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What these papers say about Lake Tahoe’s cables

The strongest findings across the Bell System Technical Journal papers in this collection, grouped by topic. Each paper’s page has its full list in a “Relevance to Lake Tahoe’s cables” box.

Each finding states only what the paper says, in its own words, with page references. The Lake Tahoe side uses only facts already published on this site:

  • the Bell System laid lead-sheathed telephone cables through the southwest corner of the lake;
  • they lay under the 1955 lakebed lease between Rubicon Bay and Baldwin Beach;
  • they had not been used since the 1980s and rested in the lake for over 70 years;
  • the water section was removed in November 2024, and the Baldwin Beach sand and Tallac Creek section in September 2025.

Coverage. 23 findings across 9 papers:

Paper Findings
Burns 1936 6
Buckley 1942 4
Gilbert 1951 3
Shaw & Fondiller 1926 3
Affel 1932 2
Hitchcock 1926 1
Buckley 1928 1
Buckley 1925 0
Blackwell 1932 0

Burns is the only paper about lead’s behaviour. The others mention lead as a material in passing, and two of them have nothing relevant.

The strongest 10

Why lead was used

1. Lead was chosen for extrusion first and corrosion resistance second.

While the choice of lead as a cable sheathing material was dictated primarily by physical requirements, notably its adaptability to extrusion, corrosion resistance has been a large factor undoubtedly in its successful use.

These are the Bell System’s own reasons for the construction later found in Lake Tahoe.

Presence of lead

2. Lead sheathing was standard for Bell telephone cable from the 1880s to at least 1950.

In the Bell System alone there are about 180,000 miles of lead alloy covered cables, about forty per cent of which are underground.

The underground cables have the same coaxial circuit as the submarine cables but in place of the mechanical protection of jute and armor they are provided with electrical protection of helical steel tapes, layers of paper and over all a lead sheath.

This places the Tahoe cables in the Bell System’s mainstream construction of the period. The 1955 lease comes a few years after Gilbert.

3. On the ocean routes in these papers, lead sits at the shore and on land, not on the deep-sea cable.

  • Catalina, 1926: the land link is “a special lead-covered cable” (Hitchcock 1926, p. 637), and the submarine cables are described only as “of the single-conductor, deep-sea type”.
  • Key West–Havana, 1930: lead covering appears only on 0.40 n.m. of shore-end cable (Table III, “l.c. = lead covered.”, Affel 1932, p. 202) and on the underground link (p. 205). The deep-sea waterproofing was the insulation:

Heretofore submarine cables having waterproof insulation, with the exception of the Catalina Island cables which are insulated with a special rubber mixture, have almost invariably been insulated with gutta percha, or balata, or a mixture of these substances.

The one paper that pairs lead-covered cable with shallow submerged routes is Buckley (1942, p. 16): “the repeater can be incorporated in lead-covered cables for shallow seas”. So the ocean cables are not direct analogues of a lead-sheathed lake-bed cable.

Known issues

4. Lead buried directly in soil corrodes seriously, and the soil matters more than the alloy.

Cable sheathing buried directly in soils is seriously corroded by differential aeration-cell action resulting from physical contact of relatively large soil particles and metal.

It will be seen that of the two variables, soil character and alloy composition, the former is decidedly the more important in its effect upon rate of corrosion.

The Bell System’s own practice was not to bury lead-covered cable without a protective coating (p. 607). This is relevant to the Baldwin Beach section under the sand. Burns describes buried cable in general, not that section’s condition.

Water exposure (cuts both ways)

5. Lead corrodes in soft, low-mineral water; dissolved minerals protect it.

It is well known that lead is markedly corroded in distilled water, and by waters low in hardness and in total solids.

Burns makes water chemistry the deciding factor. This set contains no data on Lake Tahoe’s water.

6. Experience with cables submerged in sea water was favourable.

The favorable experience with cables submerged in sea water or mixtures of sea water and soil waters indicates that corrosion inhibitive agents exert under these exposures a predominating influence.

Burns reports this for sea water and soil waters only, and has nothing on lakes. Neither #5 nor #6 transfers to Tahoe without other evidence.

Lifespan and maintenance (cuts both ways)

7. A protective film can preserve lead indefinitely, but only if the environment allows it to form and it is left undisturbed.

Once a protective film has formed on lead the metal may be preserved indefinitely if not physically disturbed.

Whether or not a protective film forms depends largely upon the character of the environment to which the metal is exposed.

8. Corrosion was rare because the plant was actively maintained.

From the description of the occurrence and general characteristics of cable sheath corrosion in the present paper it may be concluded that although there are many conditions under which cables may corrode, the actual incidence of corrosion is small owing to the maintenance of non-corrosive chemical and electrical environments in the cable plant.

Burns also credits “the vigilance of the electrolysis engineers and the plant forces” (Burns 1936, p. 603).

9. Design lives of 10–20 years are for repeater tubes and components, not cable sheaths.

  • Gilbert (1951, p. 65): the repeaters “over an extended period of perhaps twenty years, should not require servicing”.
  • Buckley (1942, p. 13): tube life “of at least ten years”; twenty years could not yet be “confidently predicted”.

Neither paper gives a service life for a cable sheath.

Removal or abandonment

10. The papers are silent on retired cable. The only removal passage concerns loading coils on overhead lines, taken out so the lines could be reused:

These general transmission considerations are resulting in the removal of coil loading from high grade open wire lines.

Gilbert (1951, p. 68) explains why lifting submerged cable is avoided: it is “expensive and time consuming”, and it disturbs the cable. That describes deep-sea repair, not removal.

What these papers do not say

  • Nothing about lakes, fresh-water lake beds or Lake Tahoe.
  • Nothing about cable left in place after retirement, or about its removal.
  • No sheath alloy for any cable resembling Tahoe’s. Burns gives the Bell standard (97/3 lead-tin to 1912, then 1% antimony; p. 604), but nothing ties a particular alloy to the Tahoe cables.
  • No measurements of lead released into water from a sheath. Burns’s water data are weight-loss tests on lead specimens (e.g. Fig. 2, p. 616), not concentrations in a lake.

Thank you

This incredible outcome was delivered by a broad range of stakeholders coming together. We’re grateful to AT&T, their 3rd party partners, the 7 government agencies that authorized removal activities, all our petition signers, and the broader Lake Tahoe community. We got the lead out!

Questions? info@tahoelead.com

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Opening frame of the Imagine5 film about the Tahoe Lead Removal Project

Film by Imagine5