Abstract
purpose. To investigate the effect of age on ultraviolet radiation-B (UVR-B)–induced cataract and to detect the maximum acceptable dose in rats of different age groups.
methods. Four age groups of 20 rats each, aged 3, 6, 10, and 18 weeks, were included. Each age group was divided into five UVR-B dose subgroups. The rats were unilaterally exposed to UVR-B (λmax = 302.6 nm, λ0.5 = 4.5 nm). The incident dose on the cornea varied between 0 and 8 kJ/m2. One week after exposure, the rats were killed, both lenses were extracted, the intensity of forward light-scattering was measured, and photographs were taken. The sensitivity of the lens to UVR-B was estimated as the maximum acceptable dose.
results. The maximum acceptable dose for 3-, 6-, 10-, and 18-week-old rats was estimated to be 1.4, 2.7, 4.3 and 5.2 kJ/m2, respectively.
conclusions. Young rats were more sensitive to UVR-B than old ones. Age should be considered when estimating the risk for UVR-B–induced cataract.
In the present study, the impact of age on ultraviolet radiation-B (UVR-B)–induced cataract was investigated.
Sunlight is the principal source of ultraviolet radiation (UVR) for most of the world’s population. Depletion of the stratospheric ozone increases the intensity of UVR. UVR is considered one of the major risk factors for cataract.
1 2 3 4 Several studies have shown that sunlight increases the risk for cortical cataract.
5 6 7 A correlation between cortical cataract and exposure to UVR was demonstrated in the Chesapeake Bay Study.
8
Effects of UVR may be analyzed from different perspectives (e.g., at molecular, cellular, tissue, individual, population, and ecosystem levels).
9 UVR damages the lens by disturbing cell proliferation in the lens epithelium,
10 by altering kinetic properties of enzymes in the energy metabolism,
11 by increasing insoluble and decreasing soluble protein,
12 13 by inducing unscheduled DNA synthesis,
14 and by disturbing the sodium potassium balance and thereby the water balance in the lens.
15 16
One of the major difficulties in epidemiologic studies has been quantification of exposure to UVR from the sun. In addition to intensity of sunlight, the ocular dose depends on other factors, such as the amount of time spent outdoors, the environment, the use of ocular protection, and the use of hats.
3 4 17 18 19
Ocular sensitivity versus wavelength
20 21 22 23 and exposure time
24 for UVR-induced cataract have been studied experimentally in animals. In pigmented rabbits, Pitts et al.
22 determined the threshold dose for UVR in the most toxic wavelength region, around 300 nm, to be 1.5 kJ/m
2 for transient and 5 kJ/m
2 for permanent lens damage. Deduction from animal data to the human situation is always questionable. However, it is the only option for development of empirically based safety recommendations for avoidance of cataract after exposure to UVR. With such knowledge, appropriate public health measures could be taken.
25
The public health significance of UVR-induced cataract is substantial. A possible thinning of the stratospheric ozone would probably translate into a large number of cataract cases worldwide. Safety limits for avoidance of UVR-induced cataract, established by animal models will help to develop appropriate public health measures.
Safety limits for UVR-B–induced cataract have been based on a dichotomous dose–response model, assuming that the outcome of UVR-B exposure is limited to a binary response: cataract/no cataract.
22 In those studies, cataract was measured qualitatively by slit lamp, with a grading scale. However, it has recently been shown with quantitative measurements of cataract that UVR-B–induced cataract has a continuous dose–response function.
26 For this reason, a new concept, maximum acceptable dose (MAD) for avoidance of UVR-B cataract, was developed for estimation of UVR-B toxicity in the lens
(Fig. 1) .
27
Based on the dose–response function, MAD is defined as the dose corresponding to a limit for pathologic forward light-scattering. The limit for pathologic forward light-scattering is settled arbitrarily, based on the frequency distribution of light-scattering in normal unexposed lenses. The limit is defined so that a certain fraction (α), of normal unexposed lenses scatter light in the forward direction to an intensity above the limit. The magnitude of the fraction is a parameter that has to be settled and is given as an index to MAD1−α.
The purpose of the present study was to determine the dependence of MAD on age.
In the current study, the age dependence of sensitivity of the ocular rat lens to in vivo exposure to UVR-B was determined. Sprague-Dawley rats were selected for this study because they are available at uniform size in large numbers and they provide a good model to gather primary empiric information that can serve as a basis for further studies. It should be pointed out, however, that the rat as an experimental model for damage from optical radiation has several limitations: It is nocturnal and the dimensions of the eye tissues are very different from the human. The rat eye has a thinner cornea than the human eye, and therefore, due to higher transmittance is expected to have a higher sensitivity to UVR-B. Data from more species are required before the details of the age aspect can be conclusively settled and interpreted to human exposure.
Empiric data on toxicity of UVR-B in the human lens can be derived only from in vitro experiments on isolated human lenses. In vitro experiments, however, have the drawback of the lack of co-reactivity with surrounding tissues. Therefore, it is necessary to perform in vivo experiments in animals to derive an empiric foundation for safety standards. We believe that, in general, the significance of an examined aspect of safety increases if the aspect can be demonstrated in several species. In the current study, age was an important variable for prediction of UVR-B toxicity in the rat lens after a close-to-threshold dose.
When risk is estimated for damage to the eye from optical radiation, energy application (intensity, exposure time and exposure pattern) and spectral radiance are essential. The currently accepted strategy for risk estimation is based on adding the individual spectral components of a source while weighting each spectral component with its relative biological efficiency according to the action spectrum. In the present study, we chose to use UVR-B in the 300-nm wavelength region and exposure for 15 minutes, because the lens has a maximum sensitivity in this wave band
22 23 and this exposure time.
24 However, we would like to point out that for the highest dose used in present experiment was 8 kJ/m
2, for 15 minutes exposure, the intensity was 0.9 mW/cm
2 at the corneal level. This intensity was 10 to 100 times higher than the expected irradiation of the human cornea in sunlight.
The current safety limits estimation for UVR-B–induced cataract was based on slit lamp observations and assuming a binary dose–response model.
22 MAD was introduced based on the objective observation and is based on the notion that UVR-B–induced cataract has a continuous dose–response model.
26 There are some limitations for estimation of MAD, because the mean and the SD for normal nonexposed control lenses were estimated from limited samples of contralateral nonexposed eyes (
n = 20), the probability for wrong classification of a normal lens as pathologic is in the strict statistical sense not exactly known. However, the strategy for estimation of MAD is a practical objective method for estimation of UVR-B toxicity and provides useful information on the relative toxicity for the ages measured.
In the present study, MAD
0.975 was estimated to be 2.7 kJ/m
2 in 6-week-old rats. This closely agrees to the previous estimates of MAD in 6-week-old rats.
23
The higher sensitivity to UVR-B presently found in young individuals may be due to a thinner cornea that thus transmits more UVR-B. This is supported by measurements of the transmittance of the cornea at 300 nm in mouse (81%), rat (76%), rabbit (71%), and man (63%).
31 Further, it was shown that UVR-B at 300 nm penetrates only approximately 0.5 mm in the lens (intensity = 1/e
2 of original).
32 It may be that the zone penetrated includes a biologically more important part of the young than of the old lens.
Michael et al.,
33 found that there is frequent occurrence of TUNEL-positive cells in the germinative zone after exposure to UVR-B in the 300-nm wavelength region. The high rate of cell division in the germinative zone in the young lens may render the young lens more sensitive to UVR-B–triggered DNA fragmentation. Further, the young lens requires more protein synthesis that includes a biologically more important part of the young than of the older lens.
12 34 Sidney Lerman
35 exposed young (first decade) and old (seventh decade) normal human lenses to low level (<0.1 kJ/cm
2) broad band UVR-B (300–400 nm) and found that the γ-crystallins were significantly affected by UVR-B in young lenses, whereas the aged lens proteins appeared to be relatively unaffected by this degree of UVR-B exposure.
Today, age is not considered in toxicity estimates for avoidance of cataract after exposure to UVR-B. The present finding that MAD for avoidance of UVR-B–induced cataract strongly depends on age
(Fig. 6) implicates that, in the future, age should be considered in safety estimations for avoidance of cataract from UVR-B. We also feel that until better data are available, the current data should be considered in toxicity estimates for avoidance of UVR-B cataract after exposure to the sun as well as to artificial sources.
Supported by grants from the Crown Princess Margaretas Foundation (KMA), the China Scholarship Council, and Carmen & Bertil Regners Research Foundation.
Submitted for publication June 5, 2002; revised September 9 and September 18, 2002; accepted September 23, 2002.
Disclosure:
X.
Dong, None;
M.
Ayala, None;
S.
Löfgren, None;
P.
G.
Söderberg, None
The publication costs of this article were defrayed in part by page charge payment. This article must therefore be marked “
advertisement” in accordance with 18 U.S.C. §1734 solely to indicate this fact.
Corresponding author: Xiuqin Dong, Research Department, St. Erik’s Eye Hospital, Karolinska Institutet, Polhemsgatan 50, S-112 82 Stockholm, Sweden;
[email protected].
Sliney, DH. (1983) Eye protection techniques for bright light Ophthalmology 90,937-944
[CrossRef] [PubMed]Sliney, DH. (1986) Physical factors in cataractogenesis: ambient ultraviolet radiation and temperature Invest Ophthalmol Vis Sci 27,781-790
[PubMed]Sliney, DH. (1995) UV radiation ocular exposure dosimetry J Photochem Photobiol B 31,69-77
[CrossRef] [PubMed]Rosenthal, FS, Phoon, C, Bakalian, AE. (1988) The ocular dose of ultraviolet radiation to outdoor workers Invest Ophthalmol Vis Sci 29,649-656
[PubMed]Graziosi, P, Rosmini, F, Bonacin, M, et al (1996) Location and severity of cortical opacities in different regions of the lens in age-related cataract Invest Ophthalmol Vis Sci 37,1698-1703
[PubMed]West, SK, Duncan, DD, Munoz, B, et al (1998) Sunlight exposure and risk of lens opacities in a population-based study: The Salisbury Eye Evaluation Project JAMA 280,714-718
[CrossRef] [PubMed]Schein, OD, West, S, Munoz, B, et al (1994) Cortical lenticular opacification: distribution and location in a longitudinal study Invest Ophthalmol Vis Sci 35,363-366
[PubMed]Taylor, HR, West, SK, Rosenthal, FS, et al (1988) Effect of ultraviolet radiation on cataract formation N Engl J Med 319,1429-1433
[CrossRef] [PubMed]Meyer-Rochow, VB. (2000) Risks, especially for the eye, emanating from the rise of solar UV-radiation in the Arctic and Antarctic regions Int J Circumpol Health 59,38-51
Li, WC, Spector, A. (1996) Lens epithelial cell apoptosis is an early event in the development of UVB-induced cataract Free Radic Biol Med 20,301-311
[CrossRef] [PubMed]Andley, UP, Song, Z, Mitchell, DL. (1999) DNA repair and survival in human lens epithelial cells with extended lifespan Curr Eye Res 18,224-230
[CrossRef] [PubMed]Zigman, S, Griess, G, Yulo, T, Schultz, J. (1973) Ocular protein alterations by near UV light Exp Eye Res 15,255-264
[CrossRef] [PubMed]Zigman, S, Schultz, J, Yulo, T. (1973) Possible roles of near UV light in the cataractous process Exp Eye Res 15,201-208
[CrossRef] [PubMed]Söderberg, PG, Philipson, BT, Lindstrm, B. (1986) Unscheduled DNA synthesis in lens epithelium after in vivo exposure to UV radiation in the 300 nm wavelength region. Acta Ophthalmol (Copenh). 64,162-168
[PubMed]Söderberg, PG. (1991) Na and K in the lens after exposure to radiation in the 300 nm wave length region J Photochem Photobiol B 8,279-294
[CrossRef] [PubMed]Söderberg, PG, Chen, E. (1989) Determination of Na and K in the rat lens by atomic absorption spectrophotometry. Acta Ophthalmol (Copenh). 67,582-592
[PubMed]Sliney, DH. (1994) UV radiation ocular exposure dosimetry [review] Doc Ophthalmol 3–4,243-254
Pitts, DG. (1973) The ocular ultraviolet action spectrum and protection criteria Health Phys 25,559-566
[CrossRef] [PubMed]Rosenthal, FS, Safran, M, Taylor, HR. (1985) The ocular dose of ultraviolet radiation from sunlight exposure Photochem Photobiol 42,163-171
[CrossRef] [PubMed]Verhoeff, FH, Bell, L, Walker, CB. (1915/16) The pathological effects of radiant energy upon the eye. Proc Am Acad Art Sci USA. 51,629-818
Bachem, A. (1956) Ophthalmic ultraviolet action spectra Am J Ophthalmol 41,969-975
[CrossRef] [PubMed]Pitts, DG, Cullen, AP, Hacker, PD. (1977) Ocular effects of ultraviolet radiation from 295 to 365 nm Invest Ophthalmol Vis Sci 16,932-939
[PubMed]Merriam, J, Lofgren, S, Michael, R, et al (2000) An Action Spectrum for UV-B Radiation and the Rat Lens Invest Ophthalmol Vis Sci 41,2642-2647
[PubMed]Ayala, MN, Michael, R, Söderberg, PG. (2000) Influence of exposure time for UV radiation-induced cataract Invest Ophthalmol Vis Sci 41,3539-3543
[PubMed]McCarty, CA, Taylor, HR. (1996) Recent developments in vision research: light damage in cataract Invest Ophthalmol Vis Sci 37,1720-1723
[PubMed]Michael, R, Söderberg, PG, Chen, E. (1998) Dose-response function for lens forward light scattering after in vivo exposure to ultraviolet radiation Graefes Arch Clin Exp Ophthalmol 236,625-629
[CrossRef] [PubMed]Michael, R. (2000) Development and repair of cataract induced by ultraviolet radiation Ophthalmic Res 32(suppl 1),1-44
[PubMed]Söderberg, PG. (1990) Experimental cataract induced by ultraviolet radiation. Acta Ophthalmol (Copenh). 68,1-77
Söderberg, PG, Chen, E. (1990) An objective and rapid method for the determination of light dissemination in the lens. Acta Ophthalmol (Copenh). 68,44-52
[PubMed]Wixson, SK, White, WJ, Hughes, HC. (1987) A comparison of pentobarbital, fentanyl-droperidol, ketamine-diazepam anesthesia in adult male rats Lab Anim Sci 37,726-730
[PubMed]Dillon, J, Zheng, L, Merriam, JC, Gaillard, ER. (1999) The optical properties of the anterior segment of the eye: implications for cortical cataract Exp Eye Res 68,785-795
[CrossRef] [PubMed]Löfgren, S. (2001) Lens lactate dehydrogenase inactivation after UV-B irradiation: an in vivo measure of UVR-B penetration Invest Ophthalmol Vis Sci 42,1833-1836
[PubMed]Michael, R, Vrensen, G, van Marle, J. (1998) Gan L, Söderberg PG Apoptosis in the rat lens after in vivo threshold dose ultraviolet irradiation. Invest Ophthalmol Vis Sci. 13,2681-2687
Zigman, S, Yulo, T, Schultz, J. (1974) Cataract induction in mice exposed to near UV light Ophthalmic Res 6,259-270
[CrossRef] Lerman, S, Megaw, JM, Moran, MN. (1985) Further studies of UV radiation on the human lens Ophthalmic Res 17,354-364
[CrossRef] [PubMed]