a 4’ x 4’ x 4’ tree pit hole, have less than one tenth of the rooting volume they need to grow large. Improving growing conditions in urban areas is essential for enabling a more diverse array of species to thrive in urban conditions. Techniques to provide rootable soil volume under paved surfaces make it possible for underground urban space that is currently used only for utility chases to also be used to grow larger and more diverse trees.

The public urban forest in the U.S. has been broken since 1945, when the advent of new mechanized equipment enabled rapid, severe soil compaction. The solution offered to fix this has always been to increase the number of city trees planted with no regard to changing the planting conditions (also called making the place right for the tree), the soil type, or the tree species being planted. Massive public tree-planting programs designed to address this problem have been repeated over and over again, mostly with massive failures. My point is this: biodiversity not just a shopping list of species. It’s providing adequate soil volume and soil quality so that we can plant a diverse urban forest that is ecologically robust and that can thrive for decades.

This is part two in a series about species diversity in the urban forest. Read part one here.

 

References:

Brashares, Edith Nevins. “Estimating the Instream Value of Lake Water Quality in Southeast Michigan.” Diss. University of Michigan, (1985).

Boyle, Kevin J., Steven R. Lawson, Holly J. Michael, and Roy Bouchard. (1998) “Lakefront Property Owners’ Economic Demand for Water Clarity in Maine Lakes.” Maine Agriculture and Forest Experiment Station Miscellaneous Report 410. University of Maine.

David, Elizabeth L. (1968) “Lakeshore Property Values: A Guide to Public Investment in Recreation.” Water Resources Research 4.4 : 697-707.

Krysel, Charles, Elizabeth Marsh Boyer, Charles Parson, and Patrick Welle. (2003). “Lakeshore

Property Values & Water Quality: Evidence from Property Sales in the Mississippi Head-waters Region.” Mississippi Headwaters Board.

Lindsey, P; Bassuk, N. (1991). “Specifying Soil Volumes to Meet the Water Needs of Mature Urban Street Trees and Trees in Containers.”  J. Arboriculture. 17(6), 141-149.

Minneapolis Park and Recreation Board. Ash Canopy Replacement Plan: Frequently Asked Questions . Viewed 05/15/2014 from http://www.minneapolisparks.org/documents/caring/EAB_Fact_Sheet.pdf

Cappaert, D., D.C. McCullough, T.M. Poland, and N.W. Siegert. (2005). Emerald ash borer in North America: A research and regulatory challenge. American Entomologist 51:152–165.

Raupp, Michael J., Anne Buckelew Cumming, and Erin C. Raupp. (2006). Street Tree Diversity in Eastern North America and Its Potential for Tree Loss to Exotic Borers. Arboriculture & Urban Forestry 32(6):297–304.

Shiffer, James Eli. “Dutch elm disease toll slowed from peak years.” Minneapolis Star Tribune. (July 28, 2012).

Skiera, B.; Moll, G. (1992). The Sad State of City Trees. Am. Forests. March/April, 61-64.

 

Beverly LibraryCC BY-NC-SA 2.0

SarahCC BY-NC-SA 2.0

 

3 comments

  1. Great article! Dutch elm is seen far to often here also. I live in the northeast and it seems that’s whats in 80% of the older neighborhoods.

Leave a Reply

Your email address will not be published. Required fields are marked *