Prostate gland development is a complex process that involves coordination of multiple signaling pathways including endocrine, paracrine, autocrine, juxtacrine and transcription factors. To put this into proper context, the present manuscript will begin with a brief overview of the stages of prostate development and a summary of androgenic signaling in the developing prostate, which is essential for prostate formation. This will be followed by a detailed description of other transcription factors and secreted morphogens directly involved in prostate formation and branching morphogenesis. Except where otherwise indicated, results from rodent models will be presented since studies that examine molecular signaling in the developing human prostate gland are sparse at the present time.

Brief exposure of rodents to estrogens during early development alters prostate branching morphogenesis and cellular differentiation in a dose-dependant manner. If estrogenic exposures are high, these disturbances lead to permanent imprints of the prostate, which include reduced growth, differentiation defects of the epithelial cells, altered secretory function and reduced responsiveness to androgens in adulthood. This process, referred to as neonatal imprinting or developmental estrogenization, is associated with an increased incidence of prostatic lesions with aging, which include hyperplasia, inflammation and dysplasia. To better understand how early estrogenic exposures can permanently alter prostate growth and function and predispose the gland to neoplasia, the effects of estrogens on prostatic steroid receptors, cell-cell communication molecules and key developmental genes were examined. Transient and permanent alterations in the expression of prostatic androgen receptors, estrogen receptors alpha (ERalpha) and beta, and retinoic acid receptors are observed. It is proposed that the estrogen-induced alterations in these critical transcription factors play a fundamental role in initiating prostatic growth and differentiation defects. Down-stream effects of the altered steroid receptor expression include disruption of TGFbeta paracrine communication, altered expression of gap junction connexin molecules and loss of epithelial cadherin on epithelial cells. Additionally, specific disruptions in the expression of prostatic developmental genes are observed in response to neonatal estrogen. An extended developmental period of hoxa-13 expression, a lack of hoxd-13 increase with maturation, and an immediate and sustained suppression of hoxb-13 was noted within prostatic tissue. A transient decrease in Nkx3.1 expression in the developing prostate was also observed. Thus subtle and overt alterations in Hox-13 and Nkx3.1 genes may be involved in the altered prostate phenotype in response to neonatal estrogen exposure. In summary, estrogen imprinting of the prostate gland is mediated through up-regulated levels of stromal ERalpha, which initiates alterations in steroid receptor expression within the developing gland. Rather than being an androgen-dominated process, as occurs normally, prostatic development is regulated by alternate steroids, including estrogens and retinoids, in the estrogenized animal. This, in turn, leads to disruptions in the coordinated expression of critical developmental genes including TGFbeta, Hox-13 genes and Nkx3.1. Since a precise temporal expression pattern of these and other molecules is normally required for appropriate differentiation of the prostatic epithelium and stroma, the estrogen-initiated disruption in this pattern would lead to permanent differentiation defects of the prostate gland. It is hypothesized that these molecular and cellular changes initiated early in life predispose the prostate to the neoplastic state upon aging.

Brief exposure of rats to high doses of natural estrogens early in life results in permanent alterations of the prostate gland, which include differentiation defects, altered gene expression, and dysplasia with aging. Whether low-dose treatments can cause similar effects in the developing prostate remains controversial. The current project was designed to determine the dose-response relationship of the prostate gland to estradiol exposure during the developmentally critical neonatal period in the rat. Male Sprague-Dawley (SD) rats were treated on Days 1, 3, and 5 of life by s.c. injections of a 7-log range of doses (0.015 microg/kg to 15.0 mg/kg) of beta-estradiol-3-benzoate (EB) in 25 microl of peanut oil (Arachis) as vehicle. In a separate block, neonatal Fisher 344 (F344) rats received 0.15, 15.0, or 1500.0 microg EB/kg. Rats were killed on Postnatal Day (PND) 35 or 90, and the prostates were microdissected, weighed, and frozen for immunohistochemistry. Preputial separation and hepatic testosterone hydroxlase activities were monitored and measured to determine the onset of puberty. On PND 35, there was an increase in prostate weights of SD rats treated with low doses of EB and a decrease in prostate weights of SD rats treated with high doses. The low-dose effect was entirely abolished by PND 90, and only high-dose suppression of organ sizes was found. The transient nature of the effect in low-dose animals suggests an advancement of puberty as the cause for increased reproductive organ weights on PND 35. F344 rats were more sensitive than SD rats to the suppressive effects of high doses of neonatal EB on PND 90. Despite this heightened responsiveness in the F344 rats, a low-dose estrogenic effect on adult prostate weights was not observed. Thus, in the rat model a sustained effect at low doses of natural estrogens is not present in the prostate glands.

Every community-based marine resource management (CBMRM) inherently takes place in a highly complex social-ecological environment, and stakeholder perceptions related to various aspects of the natural and social environment guide behavior in every stage of the management process. This paper provides an introduction to the psychology of perception with regard to marine resource management. In particular, it offers a typology of CBMRM relevant perceptions along with an analysis of psychological, societal, and physical factors that modulate them. Based on this analysis, we propose the introduction of specially trained local Perception Experts (PE's), whose role will be to recognize and reflect individual perceptions of involved stakeholders, and to communicate them at community meetings where decisions are made. This empirically testable addition to current CBMRM schemes could help to increase participation, develop management measures that fit the capacities of the involved stakeholders more accurately, and hence, contribute to a faster rehabilitation of marine resources.

Environmental contaminants with estrogenic properties have been cause for heightened concern about their possible role in inducing adverse health effects. Brief exposure of rodents to high doses of natural estrogens early in life results in permanent alterations of the male reproductive tissues, but the question of whether environmentally relevant doses can cause the same effects remains controversial. The current project was designed to determine the dose-response relationship between neonatal estradiol exposure and the development of the male reproductive tract in the rat. Neonatal male Sprague-Dawley (SD) and Fisher 344 (F344) rats were exposed to beta-estradiol-3-benzoate (EB) at concentrations ranging from 0.015 microg/kg body weight (BW) to 15.0 mg/kg BW and 0.15 microg/kg BW to 1.5 mg/kg BW, respectively. Results showed an inverted U-shaped dose-response profile for testis and epididymis weights in 35-day-old SD rats, with increased organ sizes at the low-dose end of the treatment. This effect was transient and was not sustained into adulthood. Increased hepatic testosterone hydroxylase activities in low-dose animals suggest an advancement of puberty as the cause for increased reproductive organ weights. On postnatal day (PND) 90, a stimulatory low-dose response to EB was present in SD rat testicular and epididymal weights, however at one order of magnitude lower dose than that seen on PND 35, suggesting a separate effect. All SD male reproductive tract organs and serum hormones showed a permanent inhibitory response to high doses of neonatal EB. F344 rats exhibited greater estrogen sensitivity on PND 90. Despite this heightened responsiveness, F344 rats did not exhibit a low-dose effect for any endpoint. These low-dose responses to estradiol are organ and strain specific.