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Lachninae : Eulachnini : Cinara pilicornis


Identification & Distribution:

Apterae of Cinara pilicornis come in two colour forms. The commonest form is a plain orange brown, but some are a greyish green (see section below for colour forms). The whole aphid is clothed with numerous fine hairs and is more or less covered with a dense mealy secretion. The legs are yellowish but the distal half of the hind femur is darker. The hind tibiae are pale, or at least paler basally and medially than at apex. Most of hairs on the outer side of the middle section of the hind tibia exceed 0.12 mm in length (cf. Cinara piceicola which has the hairs on the outer side of the hind tibiae all less than 0.12 mm long). The second hind tarsal segment is sickle shaped and longer than the maximum diameter of the siphuncular cones (cf. Cinara costata and Cinara pruinosa which have the second tarsal segment shorter than the maximum diameter of the cones). The siphunculi are small and pale brownish. Body length of the adult Cinara pilicornis aptera is 2.1-4.7 mm.

The Cinara pilicornis alate (see above, second) is greyish-brown with transverse waxy bars and little sclerotization. The apterous males are green with an elongate flattened body.

The spruce shoot aphid may be found on the young growth of many different spruce species including Norwegian spruce (Picea abies) and Sitka spruce (Picea sitchensis). It may also colonise western hemlock (Tsuga heterophylla). Cinara pilicornis is found throughout Europe through to China and Japan and it has been introduced to Australia, New Zealand, North and South America.


Biology & Ecology

Life cycle

Cinara pilicornis lays its eggs in autumn on current year needles. The eggs begin hatching early the next March before bud burst. Initially small colonies develop on undersides of the previous year's twigs, but these move on to new growth after bud-burst as shown below. The nymphs are very cryptic and can be difficult to spot amongst the young needles.


By the second and third instar the mealy covering becomes more apparent (see picture below). The species is usually not ant attended.

The young aphids develop into apterous fundatrices (see first picture below) which are larger and somewhat darker than their eventual offspring.

There are then a series of parthenogenetic generations with both wingless (see picture below) and winged viviparae.

The proportion of winged viviparae in Cinara pilicornis is higher than in any other Cinara species. Numerous alatae are produced in May-July (see picture below).

Oviparae and males are produced in early August-November.


Cinara pilicornis has two colour forms - orange brown or greyish green. An apterous adult of the orange-brown form is pictured below, together with immatures of the green form (or possibly green males).

Image copyright Sandy Rae, all rights reserved

Population dynamics

In Britain Carter & Maslen (1982) report that in some years Cinara pilicornis is extremely abundant among young spruce plantations. They also comment that it was far less common in the 1950s and 1960s than it was in the 1980's. Our own impression is that it is now less common than at the time Carter & Maslen were writing, possibly because of a decline in the planting of spruce.

Parry (1979) looked at factors affecting the low temperature survival of the eggs on Sitka spruce. Glycerol and mannitol were present in the eggs but neither appeared to be related to their supercooling ability which was related to the temperature in the period preceding collection.

Various predators have been recorded attacking the spruce shoot aphid. Kula (1982) found the larvae of fifteen different species of Syrphidae in colonies of Cinara pilicornis. The most abundant species was Episyrphus balteatus, the larva of which is pictured below on Picea.


The spruce shoot aphid has been found to be common in polluted areas. Holopainen (1991) looked at the effect of high levels of pollution on the spruce shoot aphid. Under experimental conditions aphid populations were found to be higher on seedlings exposed to pollutants (gaseous sulphur dioxide, sodium fluoride, calcium nitrate and ammonium sulphate) than on those not exposed. Fluoride had a stronger positive effect on aphid numbers than sulphur dioxide or nitrogen.

Stadler (1997) studied the egg distribution and survival of Cinara pilicornis on damaged and undamaged Norway spruce (Picea abies). Host trees showing either heavy symptoms of needle-yellowing or looking green and healthy were compared. Host plant quality did not seem to influence the proportion of eggs surviving to spring. Also, the biomass of developing first instar larvae of the fundatrices was independent of the degree of needle-yellowing. Damaged or stressed trees did not seem to be better hosts for Cinara pilicornis.


Other aphids on same host:

Cinara pilicornis has been recorded on 16 Picea species, but only 1 Tsuga species (Tsuga heterophylla, from which 4 aphids are known worldwide: Adelges tsugae, Cinara pilicornis, Cinara tsugae, Illinoia patriciae).

Blackman & Eastop list about 170 species of aphids as feeding on spruces (Picea) worldwide, and provide formal identification keys.


Damage and control

Cinara pilicornis provides an important source of honeydew for bee populations. Hence bee keepers view this aphid very favourably, although it can damage young trees. Moulds growing on honey dew may stain shoots black. There is some evidence that the aphid can cause the current year's needles to turn yellow and fall from the lower side of the shoots that have supported colonies.


We especially thank Sandy Rae for some of the images on this page, the UK Forestry Commission, Bedgebury Pinetum, for their kind assistance, and King John's Nursery, East Sussex, for permission to sample.

Whilst we make every effort to ensure that identifications are correct, we cannot absolutely warranty their accuracy. We have mostly made identifications from high resolution photos of living specimens, along with host plant identity. In the great majority of cases, identifications have been confirmed by microscopic examination of preserved specimens. We have used the keys and species accounts of Blackman & Eastop (1994) and Blackman & Eastop (2006) supplemented with Blackman (1974), Stroyan (1977), Stroyan (1984), Blackman & Eastop (1984), Heie (1980-1995), Dixon & Thieme (2007) and Blackman (2010). We fully acknowledge these authors as the source for the (summarized) taxonomic information we have presented. Any errors in identification or information are ours alone, and we would be very grateful for any corrections. For assistance on the terms used for aphid morphology we suggest the figure provided by Blackman & Eastop (2006).

Useful weblinks


  •  Carter, C.R. & Maslen, N.R. (1982). Conifer Lachnids. Forestry Commission Bulletin No. 58, 75pp.

  •  Holopainen, J.K. (1991). Effect of exposure to fluoride, nitrogen compounds and SO2 on the numbers of spruce shoot aphids on Norway spruce seedlings. Oecologia, 86 (1), 51-56. Abstract

  •  Kula, E. (1982). The syrphid flies of spruce forest. Folia Facultatis Scientarum Naturalium Universitatis Purkynianae Brunensis, Biologia, 23 (7), 61-64. Abstract

  •  Parry, W.H. (1979). Factors affecting low temperature survival of Cinara pilicornis eggs on Sitka spruce. International Journal of Biometeorology 23 (3), 185-193. Abstract

  •  Stadler, B (1997). Egg distribution and survival of Cinara pilicornis (Hartig) on damaged and undamaged Norway spruce (Picea abies) (L.) Karst., Journal of Applied Entomology, 121, 71-75.  Abstract